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-Project Gutenberg's Sewerage and Sewage Treatment, by Harold Eaton Babbitt
-
-This eBook is for the use of anyone anywhere in the United States and
-most other parts of the world at no cost and with almost no restrictions
-whatsoever. You may copy it, give it away or re-use it under the terms
-of the Project Gutenberg License included with this eBook or online at
-www.gutenberg.org. If you are not located in the United States, you'll
-have to check the laws of the country where you are located before using
-this ebook.
-
-
-
-Title: Sewerage and Sewage Treatment
-
-Author: Harold Eaton Babbitt
-
-Release Date: April 7, 2020 [EBook #61773]
-
-Language: English
-
-Character set encoding: UTF-8
-
-*** START OF THIS PROJECT GUTENBERG EBOOK SEWERAGE AND SEWAGE TREATMENT ***
-
-
-
-
-Produced by Richard Tonsing and the Online Distributed
-Proofreading Team at https://www.pgdp.net (This file was
-produced from images generously made available by The
-Internet Archive)
-
-
-
-
-
-
-[Illustration:
-
- FIG. 1.—Construction of Peck’s Run Sewer, Baltimore, Maryland.
-
- _Frontispiece._
-]
-
-
-
-
- SEWERAGE
- AND
- SEWAGE TREATMENT
-
- BY
-
- HAROLD E. BABBITT, M.S.
-
- _Assistant Professor, Municipal and Sanitary Engineering, University of
- Illinois; Associate Member American Society of Civil Engineers_
-
-
- NEW YORK
- JOHN WILEY & SONS, INC.
- LONDON: CHAPMAN & HALL, LIMITED
- 1922
-
-
-
-
- Copyright, 1922, by
- HAROLD E. BABBITT, M.S.
-
-
- PRESS OF
- BRAUNWORTH & CO.
- BOOK MANUFACTURERS
- BROOKLYN, N. Y.
-
-------------------------------------------------------------------------
-
-
-
-
- PREFACE
-
-
-This book is a development of class-room and lecture notes prepared by
-the author for use in his classes at the University of Illinois. He has
-found such notes necessary, since among the many books dealing with
-sewerage and sewage treatment he has found none suitable as a text-book
-designed to cover the entire subject. The need for a single book of the
-character described has been expressed by engineers in practice, and by
-students and teachers for use in the class-room. This book has been
-prepared to meet both these needs. It is hoped that the searching
-questions propounded by students in using the original notes, and the
-suggestions and criticisms of engineers and teachers who have read the
-manuscript, have resulted in a text which can be readily understood.
-
-The ground covered includes an exposition of the principles and methods
-for the designing, construction and maintenance of sewerage works, and
-also of the treatment of sewage. In covering so wide a field the author
-has deemed it necessary to include some chapters which might equally
-well appear in works on other branches of engineering, such as the
-chapter on Pumps and Pumping Stations. Special stress has been laid on
-the fundamentals of the subject rather than the details of practice,
-although illustrations have been drawn freely from practical work. The
-quotation of expert opinions which may be in controversy, or the
-citation of examples of different methods of accomplishing the same
-thing, has been avoided when possible in order to simplify explanations
-and to avoid confusing the beginner.
-
-The work is to some extent a compilation of notes and quotations which
-have been collected by the author during years of study and teaching the
-subject. Credit has been given wherever due, and at the same time
-references have pointed out the original sources whenever possible.
-These references, which have been supplemented by brief bibliographies
-at the end of certain chapters, will be useful to the student and
-engineer interested in further study. Occasionally the original
-reference has been lost or the phraseology of a quotation has been so
-altered by class-room use, as to make it impossible to trace the
-original source, so that in some few instances full credit may be
-lacking.
-
-The author is indebted to many of his friends for their criticisms and
-suggestions in the preparation of the manuscript; but he desires
-particularly to acknowledge the assistance of Professor A. N. Talbot,
-Professor of Municipal and Sanitary Engineering at the University of
-Illinois, and of Professor M. L. Enger, Professor of Mechanics and
-Hydraulics at the University of Illinois, in the entire work; also that
-of Mr. T. D. Pitts, Principal Assistant Engineer of the Baltimore
-Sewerage Commission during the construction of the Baltimore sewers, for
-his suggestions on the first half of the book; and to Mr. Paul Hansen,
-consulting engineer, of Chicago, and to Mr. Langdon Pearse, Sanitary
-Engineer of the Sanitary District of Chicago, for their help on the
-section covering the treatment of sewage; and to Professor Edward
-Bartow, Professor of Chemistry at the University of Iowa, for his review
-of the chapter on Activated Sludge; in general his thanks are due to all
-others who have furnished suggestions, illustrations, or quotations,
-acknowledgments of which have been included in the text.
-
- H. E. B.
-
- URBANA, ILLINOIS, 1922.
-
-
-
-
- TABLE OF CONTENTS
-
-
- CHAPTER I
-
- INTRODUCTION
-
- PAGES
- 1. Sewerage and the Sanitary Engineer. 2. Historical. 3.
- Methods of Collection. 4. Methods of Disposal. 5. Methods of
- Treatment. 6. Definitions. 1–8
-
-
- CHAPTER II
-
- WORK PRELIMINARY TO DESIGN
-
- 7. Division of Work. 8. Preliminary. 9. Estimate of cost.
- METHODS OF FINANCING. 10. Bond Issues. 11. Special
- Assessment. 12. General Taxation. 13. Private Capital.
- PRELIMINARY WORK. 14. Preparing for Design. 15. Underground
- Surveys. 16. Borings. 9–23
-
-
- CHAPTER III
-
- QUANTITY OF SEWAGE
-
- 17. Dry Weather Flow. 18. Methods for Predicting Population.
- 19. Extent of Prediction. 20. Sources of Information on
- Population. 21. Density of Population. 22. Changes in Area.
- 23. Relation between Population and Sewage Flow. 24.
- Character of District. 25. Fluctuations in Rate of Sewage
- Flow. 26. Effect of Ground Water. 27. Résumé of Method for
- Determination of Quantity of Dry weather Sewage. QUANTITY OF
- STORM WATER. 28. The Rational Method. 29. Rate of Rainfall.
- 30. Time of Concentration. 31. Character of Surface. 32.
- Empirical Formulas. 33. Extent and Intensity of Storms. 24–50
-
-
- CHAPTER IV
-
- HYDRAULICS OF SEWERS
-
- 34. Principles. 35. Formulas. 36. Solution of Formulas. 37. Use
- of Diagrams. 38. Flow in Circular Pipes Partly Full. 39.
- Sections Other than Circular. 40. Non-Uniform Flow. 51–77
-
-
- CHAPTER V
-
- DESIGN OF SEWERAGE SYSTEMS
-
- 41. The Plan. 42. Preliminary Map. 43. Layout of the Separate
- System. 44. Location and Numbering of Manholes. 45. Drainage
- Areas. 46. Quantity of Sewage. 47. Surface Profile. 48. Slope
- and Diameter of Sewers. 49. The Sewer Profile. DESIGN OF A
- STORM-WATER SEWER SYSTEM. 50. Planning the System. 51.
- Location of Street Inlets. 52. Drainage Areas. 53.
- Computation of Flood Flow by McMath Formula. 54. Computation
- of Flood Flow by Rational Method. 78–98
-
-
- CHAPTER VI
-
- APPURTENANCES
-
- 55. General. 56. Manholes. 57. Lampholes. 58. Street Inlets.
- 59. Catch-basins. 60. Grease Traps. 61. Flush-tanks. 62.
- Siphons. 63. Regulators. 64. Junctions. 65. Outlets. 66.
- Foundations. 67. Underdrains. 99–126
-
-
- CHAPTER VII
-
- PUMPS AND PUMPING STATIONS
-
- 68. Need. 69. Reliability. 70. Equipment. 71. The Building. 72.
- Capacity of Pumps. 73. Capacity of Receiving Well. 74. Types
- of Pumping Machinery. 75. Sizes and Descriptions of Pumps.
- 76. Definitions of Duties and Efficiency. 77. Details of
- Centrifugal Pumps. 78. Centrifugal Pump Characteristics. 79.
- Setting of Centrifugal Pumps. 80. Steam Pumps and Pumping
- Engines. 81. Steam Turbines. 82. Steam Boilers. 83. Air
- Ejectors. 84. Electric Motors. 85. Internal Combustion
- Engines. 86. Selection of Pumping Machinery. 87. Costs of
- Pumping Machinery. 88. Cost Comparisons of Different Designs.
- 89. Number and Capacity of Pumping Units. 127–163
-
-
- CHAPTER VIII
-
- MATERIALS FOR SEWERS
-
- 90. Materials. 91. Vitrified Clay Pipe. 92. Cement and Concrete
- Pipe. 93. Proportioning of Concrete. 94. Waterproofing of
- Concrete. 95. Mixing and Placing Concrete. 96. Sewer Brick.
- 97. Vitrified Clay Sewer Block. 98. Cast Iron, Steel, and
- Wood. 164–193
-
-
- CHAPTER IX
-
- DESIGN OF THE SEWER RING
-
- 99. Stresses in Buried Pipe. 100. Design of Steel Pipe. 101.
- Design of Wood Stave Pipe. 102. External Loads on Buried
- Pipe. 103. Stresses in Circular Ring. 104. Analysis of Sewer
- Arches. 105. Reinforced Concrete Sewer Design. 194–210
-
-
- CHAPTER X
-
- CONTRACTS AND SPECIFICATIONS
-
- 106. Importance of the Subject. 107. Scope of the Subject. 108.
- Types of Contracts. 109. The Agreement. 110. The
- Advertisement. 111. Information and Instructions for Bidders.
- 112. Proposal. 113. General Specifications. 114. Technical
- Specifications. 115. Special Specifications. 116. The
- Contract. 117. The Bond. 211–232
-
-
- CHAPTER XI
-
- CONSTRUCTION
-
- 118. Elements. WORK OF THE ENGINEER. 119. Duties. 120.
- Inspection. 121. Interpretation of Contract. 122. Unexpected
- Situations. 123. Cost Data and Estimates. 124. Progress
- Reports. 125. Records. EXCAVATION. 126. Specifications. 127.
- Hand Excavation. 128. Machine Excavation. 129. Types of
- Machines. 130. Continuous Bucket Excavators. 131. Cableway
- and Trestle Excavators. 132. Tower Cableways. 133. Steam
- Shovels. 134. Drag Line and Bucket Excavators. 135.
- Excavation in Quicksand. 136. Pumping and Drainage. 137.
- Trench Pump. 138. Diaphragm Pump. 139. Jet Pump. 140. Steam
- Vacuum Pumps. 141. Centrifugal and Reciprocating Pumps. 142.
- Well Points. 143. Rock Excavation. 144. Power Drilling. 145.
- Steam or Air for Power. 146. Depth of Drill Hole. 147.
- Diameter of Drill Hole. 148. Spacing of Drill Holes. SHEETING
- AND BRACING. 149. Purposes and Types. 150. Stay Bracing. 151.
- Skeleton Sheeting. 152. Poling Boards. 153. Box Sheeting.
- 154. Vertical Sheeting. 155. Pulling Wood Sheeting. 156.
- Earth Pressures. 157. Design of Sheeting and Bracing. 158.
- Steel Sheet Piling. LINE AND GRADE. 159. Locating the Trench.
- 160. Final Line and Grade. 161. Transferring Grade and Line
- to the Pipe. 162. Line and Grade in Tunnel. TUNNELLING. 163.
- Depth. 164. Shafts. 165. Timbering. 166. Shields. 167. Tunnel
- Machines. 168. Rock Tunnels. 169. Ventilation. 170.
- Compressed Air. EXPLOSIVES AND BLASTING. 171. Requirements.
- 172. Types of Explosives. 173. Permissible Explosives. 174.
- Strength. 175. Fuses and Detonators. 176. Care in Handling.
- 177. Priming, Loading, and Firing. 178. Quantity of
- Explosive. PIPE SEWERS. 179. The Trench Bottom. 180. Laying
- Pipe. 181. Joints. 182. Labor and Progress. BRICK AND BLOCK
- SEWERS. 183. The Invert. 184. The Arch. 185. Block Sewers.
- 186. Organization. 187. Rate of Progress. CONCRETE SEWERS.
- 188. Construction in Open Cut. 189. Construction in Tunnels.
- 190. Materials for Forms. 191. Design of Forms. 192. Wooden
- Forms. 193. Steel-lined Wooden Forms. 194. Steel Forms. 195.
- Reinforcement. 196. Cost of Concrete Sewers. BACKFILLING.
- 197. Method. 233–331
-
-
- CHAPTER XII
-
- MAINTENANCE OF SEWERS
-
- 198. Work Involved. 199. Causes of Troubles. 200. Inspection.
- 201. Repairs. 202. Cleaning of Sewers. 203. Flushing Sewers.
- 204. Cleaning Catch-basins. 205. Protection of Sewers. 206.
- Explosions in Sewers. 207. Valuation of Sewers. 332–351
-
-
- CHAPTER XIII
-
- COMPOSITION AND PROPERTIES OF SEWAGE
-
- 208. Physical Characteristics. 209. Chemical Composition. 210.
- Significance of Chemical Constituents. 211. Sewage Bacteria.
- 212. Organic Life in Sewage. 213. Decomposition of Sewage.
- 214. The Nitrogen Cycle. 215. Plankton and Macroscopic
- Organisms. 216. Variations in the Quality of Sewage. 217.
- Sewage Disposal. 218. Methods of Sewage Treatment. 352–371
-
-
- CHAPTER XIV
-
- DISPOSAL BY DILUTION
-
- 219. Definition. 220. Conditions Required for Success. 221.
- Self-purification of Running Streams. 222. Self-purification
- of Lakes. 223. Dilution in Salt Water. 224. Quantity of
- Diluting Water Needed. 225. Governmental Control. 226.
- Preliminary Treatment. 227. Preliminary Investigations. 372–382
-
-
- CHAPTER XV
-
- SCREENING AND SEDIMENTATION
-
- 228. Purpose. 229. Types of Screens. 230. Sizes of Openings.
- 231. Design of Fixed and Movable Screens. PLAIN
- SEDIMENTATION. 232. Theory of Sedimentation. 233. Types of
- Sedimentation Basins. 234. Limiting Velocities. 235. Quantity
- and Character of Grit. 236. Dimensions of Grit Chambers. 237.
- Existing Grit Chambers. 238. Number of Grit Chambers. 239.
- Quantity and Characteristics of Sludge from Plain
- Sedimentation. 240. Dimensions of Sedimentation Basins.
- CHEMICAL PRECIPITATION. 241. The Process. 242. Chemicals.
- 243. Preparation and Addition of Chemicals. 244. Results. 383–409
-
-
- CHAPTER XVI
-
- SEPTICIZATION
-
- 245. The Process. 246. The Septic Tank. 247. Results of Septic
- Action. 248. Design of Septic Tanks. 249. Imhoff Tanks. 250.
- Design of Imhoff Tanks. 251. Imhoff Tank Results. 252. Status
- of Imhoff Tanks. 253. Operation of Imhoff Tanks. 254. Other
- Tanks. 410–430
-
-
- CHAPTER XVII
-
- FILTRATION AND IRRIGATION
-
- 255. Theory. 256. The Contact Bed. 257. The Trickling Filter.
- 258. Intermittent Sand Filter. 259. Cost of Filtration.
- IRRIGATION. 260. The Process. 261. Status. 262. Preparation
- and Operation. 263. Sanitary Aspects. 264. The Crop. 431–464
-
- CHAPTER XVIII
-
- ACTIVATED SLUDGE
-
- 265. The Process. 266. Composition. 267. Advantages and
- Disadvantages. 268. Historical. 269. Aëration Tank. 270.
- Sedimentation Tank. 271. Reaëration Tank. 272. Air
- Distribution. 273. Obtaining Activated Sludge. 274. Cost. 465–479
-
-
- CHAPTER XIX
-
- ACID PRECIPITATION, LIME AND ELECTRICITY, AND DISINFECTION
-
- 275. The Miles Acid Process. ELECTROLYTIC TREATMENT. 276. The
- Process. DISINFECTION. 277. Disinfection of Sewage. 482–493
-
-
- CHAPTER XX
-
- SLUDGE
-
- 278. Methods of Disposal. 279. Lagooning. 280. Dilution. 281.
- Burial. 282. Drying. 495–505
-
-
- CHAPTER XXI
-
- AUTOMATIC DOSING DEVICES
-
- 283. Types. 284. Operation. 285. Three Alternating Siphons.
- 286. Four or More Alternating Siphons. 287. Timed Siphons.
- 288. Multiple Alternating and Timed Siphons. 506–512
-
-
-
-
- SEWERAGE AND SEWAGE TREATMENT
-
-
-
-
- CHAPTER I
- INTRODUCTION
-
-
-=1. Sewerage and the Sanitary Engineer.=—Present day conceptions of
-sanitation are based on the scientific discoveries which have resulted
-so much in the increased comfort and safety of human life during the
-past century, in the increase of our material possessions, and the
-extent of our knowledge. The danger to health in the accumulation of
-filth, the spreading of disease by various agents, the germ theory of
-disease, and other important principles of sanitation can be counted
-among the more recent scientific discoveries and pronouncements.
-Experience has shown, and continues to show, that the increase of
-population may be inhibited by accumulations of human waste in populous
-districts. The removal of these wastes is therefore essential to the
-existence of our modern cities.
-
-The greatest need of a modern city is its water supply. Without it city
-life would be impossible. The next most important need is the removal of
-waste matters, particularly wastes containing human excreta or the germs
-of disease. To exist without street lights, pavements, street cars,
-telephones, and the many other attributes of modern city life might be
-possible, although uncomfortable. To exist in a large city without
-either water or sewerage would be impossible. The service rendered by
-the sanitary engineer to the large municipality is indispensable. In
-addition to the service necessary to the maintenance of life in large
-cities, the sanitary engineer serves the smaller city, the rural
-community, the isolated institution, and the private estate with
-sanitary conveniences which make possible comfortable existence in them,
-and which are frequently considered as of paramount necessity. Training
-for service in municipal sanitation is training for a service which has
-a more direct beneficial effect on humanity than any other engineering
-work, or any other profession. W. P. Gerhard states:
-
- _A Sanitary Engineer_ is an engineer who carries out those works
- of civil engineering which have for their object:
-
- (_a_) The promotion of the public and individual health;
-
- (_b_) The remedying of insanitary conditions;
-
- (_c_) The prevention of epidemic diseases.
-
- A well-educated sanitary engineer should have a thorough knowledge
- of general civil engineering, of architecture, and of sanitary
- science. The practice of the sanitary engineer embraces water
- supply, sewerage, and sewage and garbage disposal for cities and
- for single buildings; the prevention of river pollution, the
- improvement of polluted water supplies; street paving and street
- cleaning, municipal sanitation, city improvement plans, the laying
- out of cities, the preparation of sanitary surveys, the regulation
- of noxious trades, disinfection, cremation, and the sanitation of
- buildings.
-
-The need of the work of the sanitary engineer in the provision of sewers
-and drains is thrust upon us in our daily experience by the clogging of
-sewers, the flooding of streets by heavy rains, filthy conditions in
-unsewered districts, increased values of property and improved
-conditions of living in sewered districts, and in many other ways. The
-increasing demand for sewerage and the amount of money expended on sewer
-construction is indicated by the information given in Table I.
-
-
-=2. Historical.=—An ordinance passed by the Roman Senate in the name of
-the Emperor about A.D. 80, states:
-
- I desire that nobody shall conduct away any excess water without
- having received my permission or that of my representatives; for
- it is necessary that a part of the supply flowing from the
- delivery tanks shall be utilized not only for cleaning our city,
- but also for flushing the sewers.[1]
-
-Neither the sewers mentioned nor the distributing pipes of the public
-water supply were connected to individual residences. The contributions
-to the sewers came from the ground and the street surface. The streets
-were the receptacles of liquid and solid wastes and were often little
-more than open sewers. A promenade after dark in an ancient, medieval,
-or early modern city was accompanied not only by the underfoot dangers
-of an uneven pavement or an encounter with a footpad, but with the
-overhead danger from the emptying of slops into the streets from the
-upper windows. Sewers were used for the collection of surface water; the
-discharge of fecal matter into them was prohibited. The problem of the
-collection of sewage remained unsolved until the Nineteenth Century.
-
- TABLE 1
-
- POPULATION TRIBUTARY TO SEWERAGE SYSTEMS
-
- ──────────────────────────────────────┬──────────┬──────────┬──────────
- │ 1905[2] │ 1915[3] │ 1920[4]
- ──────────────────────────────────────┼──────────┼──────────┼──────────
- Population discharging raw sewage into│ │ │
- the sea or tidal estuaries │ 6,500,000│ 8,500,000│
- Population discharging raw sewage into│ │ │
- inland streams or lakes │20,400,000│26,400,000│
- Population connected to systems where │ │ │
- sewage is treated in some way │ 1,100,000│ 6,900,000│
- Population connected with sewerage │ │ │
- systems │28,000,000│41,800,000│46,300,000
- ──────────────────────────────────────┴──────────┴──────────┴──────────
-
-The development of the London sewers was commenced early in the
-Nineteenth Century. The sewerage system of Hamburg, Germany, was laid
-out in 1842 by Lindley, an English engineer who with other English
-engineers performed similar work in other German cities because of their
-earlier experience in English communities. Berlin’s present system dates
-from 1860. The construction of storm-water drains in Paris dates from
-1663.[5] They were intended only as street drains but are now included
-in the comprehensive system of the city. The first comprehensive
-sewerage system in the United States was designed by E. S. Chesbrough
-for the City of Chicago in 1855. Previous to this time sewers had been
-installed in an indifferent manner and without definite plan. The
-installation of a comprehensive sewerage system in Baltimore in 1915
-marks the completion of installation of sewerage systems in all large
-American cities.
-
-In the early days of sewerage design it was considered unsafe to
-discharge domestic wastes into the sewers as the concentration of so
-much sewage was expected to create great nuisances and dangers to
-health. That the fear that the concentration of large quantities of
-sewage would create a nuisance was not ill founded is proven by the
-conditions on the Thames at London in 1858–59. Dr. Budd states:[6]
-
- For the first time in the history of man, the sewage of nearly
- three millions of people had been brought to seethe and ferment
- under a burning sun in one vast open _cloaca_ lying in their
- midst.
-
- The result we all know. Stench so foul we may well believe had
- never before ascended to pollute this lower air. Never before at
- least had a stink risen to the height of an historic event.... For
- months together the topic almost monopolized the public prints....
- ‘India is in revolt and the Thames stinks’ were the two great
- facts coupled together by a distinguished foreign writer, to mark
- the climax of a national humiliation.[7]
-
-The problem of sewage disposal followed the more or less successful
-solutions of the problem of sewage collection. In England the British
-Royal Commission on Sewage Disposal was appointed in 1857 and issued its
-first report in 1865. The first studies in the United States were
-started in 1887 by the establishment of an experiment station at
-Lawrence, Massachusetts, where valuable work has been done. The station
-is under the State Board of Health, which issued its first report
-containing the results of the work at the station, in 1890.
-
-Various methods of sewage treatment preparatory to disposal have been
-devised from time to time. Some have fallen into disuse, such as the A.
-B. C. (alum, blood and clay) process, and others have taken a permanent
-place, such as the septic tank. The unsolved problems of sewage
-collection, and the number of persons still unserved by sewerage and
-sewage disposal opens a wide field to the study and construction of
-sewerage works.
-
-
-=3. Methods of Collection.=—The method of collection which involves the
-removal of night soil from a privy vault, the pail system which involves
-the collection of buckets of human excreta from closets and homes,
-indoor chemical closets, and other makeshift methods of collection are
-of extreme importance where no sewers exist, but they are not properly
-considered as sewerage systems or sewerage works. These methods of
-collection are generally confined to rural districts and to outlying
-parts of urban communities. They require constant attention for their
-proper conduct and little skill for their installation, the principal
-requirements being to make the receptacles fly-proof.
-
-The pneumatic system was introduced by Liernur, a Dutch engineer.[8] It
-is used in parts of a few cities in Europe, but it is not capable of use
-on a large scale. It consists of a system of air-tight pipes, connecting
-water closets, kitchen sinks, etc., with a central pumping station at
-which an air-tight tank is provided from which the air is partly
-exhausted. As little water as possible is allowed to mix with the fecal
-matter and other wastes in order not to overtax the system. Solid and
-liquid wastes are drawn to the central station when the waste valve on
-the plumbing fixture is opened.
-
-The collection of sewage in a system of pipes through which it is
-conducted by the buoyant effect and scouring velocity of water is known
-as the water-carriage system. This is the only method of sewage
-collection in general use in urban communities. In this system solid and
-liquid wastes are so highly diluted with water as either to float or to
-be suspended therein. The mixture resulting from this high dilution
-follows the laws of hydraulics as applied to pure water, or water
-containing suspended matter. It will flow freely through properly
-designed conduits and will concentrate the sewage wastes at the point of
-ultimate disposal.
-
-
-=4. Methods of Disposal.=—Sewage is disposed of by dilution in water, by
-treatment on land, or occasionally by discharging it into channels that
-contain no diluting water. Some form of treatment to prepare sewage for
-ultimate disposal is frequently necessary and will undoubtedly be
-required in a comparatively short time for all sewage discharged into
-watercourses. The solid matters removed by treatment may be buried,
-burned, dumped into water, or used as a fertilizer.
-
-If the volume of diluting water, or the area and character of land used
-for disposal are not as they should be, a nuisance will be created. The
-aim of all methods of sewage treatment has so far been to produce an
-effluent which could be disposed of without nuisance and in certain
-exceptional cases to protect public water supplies from pollution.
-Financial returns have been sought only as a secondary consideration. A
-few sewage farms and irrigation projects might be considered as
-exceptions to this as the value of the water in the sewage as an
-irrigant has been the primary incentive to the promotion of the farm.
-
-It is to be remembered that since the aim of all sewage treatment is to
-produce an effluent that can be disposed of without causing a nuisance,
-the simplest process by which this result can be attained under the
-conditions presented is the process to be adopted. No attempt is made to
-_purify_ sewage completely, or on a practical scale to make drinking
-water.
-
-
-=5. Methods of Treatment.=—Screening and sedimentation are the primary
-methods for the treatment of sewage. By these methods a portion of the
-floating and settleable solids are removed, preventing the formation of
-unsightly scum and putrefying sludge banks. Chemicals are sometimes
-added to the sewage to form a heavy flocculent precipitate which hastens
-sedimentation of the solid matters in the sewage. The process in these
-methods is mechanical and the solid matters removed from the sewage must
-be disposed of by other methods than dilution with the sewage effluent.
-More complete methods of treatment are dependent on biologic action.
-Under these methods of treatment complete stabilization of the effluent
-is approached, and in the most complete treatment an effluent is
-produced which is clear, sparkling, non-odorous, non-putrescible, and
-sterile. Sterilization of sewage, usually with chlorine or some of its
-compounds, has been used, not to reduce the amount of diluting water
-necessary, but to reduce the number of pathogenic germs and to minimize
-the danger of the transmission of disease.
-
-
-=6. Definitions.=—Sewage and sewerage are not synonymous terms although
-frequently confused. Sewage is the spent water supply of a community
-containing the waste from domestic, industrial or commercial use, and
-such surface and ground water as may enter the sewer.[9] Sewerage is the
-name of the system of conduits and appurtenances designed to carry off
-the sewage. It is also used to indicate anything pertaining to sewers.
-
-A difference is made between sanitary sewage, storm sewage, and
-industrial wastes. Sanitary sewage, sometimes called domestic sewage, is
-the liquid wastes discharged from residences or institutions, and
-contains water closet, laundry and kitchen wastes. Storm sewage is the
-surface run-off which reaches the sewers during and immediately after a
-storm. Industrial wastes are the liquid waste products discharged from
-industrial plants.
-
-A sewer is a conduit used for conveying sewage.
-
-The names of the conduits through which sewage may flow are:
-
-_Soil Stack._—A vertical pipe in a building through which waste water
-containing fecal matter or urine is allowed to flow.
-
-_Waste Pipe._—A vertical pipe in a building through which waste water
-containing no fecal matter is allowed to flow.
-
-_House Drain._—The approximately horizontal portion of a house drainage
-system which conveys the drainage from the soil stack or waste pipe to
-the point of discharge from the building.
-
-_House Sewer._—The pipe which leads from the outside wall of the
-building to the sewer in the street.
-
-_Lateral Sewer._—The smallest branch in a sewerage system, exclusive of
-the house sewers.
-
-_Sub-main or Branch Sewer._—A sewer from which the sewage from two or
-more laterals is discharged.[10]
-
-_Main or Trunk Sewer._—A sewer into which the sewage from two or more
-sub-main or branch sewers is discharged.[11]
-
-_Intercepting Sewer._—A sewer generally laid transversely to a sewerage
-system to intercept some portion or all of the sewage collected by the
-system.
-
-_Relief Sewer._—A sewer intended to carry a portion of the flow from a
-district already provided with sewers of insufficient capacity and thus
-preventing overtaxing the latter.[12]
-
-_Outfall Sewer._—That portion of a main or trunk sewer below all
-branches.
-
-_Flushing Sewer._—A conduit through which water is conveyed for flushing
-portions of a sewerage system.
-
-_Force Main._—A conduit through which sewage is pumped under pressure.
-
-
-
-
- CHAPTER II
- WORK PRELIMINARY TO DESIGN
-
-
-=7. Division of Work.=—Engineering work on sewerage can be divided into
-four parts, namely: preliminary, design, construction and maintenance.
-An engineer may be engaged during any one or all of these periods on the
-same sewerage system, and should therefore be acquainted with his duties
-during each period.
-
-
-=8. Preliminary.=—The demand for sewerage normally follows the
-installation or extension of the public water supply. It may be caused
-by: a lack of drainage on some otherwise desirable tract of real estate;
-from a public realization of unpleasant or unhealthful conditions in a
-built-up district; or through the realization by the municipal
-administration of the necessity for caring for the future. In whatever
-way the demand may be created the engineer should take an active part in
-the promotion of the work.
-
-The engineer’s duties during the preliminary period are: to make a study
-of the possible methods by which the demand for sewerage can be
-satisfied; to present the results of this study in the form of a report
-to the committee or organization responsible for the promotion of the
-work; and so to familiarize himself with the conditions affecting the
-installation of the proposed plans as to be able to answer all inquiries
-concerning them. This work will require the general qualities of
-character, judgment, efficiency and the understanding of men in
-addressing interested persons individually and collectively on the
-features of the proposed plans, and the exercise of engineering
-technique in the survey and the drawing of the plans. The engineer
-should assure himself that all legal requirements in the drawing of
-petitions, advertising, permits, etc., have been complied with. This
-requires some knowledge of national, state, and local laws. Although
-none the less essential their description is not within the scope of
-this book.
-
-The engineer’s preliminary report should contain a section devoted to
-the feasibility of one or more plans which may be explained in more or
-less detail with a statement of the cost and advantages of each. A
-conclusion should be reached as to the most desirable plan and a
-recommendation made that this plan be installed. Other sections of the
-report may be devoted to a history of the growing demand, a description
-of the conditions necessitating sewerage, possible methods of financing,
-and such other subjects as may be pertinent. The making of the
-preliminary plan and the design of sewerage works are described in
-subsequent chapters.
-
-
-=9. Estimate of Cost.=—In making an estimate of cost the information
-should be presented in a readable and easily comprehended manner. It is
-necessary that the items be clearly defined and that all items be
-included. The method of determining the costs of doubtful items such as
-depreciation, interest charges, labor, etc., and the probability of the
-fluctuation of the costs of certain items should be explained.
-
-The engineer’s estimate may be divided somewhat as follows:
-
- Labor.
-
- Material.
-
- Overhead. This may include construction plant, office expense,
- supervision, bond, interest on borrowed capital, insurance,
- transportation, etc. The amount of the item is seldom less than 15
- per cent and is usually over 20 per cent of the contract price.
-
- Contingencies. This allowance is usually 10 to 15 per cent of the
- contract price.
-
- Profit. This should be from 5 to 10 per cent of the sum of the
- four preceding items.
-
-The contract price is the sum of these items. To this may be added:
-
- Engineering. 2 to 5 per cent of the contract price.
-
- Extra Work. Zero to 15 per cent of the contract price; dependent
- on the character of the work, the completeness of the preliminary
- information, the completeness of the plans, etc.
-
- Legal expense.
-
- Purchase of land, rights of way, etc., etc.
-
-The cost of the sewer may be stated as so much per linear foot for
-different sizes of pipe, including all appurtenances such as manholes,
-catch-basins, etc., or the items may be separated in great detail
-somewhat as follows:
-
- Earth excavation, per cu. yd.
- Rock excavation, per cu. yd.
- Backfill, per cu. yd.
- Brick manholes, 3 feet by 4 feet, per foot of depth.
- Vitrified sewer pipe with cement joints, in place,
- ... inches in diameter, 0 to 6 feet deep
- 6 to 8 feet deep
- 8 to 10 feet deep
- Repaving, macadam per sq. yd.
- asphalt per sq. yd.
- Flush-tanks, ... gal. capacity, per tank.
- Service pipes to flush-tanks, per linear foot., etc., etc.
-
-These methods represent the two extremes of presenting cost estimates.
-Each method, or modification thereof, may have its use, dependent on
-circumstances.
-
-Reliable cost data are difficult to obtain. Lists of prices of materials
-and labor are published in certain engineering and trade periodicals.
-The Handbook of Cost Data by H. P. Gillette contains lists of the amount
-of material and labor used on certain specific jobs and types of
-construction. The price of labor and materials on the local market can
-be obtained from the local Chamber of Commerce, contractors and other
-employers of labor, and dealers in the desired commodities. Contract
-prices for sewerage work published in the construction news sections of
-engineering periodicals may be a guide to the judgment of the probable
-cost of proposed work, but are generally dangerous to rely upon as full
-details are lacking in the description of the work. A wide experience in
-the collection and use of cost data is the desirable qualification for
-making estimates of cost. It is possessed by few and is not an
-infallible aid to the judgment.
-
-Having completed the design and summary of the bills of material and
-labor necessary for each structure or portion of the sewerage system,
-the product of the unit cost and the amount of each item plus an
-allowance for overhead will equal the cost of the item. The total cost
-will be the sum of the costs of each item. The items should be so
-grouped that the cost of the different portions of the system are
-separated in order that the effect on the total cost resulting from
-different combinations of items or the omission of any one item may be
-readily computed.
-
-A method for estimating the approximate cost of sewers, devised by W. G.
-Kirchoffer[13] depends upon the use of the diagram shown in Fig. 2. The
-factors for local conditions are shown in Table 2. For example, let it
-be required to find the cost of a 15–inch vitrified pipe sewer at a
-depth of 9 feet, if the unit costs of labor and material and the
-conditions are the same as shown in Table 3.
-
-[Illustration:
-
- FIG. 2.—Diagram for Estimating the Cost of Sewers.
-
- Eng. News, Vol. 76, p. 781.
-]
-
- _Solution_
-
- First: To find the factor depending on local conditions, enter the
- diagram at the 10–inch diameter and continue down until the
- intersection with the depth of trench at 8.2 feet is found. Now go
- diagonally parallel to lines running from left to right upwards to
- the intersection with the vertical line through a cost of 45 cents
- per foot. The diagonal line running from left to right downwards
- through this intersection corresponds to a factor of about 11.
-
- TABLE 2
-
- FACTORS FOR COSTS OF SEWERS TO BE USED WITH FIGURE 2
-
- ────────────────────────────────────────────────────────────────┬──────
- Character of Material │Factor
- ────────────────────────────────────────────────────────────────┼──────
- Clay, gravel and boulders, Medford │22–26
- Mostly sand, deep trenches sheeted. Wages medium. Richland │
- Center. │21–22
- Sandy clay. Wages medium. Labor conditions good at Kiel. │15–20
- Sand. _Sandy_ clay, some water. Labor conditions good. Pipe │
- prices medium at Manston. │14–20
- Gravelly clay, ⅒th laid in concrete at Burlington. │13–22
- Sandy clay, some water, sheeting at La Farge. │17–23
- Sand with water. │ 20
- Gravel and boulders. High wages. │ 26
- Clay soil. Good digging. │ 17
- Sandy clay. Some water. │ 23
- Clay 2 miles inland. Laborers boarded at sanitarium, Wales │ 35
- Clay, gravel and boulders at Plymouth. │20–27
- Sand, clay and good digging at Lake Mills. │16–19
- Red clay. Machine work at North Milwaukee. │20–24
- Good digging. Wages medium at West Salem. │17–19
- Sandy soil, bracing only required. No water. Wages and pipe │
- medium. │ 14
- Red sticky clay. │ 24
- Good digging in any soil. Work scarce. │ 15
- Red clay. No bracing. │ 20
- Work inland from railroad. Boarding laborers _and_ other │
- expenses. │ 35
- ────────────────────────────────────────────────────────────────┴──────
-
- Second: To find the cost of 15–inch pipe at a depth of 9.0 feet,
- enter the diagram at a diameter of 15 inches and continue down
- until the intersection with a depth of trench at 9 feet is found.
- Now go diagonally parallel to lines running from left to right
- upwards to the intersection with the diagonal line running from
- left to right downwards corresponding to the factor of 11 found
- above. The vertical line passing through this point shows the cost
- to be 67 cents per foot.
-
- TABLE 3
-
- COST OF SEWER CONSTRUCTION AT ATLANTIC, IOWA
-
- (From Gillette’s Handbook of Cost Data)
-
- Material: Clay, not difficult to spade and requiring little or no
- bracing and practically no pumping. All hand work except backfill which
- was done by team and scraper. Depth of trench averaged 8.2 feet; width
- 30 inches. Diameter of pipe 10 inches.
-
- ───────────────────────────────────────────────────────────┬─────┬─────
- Item │Wage,│Cost,
- │Cents│Cents
- │ per │ per
- │Hour │Foot.
- ───────────────────────────────────────────────────────────┼─────┼─────
- Pipe. │ │0.20
- Hauling team and driver. │ 30│ .003
- Hauling. Man helping. │ 17│ .001
- Cement and sand. │ │ .006
- Pipe layers. │ 22│ .014
- Pipe layer’s helper. │ 17│ .014
- Trenching. Top men. │ 17│ .027
- Trenching. Bottom men. │ 17│ .130
- Trenching. Scaffold men. │ 17│ .002
- Trenching. Bracing men. │ 17│ .002
- Backfilling. Shovel. │ 17│ .010
- Backfilling. Team and scraper. │ 30│ .008
- Backfilling. Man and scraper. │ 17│ .005
- Water boy. │ 10│ .006
- Foreman. │ 30│ .022
- ───────────────────────────────────────────────────────────┼─────┼─────
- Total. │ │ .450
- ───────────────────────────────────────────────────────────┴─────┴─────
-
-
- METHODS OF FINANCING
-
-The construction of sewerage works may be paid for by the issue of
-municipal bonds, by special assessment, by funds available from the
-general taxes, or by private enterprise.
-
-
-=10. Bond Issues.=—A municipal bond is a promise by the municipality to
-pay the face value of the bond to the holder at a certain specified
-time, with interest at a stipulated rate during the interim. The
-security on the bond is the taxable property in the municipality. The
-legal restrictions thrown around municipal bond issues, the value of the
-taxable property in the municipality, all of which may be used as
-security for municipal bonds, and the fact that a municipality can be
-sued in case of default, make municipal bonds desirable and provide a
-good market for their sale. The funds available from a municipal bond
-issue are limited by the amount that the legal limit is in excess of the
-outstanding issues. The legal limit varies in different states from
-about 5 to 15 per cent of the assessed value of the property in the
-municipality. In some cases the amount available from municipal bonds
-has been increased by forming a municipality within a municipality such
-as a sanitary district, a park district, a drainage district, etc.,
-which comprises a large portion or all of an existing municipal
-corporation. This case is well illustrated in some parts of the City of
-Chicago where the municipal taxing powers are shared by the City
-government, the Sanitary District, and Park Commissioners. The right to
-create a new municipal corporation must be granted by the state
-legislature. Knowledge of fixed bonds, serial bonds, life of bonds,
-sinking funds, etc. is an important part of an engineer’s education.[14]
-
-Bond issues must usually be presented to the voters for approval at an
-election. If approved, and other legal procedure has been followed, the
-bonds may be bought by some of the many bonding houses, or by private
-individuals, and the money is immediately available for construction.
-The bonds are redeemed by general taxation spread over the period of the
-issue.
-
-
-=11. Special Assessment.=—A special assessment is levied against
-property benefited directly by the structure being paid for. Special
-assessments are used for the payment for the construction of lateral
-sewers which are a direct benefit to separate districts but are without
-general benefit to the city. In case the construction of an outfall
-sewer or the erection of a treatment plant, which may be of some general
-benefit, is necessary to care for a separate district, a part of the
-expense may be borne by funds available from general taxation. The legal
-procedure for the raising of funds by special assessment and the purpose
-to which the funds so raised may be applied are stipulated in great
-detail in different states and their directions must be followed
-implicitly. Illinois procedure, which is similar to that in some other
-states, is as follows: a meeting of the interested property owners is
-called by a committee or board of the municipal government, as the
-result of a petition by interested persons or through the independent
-action of the Board. At this preliminary meeting or public hearing
-arguments for and against the proposed improvement are heard. The
-engineer is present at this meeting to answer questions and to advise
-concerning the engineering features of the plan. If approval is given by
-the Board the plan and specifications are prepared complete in every
-detail and incorporated in an ordinance which is presented to the
-legislative branch of the city government for passage. If the project is
-adopted it is taken to the county court. An assessment roll is prepared
-by a commissioner appointed by the court. This roll shows the amount to
-be assessed against each piece of property benefited. A hearing is then
-held in the county court at which the owner of any assessed property may
-voice objections to the continuation of the project. The project may be
-thrown out of court for many different reasons, such as the misspelling
-of a street name, an error in an elevation, an error in the description
-of a pavement, but most important of all is definite proof that the
-benefit is not equal to the assessment. The many minor irregularities
-which may nullify the procedure in a special assessment differ in
-different states and in different courts in the same state, but in
-general no court can approve an assessment greater than the benefits
-given. After the project has passed through the county court and the
-assessment roll has been approved, bonds may be issued for the payment
-of the contractor. Special assessment bonds are liens against the
-property assessed and have not the same security as a general municipal
-bond. For this reason a city which has reached its legal limit of
-municipal bond issues can still pay for work by special assessment.
-
-The funds available from special assessments are limited only by the
-benefit to the property assessed. The amount of the benefit is difficult
-to fix and may lead to much controversy. It should not exceed the amount
-demanded for similar work in other localities, unless unusual and
-well-understood reasons can be given.
-
-
-=12. General Taxation.=—In paying for public improvements by general
-taxation the money is taken from the general municipal funds which have
-been apportioned for that purpose by the legislative department of the
-municipal government. This method of raising funds for sewerage
-construction is seldom used unless the political situation is
-unfavorable to the success of a bond issue or special assessment and the
-need for the improvement is great. It is usually difficult to
-appropriate sufficient funds for new construction as the general tax is
-apportioned to support only the operating expenses of the city, and
-statutory provisions limit the amount of tax which can be levied.
-
-
-=13. Private Capital.=—Private capital has been used for financing
-sewerage works in some cases because of the aversion of the public in
-some cities to the payment of a tax for the negative service performed
-by a sewer. Sewers are buried, unseen, and frequently forgotten, but
-knowledge of their necessity has spread and the number of privately
-owned sewerage works is diminishing because of the better service which
-can be provided by the municipality.
-
-Franchises are granted to private companies for the construction of
-sewers only after the city has exhausted other methods for the raising
-of capital. The return on the private capital invested is received from
-a rental paid by the city, or paid directly by the users of the system,
-an initial payment usually being demanded for connection to the system.
-To be successful the enterprise must be popular and must fill a great
-need. This method of financing sewerage works is seldom employed as
-favorable conditions are not common.
-
-
- PRELIMINARY WORK
-
-
-=14. Preparing for Design.=—Methods for the design of sewerage systems
-are given in Chapter V. Before the design is made certain information is
-essential. A survey must be made from which the preliminary map can be
-prepared as described in Art. 42. Other necessary information which is
-the basis of subsequent estimates of the quantity of sewage to be cared
-for must be obtained by a study of rates of water consumption and the
-density and growth of population, the measurement of the discharge from
-existing sewers, and the compilation of rainfall and run-off data. If no
-rainfall data are available estimates must be made from the nearest
-available data. Observations of rainfall or run-off for periods of less
-than 10 to 20 years are likely to be misleading. Methods for gathering
-and using this information are explained in subsequent chapters.
-
-Underground surveys are desirable along the lines of the proposed sewers
-to learn of obstructions, difficult excavation and other conditions
-which may be met. All such data are seldom gathered except for sewerage
-systems involving the expenditure of a large amount of money. For
-construction in small towns or small extensions to an existing system
-the funds are usually insufficient for extensive preliminary
-investigation. The saving in this respect is paid unknowingly to the
-contractor as compensation for the risk in bidding without complete
-information.
-
-
-=15. Underground Surveys.=—These may be more or less extensive dependent
-on the character of the district in which construction is to take place.
-In built-up districts the survey should be more thorough than in
-sparsely settled districts where only the character of the excavated
-material is of interest and no obstructions are to be met.
-
-Underground surveys furnish to the engineer and to prospective bidders
-on contract work information on which the design and estimate of cost
-and the contractor’s bid may be based and without which no intelligent
-work can be done. By removing much of the uncertainty of the conditions
-to be met in the construction of the sewer, the design can be made more
-economical and the contractor’s bid should be markedly lower,
-sufficiently so to repay more than the expense of the survey. The
-information to be obtained consists of the location of the ground-water
-level, and the location and sizes of water, gas, and sewer pipes,
-telephone and electric conduits, street-car tracks, steam pipes, and all
-other structures which may in any way interfere with subsurface
-construction. These structures should be located by reference to some
-permanent point on the surface. The elevation of the top of the pipes,
-except sewers, rather than the depth of cover should be recorded, as the
-depth of cover is subject to change. The elevation of sewers should be
-given to the invert rather than to the top of the pipe.
-
-A portion of the map of the subsurface conditions at Washington, D. C.,
-is shown in Fig. 3. Many of the dimensions and notations are not shown
-to avoid confusion on this small reproduction.[15] Colors are generally
-used instead of different forms of cross hatching to show the different
-classes of pipe and structures. In addition to a record of the
-underground structures the character of the ground and the pavement
-should be recorded. A comprehensive underground survey is seldom
-available nor does time usually permit its being made preliminary to the
-design of a sewerage system. The character of the material through which
-the sewer is to pass should be determined in all cases.
-
-[Illustration:
-
- FIG. 3.—Record Map of Underground Structures, Washington, D. C.
-
- Eng. Record, Vol. 74, p. 263.
-
- The various subsurface lines are differentiated by colors as follows:
- _A_—Sewers, vermilion. _B_—Water mains, blue. _C_—Potomac Electric
- Power Co., carmine. _D_—Washington Railway and Electric Co.,
- carmine. _E_—Capital Traction Co., violet. _F_—Chesapeake and
- Potomac Telephone Co., green. _G_—Washington Gas Light Co., green.
- _H_—Western Union Telegraph Co., orange. _I_—Postal Telegraph Co.,
- orange. _K_—Private vaults, black. _L_—City Electric Co., yellow.
-]
-
-[Illustration:
-
- FIG. 4.
-
- Punch Drill.
-]
-
-Underground pipes and structures are located by excavations, which may
-be quite extensive in some cases. Their position is fixed by
-measurements referred to manholes and other underground structures which
-are somewhat permanent in position. A city engineer should grasp every
-opportunity to record underground structures when excavations are made
-in the streets. The character of the material through which the sewer is
-to pass is determined by borings.
-
-
-=16. Borings.=—Methods used for the investigation of subsurface
-conditions preliminary to sewer construction are: punch drilling, boring
-with earth auger, jet boring, wash boring, percussion drilling, abrasive
-drilling, and hydraulic drilling. The last three methods named are used
-only for unusually deep borings or in rock.
-
-Punch drills are of two sorts. The simplest punch drill consists of an
-iron rod ⅞ of an inch to 1 inch in diameter, in sections about 4 feet
-long. One section is sharpened at one end and threaded at the other so
-that the next section can be screwed into it without increasing the
-diameter of the rod, as shown in Fig. 4. The drill is driven by a sledge
-striking upon a piece of wood held at the top of the drill to prevent
-injury to the threads. The drill should be turned as it is driven to
-prevent sticking. It is pulled out by a hook and lever as shown in Fig.
-5. It is useful in soft ground for soundings up to 8 to 12 feet in
-depth. Another form of punch drill described by A. C. Veatch[16]
-consists of a cylinder of steel or iron, one to two feet long split
-along one side and slightly spread. The lower portion is very slightly
-expanded and tempered into a cutting edge. In use it is attached to a
-rope or wooden poles and lifted and dropped in the hole by means of a
-rope given a few turns about a windlass or drum. By this process the
-material is forced up into the bit, slightly springs it, and so is held.
-When the bit is filled it is raised to the surface and emptied. Much
-deeper holes can be made with this than with the sharpened solid rod.
-
-[Illustration:
-
- FIG. 5.—Lever for Pulling Punch Drill.
-]
-
-[Illustration:
-
- FIG. 6.—Earth Augers.
-]
-
-Types of earth augers about 1½-inches in diameter are shown in Fig. 6.
-They are screwed on to the end of a section of the pipe or rod and as
-the hole is deepened successive lengths of pipe or rod are added. The
-device is operated by two men. It is pulled by straight lifting or with
-the assistance of a link and lever similar to that shown in Fig. 5. The
-device is suitable for soft earth or sand free from stones, and can be
-used for holes 15 to 25 feet in depth. For deeper holes a block and
-tackle should be used for lifting the auger from the hole. It is not
-suitable for holes deeper than about 35 feet.
-
-In the jetting method water is led into the hole through a ¾-inch or
-1–inch pipe, and forced downward through the drill bit or nozzle against
-the bottom of the hole. The complete equipment is shown in Fig. 7.[17]
-It is not always necessary to case the hole as shown in the figure as
-the muddy water and the vibration of the pipe puddle the sides so that
-they will stand alone. The jet pipe may be churned in the hole by a rope
-passing over a block and a revolving drum. In suitable soft materials
-such as clay, sand, or gravel, holes can be bored to a depth of 100 feet
-and samples collected of the material removed. An objection to the
-method is the difficulty of obtaining sufficient water.
-
-[Illustration:
-
- FIG. 7.—Jetting Outfit.
-
- U. S. Geological Survey, Water Supply Paper, No. 257
-
- 1. Simple Jetting Outfit. 2. Jetting Process. 3. Common Jetting Drill.
- 4_a_ and 4_b_. Expansion Bit or Paddy. 5. Drive Shoe.
-]
-
-Methods of drilling in rock up to depths of 20 feet are described in
-Chapter XI under Rock Drilling. For deeper holes percussion, abrasive,
-or hydraulic methods as used for deep well drilling must be employed.
-
-
-
-
- CHAPTER III
- QUANTITY OF SEWAGE
-
-
-=17. Dry weather Flow.=—Estimates of the quantity of sewage flow to be
-expected are ordinarily based on the population, the character of the
-district, the rate of water consumption, and the probable ground-water
-flow. Future conditions are estimated and provided for, as the sewers
-should have sufficient capacity to care for the sewage delivered to them
-during their period of usefulness.
-
-
-=18. Methods for Predicting Population.=—Methods for the prediction of
-future population are given in the following paragraphs.
-
-The method of _graphical extension_. This is the quickest and most
-simple of all. In this method a curve is plotted on rectangular
-coordinates to any convenient scale, with population as ordinates and
-years as abscissas. The curve is extended into the future by judgment of
-its general tendency. An example is given of the determination of the
-population of Urbana, Illinois, in 1950. Table 4 contains the population
-statistics which have been plotted on line A in Fig. 8 and extended to
-1950. The probable population in 1950 is shown by this line to be about
-21,000.
-
-The method of _geometrical progression_. In this method the rate of
-increase during the past few years or decades is assumed to be constant
-and this rate is applied to the present population to forecast the
-population in the future. For example the rate of increase of population
-in Urbana for the past 7 decades has varied widely, but indications are
-that for the next few decades it will be about 20 per cent. Applying
-this rate from 1920 to 1950 the population in 1950 is shown to be about
-17,800. It is evident that this method may lead to serious error as
-insufficient information is given in the table to make possible the
-selection of the proper rate of increase.
-
- TABLE 4
-
- POPULATION STUDIES
-
- ────┬────────────────────────────
- │ Urbana, Illinois
- ────┼──────────┬────────┬────────
- Year│Population│Absolute│Per Cent
- │ │Increase│Increase
- │ │for Each│for Each
- │ │ Decade │ Decade
- ────┼──────────┼────────┼────────
- 1850│ 210│ │
- 1860│ 2,038│ 1828│ 85.6
- 1870│ 2,277│ 239│ 10.5
- 1880│ 2,942│ 665│ 22.6
- 1890│ 3,511│ 569│ 16.2
- 1900│ 5,728│ 2217│ 38.7
- 1910│ 8,245│ 2517│ 30.5
- 1920│ 10,230│ 1985│ 19.4
- ────┴──────────┴────────┴────────
-
- ────┬───────────────────────────────────────────────────────────────
- │ Population of
- ────┼───────┬────────┬─────────┬────────┬──────┬───────────┬────────
- Year│Decatur│Danville│Champaign│Kankakee│Peoria│Bloomington│ Ann,
- │ │ │ │ │ │ │ Arbor
- │ │ │ │ │ │ │Michigan
- │ │ │ │ │ │ │
- ────┼───────┼────────┼─────────┼────────┼──────┼───────────┼────────
- 1850│ │ 736│ │ │ 5,095│ 1,594│
- 1860│ 3,839│ 1,632│ 1,727│ 2,984│14,045│ 7,075│ 5,097
- 1870│ 7,161│ 4,751│ 4,625│ 5,189│22,849│ 14,590│ 7,368
- 1880│ 9,547│ 7,733│ 5,103│ 5,651│29,259│ 17,180│ 8,061
- 1890│ 16,841│ 11,491│ 5,839│ 9,025│41,024│ 20,484│ 9,431
- 1900│ 20,754│ 16,354│ 9,098│ 13,595│56,100│ 23,286│ 14,509
- 1910│ 31,140│ 27,871│ 12,421│ 13,986│66,950│ 25,786│ 14,817
- 1920│ 43,818│ 33,750│ 15,873│ 16,721│76,121│ 28,638│ 19,516
- ────┴───────┴────────┴─────────┴────────┴──────┴───────────┴────────
-
-[Illustration:
-
- FIG. 8.—Diagram Showing Methods for Estimating Future Population.
-]
-
-The method of utilizing a _decreasing rate of increase_. This method
-attempts to correct the error in the assumption of a constant rate of
-increase. After a certain period of growth, as the age of a city
-increases its rate of increase diminishes. In applying this knowledge to
-a prediction of the future population of a city the population curve is
-plotted, as in the graphical method and a straight line representing a
-constant rate or increase is drawn tangent to the curve at its end. The
-curve is then extended at a flatter rate in accordance with the rate of
-change of a similar nearby larger city. This method has not been applied
-to any of the cities included in Table 4, as none has reached that
-limiting period where the rate of increase has begun to diminish.
-
-The method of utilizing an _arithmetical rate of increase_. This method
-allows for the error of the geometrical progression which tends to give
-too large results for old and slow-growing cities. This method generally
-gives results that are too low. The absolute increase in the population
-during the past decade or other period is assumed to continue throughout
-the period of prediction. Applying this method to the same case, the
-increase in the population during the past decade was 2,000. Adding
-three times this amount to the population in 1920, the population of
-Urbana in 1950 will be about 16,000.
-
-The method involving the _graphical comparison with other cities_ with
-similar characteristics. In this method population curves of a number of
-cities larger than Urbana but having similar characteristics, are
-plotted with years as abscissas and population as ordinates, with the
-present population of Urbana as the origin of coordinates. The
-population curve for Urbana is first plotted. It will lie entirely in
-the third quadrant as shown by the heavy full line in Fig. 8. The
-population curves of some larger cities are then plotted in such a
-manner that each curve passes through the origin at the time their
-population was the same as that of the present population of Urbana.
-These curves lie in the first and third quadrants. The population curve
-of the city in question is then extended to conform with the curves of
-older cities in the most probable manner as dictated by judgment. Such a
-series of plots has been made in Fig. 8. The results indicate that the
-population of Urbana in 1950 will be about 25,500.
-
-The last method described will give the most probable result as it is
-the most rational. For quick approximations the geometrical progression
-is used. The arithmetical progression is useful only as an approximate
-estimate for old cities.
-
-
-=19. Extent of Prediction.=—The period for which a sewerage system
-should be designed is such that each generation bears its share of the
-cost of the system. It is unfair to the present generation to build and
-pay for an extensive system that will not be utilized for 25 years. It
-is likewise unfair to the next generation to construct a system
-sufficient to comply with present needs only, and to postpone the
-payment for it by a long term bond issue. An ideal solution would be to
-plan a system which would satisfy present and future needs and to
-construct only those portions which would be useful during the period of
-the bond issue. Unfortunately this solution is not practical, because,
-1st, it is less expensive to construct portions of the system such as
-the outfall, the treatment plant, etc., to care for conditions in
-advance of present needs, and 2nd, the life of practically all portions
-of a sewerage system is greater than the legal or customary time limit
-on bond issues.
-
-A compromise between the practical and the ideal is reached by the
-design of a complete system to fulfill all probable demands, and the
-construction of such portions as are needed now in accordance with this
-plan. The payment should be made by bond issues with as long life as is
-financially or legally practical, but which should not exceed the life
-of the improvement.
-
-The prediction of the population should therefore be made such that a
-comprehensive system can be designed with intelligence. Practice has
-seldom called for predictions more than 50 years in the future.
-
-
-=20. Sources of Information on Population.=—The United States decennial
-census furnishes the most complete information on population.
-Unfortunately it becomes somewhat old towards the end of a decade. More
-recent information can be obtained from local sources. Practically every
-community takes an annual school census the accuracy of which is fairly
-reliable. The general tendencies of the population to change can be
-learned by a study of the post office records showing the amount of mail
-matter handled at various periods. Local chambers of commerce and
-newspapers attempt to keep records of population, but they are often
-inaccurate. Another source of information is the gross receipts of
-public service companies, such as street railways, water, gas,
-electricity, telephone, etc. The population can be assumed to have
-increased almost directly as their receipts, with proper allowance for
-change in rates, character of management, and other factors.
-
-
-=21. Density of Population.=—So far the study of population has been
-confined to the entire city. It is frequently necessary to predict the
-population of a district or small section of a city. A direct census may
-be taken, or more frequently its population is determined by estimating
-its density based on a comparison with similar districts of known
-density, and multiplying this density by the area of the district. In
-determining the density, statistics of the population of the entire city
-will be helpful but are insufficient for such a problem. A special
-census of the area involved would be conclusive but is generally
-considered too expensive. A count of the number of buildings in the
-district can be made quickly, and the density determined by
-approximating the number of persons per building. Statistics of the
-population of various districts together with a description of the
-character of the district are given in Table 5.
-
-[Illustration:
-
- FIG. 9.—Density, Area, and Population, Cincinnati, Ohio. 1850 to 1950.
-]
-
- TABLE 5
-
- DENSITIES OF POPULATION
-
- ────────────┬────────────────────────────────────────┬────────┬────────
- City │ Character of District │ Area, │Density
- │ │ Acres │per Acre
- ────────────┼────────────────────────────────────────┼────────┼────────
- Philadelphia│Thomas Run. Residential. Mostly pairs of│ │
- │ two and three-story houses. 1204 acres│ │
- │ settled. │ 1,840│ 59
- │Pine Street. Residential. Mostly solid │ │
- │ four to six-story houses. 156 acres │ │
- │ settled. │ 160│ 97
- │Shunk Street. Residential. Mostly pairs │ │
- │ of two and three-story houses. 539 │ │
- │ acres settled. │ 539│ 119
- │Lombard Street. Tenements and hotels, │ │
- │ 145 acres settled. │ 147│ 113
- │York Street. Residential and │ │
- │ manufacturing. 354 acres settled. │ 358│ 94
- │ │ │
- New York │Residential. Three-story dwellings with │ │
- City │ 18–foot frontage, and four-story flats│ │
- │ with 20–foot frontage. │ │ 100
- │Residential. Five-story flats. │ │520–670
- │Residential. Six-story flats. │ │800–1000
- │Residential. Six-story apartments. High │ │
- │ class. │ │ 300
- │ │ │
- Chicago │1st Ward. Retail and commercial. The │ │
- │ “Loop”. │ 1,440│ 20.5
- │2d Ward. Commercial and low-class │ │
- │ residential solidly built up. │ 800│ 53.5
- │3d Ward. Low-class residential. │ 960│ 48.1
- │5th Ward. Industrial. Some low-class │ │
- │ residences. Not solidly built up. │ 2,240│ 25.51
- │6th Ward. Residential. Four and │ │
- │ five-story apartments. A few detached │ │
- │ residences. │ 1,600│ 47.0
- │7th Ward. Same as Ward 6. Not solidly │ │
- │ built up. Contains a large park. │ 4,160│ 21.7
- │8th Ward. Industrial. Sparsely settled. │ 13,624│ 4.8
- │9th Ward. Industrial and low-class │ │
- │ residential. Solidly built up. │ 640│ 70.0
- │10th Ward. Same as Ward 9. │ 640│ 80.8
- │13th Ward. Low-class residential. │ │
- │ Solidly built with three and │ │
- │ four-story flats. │ 6,100│ 36.7
- │16th Ward. Middle-class residential. │ │
- │ Some industries. Well built up. │ 800│ 81.5
- │19th Ward. Industrial and commercial. │ │
- │ Some low-class residences. │ 640│ 90.7
- │20th Ward. Low-class residential. Some │ │
- │ industries. Entirely built up. │ 800│ 77.1
- │21st Ward. Industrial. Entirely built │ │
- │ up. │ 960│ 49.9
- │23d Ward. Industrial and residential. │ 800│ 55.4
- │24th Ward. Residential apartment houses │ │
- │ and middle-class residences. │ 1,120│ 46.8
- │25th Ward. Residential. High-class │ │
- │ apartments. Wealthy homes. Contains a │ │
- │ large park. │ 4,160│ 24.0
- │26th Ward. Residential. Middle-class │ │
- │ homes and apartments. Fairly well │ │
- │ built up. │ 4,640│ 16.1
- │27th Ward. Residential. Sparsely │ │
- │ settled. │ 20,480│ 5.5
- │29th Ward. Low-class residential. │ │
- │ Two-story frame houses. “Back of the │ │
- │ Yards”. │ 6,400│ 12.8
- │30th Ward. The Stock Yards. │ 1,280│ 40.1
- │32d Ward. Scattered residences. │ 8,480│ 8.3
- │33d Ward. Scattered residences. │ 12,944│ 5.5
- │35th Ward. Scattered residences. │ 4,960│ 12.0
- │ │ │
- General │The most crowded conditions with │ │
- average │ five-story and higher, contiguous │ │
- │ buildings in poor class districts. │ │750–1000
- │Five and six-story contiguous flat │ │
- │ buildings. │ │500–750
- │Six-story high-class apartments. │ │300–500
- │Three and four-story dwellings, business│ │
- │ blocks and industrial establishments. │ │
- │ Closely built up. │ │100–300
- │Separate residences, 50 to 75–foot │ │
- │ fronts, commercial districts, │ │
- │ moderately well built up. │ │ 50–100
- │Sparsely settled districts and scattered│ │
- │ frame dwellings for individual │ │
- │ families. │ │ 0–50
- ────────────┴────────────────────────────────────────┴────────┴────────
-
-The density of population in Cincinnati from 1850 to 1913 with
-predictions to 1950 is given in Fig. 9.[18] This shows the densities for
-the entire city and is illustrative of the manner in which future
-conditions were predicted for the design of an intercepting sewer. The
-data given in Table 5 are of value in estimating the densities of
-population in various districts. The Committee on City Plan of the Board
-of Estimate and Apportionment of New York City obtained some valuable
-information on this point, especially in Manhattan. Three-story
-dwellings with 18–foot frontage, or four-story flats with 20–foot
-frontage, presumably contiguous, were found to hold 100 persons to the
-acre. Five-story flats held 520 to 670 persons per acre. Six-story flats
-held 800 to 1,000 persons per acre, and high-class six-story apartments
-held less than 300 per acre.
-
-
-=22. Changes in Area.=—In order to determine the probable extent of a
-proposed sewerage system it is important to estimate the changes in the
-area of a city as well as the changes in the population. With the same
-population and an increased area the quantity of sewage will be
-increased because of the larger amount of ground water which will enter
-the sewers. Predictions of the area of a city are less accurate than
-predictions of population because the factors affecting changes cannot
-be so easily predicted. An area curve plotted against time would be
-helpful in guiding the judgment, but its extension into the future based
-on past occurrences would be futile. A knowledge of the city, its
-political tendencies, possibilities of extension, and other factors must
-be weighed and judged. The engineer, if he is ignorant of the city for
-which he is making provision, is dependent upon the testimony of real
-estate men, business men and others acquainted with the local situation.
-
-
-=23. Relation between Population and Sewage Flow.=—The amount of sewage
-discharged into a sewerage system is generally equal to the amount of
-water supplied to a community, exclusive of ground water. The entire
-public water supply does not reach the sewers, but the losses due to
-leakage, lawn sprinkling, manufacturing processes, etc., are made up by
-additions from private water supplies, surface drainage, etc. The
-estimated quantity of water used but which did not reach the sewers in
-Cincinnati is shown in Table 6. The amount shown represents 38 per cent
-of the total consumption. Unless direct observations have been made on
-existing sewers or other factors are known which will affect the
-relation between water supply and sewage, the average sewage flow
-exclusive of ground water, should be taken as the average rate of water
-consumption. Experience has shown that water consumption increases after
-the installation of sewers.
-
- TABLE 6
-
- ESTIMATED QUANTITY OF WATER USED BUT NOT DISCHARGED INTO THE SEWERS IN
- CINCINNATI
-
- Expressed in gallons per capita per day, and based on a total
- consumption of 125 to 150 gallons per capita per day.
-
- ──────────────────────────────────────────────────────────────┬────────
- Steam railroads. │6 to 7
- Street sprinklers. │6 to 7
- Consumers not sewered. │9 to 10½
- Manufacturing and mechanical. │6 to 7
- Lawn sprinklers. │3 to 3½
- Leakage. │18 to 21
- ──────────────────────────────────────────────────────────────┴────────
-
-The public water supply is generally installed before the sewerage
-system. By collecting statistics on the rate of supply of water a fair
-prediction can be made of the quantity of sewage which must be cared
-for. The rate of water supply varies widely in different cities. It is
-controlled by many factors such as meters, cost and availability of
-water, quality of water, climate, population, etc. In American cities a
-rough average of consumption is 100 gallons per capita per day. Other
-factors being equal the rate of consumption after meters have been
-installed will be about one-half the rate before the meters were
-installed. Low cost, good quantity and good quality will increase the
-rate of consumption, and the rate will increase slowly with increasing
-population. Statistics of rates of water consumption are given in Table
-7.
-
-
-=24. Character of District.=—The various sections of a city are
-classified as commercial, industrial, or residential. The residential
-districts can be subdivided into sparsely populated, moderately
-populated, crowded, wealthy, poor, etc. Commercial districts may be
-either retail stores, office buildings, or wholesale houses. Industrial
-districts may be either large factories, foundries, etc., or they may be
-made up of small industries housed in loft buildings.
-
-In cities of less than 30,000 population the refinement of such
-subdivisions is generally unnecessary in the study of sewage flow, all
-districts being considered the same. The data given in Tables 8 and 9
-indicate the difference to be found in different districts of large
-cities. The Milwaukee data are presented in a form available for
-estimates on different bases. These data are shown in Table 10.
-
- TABLE 7
-
- RATES OF WATER CONSUMPTION
-
- From Journals of American and New England Water Works Associations
- ───────────────────────────────────┬───────────┬───────────┬───────────
- City │Population │ Per Cent │Consumption,
- │ in │ Metered │ Gal. per
- │ Thousands │ │Capita per
- │ │ │ Day
- ───────────────────────────────────┼───────────┼───────────┼───────────
- Tacoma, Wash. │ 100 │ 11.6│ 460
- Buffalo, N. Y. │ 450 │ 4.9│ 310
- Cheyenne, Wyo. │ 13 │ │ 270
- Erie, Pa. │ 72 │ 3.0│ 198
- Philadelphia, Pa. │ 1611 │ 4.6│ 180
- St. Catherines, Ont. │ 17 │ 3.2│ 160
- Port Arthur, Ont. │ 18 │ 14.7│ 145
- Ogdensburg, N. Y. │ 18 │ 0.2│ 140
- Los Angeles, Cal. │ 516 │ 77.9│ 140
- Wilmington, Del. │ 92 │ 43.7│ 125
- Lancaster Pa. │ 60 │ 34.6│ 120
- Richmond, Va. │ 120 │ 75.2│ 115
- St. Louis, Mo. │ 730 │ 6.7│ 110
- Springfield, Mass. │ 100 │ 94.4│ 110
- Keokuk, Ia. │ 14 │ 64.5│ 105
- Jefferson City, Mo. │ 13.5│ 34.4│ 100
- Muncie, Ind. │ 30 │ 23.8│ 95
- Burlington, Ia. │ 24 │ 4.5│ 90
- Council Bluffs, Ia. │ 32 │ 75.5│ 80
- San Diego, Cal. │ 85 │ 100 │ 80
- Monroe, Wis. │ 3 │ 100 │ 80
- Yazoo City, Miss. │ 7 │ 84.1│ 75
- Oak Park, Illinois. │ 26 │ 100 │ 70
- Portsmouth, Va. │ 75 │ 8.1│ 65
- New Orleans, La. │ 360 │ 99.7│ 60
- Rockford, Ill. │ 53 │ 93.0│ 55
- Fort Dodge, Ia. │ 20 │ 96.0│ 50
- Manchester, Vt. │ 1.5│ 69.0│ 45
- Woonsocket, R. I. │ 47.5│ 95.6│ 35
- ───────────────────────────────────┴───────────┴───────────┴───────────
-
-Attempts have been made to express the rate of sewage flow in different
-units other than in gallons per capita per day. A unit in terms of
-gallons per square foot of floor area tributary has been suggested for
-commercial and industrial districts. It has not been generally adopted.
-The rates of flow in New York City as reported in this unit by W. S.
-McGrane are given in Table 11.
-
-The most successful way to predict the flow from commercial or
-industrial districts is to study the character of the district’s
-activities and to base the prediction on the quantity of water demanded
-by the commerce and industry of the district affected.
-
-
-=25. Fluctuations in Rate of Sewage Flow.=—The rate of flow of sewage
-from any district varies with the season of the year, the day of the
-week, and the hour of the day. The maximum and minimum rates of sewage
-flow are the controlling factors in the design of sewers. The sewers
-must be of sufficient capacity to carry the maximum load which may be
-put upon them, and they must be on such a grade that deposits will not
-occur during periods of minimum flow. The maximum and minimum rates of
-flow are usually expressed as percentages of the average rate of flow.
-
- TABLE 8
-
- SEWAGE FLOW FROM DIFFERENT CLASSES OF DISTRICTS
-
- Arranged from data by Kenneth Allen in Municipal Engineer’s Journal,
- Feb., 1918.
-
- ──────────────────────────────────────────────────────┬───────┬───────
- District │Gallons│Gallons
- │ per │ per
- │Capita │ Acre
- │per Day│per Day
- ──────────────────────────────────────────────────────┼───────┼───────
- Buffalo, N. Y. From Report of International Joint │ │
- Commission on the Pollution of Boundary Waters: │ │
- Industrial: Metal and automobile plants. Maximum. │ │ 13,000
- Industrial: Meat packing, chemical and soap. │ │ 16,000
- Commercial: Hotels, stores and office buildings. │ │ 60,000
- Domestic: Average. │ 80 │
- Domestic: Apartment houses. │ 147 │
- Domestic: First-class dwellings. │ 129 │
- Domestic: Middle-class dwellings. │ 81 │
- Domestic: Lowest-class dwellings. │ 35.5│
- │ │
- Cincinnati, Ohio. 1913 Report on Sewerage Plan: │ │
- Industrial, in addition to residential and ground │ │
- water. │ │ 9,000
- Commercial, in addition to residential and ground │ │
- water. │ │ 40,000
- Domestic. │ 135 │
- │ │
- Detroit, Mich.: │ │
- Domestic. │ 228 │
- Industrial, in addition to residential and ground │ │
- water. │ │ 12,000
- Commercial, in addition to residential and ground │ │
- water. │ │ 50,000
- │ │
- Milwaukee, Wis. 1915 Report of Sewerage Commission: │ │
- Industrial, maximum. │ 81 │ 16,600
- Industrial, average. │ 31 │ 8,300
- Commercial, maximum. │ │ 60,500
- Commercial, average. │ │ 37,400
- Wholesale commercial, maximum. │ │ 20,000
- Wholesale commercial, average. │ │ 9,650
- ──────────────────────────────────────────────────────┴───────┴───────
-
- TABLE 9
-
- OBSERVED WATER CONSUMPTION IN DIFFERENT CLASSES OF DISTRICTS IN NEW YORK CITY
-
- From data by Kenneth Allen in Municipal Engineers Journal, for 1918
- ─────────────┬─────────────┬──────────┬─────────────┬───────────┬─────────────
- Hotels │ Daily Cons. │Tenements │ Daily Cons. │Office and │ Daily Cons.
- │ Gals. per │ │ Gals. per │ Loft │ Gals. per
- │1000 Sq. Ft. │ │1000 Sq. Ft. │ Buildings │1000 Sq. Ft.
- │ Floor Area │ │ Floor Area │ │ Floor Area
- ─────────────┼────────┬────┼──────────┼────────┬────┼───────────┼────────┬────
- Building │Max.[19]│Avg.│ Location │Max.[19]│Avg.│ Building │Max.[19]│Avg.
- ─────────────┼────────┼────┼──────────┼────────┼────┼───────────┼────────┼────
- Hotel │ │ │78th–79th │ │ │McGraw │ │
- Biltmore. │ │ │ St. and │ │ │ Bldg. │ │
- │ 470 │368 │ B’way. │ 256 │192 │ │ 309 │206
- Hotel │ │ │410 E. │ │ │N. Y. │ │
- McAlpin. │ │ │ 65th St.│ │ │ Telephone│ │
- │ 753 │694 │ │ 350 │295 │ Bldg. │ │194
- Hotel Plaza. │ │ │30th St. │ │ │Met. Life │ │
- │ │ │ and │ │ │ Bldg. │ │
- │ │ │ Madison │ │ │ │ │
- │ 630 │578 │ Ave │ 306 │188 │ │ │256
- Hotel Waldorf│ │ │27 Lewis │ │ │42d St. │ │
- Astoria. │ 618 │482 │ St. │ 307 │250 │ Bldg │ │271
- Hotel Astor. │ │ │258 │ │ │Municipal │ │
- │ │ │ Delancey│ │ │ Bldg. │ │
- │ 732 │492 │ St. │ 267 │226 │ │ │118
- Hotel │ │ │ │ │ │Equitable │ │
- Vanderbilt.│ 604 │545 │ │ │ │ Bldg. │ 366 │268
- ─────────────┼────────┼────┼──────────┼────────┼────┼───────────┼────────┼────
- Average │ 634 │526 │ Average │ 297 │230 │ Average │ 338 │219
- ─────────────┴────────┴────┴──────────┴────────┴────┴───────────┴────────┴────
-
- TABLE 10
-
- SEWAGE FLOW FROM DIFFERENT CLASSES OF DISTRICTS BASED ON 1915 REPORT OF
- MILWAUKEE SEWERAGE COMMISSION
-
- ────────────────────────────────────────────────────────────────┬──────
- Ratio of maximum to average rate for department store district. │ 1.755
- Ratio of maximum to average rate for hotel district. │ 1.65
- Ratio of maximum to average rate for office building district. │ 1.51
- Ratio of maximum to average rate for wholesale commercial │
- district. │ 2.1
- │
- │——————│——————
- Average and maximum gallons per thousand square feet of │ │
- floor area: │ Avg. │ Max.
- │——————│——————
- For department store district. │ 232│ 407
- For office building district. │ 541│ 891
- For wholesale commercial district. │ 164│ 344
- For all districts except wholesale commercial. │ 381│ 618
- │ │
- Average and maximum gallons per day: │ │
- For all districts except wholesale commercial. │17,700│29,800
- For wholesale commercial district. │ 9,650│20,000
- ─────────────────────────────────────────────────────────┴──────┴──────
-
- TABLE 11
-
- RATES OF CONSUMPTION PREDICTED FOR DIFFERENT DISTRICTS IN NEW YORK CITY
-
- ────────────┬───────────┬──────┬────────┬────────┬─────────
- │ Net Bldg. │ │Observed│Observed│
- │Area in Sq.│ Avg. │Cons. in│Cons. in│Predicted
- District │ Ft. per │Number│ g.p.d. │ g.p.d. │ Mean
- │ Acre for │ of │per 1000│per 1000│ Cons.
- │ Ultimate │Floors│Sq. Ft. │Sq. Ft. │
- │Consumption│ │ Max. │ Avg. │
- ────────────┼───────────┼──────┼────────┼────────┼─────────
- Hotel and │ 24,800│ 15│ 634│ 526│ 500
- midtown. │ │ │ │ │
- Midtown and │ 24,800│ 15│ 338│ 219│ 300
- financial.│ │ │ │ │
- East and │ │ │ │ │
- West of │ 24,800│ 10│ 297│ 230│ 300
- midtown. │ │ │ │ │
- Apartment, │ │ │ │ │
- 59th to │ 20,400│ 7│ │ 230│ 300
- 155th Sts.│ │ │ │ │
- Manhattan │ │ │ │ │
- north of │ 20,400│ 5│ │ 230│ 300
- 155th St. │ │ │ │ │
- ────────────┴───────────┴──────┴────────┴────────┴─────────
-
- ────────────┬─────────┬─────────┬─────────┬────────┬────────
- │Predicted│Predicted│Predicted│Measured│Measured
- │ Mean in │ Dry │Max. Dry │Avg. Dry│Max. Dry
- District │ Million │ Weather │ Weather │Weather │Weather
- │Gals. per│ Flow, │ Flow, │ Flow, │ Flow,
- │Acre per │ c.f.s. │ c.f.s. │ c.f.s. │ c.f.s.
- │ Day │per Acre │per Acre │per Acre│per Acre
- ────────────┼─────────┼─────────┼─────────┼────────┼────────
- Hotel and │ .20 │ .29│ .34│ 1.04 │ .146
- midtown. │ │ │ │ │
- Midtown and │ .12 │ .18│ .23│ .078│ .110
- financial.│ │ │ │ │
- East and │ │ │ │ │
- West of │ .074│ .12│ .15│ .057│ .097
- midtown. │ │ │ │ │
- Apartment, │ │ │ │ │
- 59th to │ .043│ .06│ .09│ │
- 155th Sts.│ │ │ │ │
- Manhattan │ │ │ │ │
- north of │ .031│ .05│ .08│ │
- 155th St. │ │ │ │ │
- ────────────┴─────────┴─────────┴─────────┴────────┴────────
-
-Midtown district consists of department stores, large railroad
-terminals, industrial and loft buildings, and sky-scraper office
-buildings.
-
-It is difficult to set any definite figure for the percentage which the
-maximum rate of flow is of the average. Fluctuations above and below the
-average are greater the smaller the tributary population. This relation
-can be expressed empirically as
-
- _M_ = 500⁄_P_^⅕,
-
-in which _M_ represents the per cent which the maximum flow is of the
-average, and _P_ represents the tributary population in thousands. The
-expression should not be used for populations below 1,000 nor above
-1,000,000. Having determined the expected average flow of sewage by a
-study of the population, water consumption, etc., the maximum quantity
-of sewage is determined by multiplying the average flow by the per cent
-which the maximum is of the average. In this connection W. G. Harmon[20]
-offers the relation
-
- _M_ = 1 + 14⁄(4 + √(_P_)),
-
-which was used in the design of the Ten Mile Creek intercepting sewer at
-Toledo, Ohio. For rough estimates and for comparative purposes the ratio
-of the average to the minimum flow can be taken the same as the ratio of
-the maximum to the average flow, unless direct gaugings or other
-information show it to be otherwise.
-
-[Illustration:
-
- Fig. 10.—Daily and Hourly Variations of Sewage Flow.
-]
-
- 1. Toledo, O.; Manufacturing average.
-
- 2. Toledo, O.; Manufacturing, Monday.
-
- 3. Toledo, O.; Manufacturing, Sunday.
-
- 4. Toledo, O.; Residential, average.
-
- 5. Toledo, O.; Residential, Monday.
-
- 6. Toledo, O.; Residential, Sunday.
-
- 7. Cincinnati, O., Industrial, average.
-
- 8. Cincinnati, O.; Residential, average.
-
- 9. Cincinnati, O.; Commercial, average.
-
- 10. Average of 7 cities.
-
-The fluctuations of flow in commercial and industrial districts are so
-different from those in residential districts that the formulas given
-should not be used in the design of sewers other than those draining
-residential areas. It is reasonable to suppose that fluctuations in
-rates of flow from industrial districts are dependent upon the character
-of the tributary industries. A study of these industries will give
-valuable light on the maximum and minimum rates at which sewage will be
-delivered to the sewers.
-
-Hourly, daily, and seasonal fluctuations in rates of sewage flow are of
-interest in the design of pumping stations to give knowledge of the
-rates at which the pumps must operate at various periods. The
-fluctuations in rates of sewage flow during various hours and days in
-different cities and districts are shown in Fig. 10. Fluctuations in
-rate of flow of sewage lag behind fluctuations in rate of water
-consumption, the time being dependent on the distance through which the
-wave of change must travel in the sewer.
-
-
-=26. Effect of Ground Water.=—Sewers are seldom laid with water-tight
-joints. Since they usually lie below the ground water level it is
-inevitable that a certain amount of ground water will enter. Various
-units have been suggested for the expression of the inflow of ground
-water in an attempt to include all of the many factors. Some of these
-units are: gallons per acre drained by the sewer per day, gallons per
-mile of pipe per day, gallons per inch diameter per mile of pipe per
-day, etc. Since the ground water enters pipe sewers at the joints, the
-longer the joints the greater the probability of the entrance of ground
-water. The last unit is therefore the most logical but the accuracy of
-the result is scarcely worthy of such refinement and the unit usually
-adopted is gallons per mile of pipe per day.
-
-No definite figure can be given for the amount of ground water to be
-expected in sewers since the character of the soil and the ground water
-pressure must be considered. Relatively normal infiltration may be found
-from 5,000 to 80,000 gallons per mile of pipe per day. The minimum is
-seldom reached in wet ground and the maximum is frequently exceeded.
-Table 12 shows the amount of ground water measured in various sewers as
-given by Brooks.[21]
-
-
-=27. Résumé of Method for Determination of Quantity of Dry weather
-Sewage.=—The steps in the determination of the quantity of sewage are:
-determine the period in the future for which the sewers are to be
-designed; estimate the population and tributary area at the end of this
-period; estimate the rate of water consumption and assume the sewage
-flow to equal the water consumption; determine the maximum and minimum
-rates of sewage flow; and finally, estimate the maximum rate of ground
-water seepage and add it to the maximum rate of sewage flow to give the
-total quantity of sewage to be carried by the proposed sewers.
-
- TABLE 12
-
- DATA ON THE INFILTRATION OF GROUND WATER INTO SEWERS
-
- Abstracted from paper by J. N. Brooks in Transactions Am. Society of Civil
- Engineers, Vol. 76, p. 1909.
- ───────────┬─────┬──────┬─────┬───────┬──────┬─────┬──────────────────────
- Place │ │Diam- │ │ │ │ │
- │ │ eter │ │ Wet │ Avg. │ │
- │ │ or │ │Trench,│ Head │Char-│
- │ │Dimen-│ │ Per │ of │acter│
- │ │sions │ │Cent of│Ground│ of │
- │ │ in │Mate-│ Total │Water,│Sub- │
- │Shape│Inches│rial │Length │ Fee │grade│ Gallons per 24 Hours
- ───────────┼─────┼──────┼─────┼───────┼──────┼─────┼─────┬──────┬─────────
- │ │ │ │ │ │ │ │ Per │
- │ │ │ │ │ │ │ │ Inch │
- │ │ │ │ │ │ │ │Diam- │
- │ │ │ │ │ │ │ │ eter │
- │ │ │ │ │ │ │ Per │ Per │
- │ │ │ │ │ │ │Foot │ Mile │
- │ │ │ │ │ │ │ of │ of │Per Mile
- │ │ │ │ │ │ │Joint│ Pipe │ of Pipe
- ───────────┼─────┼──────┼─────┼───────┼──────┼─────┼─────┼──────┼─────────
- Boston, │ │ 8 to │ │ │ │ │ │ │
- Mass. │Circ.│ 36 │V.P. │ │ │ │ 2.6│ 1,818│ 40,000
- East │ │ │ │ │ │ │ │ │
- Orange, │ │ │ │ │ │ │ │ │
- N. J. │ │ │ │ │ 10│ Q. │ │ │ 22,400
- East │ │ │ │ │ │ │ │ │
- Orange, │ │ 8 to │ │ │ │ │ │ │
- N. J. │ │ 24 │V.P. │ │ │ │ 0.8│ 540│ 8,650
- Joint trunk│ │ │ │ │ │ │ │ │
- sewer, │ │ │ │ │ │ │ │ │
- New │ │ │ │ │ │G. & │ │ │
- Jersey │ │ │ │ │ │ Q. │ │ │ 25,000
- Rogers │ │ │ │ │ │ │ │ │
- Park, │ │ │ │ │ │ │ │ │
- Ill. │ │ 6 │ │ │ │ │ 0.3│ 207│ 1,240
- Altoona, │ │ │ │ │ │ │ │ │
- Pa. │ │ 30 │ │ │ │ │ 5.0│ 2,890│ 86,592
- Concord, │ │ │ │ │ │ │ │ │
- Mass. │ │ │ │ 18│ 8│ │ │ │ 43,000
- Malden, │ │ │ │ │ │ │ │ │
- Mass. │Circ.│ │V.P. │ 60│ │ │ │ │ 50,000
- Westboro, │ │ │ │ │ │ │ │ │
- Mass. │ │ 15 │V.P. │ 100│ │ │ │88,100│1,320,300
- Fond du │ │ │ │ │ │ │ │ │
- Lac, Wis.│Circ.│ 24 │V.P. │ 100│ 5│ C. │ 1.5│ 1,010│ 24,370
- East │ │ │ │ │ │ │ │ │
- Orange, │ │10 to │ │ │ │ │ │ │
- N. J. │Circ.│ 24 │V.P. │ 100│ │ │ 4.7│ 2,540│ 43,250
- Ocean │ │ │ │ │ │ │ │ │
- Grove, N.│ │ 4 to │ │ │ │ │ │ │
- J. │Circ.│ 12 │V.P. │ 100│ 3│S.C. │ 2.7│ 1,890│ 15,126
- Ocean │ │ │ │ │ │ │ │ │
- Grove, N.│ │ 4 to │ │ │ │ │ │ │
- J. │Circ.│ 12 │V.P. │ 100│ 4│S.C. │ 7.9│ 5,480│ 43,764
- East │ │ │ │ │ │ │ │ │
- Orange, │ │ 24 × │ │ │ │ │ │ │
- N. J. │Rect.│ 36 │Brick│ 100│ │ │ │ │ 570,000
- Westboro, │ │ │ │ │ │ │ │ │
- Mass. │ │ │Brick│ │ │ │ │ │ 415,850
- Altoona, │ │ 33 × │B. & │ │ │ │ │ │
- Pa. │Rect.│ 44 │ C. │ │ │ │ │ 5,390│ 264,000
- Columbus, │ │ 42 × │Con- │ │ │ │ │ │
- Ohio. │H.S. │ 42 │crete│ │ │ │ │ 120│ 6,340
- Bronx │ │ │ │ │ │ │ │ │
- Valley, │ │44 to │Con- │ │ │ │ │ │
- N. Y. │Circ.│ 72 │crete│ │ │ G. │ │ 123│ 7,266
- Cincinnati,│ Estimated in design. Data not │ │ │ │
- Ohio. │ from Brooks │ │ │ │ 67,500
- Milwaukee, │ Residential districts, gals. per acre per │ │ 1460 to
- Wis. │ day. Not taken from Brooks │ │ 2200
- ───────────┴─────────────────────────────────────────────┴──────┴─────────
-
- Abbreviations: H.S. = horseshoe shaped; B. & C = Brick and concrete; V.P.
- = vitrified pipe; G. = gravel; Q. = quicksand; S. C. = sand clay; C. =
- clay.
-
-
- QUANTITY OF STORM WATER
-
-
-=28. The Rational Method.=—The water which falls during a storm must be
-removed rapidly in order to prevent the flooding of streets and
-basements, and other damages. The quantity of water to be cared for is
-dependent upon: the rate of rainfall, the character and slope of the
-surface, and the area to be drained. All methods for the determination
-of storm-water run-off, whether rational or empirical, depend upon these
-factors.
-
-The so-called Rational Method can be expressed algebraically, as,
-
- _Q_ = _AIR_,
-
- in which _Q_ = rate of run-off in cubic feet per second;
-
- _A_ = area to be drained expressed in acres;
-
- _I_ = percentage imperviousness of the area;
-
- _R_ = maximum average rate of rainfall over the entire
- drainage area, expressed in inches per hour, which
- may occur during the time of concentration.
-
-The area to be drained is determined by a survey. A discussion of _R_
-and _I_ follows in the next two sections. An example of the use of the
-Rational Method is given on page 95.
-
-
-=29. Rate of Rainfall.=—Rainfall observations have been made over a long
-period of time by United States Weather Bureau observers and others.
-Continuous records are available in a few places in this country showing
-rainfall observations covering more than a century. Such records have
-been the bases for a number of empirical formulas for expressing the
-probable maximum rate of rainfall in inches per hour, having given the
-duration of the storm. Table 13 is a collection of these formulas with a
-statement as to the conditions under which each formula is applicable.
-The formula most suitable to the problem in hand should be selected for
-its solution.[22]
-
- TABLE 13
-
- RAINFALL FORMULAS
-
- ────────────┬─────────────────────────┬────────────────────────────────
- Name of │ Conditions for which │ Formula
- Originator │ Formula is Suitable │
- ────────────┼─────────────────────────┼────────────────────────────────
- E. S. Dorr │ │_i_ = 150⁄(_t_ + 30)
- A. N. Talbot│Maximum storms in Eastern│_i_ = 360⁄(_t_ + 30)
- │ United States │
- A. N. Talbot│Ordinary storms in │_i_ = 105⁄(_t_ + 15)
- │ Eastern United States │
- Emil │Heavy rainfall near New │_i_ = 120⁄(_t_ + 20), etc.
- Kuichling │ York City │
- L. J. Le │For San Francisco. See T.│
- Conte │ A. S. C. E. v. 54, p. │_i_ = 7⁄_t_^½
- │ 198 │
- Sherman │Maximum for Boston, Mass.│_i_ = 25.12⁄_t_^{.687}
- Sherman │Extraordinary for Boston,│_i_ = 18⁄_t_ ^½
- │ Mass. │
- Webster │Ordinary for │_i_ = 12⁄_t_^{0.6}
- │ Philadelphia, Pa. │
- │Ordinary storms for │
- Hendrick │ Baltimore. Eng. & │_i_ = 105⁄(_t_ + 10)
- │ Cont., Aug. 9. 1911 │
- J. de │Ordinary storms for │_i_ = 163⁄(_t_ + 27)
- Bruyn-Kops│ Savannah, Ga. │
- C. D. Hill │For Chicago, Ill. │_i_ = 120⁄(_t_ + 15)
- Metcalf and │Louisville, Ky. Am. Sew. │_i_ = 14⁄_t_^½
- Eddy │ Prac., Vol I. │
- W. W. Horner│St. Louis, Mo. Eng. News,│_i_ = 56⁄(_t_ + 5)^{.85}
- │ Sept. 29, 1910 │
- R. A. │For Spokane, Wash. Eng. │_i_ = 23.92⁄(_t_ + 2.15) + 0.154
- Brackenbuy│ Record, Aug. 10, 1912 │
- Metcalf and │New Orleans │_i_ = 19⁄_t_^½
- Eddy │ │
- Metcalf and │For Denver, Colo. │_i_ = 84⁄(_t_ + 4)
- Eddy │ │
- │Central Park, N. Y. │
- Kenneth │ 51–Year Record. Eng. │_i_ = 400⁄(2_t_ + 40)[23]
- Allen │ News-Record, April 7, │
- │ 1921, p. 588 │
- ────────────┴─────────────────────────┴────────────────────────────────
-
-
-=30. Time of Concentration.=—By the time of concentration is meant the
-longest time without unreasonable delay that will be required for a drop
-of water[24] to flow from the upper limit of a drainage area to the
-outlet. Assuming a rainfall to start suddenly and to continue at a
-constant rate and to be evenly distributed over a drainage area of 100
-per cent imperviousness and even slope towards one point, the rate of
-run-off would increase constantly until the drop of water from the upper
-limit of the area reached the outlet, after which the rate of run-off
-would remain constant. In nature the rate of rainfall is not constant.
-The shorter the duration of a storm the greater the intensity of
-rainfall. Therefore the maximum run-off during a storm will occur at the
-moment when the upper limit of the area has commenced to contribute.
-From that time on the rate of run-off will decrease.
-
-The time of concentration can be measured fairly well by observing the
-moment of the commencement of a rainfall, and the time of maximum
-run-off from an area on which the rain is falling. A prediction of the
-time of concentration is more or less guess work. As the result of
-measurements some engineers assume the time of concentration on a city
-block built up with impervious roofs and walks, and on a moderate slope,
-is about 5 to 10 minutes. This is used as a basis for the judgment of
-the time of concentration on other areas. For relatively large drainage
-areas such a method cannot be used. The procedure is to measure the
-length of flow through the drainage channels of the area, to assume the
-velocity of the flood crest through these channels and thus to determine
-the time of concentration. Table 14 shows the flood crest velocities in
-various streams of the Ohio River Basin under flood conditions. The
-velocity over the surface of the ground may be approximated by the use
-of the formula[25]
-
- _V_ = 2,000_I_√(_S_),
-
- in which _V_ = the velocity of flow over the surface of the ground in
- feet per minute;
-
- _I_ = the percentage imperviousness of the ground;
-
- _S_ = the slope of the ground.
-
-For areas up to 100 acres where natural drainage channels are not
-existent this formula will give more satisfactory results than guesses
-based on the time of concentration of certain known areas.
-
-Having determined the time of concentration, the rate of rainfall _R_ to
-be used in the Rational Method is found by substitution in some one of
-the rainfall formulas given in Table 13.
-
- TABLE 14
-
- FLOOD CREST VELOCITIES IN OHIO RIVER BASIN IN MARCH, 1913
-
- From Table 12. U. S. G. S., Water Supply Paper. No. 334
- ───────────┬───────────────┬────────┬────────┬───────────────┬─────────┬───────────┬────────
- River │ Stations │ │Distance│ Distance of │Velocity │ Velocity │
- │ │Distance│to Mouth│ Lower Station │ between │ from │ Time
- │ │between │ of │ below │Stations,│Pittsburgh,│between
- │ │Stations│ River, │Starting-point,│Miles per│ Miles per │Stations
- │ │in Miles│ Miles │ Miles │ Hour │ Hour │in Hours
- ───────────┼───────────────┼────────┼────────┼───────────────┼─────────┼───────────┼────────
- Ohio │Pittsburgh, │ │ │ │ │ │
- │ Pa., to │ │ │ │ │ │
- │ Wheeling, W. │ │ │ │ │ │
- │ Va. │ 90│ 967│ 90│ 9.0│ 9.0│ 10.0
- Ohio │Wheeling, W. │ │ │ │ │ │
- │ Va., to │ │ │ │ │ │
- │ Marietta, │ │ │ │ │ │
- │ Ohio │ 82│ 877│ 172│ 5.9│ 7.2│ 14
- Ohio │Marietta, Ohio,│ │ │ │ │ │
- │ to │ │ │ │ │ │
- │ Parkersburg, │ │ │ │ │ │
- │ W. Va. │ 12│ 795│ 184│ 0.9│ 4.8│ 14
- Ohio │Parkersburg to │ │ │ │ │ │
- │ Point │ │ │ │ │ │
- │ Pleasant, W. │ │ │ │ │ │
- │ Va. │ 80│ 783│ 264│ 6.7│ 5.3│ 12
- Ohio │Point Pleasant │ │ │ │ │ │
- │ to │ │ │ │ │ │
- │ Huntington, │ │ │ │ │ │
- │ W. Va. │ 44│ 703│ 308│ 11.0│ 5.7│ 4
- Ohio │Huntington to │ │ │ │ │ │
- │ Catlettsburg,│ │ │ │ │ │
- │ W. Va. │ 9│ 659│ 317│ 0.8│ 4.1│ 11
- Ohio │Catlettsburg, │ │ │ │ │ │
- │ W. Va., to │ │ │ │ │ │
- │ Portsmouth, │ │ │ │ │ │
- │ Ohio │ 38│ 650│ 355│ │ 5.0│
- Ohio │Portsmouth │ │ │ │ │ │
- │ Ohio, to │ │ │ │ │ │
- │ Maysville, │ │ │ │ │ │
- │ Ky. │ 52│ 612│ 407│ 5.2│ 5.0│ 10
- Ohio │Maysville, Ky.,│ │ │ │ │ │
- │ to │ │ │ │ │ │
- │ Cincinnati, │ │ │ │ │ │
- │ Ohio │ 61│ 560│ 468│ 6.8│ 5.2│ 9
- Ohio │Cincinnati, │ │ │ │ │ │
- │ Ohio, to │ │ │ │ │ │
- │ Louisville, │ │ │ │ │ │
- │ Ky. │ 136│ 499│ 604│ 11.4│ 5.9│ 12
- Ohio │Louisville, │ │ │ │ │ │
- │ Ky., to │ │ │ │ │ │
- │ Evansville, │ │ │ │ │ │
- │ Ind. │ 183│ 363│ 787│ 1.9│ 5.3│ 96
- Ohio │Evansville, │ │ │ │ │ │
- │ Ind., to Mt. │ │ │ │ │ │
- │ Vernon Ind. │ 36│ 180│ 823│ 9.0│ 5.3│ 4
- Ohio │Mt. Vernon, │ │ │ │ │ │
- │ Ind., to │ │ │ │ │ │
- │ Paducah, Ky.│ 101│ 144│ 924│ 2.1│ 4.6│ 48
- Ohio │Paducah, Ky. to│ │ │ │ │ │
- │ Cairo, Ill. │ 43│ 43│ 967│ 2.9│ 4.2│ 15
- Monongahela│Fairmont, W. │ │ │ │ │ │
- │ Va., to Lock │ │ │ │ │ │
- │ No. 2 Pa. │ │ │ │ │ │
- │ (Upper) │ 107│ 119│ 107│ 6.7│ │ 16
- Little │Creston, W. │ │ │ │ │ │
- Kanawha │ Va., to Dam. │ │ │ │ │ │
- │ No. 4 W. Va. │ │ │ │ │ │
- │ (Upper) │ 16│ 48│ 16│ 16.0│ │ 1
- New │Radford, W. │ │ │ │ │ │
- │ Va., to │ │ │ │ │ │
- │ Hinton, W. │ │ │ │ │ │
- │ Va. │ 78│ 139│ 78│ 3.0│ │ 26
- Kanawha │Kanawha Falls, │ │ │ │ │ │
- │ W. Va. to │ │ │ │ │ │
- │ Charleston, │ │ │ │ │ │
- │ W. Va. │ 37│ 95│ 37│ 2.6│ │ 14
- Scioto │Columbus, Ohio,│ │ │ │ │ │
- │ to │ │ │ │ │ │
- │ Chillicothe, │ │ │ │ │ │
- │ Ohio │ 52│ 110│ 52│ 4.7│ │ 11
- Miami │Dayton, Ohio, │ │ │ │ │ │
- │ to Hamilton, │ │ │ │ │ │
- │ Ohio │ 44│ 77│ 44│ 14.7│ │ 3
- Kentucky │Highbridge, │ │ │ │ │ │
- │ Ky., to │ │ │ │ │ │
- │ Frankfort, │ │ │ │ │ │
- │ Ky. │ 52│ 117│ 52│ 5.2│ │ 10
- Cumberland │Celina, Tenn. │ │ │ │ │ │
- │ to Nashville,│ │ │ │ │ │
- │ Tenn. │ 190│ 383│ 190│ 2.9│ │ 64.5
- Tennessee │Knoxville to │ │ │ │ │ │
- │ Chattanooga, │ │ │ │ │ │
- │ Tenn. │ 183│ 635│ 183│ 3.2│ │ 57
- ───────────┴───────────────┴────────┴────────┴───────────────┴─────────┴───────────┴────────
- NOTE.—The velocities shown are the velocities of the crest of the flood wave and are not the
- average velocity of the flow of the river. The velocity of the crest of the flood wave
- should be used in determining the time of concentration. The flood crest velocity is slower
- then that of the river because of the storage in the river basin.
-
-
-=31. Character of Surface.=—The proportion of total rainfall which will
-reach the sewers depends on the relative porosity, or imperviousness,
-and the slope of the surface. Absolutely impervious surfaces such as
-asphalt pavements or roofs of buildings will give nearly 100 per cent
-run-off regardless of the slope, after the surfaces have become
-thoroughly wet. For unpaved streets, lawns, and gardens the steeper the
-slope the greater the per cent of run-off. When the ground is already
-water soaked or is frozen the per cent of run-off is high, and in the
-event of a warm rain on snow covered or frozen ground, the run-off may
-be greater than the rainfall. The run-off during the flood of March,
-1913, at Columbus, Ohio, was over 100 per cent of the rainfall. Table
-15[26] shows the relative imperviousness of various types of surfaces
-when dry and on low slopes. The estimates for relative imperviousness
-used in the design of the Cincinnati intercepter are given in Table 16.
-
- TABLE 15
-
- VALUES OF RELATIVE IMPERVIOUSNESS
-
- Roof surfaces assumed to be water-tight 0.70– 0.95
- Asphalt pavements in good order .85– .90
- Stone, brick, and wood-block pavements with tightly cemented
- joints .75– .85
- The same with open or uncemented joints .50– .70
- Inferior block pavements with open joints .40– .50
- Macadamized roadways .25– .60
- Gravel roadways and walks .15– .30
- Unpaved surfaces, railroad yards, and vacant lots .10– .30
- Parks, gardens, lawns, and meadows, depending on surface
- slope and character of subsoil .05– .25
- Wooded areas or forest land, depending on surface slope and
- character of subsoil .01– .20
- Most densely populated or built up portion of a city .70– .90
-
- TABLE 16
-
- COEFFICIENTS OF IMPERVIOUSNESS USED IN THE DESIGN OF THE CINCINNATI SEWERS
-
- ──────────────┬─────────────────────────────┬──────────────────┬───────────
- Character of │ │ │Residential,
- Improvement │ │ │291.1 A. 20
- │ │ │ per Acre,
- │ │ │ Middle
- │ │ │ Class,
- │ │ │ Detached
- │ │ │Dwellings,
- │ │ │Yellow and
- │ │Combined Tenement │ Blue Clay
- │ │ and Industrial. │ Overlying
- │Typical Commercial Area, 30.4│ 35.6 A., 55 per │ Beds of
- │A. None Undeveloped. Sand and│ Acre. Clay, Sand │ Shale and
- │ Gravel │ and Gravel │ Sandstone
- ──────────────┼──────┬─────┬─────┬──────────┼──────┬─────┬─────┼─────┬─────
- │ Area │ │ │Equivalent│ Area │ │ │ Per │
- │ in │ Per │ │Imp. Area,│ in │ Per │ │Cent │
- │1000’s│Cent │ I, │ 1000’s │1000’s│Cent │ I, │ of │ I,
- │Square│Total│Esti-│ Square │Square│Total│Esti-│Total│Esti-
- │ Feet │Area │mated│ Feet │ Feet │Area │mated│Area │mated
- ──────────────┼──────┼─────┼─────┼──────────┼──────┼─────┼─────┼─────┼─────
- Roofs: │ │ │ │ │ │ │ │ │
- Public and │ │ │ │ │ │ │ │ │
- commercial│ 881.2│ 66.5│ 0.90│ 793.0│ 66.8│ 4.3│ 0.40│ 4.8│ 0.40
- Residences │ │ │ │ │ 289.2│ 18.6│ .90│ 13.1│ .90
- Barns and │ │ │ │ │ │ │ │ │
- sheds │ │ │ │ │ 79.2│ 5.1│ .75│ 1.4│ .75
- │ │ │ │ │ │ │ │ │
- Interior │ │ │ │ │ │ │ │ │
- Walks: │ │ │ │ │ │ │ │ │
- Brick │ 7.5│ 0.6│ .40│ 3.0│ 35.6│ 2.3│ .40│ 0.6│ .40
- Cement │ 10.0│ 0.7│ .75│ 7.5│ 22.6│ 1.5│ .75│ 2.6│ .75
- │ │ │ │ │ │ │ │ │
- Street Walks: │ │ │ │ │ │ │ │ │
- Brick │ 6.1│ 0.5│ .40│ 2.4│ 48.2│ 3.1│ .40│ 1.0│ .40
- Cement │ 139.3│ 10.5│ .75│ 104.5│ 78.1│ 5.0│ .75│ 3.4│ .75
- │ │ │ │ │ │ │ │ │
- Street │ │ │ │ │ │ │ │ │
- Pavements: │ │ │ │ │ │ │ │ │
- Asphalt, │ │ │ │ │ │ │ │ │
- brick, │ │ │ │ │ │ │ │ │
- wood block│ 145.5│ 11.0│ .85│ 123.7│ │ │ │ 5.0│ .85
- Granite │ │ │ │ │ │ │ │ │
- block │ 111.4│ 8.4│ .75│ 83.6│ │ │ │ 1.0│ .75
- Macadam and │ │ │ │ │ │ │ │ │
- cobble │ 23.2│ 1.8│ .40│ 9.3│ 238.6│ 15.4│ .40│ 4.8│ .40
- Granite and │ │ │ │ │ │ │ │ │
- poor │ │ │ │ │ │ │ │ │
- macadam │ │ │ │ │ │ │ │ 0.4│ .20
- │ │ │ │ │ │ │ │ │
- Unimproved │ │ │ │ │ │ │ │ │
- yards and │ │ │ │ │ │ │ │ │
- lawns: │ │ │ │ │ 692.4│ 44.7│ .15│ │
- Tributary to│ │ │ │ │ │ │ │ │
- paved │ │ │ │ │ │ │ │ │
- gutters │ │ │ │ │ │ │ │ 57.1│ .15
- Not │ │ │ │ │ │ │ │ │
- tributary │ │ │ │ │ │ │ │ │
- to paved │ │ │ │ │ │ │ │ │
- gutters │ │ │ │ │ │ │ │ 7.9│ .10
- ──────────────┼──────┼─────┼─────┼──────────┼──────┼─────┼─────┼─────┼─────
- Total │1324.2│100.0│ │ 1127.0│1550.7│100.0│ │100.0│
- ──────────────┼──────┴─────┴─────┴──────────┼──────┴─────┴─────┼─────┴─────
- Impervious │ │ │
- coefficient │ │ │
- for the │ │ │
- district │ 85.1 │ 44.4 │ 35.9
- ──────────────┴─────────────────────────────┴──────────────────┴───────────
-
-C. E. Gregory[27] states that _I_, in the expression _Q_ = _AIR_ is a
-function of the time of concentration or the duration of the storm. If
-_t_ represents the time of concentration and _T_ represents the duration
-of the storm, then when _T_ is less than _t_
-
- _I_ = 0.175_t_^⅓,
-
-but when _T_ is greater than _t_,
-
- _I_ = 0.175⁄_t_(_T_^{4/3} − (_T_ − _t_)^{4/3}).
-
-Gregory condenses Kuichling’s rules with regard to the per cent run-off,
-as follows:
-
- 1. The per cent of rainfall discharged from any given drainage
- area is nearly constant for heavy rains lasting equal periods of
- time.
-
- 2. This per cent varies directly with the area of impervious
- surface.
-
- 3. This per cent increases rapidly and directly or uniformly with
- the duration of the maximum intensity of the rainfall until a
- period is reached which is equal to the time required for the
- concentration of the drainage waters from the entire area at the
- point of observation, but if the rainfall continues at the same
- intensity for a longer period this per cent will continue to
- increase at a much smaller rate.
-
- 4. This per cent becomes larger when a moderate rain has
- immediately preceded a heavy shower on a partially permeable
- territory.
-
-Gregory’s formulas have not been generally accepted and are not widely
-used in practice. Marston stated:[28]
-
- All that engineers are at present, warranted in doing is to make
- some deduction from 100 per cent run-off ... the deduction ...
- being at present left to the engineer in view of his general
- knowledge and his familiarity with local conditions.
-
-Burger states[29] in the same connection:
-
- In its application there will usually be as many results
- (differing widely from each other) as the number of men using it.
-
-In spite of these objections the Rational Method is in more favor with
-engineers than any other method.
-
-
-=32. Empirical Formulas.=—The difficulty of determining run-off with
-accuracy has led to the production by engineers of many empirical
-formulas for their own use. Some of these formulas have attracted wide
-attention and have been used extensively, in some cases under conditions
-to which they are not applicable. In general these formulas are
-expressions for the run-off in terms of the area drained, the relative
-imperviousness, the slope of the land, and the rate of rainfall.
-
-The Burkli-Ziegler formula, devised by a Swiss engineer for Swiss
-conditions and introduced into the United States by Rudolph Hering, was
-one of the earliest of the empirical formulas to attract attention in
-this country. It has been used extensively in the form
-
- _Q_ = _CiA_∜(_S_⁄_A_),
-
- in which_Q_ = the run-off in cubic feet per second;
-
- _i_ = the maximum rate of rainfall in inches per hour over
- the entire area. This is determined only by
- experience in the particular locality, and is usually
- taken at from 1 to 3 inches per hour;
-
- _S_ = the slope of the ground surface in feet per thousand,
-
- _A_ = the area in acres;
-
- _C_ = an expression for the character of the ground surface,
- or relative imperviousness. In this form of the
- expression _C_ is recommended as 0.7.
-
-The McMath formula was developed for St. Louis conditions and was first
-published in Transactions of the American Society of Civil Engineers,
-Vol. 16, 1887, p. 183. Using the same notation as above, the formula is,
-
- _Q_ = _CiA_⁵√(_S_⁄_A_),
-
-McMath recommended the use of _C_ equal to 0.75, _i_ as 2.75 inches per
-hour, and _S_ equal to 15. The formula has been extended for use with
-all values of _C_, _i_, _S_, and _A_ ordinarily met in sewerage
-practice. Fig. 11 is presented as an aid to the rapid solution of the
-formula.
-
-[Illustration:
-
- FIG. 11.—Diagram for the Solution of McMath’s Formula,
- _Q_ = _Aci_⁵√_S_⁄_A_.
-]
-
-Other formulas have been devised which are more applicable to drainage
-areas of more than 1,000 acres.[30] Such areas are met in the design of
-sewers to enclose existing stream channels draining large areas.
-Kuichling’s formulas, published in 1901 in the report of the New York
-State Barge Canal, were devised for areas greater than 100 square miles.
-The following modification of these formulas for ordinary storms on
-smaller areas was published for the first time in American Sewerage
-Practice, Volume I, by Metcalf and Eddy:
-
- _Q_ = 25,000⁄(_A_ + 125) + 15.
-
-[Illustration:
-
- FIG. 12.—Comparison of Empirical Run-off Formulas.
-]
-
-It is to be noted that the only factor taken into consideration is the
-area of the watershed. It is obvious that other factors such as the rate
-of rainfall, slope, imperviousness, etc., will have a marked effect on
-the run-off.
-
-There are other run-off formulas devised for particular conditions, some
-of which are of as general applicability as those quoted. Two formulas
-which are frequently quoted are: Fanning’s, _Q_ = 200_M_^⅝ and Talbot’s
-_Q_ = 500_M_^¼, in which _M_ is the area of the watershed in square
-miles. A comprehensive treatment of the subject is given in American
-Sewerage Practice, Vol. I, by Metcalf and Eddy.
-
-A comparison of the results obtained by the application of a few
-formulas to the same conditions is shown graphically in Fig. 12. It is
-to be noted that the divergence between the smallest and largest results
-is over 100 per cent. As these formulas are not all applicable to the
-same conditions, the differences shown are due partially to an extension
-of some of them beyond the limits for which they were prepared.
-
-
-=33. Extent and Intensity of Storms.=—In the design of storm sewers it
-is necessary to decide how heavy a storm must be provided for. The very
-heaviest storms occur infrequently. To build a sewer capable of caring
-for all storms would involve a prohibitive expense over the investment
-necessary to care for the ordinary heavy storms encountered annually or
-once in a decade. This extra investment would lie idle for a long period
-entailing a considerable interest charge for which no return is easily
-seen. The alternative is to construct only for such heavy storms as are
-of ordinary occurrence and to allow the sewers to overflow on
-exceptional occasions. The result will be a more frequent use of the
-sewerage system to its capacity, a saving in the cost of the system, and
-an occasional flooding of the district in excessive storms. The amount
-of damage caused by inundations must be balanced against the extra cost
-of a sewerage system to avoid the damage. A municipality which does not
-provide adequate storm drainage is liable, under certain circumstances,
-for damages occasioned by this neglect. It is not liable if no drainage
-exists, nor is it liable if the storm is of such unusual character as to
-be classed legally as an act of God.
-
-Kuichling’s studies of the probabilities of the occurrence of heavy
-storms are published in Transactions of the American Society of Civil
-Engineers, Vol. 54, 1905, p. 192. Information on the extent of rain
-storms is given by Francis in Vol. 7, 1878, p. 224, of the same
-publication. Kuichling expresses the intensity of storms which will
-occur,
-
- once in 10 years as _i_ = 105⁄(_t_ + 20),
-
- once in 15 years as _i_ = 120⁄(_t_ + 20),
-
-in which _i_ is the intensity of rainfall in inches per hour and _t_ is
-the duration of the storm in minutes.
-
-
-
-
- CHAPTER IV
- THE HYDRAULICS OF SEWERS
-
-
-=34. Principles.=—The hydraulics of sewers deals with the application of
-the laws of hydraulics to the flow of water through conduits and open
-channels. In so far as its hydraulic properties are concerned the
-characteristics of sewage are so similar to those of water that the same
-physical laws are applicable to both. In general it is assumed that the
-energy lost due to friction between the liquid and the sides of the
-channel varies as some function of the velocity, usually the square, and
-that the total energy passing any section of the stream differs from the
-energy passing any other section only by the loss of energy due to
-friction.
-
-The general expression for the flow of sewage would then be,
-
- _h_ = (_f_)_V_^n,
-
-in which _h_ is the head or energy lost between any two sections, and
-_V_ is the average velocity of flow between these sections. It is to be
-noted in this general expression that the quantity and rate of flow past
-all sections is assumed to be constant. This condition is known as
-_steady flow_. Problems are encountered in sewerage design which involve
-conditions of unsteady flow, and methods of solution of them have been
-developed based on modifications of this general expression. The average
-velocity of flow is computed by dividing the rate (quantity) of flow
-past any section by the cross-sectional area of the stream at that
-section. This does not represent the true velocity at any particular
-point in the stream, as the velocity near the center is faster than that
-near the sides of the channel. The distribution of velocities in a
-closed circular channel is somewhat in the form of a paraboloid
-superimposed on a cylinder.
-
-The laws of flow are expressed as formulas the constants of which have
-been determined by experiment. It has been found that these constants
-depend on the character of the material forming the channel and the
-hydraulic radius. The _hydraulic radius_ is defined as the ratio of the
-cross-sectional area of the stream to the length of the wetted
-perimeter, or line of contact between the liquid and the channel,
-exclusive of the horizontal line between the air and the liquid.
-
-
-=35. Formulas.=—The loss of head due to friction caused by flow through
-circular pipes flowing full as expressed by Darcy is,
-
- _h_ = _f_(_l_⁄_d_) (_V_^2⁄2_g_),
-
-in which _h_ is the head lost due to friction in the distance _l_, _V_
-is the velocity of flow, _g_ is the acceleration due to gravity, and _f_
-is a factor dependent on _d_ and the material of which the pipe is made.
-A formula for _f_ expressed by Darcy as the result of experiments on
-cast-iron pipe is,
-
- _f_ = 0.0199 + 0.00166⁄_d_,
-
-in which _d_ is the diameter in feet. In using the formula with this
-factor the units used must be feet and seconds.
-
-Another form of the same expression is known as the Chezy formula. It is
-an algebraic transformation of the Darcy formula, but in the form shown
-here, by the use of the hydraulic radius, it is made applicable to any
-shape of conduit either full or partly full. The Chezy formula is,
-
- _V_ = _C_√(_RS_),
-
-in which _R_ is the hydraulic radius, _S_ the slope ratio of the
-hydraulic gradient, and _C_ a factor similar to _f_ in the Darcy
-formula.
-
-Kutter’s formula was derived by the Swiss engineers, Ganguillet and
-Kutter, as the result of a series of experimental observations. It was
-introduced into the United States by Rudolph Hering and its derivation
-is given in Hering and Trautwine’s translation of “The Flow of Water in
-Open Channels by Ganguillet and Kutter.” In English units it is,
-
- _V_ = {(1.81/_n_ + 41.67 + .0028/_S_)/(1 + (_n_/√_R_)(41.67 +
- (.0028/_S_)))}√(_RS_),
-
-in which _n_ is a factor expressing the character of the surface of the
-conduit and the other notation is as in the Chezy formula. _V_ is the
-velocity in feet per second, _S_ is the slope ratio, and _R_ the
-hydraulic radius in feet. The values of _n_ to be used in all cases are
-not agreed upon, but in general the values shown below are used in
-practice.
-
- VALUES OF _n_ IN KUTTER’S FORMULA
-
- _n_ CHARACTER OF THE MATERIALS
-
- 0.009 Well-planed timber.
-
- 0.010 Neat cement or very smooth pipe.
-
- 0.012 Unplaned timber. Best concrete.
-
- Smooth masonry or brickwork, or concrete sewers under ordinary
- 0.013 conditions.
-
- 0.015 Vitrified pipe or ordinary brickwork.
-
- 0.017 Rubble masonry or rough brickwork.
-
- 0.020 } Smooth earth.
- 0.035
-
- 0.030 } Rough channels overgrown with grass.
- 0.050
-
-Kutter’s formula is of general application to all classes of material
-and to all shapes of conduits. It is the most generally used formula in
-sewerage design.
-
-The cumbersomeness of Kutter’s formula is caused somewhat by the attempt
-to allow for the effect of the low slopes of the Mississippi River
-experiments on the coefficients. The correctness of these experiments
-has not been well established and the slopes are so flat that the
-omission of the term 0.0028⁄_S_ will have no appreciable effect on the
-value of _V_ ordinarily used in sewer design. The difference between the
-value of _V_ determined by the omission of this term and the value of
-_V_ found by including it is less than 1 per cent for all slopes greater
-than 1 in 1,000 for 8 inch pipe (_R_ = 0.167 feet). As the diameter of
-the pipe or the hydraulic radius of the channel increases up to a
-diameter of 13.02 feet (_R_ = 3.28 feet), the difference becomes less
-and at this value of _R_ there is no difference whether the slope is
-included or not. For larger pipes the difference increases slowly. For a
-16 foot pipe (_R_ = 4 feet) on a slope of 1 in 1,000 the difference is
-less than 0.2 per cent, and on a slope of 1 in 10,000 the difference is
-approximately 1 per cent. Flatter slopes than these are seldom used in
-sewer design, except for very large sewers where careful determinations
-of the hydraulic slope are necessary. It is therefore safe in sewer
-design to use Kutter’s formula in the modified form shown below in which
-the term (.0028)⁄_S_ has been omitted.
-
- _V_ = (1.81 + 41.67_n_)_R_√_S_/_n_(√_R_ + 41.67_n_).
-
-Bazin’s formula is
-
- _V_ = √(_RS_)/√(α + β/_d_)
-
-in which α and β are constants for different classes of material. For
-cast-iron pipe α is 0.00007726 and β is 0.00000647. This formula is
-seldom used in sewerage design.
-
-Exponential formulas have been developed as the result of experiments
-which have demonstrated that _V_ does not vary as the one-half power of
-_R_ and _S_ but that the relation should be expressed as,
-
- _V_ = _CR_^{_p_}_S_^{_q_},
-
-in which _p_ and _q_ are constants and _C_ is a factor dependent on the
-character of the material. The various formulas coming under this
-classification have been given the names of the experimenters proposing
-them. Examples of these formulas are: Flamant’s, in English units, for
-new cast-iron pipe, which is,
-
- _V_ = 232_R_^{.715}_S_^{.572},
-
-and Lampé’s for the same material which is,
-
- _V_ = 203.3_R_^{.694}_S_^{.555}.
-
-These formulas are useful only for the material to which they apply, but
-they can be used for conduits of any shape. A. V. Saph and E. W. Schoder
-have shown[31] that the general formula for all materials lies between
-the limits,
-
- _V_ = (93 to 142)_S_^{.50 to .55}_R_^{.63 to .69}.
-
-Hazen and Williams’ formula is in the form,
-
- _V_ = 1.31_CR_^{.63}_S_^{.54},
-
-in which _C_ is a factor dependent on the character of the material of
-the conduit. The values of _C_ as given by Hazen and Williams are,
-
- _C_ CHARACTER OF MATERIAL
- 95 Steel pipe under future conditions. (Riveted steel.)
- Cast iron under ordinary future conditions and brick
- 100 sewers in good condition.
- 110 New riveted steel, and cement pipe.
- 120 Smooth wood or masonry conduits under ordinary conditions.
- Masonry conduits after some time and for very smooth pipes
- such as glass, brass, lead, etc., when old, and for new
- 130 cast-iron pipe under ordinary conditions.
-
-This formula is of as general application as Kutter’s formula and is
-easier of solution, but being more recently in the field and because of
-the ease of the solution of Kutter’s formula by diagrams it is not in
-such general use. Exponential formulas are used more in waterworks than
-in sewerage practice.
-
-Manning’s formula is in the form,
-
- _V_ = 1.486⁄_n__R_^⅔_S_^½
-
-in which _n_ is the same as for Kutter’s formula. Charts for the
-solution of Manning’s formula are given in Eng. News-Record, Vol. 85,
-1920, p. 837.
-
-
-=36. Solution of Formulas.=—The solution of even the simplest of these
-formulas, such as Flamant’s, is laborious because of the exponents
-involved. Darcy’s and Kutter’s formulas are even more cumbersome because
-of the character of the coefficient. The labor involved in the solution
-of these formulas has resulted in the development of a number of
-diagrams and other short cuts. Since each formula involves three or more
-variables it cannot be represented by a single straight line on
-rectangular coordinate paper. The simplest form of diagram for the
-solution of three or more variables is the nomograph, an example of
-which is shown in Fig. 13 for the solution of Flamant’s formula. A
-straight-edge placed on any two points of the scales of two different
-vertical lines will cross the other line at a point on the scale
-corresponding to its correct value in the formula. Such a diagram is in
-common use for the solution of problems for the flow of water in
-cast-iron pipe.
-
-[Illustration:
-
- FIG. 13.—Diagram for the Solution of Flamant’s Formula for the Flow of
- Water in Cast-iron Pipe.
-]
-
-Fig. 14 has been prepared to simplify the solution of Hazen and
-Williams’ formula. The scales of slope for different classes of material
-are shown on vertical lines to the left of the slope line. For use these
-scales must be projected horizontally on the slope line. The scales for
-other factors are shown on independent reference lines.
-
- For example let it be required to find the loss of head in a 12
- inch pipe carrying 1 cubic foot per second when the coefficient of
- roughness is 100. A straight-edge placed at 1.0 cubic feet per
- second on the quantity scale, and 12 inches on the diameter scale
- crosses the slope line at .00092 opposite the slope scale for _c_
- = 100. It crosses the velocity line at 1.31 feet per second.
-
-Kutter’s formula is the most commonly used for sewer design and has been
-generally accepted as a standard in spite of its cumbersomeness. Fig. 15
-is a graphical solution of Kutter’s formula for small pipes, and Fig. 16
-for larger pipes. The diagrams are drawn on the nomographic principle
-and give solutions for a wide range of materials, but they are specially
-prepared for the solution of problems in which _n_ = .015. In their
-preparation the effect of the slope on the coefficient has been
-neglected. Fig. 17 is drawn on ordinary rectangular coordinate paper and
-can be used only for the solution of problems in which _n_ = .015. Both
-diagrams are given for practice in the use of the different types.
-
-[Illustration:
-
- FIG. 14.—Diagram for the Solution of Hazen and Williams’ Formula.
-]
-
-[Illustration:
-
- FIG. 15.—Diagram for the Solution of Kutter’s Formula.
-
- For values of _n_ between 0.010 and 0.020. Specially arranged for _n_
- = 0.015. Values of Q from 0.1 to 10 second-feet.
-]
-
-[Illustration:
-
- FIG. 16.—Diagram for the Solution of Kutter’s Formula.
-
- For values of _n_ between 0.010 and 0.020. Specially arranged for _n_
- = 0.015. Values of Q from 10 to 1,000 second-feet.
-]
-
-[Illustration:
-
- FIG. 17.—Diagram for the Solution of Kutter’s Formula.
-]
-
-[Illustration:
-
- FIG. 18.—Conversion Factors for Kutter’s Formula.
-]
-
-In Figs. 15 and 16 the diameter scales are varied for different values
-of the roughness coefficient _n_. The velocity scale is shown _only for
-a value of n = .015_. The velocity for other values of _n_ can be
-determined by the method given in the following paragraphs.
-
-37. =Use of Diagrams.=—There are five factors in Kutter’s formula: _n_,
-_Q_, _V_, _d_ (or _R_), and _S_. If any three of these are given the
-other two can be determined, except when the three given are _Q_, _V_,
-and _d_. These three are related in the form _Q_ = _AV_, which is
-independent of slope or the character of the material. There are only
-nine different combinations possible with these five factors, which will
-be met in the solution of Kutter’s formula. The solution of the problems
-by means of the diagrams is simple when the data given include _n_
-= .015. For other given values of _n_ the solution is more complicated.
-Results of the solution of types of each of the nine problems are given
-in Table 17 and the explanatory text below.
-
-_If n is given and is equal to .015_, the solution is simple.
-
- For example in Table 17 _case 1, example 1_; to be solved on Fig.
- 15. Place a straight-edge at 1.0 on the _Q_ line and at 6 inches
- on the diameter line for _n_ = .015. The slope and the velocity
- will be found at the intersection of the straight-edge with these
- respective scales.
-
-All problems in which _n_ is given as .015 and the solution for which
-falls within the limits of Fig. 15 or 16 should be solved by placing a
-straight-edge on the two known scales and reading the two unknown
-results at the intersection of the straight-edge and the remaining
-scales.
-
- For example in _case 1_, _example 2_ find the intersection of the
- horizontal line representing _Q_ = 100 with the sloping diameter
- line representing _d_ = 48 inches. The vertical slope line passing
- through this point represents _S_ = .0065 and the sloping velocity
- line passing through this point represents 8.5 feet per second.
-
-In general problems in which _n_ = .015, can be solved on Fig. 17 by
-finding the intersection of the two lines representing the given data,
-and reading the values of the remaining variables represented by the
-other two lines passing through this point.
-
- TABLE 17
-
- SOLUTIONS OF PROBLEMS BY KUTTER’S FORMULA
-
- ─────┬───────┬────────────────────────────┬────────────────────────────
- Case │Example│ Given │ Found
- ─────┼───────┼─────┬─────┬────┬────┬──────┼─────┬─────┬────┬────┬──────
- │ │ _n_ │ _Q_ │_V_ │_d_ │ _S_ │ _n_ │ _Q_ │_V_ │_d_ │ _S_
- ─────┼───────┼─────┼─────┼────┼────┼──────┼─────┼─────┼────┼────┼──────
- 1 │ 1 │0.015│ 1.0│ 2.5│ 6│ │ │ │5.0 │ │0.0575
- 1 │ 2 │ .015│100.0│ │ │ │ │ │8.5 │ │.0065
- 1 │ 3 │ .020│ 1.0│ │ 6│ │ │ │5.0 │ │.13
- 1 │ 4 │ .020│100.0│ │ 48│ │ │ │8.5 │ │.0125
- 2 │ 1 │ .015│ 5.0│ │ │0.0003│ │ │1.2 │28 │
- 2 │ 2 │ .010│ 5.0│ │ │.0003 │ │ │1.7 │23.5│
- 3 │ 1 │ .015│ │ │ 18│.002 │ │ 4.0│2.25│ │
- 3 │ 2 │ .018│ │ │ 18│.0008 │ │ 2.0│1.1 │ │
- 4 │ 1 │ .015│ 2.0│ 2.5│ │ │ │ │ │12 │.00475
- 4 │ 2 │ .011│ 2.0│ 2.5│ │ │ │ │ │12 │.0022
- 5 │ 1 │ .015│ │ 5.0│ 36│ │ │ 35.0│ │ │.0038
- 6 │ 1 │ .018│ │ 5.0│ │.001 │ │185.0│ │80 │
- 7 │ 1 │ │ 3.0│ │ 18│.002 │0.019│ │1.7 │ │
- 7 │ 2 │ │ 50.0│ │ 36│.005 │ .012│ │7.0 │ │
- 8 │ 1 │ │ 6.0│ 2.5│ │.003 │ .018│ │ │21 │
- 9 │ 1 │ │ │ 4.2│ 66│.00059│ .011│100.0│ │ │
- ─────┴───────┴─────┴─────┴────┴────┴──────┴─────┴─────┴────┴────┴──────
-
-_If n is given and is not equal to .015_ the solution is not so simple.
-In Fig. 15 and 16 the diagram is so drawn that the _position_ of the
-diameter scales for all values of _n_ is fixed on the vertical
-“diameter” line. The _scales_ of diameter change for each value of _n_.
-These scales of diameter are shown for each value of _n_ from .010
-to .020 on vertical lines to the left of the “diameter” line. For use,
-the proper diameter scale for any given value of _n_ must be projected
-horizontally upon the vertical “diameter” line. The velocity can be
-determined on Fig. 15 and 16, _only when the diameter has been
-determined_ and then _only when the diameter scale for n equal .015 is
-used, since the only scale shown for velocity is for n = .015._
-
- For example, in _Case 1_, _Example 3_ there are given _n_ = .020,
- _Q_, and _d_. Find the intersection of the vertical line for _n_ =
- .020 with the sloping diameter line for _d_ = 6 inches. Project
- the intersection horizontally to the right to the vertical
- “diameter” line. Place a straight-edge at this point and at _Q_ =
- 1.0 on the quantity scale. The required value of _S_ is read at
- the intersection of the straight-edge and the slope scale and is
- equal to 0.13. The intersection of the straight-edge in this
- position with the velocity scale is not the required value of the
- velocity since the velocity scale is made out for _n_ = .015 and
- not .020. It is necessary to change the position of the
- straight-edge so that it may lie on _Q_ equal 1.0 and on _d_ equal
- 6 inches for _n_ equal .015. The value of _V_ is shown in this
- position as 5 feet per second.
-
- The reverse process for Fig. 15 and 16 is illustrated _by Case 4_,
- _Example 2_ in which _n_ = .011 and _Q_ and _V_ are also given.
- When _Q_ and _V_ are given the value of _d_ is fixed independent
- of all other factors. Therefore the value of _d_ can be read from
- the scale with _n_ = .015 and is found to be 12 inches. Now find
- the value of _d_ = 12 inches on the scale for _n_ = .011 and
- project on to the “diameter” line. Place the straight-edge at this
- point and at _Q_ = 2. The required slope is read as .0022.
-
-Fig. 17 is prepared for the solution of problems in which _n_ = .015
-only. For problems in which _n_ has some other value it is necessary to
-transform the data to equivalent conditions in which _n_ = .015. This is
-done by means of the conversion factors shown in Fig. 18. The given
-slope or velocity is multiplied by the proper factor to convert from or
-to the value of _n_ = .015.
-
- For example in _Case 1_, _Example 4_ there are given _n_ = .020,
- _Q_, and _d_. With _Q_ and _d_ given the value of _V_ can be read
- from Fig. 17 without conversion. The corresponding value of _S_
- for _n_ = .015 is .0065. It is now necessary to use the
- transformation diagram Fig. 18. The hydraulic radius of the given
- pipe is one foot. On Fig. 18 at the intersection of the slope line
- for _R_ = 1.0 foot and _n_ = .020 the value of the factor is read
- as 1.92. Since the given _n_ is for rougher material than that
- represented by _n_ = .015 the required slope must be greater than
- for _n_ = .015 to give the same velocity. It is therefore
- necessary to multiply .0065 × 1.92 and the required slope is
- .0125.
-
- In _Case 6_, _Example 1_ there are given _n_ = .018, _d_, and _S_.
- The remaining factors are to be solved by Fig. 17. Solve first as
- though _n_ = .015 in order to find an approximate value of _d_ or
- _R_. In this case it is evident that _d_ is greater than 57
- inches. The value of _R_ is therefore about 1.25. Referring to
- Fig. 18 the conversion factor for the slope for _n_ = .018 is
- about 1.52. Since the given slope for _n_ = .018 is .001, for an
- equal velocity and for _n_ = .015 the slope should be less.
- Therefore in reading Fig. 17 it is necessary to use a slope of
- .001⁄1.52 = .00066. The diameter is found to be about 80 inches.
- Since this is nearer to the correct diameter the value of the
- conversion factor must be corrected for this approximation. The
- hydraulic radius for an 80 inch pipe is 1.67 feet, and the
- conversion factor from Fig. 18 is about 1.48. The slope for _n_ =
- .015 should be therefore .001⁄1.48 = .000675 and from Fig. 17 the
- required diameter and quantity are read as 80 inches and 185
- second-feet, respectively.
-
-_If n is not given_ but must be solved for, the solution on Fig. 15 and
-16 is relatively simple. The desired value of _n_ is read at the
-intersection of the sloping diameter line representing the known
-diameter and the horizontal projection of the intersection of the
-straight-edge with the vertical “diameter” line.
-
- For example in _Case 7_, _Example 1_ there are given _Q_, _d_, and
- _S_. Lay the straight-edge on the given values of _Q_ = 3 and _S_
- = .002. At the point where the straight-edge crosses the vertical
- “diameter” line project a horizontal line to the sloping diameter
- line for _d_ = 18 inches. The vertical line passing through this
- point represents a value of _n_ = .019. In order to find the value
- of _V_ lay the straight-edge on _Q_ = 3 and _d_ = 18 inches for
- _n_ = .015. The value of _V_ is read as 1.7.
-
- A slightly different condition is illustrated in the solution of
- _Case 8_, _Example 1_ in which _Q_, _V_ and _S_ are given.
- Determine first the value of _d_ as though _n_ = .015. Then
- proceed to determine _n_ as in the preceding examples.
-
-The solution for an unknown value of _n_ on Fig. 17 is not so simple. It
-must be determined by working backwards from the conversion factor.
-
- For example in _Case 7_, _Example 2_ there are given _Q_, _d_, and
- _S_. The value of _V_ is read directly as though _n_ = .015 as 7
- feet per second. The value of _S_ read for _n_ = .015 is .0075.
- But the given slope is .005. Since the given slope is flatter than
- that for _n_ = .015 the conversion factor is less than unity and
- is therefore .005⁄.0075 = 0.67. With this value of the conversion
- factor and the value of _R_ given as 0.75 the value of _n_ is read
- from Fig. 18 as slightly greater than .012.
-
-
-=38. Flow in Circular Pipes Partly Full.=—The preceding examples have
-involved the flow in circular pipes completely filled. The same methods
-of solution can be used for pipes flowing partly full except that the
-hydraulic radius of the wetted section is used instead of the diameter
-of the pipe. Diagrams are used to save labor in finding the hydraulic
-radius and the other hydraulic elements of conduits flowing partly full.
-
-The hydraulic elements of a conduit for any depth of flow are: (_a_) The
-hydraulic radius, (_b_) the area, (_c_) the velocity of flow, and (_d_)
-the quantity or rate of discharge. The velocity and quantity when partly
-full as expressed in terms of the velocity and quantity when full as
-calculated by Kutter’s formula will vary slightly with different
-diameters, slopes and coefficients of roughness. The other elements are
-constant for all conditions for the same type of cross-section. The
-hydraulic elements for all depths of a circular section for two
-different diameters and slopes are shown in Fig. 19. The differences
-between the velocity and quantity under the different conditions are
-shown to be slight, and in practice allowance is seldom made for this
-discrepancy.
-
-In the solution of a problem involving part full flow in a circular
-conduit the method followed is to solve the problem as though it were
-for full flow conditions and then to convert to partial flow conditions
-by means of Fig. 19, or to convert from partial flow conditions to full
-flow conditions and solve as in the preceding section.
-
- For example let it be required to determine the quantity of flow
- in a 12–inch diameter pipe with _n_ = .015 when on a slope of .005
- and the depth of flow is 3 inches. First find the quantity for
- full flow. From Fig. 15 this is 2.0 cubic feet per second. The
- depth of flow of 3 inches is one-fourth or 0.25 of the full depth
- of 12 inches. From Fig. 19, running horizontally on the 0.25 depth
- line to meet the quantity curve, the proportionate quantity at
- this depth is found to be on the 0.13 vertical line, and the
- quantity of flow is therefore 2 × 0.13 = 0.26 cubic feet per
- second.
-
-[Illustration:
-
- FIG. 19.—Hydraulic Elements of Circular Sections.
-]
-
- _d_ = 12′ 0″ _s_ = .0004 _n_ = .015
- _d_ = 1′ 0″ _s_ = .01 _n_ = .013
-
-Another problem, involving the reversal of this process is illustrated
-by the following example:
-
- Let it be required to determine the diameter and full capacity of
- a vitrified pipe sewer on a grade of 0.002 if the velocity of flow
- is 3.0 feet per second when the sewer is discharging at 30 per
- cent of its full capacity, the depth of flow being 12 inches. From
- Fig. 19 the depth of flow when the sewer is carrying 30 per cent
- of its full capacity is 0.38 of its full depth. Since the partial
- depth is 12 inches the full diameter is 12⁄.038 = 31.6 inches. The
- velocity of flow at 38 per cent depth is 86 per cent of the full
- velocity. Since the velocity given is 3.0 feet per second, the
- full velocity is 3.0⁄.86 = 3.5 feet per second. With a full
- velocity of 3.5 feet per second and a diameter of 31.6 inches from
- Fig. 16 the full capacity of the sewer is 18 cubic feet per
- second.
-
-
-=39. Sections Other than Circular.=—The ordinary shape used for small
-sewers is circular. The difficulty of constructing large sewers in a
-circular shape, special conditions of construction such as small head
-room, soft foundations, etc., or widely fluctuating conditions of flow
-have led to the development of other shapes. For conduits flowing full
-at all times a circular section will carry more water with the same loss
-of head than any other section under the same conditions. In any section
-the smaller the flow the slower the velocity, an undesirable condition.
-The ideal section for fluctuating flows would be one that would give the
-same velocity of flow for all quantities. Such a section is yet to be
-developed. Sections have been developed that will give relatively higher
-velocities for small quantities of flow than are given by a circular
-section. The best known of these sections is the egg shape, the
-proportions and hydraulic elements of which are shown in Fig. 20. Other
-shapes that have the same property, but which were not developed for the
-same purpose are the rectangular, the U-shape, and the section with a
-cunette. The egg-shaped section has been more widely used than any other
-special section. It is, however, more difficult and expensive to build
-under certain conditions, and has a smaller capacity when full than a
-circular sewer of the same area of cross-section. Various sections are
-illustrated in Fig. 22 and 23.
-
-The U-shaped section is suitable where the cover is small, or close
-under obstructions where a flat top is desirable and the fluctuations of
-flow are so great as to make advantageous a special shape to increase
-the velocity of low flows. The proportions of a U-shaped section are
-shown in Fig. 23 (6). Other sections used for the same purpose are the
-semicircular and special forms of the rectangular section.
-
-The proportions and the hydraulic elements of the square-shaped section
-are shown in Fig. 21. This is useful under low heads where a flat roof
-is required to carry heavy loads, and the fluctuations of flow are not
-large.
-
-Sections with cunettes have not been standardized. A cunette is a small
-channel in the bottom of a sewer to concentrate the low flows, as shown
-in Fig. 22 (7). A cunette can be used in any shape of sewer.
-
-[Illustration:
-
- FIG. 20.—Hydraulic Elements of an Egg-shaped Section.
-
- _d_ = 6′ 0″ _s_ = .00065 _n_ = .015
-]
-
-[Illustration:
-
- FIG. 21.—Hydraulic Elements of a Square Section.
-
- _d_ = 10′ 0″ _s_ = .0004 _n_ = .015
-]
-
-Sections developed mainly because of the greater ease of construction
-under certain conditions are the basket handle, the gothic, the
-catenary, and the horse shoe. Some of these shapes are shown in Fig. 22
-and 23. They are suitable for large sewers on soft foundations, where it
-is desirable to build the sewer in three portions, such as invert, side
-walls, and arch. They are also suitable for construction in tunnels
-where the shape of the sewer conforms to the shape of the timbering, or
-in open cut work where the shape of the forms are easier to support.
-
-Problems of flow in all sections can be solved by determining the
-hydraulic radius involved, and substituting directly in the desired
-formula, or by the use of one of the diagrams after converting to the
-equivalent circular diameter. The determination of the hydraulic radius
-of these special sections is laborious, and hence other less difficult
-methods are followed. Problems are more commonly solved by converting
-the given data into an equivalent circular sewer, solving for the
-elements of this circular sewer and then reconverting into the original
-terms, or by working in the other direction. The hydraulic elements of
-various sections when full are given in Table 18.
-
- TABLE 18
-
- HYDRAULIC ELEMENTS OF SEWER SECTIONS. SEWERS FLOWING FULL.
-
- ───────────────┬─────────────┬─────────────┬─────────────┬──────────────
- Section │Area in Terms│ Hydraulic │ Vert. Dia. │ Source
- │ Vertical │ Radius in │_D_ in Terms │
- │ Diameter │ terms of │ of Dia. _d_ │
- │Squared _D_^2│Vertical Dia.│of Equivalent│
- │ │ _D_ │ Circular │
- │ │ │ Section │
- ───────────────┼─────────────┼─────────────┼─────────────┼──────────────
- Circular │ 0.7854│ 0.250 │1.000 │
- Egg │ 0.5150│ .1931│1.295 │Eng. Record,
- │ │ │ │ Vol. 72: 608
- Ovoid │ 0.5650│ .2070│1.208 │Eng. Record,
- │ │ │ │ Vol. 72: 608
- Semi-elliptical│ 0.8176│ .2487│1.041 │Eng. News,
- │ │ │ │ Vol. 71: 552
- Catenary │ 0.6625│ .2237│1.1175 │Eng. Record,
- │ │ │ │ Vol. 72: 608
- Horseshoe │ 0.8472│ .2536│0.985 │Eng. Record,
- │ │ │ │ Vol. 72: 608
- Basket handle │ 0.8313│ .2553│0.979 │Eng. Record,
- │ │ │ │ Vol. 72: 608
- Rectangular │ 1.3125│ .2865│0.7968 │Hydraulic
- │ │ │ │ Dgms. and
- │ │ │ │ Tbls.
- │ │ │ │ Garrett
- Square (3 sides│ 1.0000│ .333 │0.7500 │Eng. Record,
- wet) │ │ │ │ Vol. 72: 608
- Square (4 sides│ 1.0000│ .250 │1.0000 │Eng. Record,
- wet) │ │ │ │ Vol. 72: 608
- ───────────────┴─────────────┴─────────────┴─────────────┴──────────────
-
-[Illustration:
-
- 1. Standard Egg-shaped Section, North Shore Intercepter, Chicago,
- Illinois.
-]
-
-[Illustration:
-
- 2. Rectangular Section, Omaha, Nebraska, Eng. Contracting, Vol. 46, p.
- 49.
-]
-
-[Illustration:
-
- 3. Trench in firm ground. 4. Trench in Rock.
-
- NOTE.—Underdrains and Wedges to be used only when Ordered by the
- Engineer.
-]
-
-[Illustration:
-
- 7. Brick and Concrete Sewer showing cunette.
-]
-
-[Illustration:
-
- 5. Soft Foundation. 6. Wet ground.
-]
-
-[Illustration:
-
- 8. Brick and Concrete Sewer, Evanston, Ill., Eng. Contracting, Vol.
- 46, p. 227.
-]
-
- FIG. 22.
-
-[Illustration]
-
- 1. Tunnel Sections. 2. Open Cut Sections.
- ───────────────────────────────────────────────────────────────────────
- Type A. Type B. Type C. Type D.
- Where Rock Where Rock Where Rock Where Rock 16′ 6″ Where Rock
- is more is more is between drops below Sewer. 25′ is above
- than 16′ than 7′ Springing Springing Fill Springing
- above and less Line and 7′ Line on Line
- Springing than 16′ above either
- Line. above Springing Side.
- Springing Line on
- Line on both Sides.
- both Sides.
-
- Mill Creek Sewer, St. Louis, Eng. Record, Vol. 70, pp. 434, 435.
-
-[Illustration:
-
- 3. Circular Concrete Section in Soft and Hard Ground, Eng. Record,
- Vol. 59, p. 570.
-]
-
-[Illustration:
-
- 4. Semi-Elliptical Section, Louisville, Ky., Eng. News, Vol. 62, p.
- 416.
-]
-
-[Illustration:
-
- 5. Reinforced Concrete Sewer, Harlem Creek, St. Louis, Eng. News, Vol.
- 60, p. 131.
-]
-
-[Illustration:
-
- 6. U-Shaped Section, San Francisco, Eng. News, Vol. 73, p. 310.
-]
-
- FIG. 23.
-
-Equivalent sections are sections of the same capacity for the same slope
-and coefficient of roughness. They have not necessarily the same
-dimensions, shape, nor area. The diameter of the equivalent circular
-section in terms of the diameter of each special section shown is given
-in Table 18. The inside height of a sewer is spoken of as its diameter.
-
- For example let it be required to determine the rate of flow in a
- 54–inch egg-shaped sewer on a slope of 0.001 when _n_ = .015.
- First convert to the equivalent circle. From Table 18 the diameter
- of the equivalent circle is 1⁄1.295 times the diameter of the
- egg-shaped sewer, which becomes in this case 43 inches. From Fig.
- 16 the capacity of a circular sewer of this diameter with _S_ =
- 0.001 and _n_ = .015 is 28 cubic feet per second, which by
- definition is the flow in the egg-shaped sewer.
-
- As an example of the reverse process let it be required to find
- the velocity of flow in an egg-shaped sewer flowing full and
- equivalent to a 48–inch circular sewer. Both sewers are on a slope
- of 0.005 and have a roughness coefficient of _n_ = .015. It is
- first necessary to find the quantity of flow in the circular
- sewer, which by definition is the quantity of flow in the
- equivalent egg-shaped sewer. The velocity of flow in the
- egg-shaped sewer is found by dividing this quantity by the area of
- the egg-shaped section. As read from the diagram the quantity of
- flow is 90 cubic feet per second. From Table 18 the area of the
- egg-shaped sewer is 0.51_D_^2 where _D_ is the diameter of the
- egg-shaped sewer, and _D_ = 1.295_d_ where _d_ is the diameter of
- the equivalent circular sewer. Therefore the area equals (0.51) ×
- (1.295 × 4)^2 = 13.5 square feet and the velocity of flow is
- 90⁄13.5 = 6.7 feet per second. This is slightly less than the
- velocity in the circular section.
-
-Some lines for egg-shaped sewers have been shown on Fig. 17 by which
-solutions can be made directly. For other shapes, and for sizes of
-egg-shaped sewers not found on Fig. 17 the preceding method or the
-original formula must be used for solution. Problems in partial flow in
-special sections are solved similarly to partial flow in circular
-sections, by converting first to the conditions of full flow or by
-working in the opposite direction.
-
-
-=40. Non-uniform Flow.=—In the preceding articles it is assumed that the
-mean velocity and the rate of flow past all sections are constant. This
-condition is known as steady, uniform flow. In this article it will be
-assumed that conditions of steady non-uniform flow exist, that is, the
-rate of flow past all sections is constant, but the velocity of flow
-past these sections is different for different sections. Under such
-conditions the surface of the stream is not parallel to the invert of
-the channel. If the velocity of flow is increasing down stream the
-surface curve is known as the drop-down curve. If the velocity of flow
-is decreasing down stream the surface curve is known as the backwater
-curve. The hydraulic jump represents a condition of non-uniform flow in
-which the velocity of flow decreases down stream in such a manner that
-the surface of the stream stands normal to the invert of the channel at
-the point where the change in velocity occurs. Above and below this
-point conditions of uniform flow may exist.
-
-Conditions of non-uniform flow exist at the outlet of all sewers, except
-under the unusual conditions where the depth of flow in the sewer under
-conditions of steady, uniform flow with the given rate of discharge
-would raise the surface of water in the sewer, at the point of
-discharge, to the same elevation as the surface of the body of water
-into which discharge is taking place. By an application of the
-principles of non-uniform flow to the design of outfall sewers, smaller
-sewers, steeper grades, greater depth of cover, and other advantages can
-be obtained.
-
-The backwater curve is caused by an obstruction in the sewer, by a
-flattening of the slope of the invert, or by allowing the sewer to
-discharge into a body of water whose surface elevation would be above
-the surface of the water in the sewer, at the point of discharge, under
-conditions of steady, uniform flow with the given rate of discharge.
-
-The drop-down curve is caused by a sudden steepening of the slope of the
-invert; by allowing a free discharge; or by allowing a discharge into a
-body of water whose surface elevation would be below the surface of the
-water in the sewer, at the point of discharge, under conditions of
-steady, uniform flow with the given rate of discharge. The last
-described condition is common at the outlet of many sewers, hence the
-common occurrence of the drop-down curve.
-
-The hydraulic jump is a phenomenon which is seldom considered in sewer
-design. If not guarded against it may cause trouble at overflow weirs
-and at other control devices, in grit chambers, and at unexpected
-places. The causes of the hydraulic jump are sufficiently well
-understood to permit designs that will avoid its occurrence, but if it
-is allowed to occur the exact place of the occurrence of the jump and
-its height are difficult, if not impossible, to determine under the
-present state of knowledge concerning them. The hydraulic jump will
-occur when a high velocity of flow is interrupted by an obstruction in
-the channel, by a change in grade of the invert, or the approach of the
-velocity to the “critical” velocity. The “critical” velocity is equal to
-√(_gh_), where _h_ is the depth of flow and _g_ is the acceleration due
-to gravity. The velocity in the channel above the jump must be greater
-than √(_gh__{1}), where _h__{1} is the depth of flow in the channel
-above the jump. The velocity in the channel below the jump must be
-greater than √(_gh__{2}), where _h__{2} is the depth of flow below the
-jump. The jump will not take place unless the slope of the invert of the
-channel is greater than _g_⁄_C_^2,in which _C_ is the coefficient in the
-Chezy formula. With this information it is possible to avoid the jump by
-slowing down the velocity by the installation of drop manholes, flight
-sewers, or by other expedients.
-
-The shape of the drop-down curve can be expressed, in some cases, by
-mathematical formulas of more or less simplicity, dependent on the shape
-of the conduit. The formula for a circular conduit is complicated. Due
-to the assumptions which must be made in the deduction of these
-formulas, the results obtained by their use are of no greater value than
-those obtained by approximate methods. A method for the determination of
-the drop-down curve is given by C. D. Hill.[32] In this method it is
-necessary that the rate of flow past all sections shall be the same;
-that the depth of submergence at the outlet shall be known; and that the
-depth of flow at some unknown distance up the stream shall be assumed.
-The shape and material of construction of the sewer and the slope of the
-invert should also be known. The problem is then to determine the
-distance between cross-sections, one where the depth of flow is known,
-and the other where the depth of flow has been assumed. This distance
-can be expressed as follows:
-
- _L_ = ((_d__{2} − _d__{1}) − (_H__{1} − _H__{2}))⁄(_S_ − S_{1}) = (_d_′
- − _H_′)⁄_S_′,
-
- in which _L_ = the distance between cross-sections;
-
- _d__{1} = the depth of flow at the lower section;
-
- _d__{2} = the depth of flow at the upper section;
-
- _H__{1} = the velocity head at the lower section;
-
- _H__{2} = the velocity head at the upper section;
-
- _S_ = the hydraulic slope of the stream surface;
-
- _S__{1} = the slope of the invert of the sewer.
-
-In order to solve such problems with a satisfactory degree of accuracy
-the difference between _d__{1} and _d__{2} should be taken sufficiently
-small to divide the entire length of the sewer to be investigated into a
-large number of sections. The solution of the problem requires the
-determination of the wetted area, the hydraulic radius, and other
-hydraulic elements at many sections. The labor involved can be
-simplified by the use of diagrams, such as Fig. 19, or by specially
-prepared diagrams such as those accompanying the original article by C.
-D. Hill. The solution of the problem can be simplified by tabulating the
-computations as follows:
-
- DROP-DOWN CURVE COMPUTATION SHEET
-
- Uniform discharge. Varying depth
-
- ┌───────────────────────────────────────────────────────────────────────┐
- │ _D_ = _Q_ = _A_ = _V_ = │
- │ _Q_⁄_A_ = _S__{1} = _L_ = (_d__{1} − _H__{1})⁄_S__{1} │
- ├───┬───┬───────┬───┬───┬───────┬───────┬───┬───┬───────┬───┬─────┬─────┤
- │ 1 │ 2 │ 3 │ 4 │ 5 │ 6 │ 7 │ 8 │ 9 │ 10 │11 │ 12 │ 13 │
- ├───┴───┴───────┼───┼───┼───────┼───────┼───┼───┼───────┼───┼─────┴─────┤
- │ Depth │_R_│_H_│_H__{1}│_d__{1}│_V_│_S_│_S__{1}│_L_│ Elevation │
- │ │ │ │ │ − │ │ │ │ │ │
- │ │ │ │ │_H__{1}│ │ │ │ │ │
- ├───┬───┬───────┼───┼───┼───────┼───────┼───┼───┼───────┼───┼─────┬─────┤
- │_D_│_d_│_d__{1}│ │ │ │ │ │ │ │ │Sewer│W. L.│
- ├───┼───┼───────┼───┼───┼───────┼───────┼───┼───┼───────┼───┼─────┼─────┤
- │ │ │ │ │ │ │ │ │ │ │ │ │ │
- ├───┼───┼───────┼───┼───┼───────┼───────┼───┼───┼───────┼───┼─────┼─────┤
- │ │ │ │ │ │ │ │ │ │ │ │ │ │
- ├───┼───┼───────┼───┼───┼───────┼───────┼───┼───┼───────┼───┼─────┼─────┤
- │ │ │ │ │ │ │ │ │ │ │ │ │ │
-
-At the head of the computation sheet should be recorded the diameter of
-the sewer in feet, the assumed volume of flow, the area of the full
-cross-section of the sewer, the velocity of the assumed volume flowing
-through the full bore of the sewer, and the gradient or slope of the
-invert. In the 1st column enter the assumed depth in decimal parts of
-the diameter for each cross-section; in the 2nd column enter the same
-depth in feet; in the 3rd column enter the difference in feet between
-the successive cross-sections; in the 4th column enter the hydraulic
-radius corresponding to the depth at each cross-section; in the 8th
-column enter the velocity, equal to the volume divided by the wetted
-area, for each cross-section; in the 5th column enter the corresponding
-velocity head; in the 6th column enter the difference between the
-velocity heads at successive cross-sections; in the 7th column enter the
-difference between the quantities in the third and in the sixth columns;
-in the 9th column enter the hydraulic slope corresponding to the
-velocity and hydraulic radius of each cross-section; in the 10th column
-enter the difference between the hydraulic slope and the slope or
-gradient of the sewer; in the 11th column enter the computed distance
-between successive cross-sections; in the 12th column enter the
-elevation of the bottom of the sewer at each cross-section; and in the
-13th column enter the corresponding elevation of the surface of the
-water.
-
-The table should be filled in until the distance to the required section
-is determined, or if the distance is known, it should be filled in until
-the depth of flow with the assumed rate of discharge has been checked.
-
-If only the depth of flow at some section is known and it is required to
-know the maximum rate of flow with a free discharge, or a discharge with
-a submergence at the outlet less than the depth of flow with the maximum
-rate of discharge, it is necessary to make a preliminary estimate of the
-maximum rate of flow in order to fill in the quantity _Q_ at the head of
-the table. The procedure should be as follows:
-
- 1st. Assume a depth of flow at the outlet.
-
- 2nd. Compute the area (_A_) and the hydraulic radius (_R_) at the known
- section and at the outlet.
-
- 3rd. Determine the area and the hydraulic radius half way between these
- two sections as the mean of the areas and the hydraulic radii of
- the two sections.
-
- 4th. Determine the rate of flow through the sewer from the condition
- that the difference in head at the two sections is the head lost
- due to friction caused by the average velocity of flow between
- the sections (equals (_lV_^2)⁄(_C_^2_R_)) plus the gain in
- velocity head (equals _V__{2}^2 − (_V__{1}^2)⁄(2_g_)), which
- then combined and transposed result in the expression:
-
- _Q_ = _AA__{1}_A__{2} √(2_Rgh_⁄(2_A__{1}^2_A__{2}^2_gl_ + (_A__{1}
- − _A__{2})(_A_^2_C_^2_R_)))
-
-
-
- in which _Q_ = rate of flow;
-
- _A_ = the area determined in the 3rd step;
-
- _A__{1} = the area at the upper cross-section;
-
- _A__{2} = the area at the lower cross-section;
-
- _C_ = the coefficient in the Chezy formula;
-
- _g_ = the acceleration due to gravity;
-
- _h_ = the difference in elevation of the surface of the
- stream at the two cross-sections;
-
- _l_ = the distance between the cross-sections;
-
- _R_ = the hydraulic radius determined in the third step.
-
- 5th. Continue this process by assuming different depths at the outlet
- until the maximum rate of discharge has been found by trial.
-
-With this rate of discharge and depth of flow at the outlet, the depth
-of flow at the known section can be checked. If appreciably in error a
-correction should be made by the assumption of a different depth of flow
-at the outlet. The approximate character of the method is scarcely
-worthy of the refinement in the results which will be obtained by
-checking back for the depth of flow at the known section. It will be
-sufficiently accurate to assume the rate of flow obtained by trial from
-the preceding expression, as the maximum rate of discharge from the
-sewer.
-
-
-
-
- CHAPTER V
- DESIGN OF SEWERAGE SYSTEMS
-
-
-=41. The Plan.=—Good practice demands that a comprehensive plan for a
-sewerage system be provided for the needs of a community for the entire
-extent of its probable future growth, and that sewers be constructed as
-needed in accordance with this plan.
-
-Sewerage systems may be laid out on any one of three systems: separate,
-storm, or combined. A separate system of sewers is one in which only
-sanitary sewage or industrial wastes or both are allowed to flow. Storm
-sewers carry only surface drainage, exclusive of sanitary sewage.
-Combined sewers carry both sanitary and storm sewage. The use of a
-combined or a separate system of sewerage is a question of expediency.
-Portions of the same system may be either separate, combined, or storm
-sewers.
-
-Some conditions favorable to the adoption of the separate system are
-where:
-
- _a._ The sanitary sewage must be concentrated at one outlet, such
- as at a treatment plant, and other outlets are available for the
- storm drainage.
-
- _b._ The topography is flat necessitating deep excavation and
- steeper grades for the larger combined sewers.
-
- _c._ The sanitary sewers must be placed materially deeper than the
- necessary depth for the storm-water drains.
-
- _d._ The sewers are to be laid in rock, necessitating more
- difficult excavation for the larger combined sewers.
-
- _e._ An existing sewerage system can be used to convey the dry
- weather flow, but is not large enough for the storm sewage.
-
- _f._ The city finances are such that the greater cost of the
- combined system cannot be met and sanitary drainage is imperative.
-
- _g._ The district to be sewered is an old residential section
- where property values are not increasing and the assessment must
- be kept down.
-
-Some additional points given in a report by Alvord and Burdick to the
-city of Billings, Montana, are:
-
-The separate system of sewerage should be used, where:
-
- 1st. Storm water does not require extensive underground removal,
- or where it can be concentrated in a few shallow underground
- channels.
-
- 2nd. Drainage areas are short and steep facilitating rapid flow of
- water over street surfaces to the natural water courses.
-
- 3rd. The sanitary sewage must be pumped.
-
- 4th. Sewers are being built in advance of the city’s development
- to encourage its growth.
-
- 5th. The existing sewer is laid at grades unsuitable for sanitary
- sewage, it can be used as a storm sewer.
-
- A combined system must be relatively larger than a separate storm
- sewer as the latter may overflow on exceptional occasions, but the
- former never.
-
-
- A combined system of sewerage should be used where:
-
- 1st. It is evident that storm and sanitary sewerage must be
- provided soon.
-
- 2nd. Both sanitary and storm sewage must be pumped.
-
- 3rd. The district is densely built up.
-
-
-=42. Preliminary Map.=—The first step in the design of a sewerage system
-is the preparation of a map of the district to be served within the
-limits of its probable growth. The map should be on a scale of at least
-200 feet to the inch in the built up sections or other areas where it is
-anticipated that sewers may be built, and where much detail is to be
-shown a scale as large as 40 feet to the inch may have to be used. The
-adoption of so large a scale will usually necessitate the division of
-the city or sewer district into sections. A key map should be drawn to
-such a scale that the various sections represented by separate drawings
-can all be shown upon it. In preparing the enlarged portions of the map
-it is not necessary to include these portions of the city in which it is
-improbable that sewers will be constructed, such as parks and
-cemeteries.
-
-The contour interval should depend on the character of the district and
-the slope of the land. In those sections drawn to a scale of 200 feet to
-the inch for slopes over 5 per cent, the contour interval need not be
-closer than 10 feet. For slopes between 1 and 5 per cent the contour
-interval should be 5 feet. For flatter slopes the interval should not
-exceed 2 feet, and a one foot interval is sometimes desirable. In
-general the horizontal distances between contours should not exceed 400
-feet and they should be close enough to show important features of the
-natural drainage. Elevations should also be given at street
-intersections, and at abrupt changes in grade. For portions of the map
-on a smaller scale the contours need be sufficiently close to show only
-the drainage lines and the general slope of the land.
-
-The following may be shown on the preliminary map: the elevation of lots
-and cellars; the character of the built up districts, whether cheap
-frame residences, flat-roof buildings, manufacturing plants, etc.;
-property lines; width of streets between property lines and between curb
-lines; the width and character of the sidewalks and pavements; street
-car and railroad tracks; existing underground structures such as sewers,
-water pipes, telephone conduits, etc.; the location of important
-structures which may have a bearing on the design of the sewers such as
-bridges, railroad tunnels, deep cuts, culverts, etc.; and the location
-of possible sewer outlets and the sites for sewage disposal plants.
-
-Fig. 24 shows a preliminary map for a section of a city, on which the
-necessary information has been entered. The map is made from survey
-notes. All streets are paved with brick. The alleys are unpaved. The
-entire section is built up with high-class detached residences averaging
-one to each lot. The lots vary from 1 to 3 feet above the elevation of
-the street.
-
-
-=43. Layout of the Separate System.=—Upon completion of the preliminary
-map a tentative plan of the system is laid out. The lines of the sewer
-pipe are drawn in pencil, usually along the center line of the street or
-alley in such a manner that a sewer will be provided within 50 feet or
-less of every lot. The location of the sewers should be such as to give
-the most desirable combination of low cost, short house connections,
-proper depth for cellar drainage, and avoidance of paved streets. Some
-dispute arises among engineers as to the advisability of placing pipes
-in alleys, although there is less opposition to so placing sewers than
-any other utility conduit. The principal advantage in placing sewers in
-alleys is to avoid disturbing the pavement of the street, but if both
-street and alley are paved it is usually more economical to place the
-sewer in the street as the house connections will be shorter. On
-boulevards and other wide streets such as Meridian Avenue in Fig. 24,
-the sewers are placed in the parking on each side of the street, rather
-than to disturb the pavement and lay long house connections to the
-center of the street.
-
-All pipes should be made to slope, where possible, in the direction of
-the natural slope of the ground. The preliminary layout of the system is
-shown in Fig. 24. The lowest point in the portion of the system shown is
-in the alley between Alabama and Tennessee Streets. The flow in all
-pipes is towards this point, and only one pipe drains away from any
-junction, except that more than one pipe may drain from a terminal
-manhole on a summit.
-
-
-=44. Location and Numbering of Manholes.=—Manholes are next located on
-the pipes of this tentative layout. Good practice calls for the location
-of a manhole at every change in direction, grade, elevation, or size of
-pipe, except in sewers 60 inches in diameter or larger. The manholes
-should not be more than 300 to 500 feet apart, and preferably as close
-as 200 to 300 feet. In sewers too small for a man to enter the distance
-is fixed by the length of sewer rods which can be worked successfully.
-In the larger sewers the distances are sometimes made greater but
-inadvisedly so, since quick means of escape should be provided for
-workmen from a sudden rise of water in the sewer, or the effect of an
-asphyxiating gas. In the preliminary layout the manholes are located at
-pipe intersections, changes in direction, and not over 300 to 500 feet
-apart on long straight runs at convenient points such as opposite street
-intersections where other sewers may enter.
-
-No standard system of manhole numbering has been adopted. A system which
-avoids confusion and is subject to unlimited extension is to number the
-manholes consecutively upwards from the outlet, beginning a new series
-of numbers prefixed by some index number or letter for each branch or
-lateral. This system has been followed with the manholes on Fig. 24.
-
-[Illustration:
-
- FIG. 24.—Typical Map Used in the Design of a Separate Sewer System.
-]
-
-[Illustration:
-
- FIG. 25.—Typical Map Used in the Design of a Storm Sewer System.
-]
-
-
-=45. Drainage Areas.=—The quantity of dry weather sewage is determined
-by the population rather than the topography. Lot lines and street
-intersections or other artificial lines marking the boundaries between
-districts are therefore taken as watershed lines for sanitary sewers.
-The quantity of sewage to be carried and the available slope are the
-determining factors in fixing the diameter of the sewer. Since there may
-be no change in diameter or slope between manholes the quantity of
-sewage delivered by a sewer into any manhole will determine the diameter
-of the sewer between it and the next manhole above. In order to
-determine the additional amount contributed between manholes a line is
-drawn around the drainage area tributary to each manhole. This line
-generally follows property lines and the center lines of streets or
-alleys, its position being such that it includes all the area draining
-into one manhole, and excludes all areas draining elsewhere. An entire
-lot is usually assumed to lie within the drainage area into which the
-building on the lot drains. In laying out these areas it is best to
-commence at the upper end of a lateral and work down to a junction. Then
-start again at the upper end of another lateral entering this junction,
-and continue thus until the map has been covered.
-
-The areas are given the same numbers as the manholes into which they
-drain. The dividing lines for the drainage areas on Fig. 24 are shown as
-dot and dash lines, and the areas enclosed are appropriately numbered.
-If more than one sewer drains into the same manhole the area should be
-subdivided so that each subdivision encloses only the area contributing
-through one sewer. Such a condition is shown at manhole _C_2. The areas
-are designated by subletters or symbols corresponding to the symbol used
-for the sewer into which they drain. For example, the two areas
-contributing to manhole _C_2 are lettered _C_2_{_K_} and _C_2_{_D_}. The
-sewer from manhole _C_3 to _C_2 receives no addition, it being assumed
-that all the lots adjacent to it drain into the sewer on the alley.
-There is therefore no area _C_2. Likewise there is no area _A_1_{_C_}.
-
-
-=46. Quantity of Sewage.=—The remaining work in the computation of the
-quantity of sewage is best kept in order by a tabulation. Table 19 shows
-the computations for the sewers discharging from the east into manhole
-No. 142. The computation should begin at the upper end of a lateral,
-continue to a junction, and then start again at the upper end of another
-lateral entering this junction. Each line in the table should be filled
-in completely from left to right before proceeding with the computations
-on the next line. In the illustrative solution in Table 19, computations
-for quantity have not been made between manholes where it was apparent
-that there would be an insufficient additional quantity to necessitate a
-change in the size of the pipe.
-
-In making these computations the assumptions of quantity and other
-factors given below indicate the sort of assumptions which must be made,
-based on such studies as are given in Chapter III. The density of
-population was taken as 20 persons per acre, the assumption being based
-on the census and the character of the district. The average sanitary
-sewage flow was taken as 100 gallons per capita per day. The per cent
-which the maximum dry weather flow is of the average was taken as _M_ =
-500⁄_P_^⅕, in which _P_ is the population in thousands. The per cent is
-not to exceed 500 nor to be less than 150. The rate of infiltration of
-ground water was assumed as 50,000 gallons per mile of pipe per day.
-
-In the first line of Table 19, the entries in columns (1) to (6) are
-self-explanatory. There are no entries in columns (7) to (10), as no
-additional sewage is contributed between manholes 3.5 and 3.4. In column
-(11), 2250 persons are recorded as the number tributary to manhole No.
-3.5 in the district to the north and west. These people contribute an
-average of 100 gallons per person per day, or a total of 0.346 second
-foot. This quantity is entered in column (13). The figure in column (14)
-is obtained from the expression _M_ = (500)⁄_P_^⅕. Column (15) is .01 of
-the product of columns (13) and (14). Column (16) is the product of the
-length of pipe between manholes 3.5 and 3.4, and the ground water unit
-reduced to cubic feet per second. Column (17) is the sum of column (16),
-and all of the ground water tributary to manhole 3.5, which is not
-recorded in the table. Column (18) is the sum of columns (15) and (17).
-
-No new principle is represented in the second and third lines.
-
-In the fourth line the first 10 columns need no further explanation. The
-(11th) column is the sum of the (10th) column, and the (11th) column in
-the third line. It represents the total number of persons tributary to
-manhole 3.4 on lateral No. 8. Column (13) in the fourth line is the sum
-of column (13) in the third line and the (12th) column in the fourth
-line, and the (15th) column in the fourth line is the product of the 2
-preceding columns in the fourth line. Note that in no case is the figure
-in column (15) the sum of any previous figures in column (15). With this
-introduction the student should be able to check the remaining figures
-in the table, and should compute the quantity of sewage entering manhole
-No. 142 from the west, making reasonable assumptions for the tributary
-quantities from beyond the limits of the map.
-
- TABLE 19
-
- COMPUTATIONS FOR QUANTITY OF SEWAGE FOR A SEPARATE SEWERAGE SYSTEM
-
- ──────────┬──────────┬──────────┬───────┬───────┬──────┬───────┬─────
- On Street │ From │To Street │ From │ To │Length│Mark of│Area,
- │ Street │ │Manhole│Manhole│ Feet │ Added │Acres
- │ │ │ │ │ │ Areas │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- ──────────┼──────────┼──────────┼───────┼───────┼──────┼───────┼─────
- Nebraska │Map margin│Alley S. │ 3.5│ 3.4│ 338│ │
- St. │ │ Grant │ │ │ │ │
- │ │ St. │ │ │ │ │
- Alley S. │Railroad │E. of │ 8.3│ 8.2│ 328│ 8.2│ 2.7
- of Grant│ │ Missouri│ │ │ │ │
- St. │ │ St. │ │ │ │ │
- Alley S. │E. of │E. of │ 8.2│ 8.1│ 355│ 8.1│ 3.41
- of Grant│ Missouri│ Kansas │ │ │ │ │
- St. │ St. │ St. │ │ │ │ │
- Alley S. │E. of │Nebraska │ 8.1│ 3.4│ 340│3.4_{8}│ 2.68
- of Grant│ Kansas │ St. │ │ │ │ │
- St. │ St. │ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 3.4│ 3.3│ 380│ │
- St. │ of Grant│ of │ │ │ │ │
- │ St. │ Meridian│ │ │ │ │
- │ │ │ │ │ │ 7.1│
- Alley S. │Railroad │Nebraska │ 7.2│ 3.3│ 800│3.3_{7}│ 7.14
- of │ │ St. │ │ │ │ │
- Meridian│ │ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 3.3│ 3.2│ 304│ │
- St. │ of │ of Smith│ │ │ │ │
- │ Meridian│ Av. │ │ │ │ │
- │ │ │ │ │ │ 6.1│
- Alley S. │Railroad │Nebraska │ 6.2│ 3.2│ 609│3.2_{6}│ 3.82
- of Smith│ │ St. │ │ │ │ │
- Ave. │ │ │ │ │ │ │
- Nebraska │Alley S. │S. of │ 3.2│ 3.1│ 300│ │
- St. │ of Smith│ Cordovez│ │ │ │ │
- │ Ave. │ St. │ │ │ │ │
- S. of │Railroad │Nebraska │ 4.1│ 3.1│ 410│3.1_{4}│ 3.10
- Cordovez│ │ St. │ │ │ │ │
- St. │ │ │ │ │ │ │
- S. of │Map margin│Nebraska │ 5.1│ 3.1│ 380│3.1_{5}│ 2.69
- Cordovez│ │ St. │ │ │ │ │
- St. │ │ │ │ │ │ │
- Nebraska │S. of │Long St. │ 3.1│ 148│ 172│ │
- St. │ Cordovez│ │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Map margin│Nebraska │ 149│ 148│ 380│ 148│ 1.53
- │ │ St. │ │ │ │ │
- Long St. │Nebraska │N. │ 148│ 147│ 492│ │
- │ St. │ Carolina│ │ │ │ │
- │ │ St. │ │ │ │ │
- Long St. │N. │Georgia │ 147│ 146│ 430│ │
- │ Carolina│ St. │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Georgia │Harris St.│ 146│ 145│ 419│ 146│ 0.81
- │ St. │ │ │ │ │ │
- │ │ │ │ │ │ 2.1│
- Long St. │Harris St.│Tennessee │ 145│ 143│ 725│143–145│ 6.6
- │ │ St. │ │ │ │ │
- │ │ │ │ │ │ │
- Column No.│ (2) │ (3) │ (4) │ (5) │ (6) │ (7) │ (8)
- (1) │ │ │ │ │ │ │
- ──────────┴──────────┴──────────┴───────┴───────┴──────┴───────┴─────
-
- ──────────┬──────────┬──────────┬──────────┬───────┬─────────┬─────────
- On Street │ From │To Street │Population│Number │ Total │ Avg.
- │ Street │ │ per Acre │ of │ Persons │Sanitary
- │ │ │ │Persons│Tributary│ Flow,
- │ │ │ │ │ │ C.F.S.
- │ │ │ │ │ │
- ──────────┼──────────┼──────────┼──────────┼───────┼─────────┼─────────
- Nebraska │Map margin│Alley S. │ │ │ 2250│ 0.0000
- St. │ │ Grant │ │ │ │
- │ │ St. │ │ │ │
- Alley S. │Railroad │E. of │ 20│ 54│ 54│ .0084
- of Grant│ │ Missouri│ │ │ │
- St. │ │ St. │ │ │ │
- Alley S. │E. of │E. of │ 20│ 68│ 122│ .0106
- of Grant│ Missouri│ Kansas │ │ │ │
- St. │ St. │ St. │ │ │ │
- Alley S. │E. of │Nebraska │ 20│ 54│ 176│ .0084
- of Grant│ Kansas │ St. │ │ │ │
- St. │ St. │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ │ │ 2428│ .0000
- St. │ of Grant│ of │ │ │ │
- │ St. │ Meridian│ │ │ │
- │ │ │ │ │ │
- Alley S. │Railroad │Nebraska │ 20│ 142│ 142│ .0221
- of │ │ St. │ │ │ │
- Meridian│ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ │ │ 2568│ .0000
- St. │ of │ of Smith│ │ │ │
- │ Meridian│ Av. │ │ │ │
- │ │ │ │ │ │
- Alley S. │Railroad │Nebraska │ 20│ 76│ 76│ .0119
- of Smith│ │ St. │ │ │ │
- Ave. │ │ │ │ │ │
- Nebraska │Alley S. │S. of │ │ │ 2644│ .0000
- St. │ of Smith│ Cordovez│ │ │ │
- │ Ave. │ St. │ │ │ │
- S. of │Railroad │Nebraska │ 20│ 62│ 62│ .0096
- Cordovez│ │ St. │ │ │ │
- St. │ │ │ │ │ │
- S. of │Map margin│Nebraska │ 20│ 54│ 54│ .0084
- Cordovez│ │ St. │ │ │ │
- St. │ │ │ │ │ │
- Nebraska │S. of │Long St. │ │ │ 2760│ .0000
- St. │ Cordovez│ │ │ │ │
- │ St. │ │ │ │ │
- Long St. │Map margin│Nebraska │ 20│ 31│ 31│ .0048
- │ │ St. │ │ │ │
- Long St. │Nebraska │N. │ │ │ 2791│ .0000
- │ St. │ Carolina│ │ │ │
- │ │ St. │ │ │ │
- Long St. │N. │Georgia │ │ │ 2791│1.000[33]
- │ Carolina│ St. │ │ │ │
- │ St. │ │ │ │ │
- Long St. │Georgia │Harris St.│ 20│ 16│ 2807│ .0025
- │ St. │ │ │ │ │
- │ │ │ │ │ │
- Long St. │Harris St.│Tennessee │ 20│ 132│ 2936│ .0205
- │ │ St. │ │ │ │
- │ │ │ │ │ │
- Column No.│ (2) │ (3) │ (9) │ (10) │ (11) │ (12)
- (1) │ │ │ │ │ │
- ──────────┴──────────┴──────────┴──────────┴───────┴─────────┴─────────
-
- ──────────┬──────────┬──────────┬──────────┬────────┬─────────
- On Street │ From │To Street │Cumulative│Per cent│ Total
- │ Street │ │ Avg. │ Max. │ Max.
- │ │ │ Sanitary │Sanitary│Sanitary,
- │ │ │ Flow, │ is of │ C.F.S.
- │ │ │ C.F.S. │Average │
- ──────────┼──────────┼──────────┼──────────┼────────┼─────────
- Nebraska │Map margin│Alley S. │ 0.346│ 425│ 1.47
- St. │ │ Grant │ │ │
- │ │ St. │ │ │
- Alley S. │Railroad │E. of │ .0084│ 500│ 0.041
- of Grant│ │ Missouri│ │ │
- St. │ │ St. │ │ │
- Alley S. │E. of │E. of │ .0190│ 500│ 0.095
- of Grant│ Missouri│ Kansas │ │ │
- St. │ St. │ St. │ │ │
- Alley S. │E. of │Nebraska │ .0274│ 500│ 0.137
- of Grant│ Kansas │ St. │ │ │
- St. │ St. │ │ │ │
- Nebraska │Alley S. │Alley S. │ .373│ 423│ 1.58
- St. │ of Grant│ of │ │ │
- │ St. │ Meridian│ │ │
- │ │ │ │ │
- Alley S. │Railroad │Nebraska │ .0221│ 500│ 0.111
- of │ │ St. │ │ │
- Meridian│ │ │ │ │
- Nebraska │Alley S. │Alley S. │ .395│ 414│ 1.63
- St. │ of │ of Smith│ │ │
- │ Meridian│ Av. │ │ │
- │ │ │ │ │
- Alley S. │Railroad │Nebraska │ .0119│ 500│ 0.060
- of Smith│ │ St. │ │ │
- Ave. │ │ │ │ │
- Nebraska │Alley S. │S. of │ .407│ 414│ 1.68
- St. │ of Smith│ Cordovez│ │ │
- │ Ave. │ St. │ │ │
- S. of │Railroad │Nebraska │ .0096│ 500│ 0.048
- Cordovez│ │ St. │ │ │
- St. │ │ │ │ │
- S. of │Map margin│Nebraska │ .0084│ 500│ 0.042
- Cordovez│ │ St. │ │ │
- St. │ │ │ │ │
- Nebraska │S. of │Long St. │ .425│ 409│ 1.74
- St. │ Cordovez│ │ │ │
- │ St. │ │ │ │
- Long St. │Map margin│Nebraska │ .0048│ 500│ 0.024
- │ │ St. │ │ │
- Long St. │Nebraska │N. │ .430│ 409│ 1.76
- │ St. │ Carolina│ │ │
- │ │ St. │ │ │
- Long St. │N. │Georgia │ .430│ 409│ 1.76
- │ Carolina│ St. │ │ │
- │ St. │ │ │ │
- Long St. │Georgia │Harris St.│ .433│ 407│ 1.76
- │ St. │ │ │ │
- │ │ │ │ │
- Long St. │Harris St.│Tennessee │ .454│ 403│ 1.83
- │ │ St. │ │ │
- │ │ │ │ │
- Column No.│ (2) │ (3) │ (13) │ (14) │ (15)
- (1) │ │ │ │ │
- ──────────┴──────────┴──────────┴──────────┴────────┴─────────
-
- ──────────┬──────────┬──────────┬─────────┬──────────┬──────┬──────
- On Street │ From │To Street │Increment│Cumulative│Total │ Line
- │ Street │ │of Ground│ Ground │Flow, │Number
- │ │ │ Water, │ Water, │C.F.S.│
- │ │ │ C.F.S. │ C.F.S. │ │
- │ │ │ │ │ │
- ──────────┼──────────┼──────────┼─────────┼──────────┼──────┼──────
- Nebraska │Map margin│Alley S. │ 0.005│ 0.0187│ 1.66│ 1
- St. │ │ Grant │ │ │ │
- │ │ St. │ │ │ │
- Alley S. │Railroad │E. of │ .0048│ .0048│ 0.046│ 2
- of Grant│ │ Missouri│ │ │ │
- St. │ │ St. │ │ │ │
- Alley S. │E. of │E. of │ .0052│ .010│ 0.105│ 3
- of Grant│ Missouri│ Kansas │ │ │ │
- St. │ St. │ St. │ │ │ │
- Alley S. │E. of │Nebraska │ .0050│ .015│ 0.152│ 4
- of Grant│ Kansas │ St. │ │ │ │
- St. │ St. │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ .0058│ .208│ 1.79│ 5
- St. │ of Grant│ of │ │ │ │
- │ St. │ Meridian│ │ │ │
- │ │ │ │ │ │
- Alley S. │Railroad │Nebraska │ .0117│ .0117│ 0.123│ 6
- of │ │ St. │ │ │ │
- Meridian│ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ .0045│ .224│ 1.85│ 7
- St. │ of │ of Smith│ │ │ │
- │ Meridian│ Av. │ │ │ │
- │ │ │ │ │ │
- Alley S. │Railroad │Nebraska │ .0089│ .0089│ 0.069│ 8
- of Smith│ │ St. │ │ │ │
- Ave. │ │ │ │ │ │
- Nebraska │Alley S. │S. of │ .0044│ .237│ 1.92│ 9
- St. │ of Smith│ Cordovez│ │ │ │
- │ Ave. │ St. │ │ │ │
- S. of │Railroad │Nebraska │ .006│ .006│ 0.054│ 10
- Cordovez│ │ St. │ │ │ │
- St. │ │ │ │ │ │
- S. of │Map margin│Nebraska │ .0056│ .0056│ 0.048│ 11
- Cordovez│ │ St. │ │ │ │
- St. │ │ │ │ │ │
- Nebraska │S. of │Long St. │ .0025│ .251│ 1.99│ 12
- St. │ Cordovez│ │ │ │ │
- │ St. │ │ │ │ │
- Long St. │Map margin│Nebraska │ .0056│ .0056│ 0.030│ 13
- │ │ St. │ │ │ │
- Long St. │Nebraska │N. │ .0072│ .264│ 2.02│ 14
- │ St. │ Carolina│ │ │ │
- │ │ St. │ │ │ │
- Long St. │N. │Georgia │ .0064│ 1.27│ 3.03│ 15
- │ Carolina│ St. │ │ │ │
- │ St. │ │ │ │ │
- Long St. │Georgia │Harris St.│ .0061│ 1.28│ 3.04│ 16
- │ St. │ │ │ │ │
- │ │ │ │ │ │
- Long St. │Harris St.│Tennessee │ .024│ 1.30│ 3.13│ 17
- │ │ St. │ │ │ │
- │ │ │ │ │ │
- Column No.│ (2) │ (3) │ (16) │ (17) │ (18) │
- (1) │ │ │ │ │ │
- ──────────┴──────────┴──────────┴─────────┴──────────┴──────┴──────
- TABLE 20
-
- COMPUTATIONS FOR SLOPE AND DIAMETER OF PIPES FOR A SEPARATE SEWERAGE
- SYSTEM
-
- ──────────┬──────────┬──────────┬───────┬───────┬──────┬───────────────
- On Street │ From │To Street │ From │ To │Length│El. of Surface
- │ Street │ │Manhole│Manhole│ Feet │
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- ──────────┼──────────┼──────────┼───────┼───────┼──────┼───────┬───────
- │ │ │ │ │ │ Upper │ Lower
- │ │ │ │ │ │Manhole│Manhole
- ──────────┼──────────┼──────────┼───────┼───────┼──────┼───────┼───────
- Nebraska │Map margin│Alley S. │ 3.5│ 3.4│ 338│ 105.8│ 102.4
- St. │ │ Grant │ │ │ │ │
- │ │ St. │ │ │ │ │
- Alley S. │Railroad │E. of │ 8.3│ 8.2│ 328│ 113.5│ 112.0
- of Grant│ │ Missouri│ │ │ │ │
- St. │ │ St. │ │ │ │ │
- Alley S. │E. of │E. of │ 8.2│ 8.1│ 355│ 112.0│ 107.7
- of Grant│ Missouri│ Kansas │ │ │ │ │
- St. │ St. │ St. │ │ │ │ │
- Alley S. │E. of │Nebraska │ 8.1│ 3.4│ 340│ 107.7│ 102.4
- of Grant│ Kansas │ St. │ │ │ │ │
- St. │ St. │ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 3.4│ 3.3│ 380│ 102.4│ 100.7
- St. │ of Grant│ of │ │ │ │ │
- │ St. │ Meridian│ │ │ │ │
- Alley S. │Railroad │Kansas St.│ 7.2│ 7.1│ 400│ 111.8│ 107.0
- of │ │ │ │ │ │ │
- Meridian│ │ │ │ │ │ │
- Alley S. │Kansas St.│Nebraska │ 7.1│ 3.3│ 400│ 107.0│ 100.7
- of │ │ St. │ │ │ │ │
- Meridian│ │ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 3.3│ 3.2│ 304│ 100.7│ 99.3
- St. │ of │ of Smith│ │ │ │ │
- │ Meridian│ Av. │ │ │ │ │
- Alley S. │Railroad │East of │ 6.2│ 6.1│ 305│ 109.3│ 105.3
- of Smith│ │ Kansas │ │ │ │ │
- Ave. │ │ St. │ │ │ │ │
- Alley S. │East of │Nebraska │ 6.1│ 3.2│ 304│ 105.3│ 99.3
- of Smith│ Kansas │ St. │ │ │ │ │
- Ave. │ St. │ │ │ │ │ │
- Nebraska │Alley S. │S. of │ 3.2│ 3.1│ 300│ 99.3│ 101.1
- St. │ of Smith│ Cordovez│ │ │ │ │
- │ Ave. │ St. │ │ │ │ │
- S. of │Railroad │Nebraska │ 4.1│ 3.1│ 410│ 100.8│ 101.1
- Cordovez│ │ St. │ │ │ │ │
- St. │ │ │ │ │ │ │
- S. of │Map margin│Nebraska │ 5.1│ 3.1│ 380│ 104.6│ 101.1
- Cordovez│ │ St. │ │ │ │ │
- St. │ │ │ │ │ │ │
- Nebraska │S. of │Long St. │ 3.1│ 148│ 172│ 101.1│ 98.7
- St. │ Cordovez│ │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Map margin│Nebraska │ 149│ 148│ 380│ 103.8│ 98.7
- │ │ St. │ │ │ │ │
- Long St. │Nebraska │N. │ 148│ 147│ 492│ 98.7│ 103.8
- │ St. │ Carolina│ │ │ │ │
- │ │ St. │ │ │ │ │
- Long St. │N. │Georgia │ 147│ 146│ 430│ 103.8│ 99.1
- │ Carolina│ St. │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Georgia │Harris St.│ 146│ 145│ 419│ 99.1│ 96.9
- │ St. │ │ │ │ │ │
- Alley S. │End of │Harris St.│ 2.2│ 2.1│ 350│ 105.2│ 98.1
- of Janis│ Janis │ │ │ │ │ │
- St. │ St. │ │ │ │ │ │
- Harris St.│Alley N. │Long St. │ 2.1│ 145│ 135│ 98.1│ 96.9
- │ of Janis│ │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Harris St.│Kentucky │ 145│ 144│ 258│ 96.9│ 94.4
- │ │ St. │ │ │ │ │
- Long St. │Kentucky │Tennessee │ 144│ 143│ 282│ 94.4│ 93.6
- │ St. │ St. │ │ │ │ │
- Tarbell │Harris St.│Long St. │ 1.1│ 143│ 417│ 98.7│ 92.6
- Ave. │ │ │ │ │ │ │
- Long St. │Tennessee │Alley W. │ 143│ 142│ 185│ 92.6│ 92.3
- │ St. │ of Tenn.│ │ │ │ │
- │ │ St. │ │ │ │ │
- │ │ │ │ │ │ │
- Column No.│ (2) │ (3) │ (4) │ (5) │ (6) │ (7) │ (8)
- (1) │ │ │ │ │ │ │
- ──────────┴──────────┴──────────┴───────┴───────┴──────┴───────┴───────
-
- ──────────┬──────────┬──────────┬──────┬──────┬──────┬────────┬────────
- On Street │ From │To Street │Total │Slope │ Dia. │Velocity│Capacity
- │ Street │ │Flow, │ │ of │ when │ when
- │ │ │C.F.S.│ │Pipe, │ Full, │ Full,
- │ │ │ │ │Inches│Ft. per │ Second
- │ │ │ │ │ │ Second │ Feet
- ──────────┼──────────┼──────────┼──────┼──────┼──────┼────────┼────────
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- ──────────┼──────────┼──────────┼──────┼──────┼──────┼────────┼────────
- Nebraska │Map margin│Alley S. │ 1.66│0.0108│ 10│ 3.25│ 1.78
- St. │ │ Grant │ │ │ │ │
- │ │ St. │ │ │ │ │
- Alley S. │Railroad │E. of │ 0.046│.00575│ 8│ 2.00│ 0.71
- of Grant│ │ Missouri│ │ │ │ │
- St. │ │ St. │ │ │ │ │
- Alley S. │E. of │E. of │ 0.105│ .0110│ 8│ 2.78│ 0.98
- of Grant│ Missouri│ Kansas │ │ │ │ │
- St. │ St. │ St. │ │ │ │ │
- Alley S. │E. of │Nebraska │ 0.152│ .0156│ 8│ 3.27│ 1.18
- of Grant│ Kansas │ St. │ │ │ │ │
- St. │ St. │ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 1.79│.00385│ 12│ 2.28│ 1.79
- St. │ of Grant│ of │ │ │ │ │
- │ St. │ Meridian│ │ │ │ │
- Alley S. │Railroad │Kansas St.│ │ .0120│ 8│ 2.90│ 1.03
- of │ │ │ │ │ │ │
- Meridian│ │ │ │ │ │ │
- Alley S. │Kansas St.│Nebraska │ 0.123│ .0157│ 8│ 3.28│ 1.18
- of │ │ St. │ │ │ │ │
- Meridian│ │ │ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 1.85│ .0042│ 12│ 2.36│ 1.85
- St. │ of │ of Smith│ │ │ │ │
- │ Meridian│ Av. │ │ │ │ │
- Alley S. │Railroad │East of │ │ .0131│ 8│ 3.00│ 1.08
- of Smith│ │ Kansas │ │ │ │ │
- Ave. │ │ St. │ │ │ │ │
- Alley S. │East of │Nebraska │ 0.069│ .0197│ 8│ 3.70│ 1.32
- of Smith│ Kansas │ St. │ │ │ │ │
- Ave. │ St. │ │ │ │ │ │
- Nebraska │Alley S. │S. of │ 1.92│.00213│ 15│ 2.00│ 2.45
- St. │ of Smith│ Cordovez│ │ │ │ │
- │ Ave. │ St. │ │ │ │ │
- S. of │Railroad │Nebraska │ │.00574│ 8│ 2.00│ 0.71
- Cordovez│ │ St. │ │ │ │ │
- St. │ │ │ │ │ │ │
- S. of │Map margin│Nebraska │ 0.054│.00854│ 8│ 2.46│ 0.87
- Cordovez│ │ St. │ │ │ │ │
- St. │ │ │ │ │ │ │
- Nebraska │S. of │Long St. │ 1.99│.00213│ 15│ 2.00│ 2.45
- St. │ Cordovez│ │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Map margin│Nebraska │ 0.030│ .0134│ 8│ 3.04│ 1.08
- │ │ St. │ │ │ │ │
- Long St. │Nebraska │N. │ 2.02│.00213│ 15│ 2.00│ 2.45
- │ St. │ Carolina│ │ │ │ │
- │ │ St. │ │ │ │ │
- Long St. │N. │Georgia │ 3.03│ .0016│ 18│ 2.00│ 3.50
- │ Carolina│ St. │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Georgia │Harris St.│ 3.04│ .0016│ 18│ 2.00│ 3.50
- │ St. │ │ │ │ │ │
- Alley S. │End of │Harris St.│ │ .0203│ 8│ 3.78│ 1.35
- of Janis│ Janis │ │ │ │ │ │
- St. │ St. │ │ │ │ │ │
- Harris St.│Alley N. │Long St. │ │ .0088│ 8│ 2.53│ 0.89
- │ of Janis│ │ │ │ │ │
- │ St. │ │ │ │ │ │
- Long St. │Harris St.│Kentucky │ │.00353│ 18│ 2.98│ 5.20
- │ │ St. │ │ │ │ │
- Long St. │Kentucky │Tennessee │ │.00635│ 18│ 4.00│ 7.00
- │ St. │ St. │ │ │ │ │
- Tarbell │Harris St.│Long St. │ │ .0146│ 8│ 3.18│ 1.14
- Ave. │ │ │ │ │ │ │
- Long St. │Tennessee │Alley W. │ 3.13│ .0016│ 18│ 2.00│ 3.50
- │ St. │ of Tenn.│ │ │ │ │
- │ │ St. │ │ │ │ │
- │ │ │ │ │ │ │
- Column No.│ (2) │ (3) │ (9) │ (10) │ (11) │ (12) │ (13)
- (1) │ │ │ │ │ │ │
- ──────────┴──────────┴──────────┴──────┴──────┴──────┴────────┴────────
-
- ──────────┬──────────┬──────────┬───────────────┬──────
- On Street │ From │To Street │ El. of Invert │ Line
- │ Street │ │ │Number
- │ │ │ │
- │ │ │ │
- │ │ │ │
- ──────────┼──────────┼──────────┼───────┬───────┼──────
- │ │ │ Upper │ Lower │
- │ │ │Manhole│Manhole│
- ──────────┼──────────┼──────────┼───────┼───────┼──────
- Nebraska │Map margin│Alley S. │ 97.80│ 94.40│ 1
- St. │ │ Grant │ │ │
- │ │ St. │ │ │
- Alley S. │Railroad │E. of │ 105.50│ 103.62│ 2
- of Grant│ │ Missouri│ │ │
- St. │ │ St. │ │ │
- Alley S. │E. of │E. of │ 103.61│ 99.70│ 3
- of Grant│ Missouri│ Kansas │ │ │
- St. │ St. │ St. │ │ │
- Alley S. │E. of │Nebraska │ 99.69│ 94.40│ 4
- of Grant│ Kansas │ St. │ │ │
- St. │ St. │ │ │ │
- Nebraska │Alley S. │Alley S. │ 94.07│ 92.61│ 5
- St. │ of Grant│ of │ │ │
- │ St. │ Meridian│ │ │
- Alley S. │Railroad │Kansas St.│ 103.80│ 99.00│ 6
- of │ │ │ │ │
- Meridian│ │ │ │ │
- Alley S. │Kansas St.│Nebraska │ 98.99│ 92.70│ 7
- of │ │ St. │ │ │
- Meridian│ │ │ │ │
- Nebraska │Alley S. │Alley S. │ 92.37│ 91.09│ 8
- St. │ of │ of Smith│ │ │
- │ Meridian│ Av. │ │ │
- Alley S. │Railroad │East of │ 101.30│ 97.30│ 9
- of Smith│ │ Kansas │ │ │
- Ave. │ │ St. │ │ │
- Alley S. │East of │Nebraska │ 97.29│ 91.30│ 10
- of Smith│ Kansas │ St. │ │ │
- Ave. │ St. │ │ │ │
- Nebraska │Alley S. │S. of │ 90.84│ 90.20│ 11
- St. │ of Smith│ Cordovez│ │ │
- │ Ave. │ St. │ │ │
- S. of │Railroad │Nebraska │ 92.80│ 90.62│ 12
- Cordovez│ │ St. │ │ │
- St. │ │ │ │ │
- S. of │Map margin│Nebraska │ 96.60│ 93.10│ 13
- Cordovez│ │ St. │ │ │
- St. │ │ │ │ │
- Nebraska │S. of │Long St. │ 90.04│ 89.87│ 14
- St. │ Cordovez│ │ │ │
- │ St. │ │ │ │
- Long St. │Map margin│Nebraska │ 95.80│ 90.70│ 15
- │ │ St. │ │ │
- Long St. │Nebraska │N. │ 89.86│ 88.94│ 16
- │ St. │ Carolina│ │ │
- │ │ St. │ │ │
- Long St. │N. │Georgia │ 88.69│ 88.00│ 17
- │ Carolina│ St. │ │ │
- │ St. │ │ │ │
- Long St. │Georgia │Harris St.│ 87.99│ 87.32│ 18
- │ St. │ │ │ │
- Alley S. │End of │Harris St.│ 97.20│ 90.10│ 19
- of Janis│ Janis │ │ │ │
- St. │ St. │ │ │ │
- Harris St.│Alley N. │Long St. │ 90.09│ 88.90│ 20
- │ of Janis│ │ │ │
- │ St. │ │ │ │
- Long St. │Harris St.│Kentucky │ 87.31│ 86.40│ 21
- │ │ St. │ │ │
- Long St. │Kentucky │Tennessee │ 86.39│ 84.60│ 22
- │ St. │ St. │ │ │
- Tarbell │Harris St.│Long St. │ 90.70│ 84.60│ 23
- Ave. │ │ │ │ │
- Long St. │Tennessee │Alley W. │ 83.77│ 83.47│ 24
- │ St. │ of Tenn.│ │ │
- │ │ St. │ │ │
- │ │ │ │ │
- Column No.│ (2) │ (3) │ (14) │ (15) │
- (1) │ │ │ │ │
- ──────────┴──────────┴──────────┴───────┴───────┴──────
-
-
-=47. Surface Profile.=—A profile of the surface of the ground along the
-proposed lines of the sewers should be drawn after the completion of the
-computations for quantity. An example of a profile is shown in Fig. 26
-for the line between manholes No. 3.5 and No. 147. The vertical scale
-should be at least 10 times the horizontal. A horizontal scale of 1 inch
-to 200 feet can be used where not much detail is to be shown, but a
-scale of one 1 to 100 feet is more common and more satisfactory and even
-one inch to 10 feet has been used. The information to be given and the
-method of showing it are illustrated on Fig. 26. The profile should show
-the character of the material to be passed through and the location of
-underground obstacles which may be encountered. The method of obtaining
-this information is taken up in Chapter II. The collection of the
-information should be completed as far as possible previous to design,
-and borings and other investigations made as soon as the tentative
-routes for the sewers have been selected.
-
-
-=48. Slope and Diameter of Sewers.=—After the quantity of sewage to be
-carried has been determined, and the profile of the ground surface has
-been drawn, it is possible to determine the slope and diameter of the
-sewer. A table such as No. 20 is made up somewhat similar to No. 19, or
-which may be an extension of Table 19 since the first 6 columns in both
-tables are the same. The elevation of the surface at the upper and lower
-manholes is read from the profile.
-
-The depth of the sewer below the ground surface is first determined.
-Sewers should be sufficiently deep to drain cellars of ordinary depth.
-In residential districts cellars are seldom more than 5 feet below the
-ground surface. To this depth must be added the drop necessary for the
-grade of the house sewer. Six-inch pipe laid on a minimum grade of 1.67
-per cent is a common size and slope restriction for house drains or
-sewers. An additional 12 inches should be allowed for the bends in the
-pipe and the depth of the pipe under the cellar floor. Where the
-elevation of the street and lots is about the same, and the street is
-not over 80 feet in width between property lines, a minimum depth of 8
-feet to the invert of sewers, 24 inches or less in diameter is
-satisfactory. This is on the assumption that the axes of the house drain
-and the sewer intersect. For larger pipes the depth should be increased
-so that when the street sewer is flowing full, sewage will not back up
-into the cellars or for any great distance into the tributary pipes.
-
-[Illustration:
-
- FIG. 26.—Typical Profile Used in the Design of a Separate Sewer
- System.
-]
-
-The grade or slope at which a sewer shall be may be fixed by: the slope
-of the ground surface; the minimum permissible self-cleansing velocity;
-a combination of diameter, velocity, and quantity; or the maximum
-permissible velocity of flow. Sewers are laid either parallel to the
-ground surface where the slope is sufficient or where possible without
-coming too near the surface they are laid on a flatter grade to avoid
-unnecessary excavation. The minimum permissible slope is fixed by the
-minimum permissible velocity.
-
-The velocity of flow in a sewer should be sufficient to prevent the
-sedimentation of sludge and light mineral matter. Such a velocity is in
-the neighborhood of 1 foot per second. Since sewers seldom flow full
-this velocity should be available under ordinary conditions of dry
-weather flow. The minimum velocity when full should therefore be about 2
-feet per second. Under this condition, the velocity of 1 foot per second
-is not reached until the sewer is less than 18 per cent full. The
-velocity in small sewers should be made somewhat faster than in large
-sewers since the velocity of flow for small depths in small pipes is
-less than for the same proportionate depth in large pipes. The maximum
-permissible velocity of flow is fixed at about 10 feet per second in
-order to avoid excessive erosion of the invert. If the sewer is
-carefully laid this limit may be exceeded in sanitary sewers.
-
-The method for determining the grade and diameter of sewers is best
-explained through an illustrative problem which is worked out in Table
-20 for the profile shown on Fig. 26. The figures are inserted in the
-table from left to right in each line, one line being completed before
-the next one is commenced. The headings in the first 6 columns are
-self-explanatory. The elevations of the surface at the upper and lower
-manholes are read from the profile. The total flow is read from column
-(18) in Table 19. The slope of the ground surface is then computed, and
-with the quantity, slope, and coefficient of roughness, the diameter of
-the pipe and the velocity of flow are read from Fig. 15.
-
-The following conditions may arise:
-
- (1) The diameter required is less than 8 inches. Use a diameter of
- 8 inches as experience has shown that the use of smaller diameters
- is unsatisfactory.
-
- (2) The velocity of flow when the sewer is full is less than 2
- feet per second. Increase the slope until the velocity when full
- is 2 feet per second.
-
- (3) The diameter of the pipe required is not one of the commercial
- sizes shown in Fig. 15. Use the next largest commercial size.
-
- (4) The slope of the ground surface is steeper than necessary to
- maintain the required minimum velocity and the upper end of the
- sewer is deeper than the required minimum depth. Place the sewer
- on the minimum permissible grade, or upon such a grade that its
- lower end will be at the minimum permissible depth.
-
- (5) The slope of the ground surface is so steep as to make the
- velocity of flow greater than the maximum rate permissible. Reduce
- the grade by deepening the sewer at the upper manhole and using a
- drop manhole at this point.
-
-It is not permissible to use a pipe larger than that called for by the
-above conditions. This is attempted sometimes in order to reduce the
-grade and thereby save excavation, under the rule of a minimum velocity
-of 2 feet per second when full. It is better to use the smaller pipe on
-the flat grade as the quantity of sewage is insufficient to fill the
-larger sewer and the minimum permissible velocity is more quickly
-reached.
-
-Having determined the slope, the diameter, and the capacity of the pipe
-to be used, these values are entered in the table. The elevations of the
-invert of the pipe at the upper and lower manholes are next computed and
-entered in the table. This method is followed until all of the
-diameters, slopes, and elevations have been determined.
-
-The slopes are computed from center to center of manholes, but an extra
-allowance of 0.01 of a foot is allowed by some designers for the
-increased loss in head in passing through the manhole. When it becomes
-necessary to increase the diameter of the sewer the top of the outgoing
-sewer is placed at the same elevation or below the top of the lowest
-incoming sewer. No extra allowance is made to compensate for loss in
-head in the manhole in this case. This case is illustrated in columns
-(14) and (15) in lines (16) and (17) of Table 20. All of the conditions
-listed above are illustrated in Table 20, except the condition for a
-velocity greater than 10 feet per second.
-
-The first condition is met at the head of practically every lateral, and
-is illustrated in the second line.
-
-The second condition is also illustrated in the second line. The slope
-of the ground surface is 0.0046, which gives a velocity of only 1.8 feet
-per second in an 8–inch pipe. The slope is therefore increased to
-0.00575, on which the full velocity is 2 feet per second.
-
-The third condition is met in the first line. The diameter called for to
-carry 1.66 cubic feet per second on a slope of 0.0108 is slightly less
-than 10 inches. A 10–inch pipe is therefore used and its full capacity
-and velocity are recorded.
-
-The fourth condition is illustrated in the fourteenth line. The cut at
-manhole No. 3.1 is 11.1 feet. The slope of the ground is 0.014, much
-steeper than is necessary to maintain the minimum velocity in a 15–inch
-pipe. The pipe is therefore placed on the minimum permissible slope, and
-excavation is saved. The student should check the figures in Table 20
-and be sure that they are understood before an attempt is made to make a
-design independently.
-
-
-=49. The Sewer Profile.=—The profile is next completed as shown in Fig.
-26, the pipe line being drawn in as the computations are made. The cut
-is recorded to the nearest ⅒th of a foot at each manhole, or change in
-grade. It should not be given elsewhere as it invites controversy with
-the contractor. The cut is the difference of the elevation of the invert
-of the lowest pipe in the trench at the point in question, and the
-surface of the ground.
-
-The stationing should be shown to the nearest ⅒th of a foot. It should
-commence at 0 + 00 at the outlet and increase up the sewer. The station
-of any point on the sewer may show the distance from it to the outlet,
-or a new system of stationing may be commenced at important junctions or
-at each junction.
-
-Elevations of the surface of the ground should be shown to the nearest
-⅒th of a foot, and the invert elevation to the nearest 1/100th of a
-foot.
-
-Only the main line sewer is shown in profile in Fig. 26. The profiles of
-the laterals computed in Table 20, have not been shown. The approximate
-location of all house inlets are shown on the profile and located
-exactly, and are made a matter of record during construction.
-
-
- DESIGN OF A STORM WATER SEWER SYSTEM
-
-
-=50. Planning the System.=—Storm sewer systems are seldom as extensive
-as separate or combined sewer systems, since storm sewage can be
-discharged into the nearest suitable point in a flowing stream or other
-drainage channel, whereas dry weather or combined sewage must be
-conducted to some point where its discharge will be inoffensive. The
-need of a comprehensive general plan of a storm sewer system is quite as
-great, however, as for a separate system. The haphazard construction of
-sewers at the points most needed for the moment results in the
-duplication of forgotten drains, expense in increasing the capacity of
-inadequate sewers, and difficult construction due to underground
-structures thoughtlessly located. A comprehensive plan permits the
-construction of sewers where they are needed as they are required, and
-enables all probable future needs to be cared for at a minimum of
-expense.
-
-The same preliminary survey, map, and underground information are
-necessary for the design of a storm sewer system as for a separate sewer
-system. The map shown on Fig. 25 has been used for the design of a
-storm-water sewer system.
-
-The steps in the design of a storm-water sewer system are:
-
-1st. Note the most advantageous points to locate the inlets and lay out
-the system to drain these inlets. 2nd. Determine the required capacity
-of the sewers by a study of the run-off from the different drainage
-areas. 3rd. Draw the profile and compute the diameter and slope of the
-pipes required.
-
-
-=51. Location of Street Inlets.=—The location of storm sewers is
-determined mainly by the desirable location of the street inlets. The
-inlets must therefore be located before the system can be planned. In
-general the inlets should be located so that no water will flow across a
-street or sidewalk, in order to reach the sewer. This requires that
-inlets be placed on the high corners at street intersections, in
-depressions between street intersections, and at sufficiently frequent
-intervals that the gutters may not be overloaded. City blocks are seldom
-so long as to necessitate the location of inlets between crossings
-solely on account of inadequate gutter capacity. The capacity of a
-gutter can be computed approximately by the application of Kutter’s
-formula. Inlet capacities are discussed in Chapter VI. When the area
-drained is sufficiently large to tax the capacity of the gutter or
-inlet, an inlet should be installed regardless of the location of the
-street intersections.
-
-The street inlets are located on the map as shown in Fig. 25. The sewer
-lines are then located so as to make the length of pipe to pass near to
-all inlets a minimum. Storm sewers are seldom placed near the center of
-a street because of the frequent crowded condition on this line.
-
-
-=52. Drainage Areas.=—The outline of a drainage area is drawn so that
-all water falling within the area outlined will enter the same inlet,
-and water falling on any point beyond the outline will enter some other
-inlet. This requires that the outline follow true drainage lines rather
-than the artificial land divisions used in locating the drainage lines
-in the design of sanitary sewers. The drainage lines are determined by
-pavement slopes, location of downspouts, paved or unpaved yards, grading
-of lawns and the many other features of the natural drainage which are
-altered by the building up of a city. The location of the drainage lines
-is fixed as the result of a study of local conditions.
-
-The watershed or drainage lines are shown on Fig. 25 by means of dot and
-dash lines. A drainage line passes down the middle of each street
-because the crown of the street throws the water to either side and
-directs it to different inlets. A watershed line is drawn about 50 feet
-west of such streets as Kentucky St., Florida St., etc., because the
-downspouts from the houses on those streets discharge or will discharge
-into the street on which they face. The location of any watershed line
-within 20 feet more or less is, in most cases, a matter of judgment
-rather than exactness. Each area is given an identifying number or mark
-which is useful only in design. It usually corresponds to the inlet
-number.
-
-
-=53. Computation of Flood Flow by McMath Formula.=—McMath’s Formula is
-used as an example of the method pursued when an empirical formula is
-adopted for the computation of run-off, and because of its frequent use
-in practice. Other formulas may be more satisfactory under favorable
-conditions.
-
-Computations should be kept in order by a tabulation such as is shown in
-Table 21, in which the quantity of storm flow discharged from the sewer
-at the foot of Tennessee St., on Fig. 25, has been computed by means of
-the McMath Formula, using the constants suggested for St. Louis
-conditions, _i_ = 2.75, and _c_ = 0.75. The solutions of the formula
-have been made by means of Fig. 11. The column headings in the Table are
-explanatory of the figures as recorded. The computation should begin at
-the upper end of a lateral, proceed to the first junction and then
-return to the head of another lateral tributary to this junction. They
-should be continued in the same manner until all tributary areas have
-been covered. Special computations will be necessary for the
-determination of the maximum quantity of storm water entering each inlet
-to avoid the flooding of an inlet or gutter. These computations have not
-been shown as they are so easily made by the application of McMath’s
-Formula to each area concerned.
-
-The determination of the average slope ratio is a matter of judgment,
-based on the average natural slope of the surface of the ground and an
-estimate of the probable future conditions.
-
-
-=54. Computation of Flood Flow by Rational Method.=—The rational method
-for the computation of storm-water run-off is described in Chapter III.
-An example of its application to storm sewer design is given here for
-the district shown in Fig. 25.[34] The computations are shown in Table
-21. As in the preceding designs the table has been filled in from left
-to right and line by line. Computations have started at the upper end of
-laterals tributary to each junction. The column headed _I_ represents
-the imperviousness factor in the expression _Q_ = _AIR_. It is based on
-judgment guided by the constants given in Chapter III concerning
-imperviousness. The column headed “Equivalent 100 per cent _I_ acres” is
-the product of the two preceding columns. It reduces all areas to the
-same terms so that they can be added for entry in the column headed
-“Total 100 per cent _I_ acres.” It may be necessary to record the values
-for this column on several lines where the imperviousnesses of the
-tributary areas are different. This condition is illustrated in the last
-line of the table, for the length of sewer nearest the outlet. In the
-preceding lines the imperviousness recorded represents an average for
-all the tributary areas.
-
- TABLE 21
-
-COMPUTATIONS FOR THE QUANTITY OF STORM SEWAGE AT THE FOOT OF TENNESSEE
- STREET ON FIGURE 25
-
- ─────────┬──────────┬──────────┬───────────┬─────────────────────────────────
- On Street│ From │To Street │Identifying│ By McMath’s Formula
- │ Street │ │ Number of │
- │ │ │ Acres │
- │ │ │ Drained │
- ─────────┼──────────┼──────────┼───────────┼──────────┬───────┬───────┬──────
- │ │ │ │Additional│ Total │ Slope │ Run
- │ │ │ │ Acres │ Acres │ of │Off in
- │ │ │ │ Drained │Drained│Surface│C.F.S.
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- ─────────┼──────────┼──────────┼───────────┼──────────┼───────┼───────┼──────
- State │N. │S. │ 91 and 92 │2.35 │ 2.35│ 0.005│ 5.5
- │ Carolina│ Carolina│ │ │ │ │
- State │S. │Georgia │88, 89 and │3.0 │ 5.35│ .005│ 10.8
- │ Carolina│ │ 90 │ │ │ │
- State │Georgia │Florida │85, 86 and │3.0 │ 8.35│ .007│ 16.5
- │ │ │ 87 │ │ │ │
- State │Florida │Kentucky │81, 83 and │3.0 │ 11.35│ .009│ 22.0
- │ │ │ 84 │ │ │ │
- State │Kentucky │Tennessee │79, 80 and │3.0 │ 14.35│ .010│ 28.0
- │ │ │ 82 │ │ │ │
- State │Texas │Louisiana │ 76 and │3.8 │ 3.8│ .005│ 8.3
- │ │ │ others │ │ │ │
- State │Louisiana │Alabama │73, 74 and │3.7 │ 7.5│ .007│ 15.0
- │ │ │ 75 │ │ │ │
- State │Alabama │Tennessee │70, 71 and │3.0 │ 10.5│ .006│ 19.0
- │ │ │ 72 │ │ │ │
- Tennessee│State │Talon │68, 69, 77 │4.3 │ 29.15│ .15│ 52
- │ │ │ and 78 │ │ │ │
- Talon │Albemarle │Tennessee │65, 66 and │2.8 │ 2.8│ .018│ 8.4
- │ │ │ 67 │ │ │ │
- Tennessee│Talon │Burnside │ 64 and │0.7 │ 29.85│ .15│ 55
- │ │ │ 64_a_ │ │ │ │
- Burnside │N. │S. │57, 58 and │2.84 │ 2.84│ .008│ 7.2
- │ Carolina│ Carolina│ 59 │ │ │ │
- Burnside │S. │Georgia │54, 55 and │3.88 │ 6.72│ .010│ 14.9
- │ Carolina│ │ 56 │ │ │ │
- Burnside │Georgia │Florida │50, 52 and │3.88 │ 10.60│ .012│ 22
- │ │ │ 53 │ │ │ │
- Burnside │Florida │Kentucky │47, 48 and │3.88 │ 14.48│ .013│ 30
- │ │ │ 51 │ │ │ │
- Burnside │Kentucky │Tennessee │44, 45 and │3.88 │ 18.36│ .013│ 36
- │ │ │ 46 │ │ │ │
- Tennessee│Burnside │Elm │ 42 and 43 │2.84 │ 51.05│ .015│ 82
- Elm │Above │Chetwood │ Included in next line below │ │
- │ Chetwood│ │ │ │
- Elm │Chetwood │Albemarle │31, 32 and │2.75 │ 2.75│ .007│ 7.0
- │ │ │ 33 │ │ │ │
- Elm │Albemarle │Tennessee │27, 28, 29 │5.75 │ 8.50│ .016│ 20
- │ │ │ and 30 │ │ │ │
- Tennessee│Elm │Varennes │25, 26 and │2.62 │ 62.17│ .017│ 100
- │ │ │ 41 │ │ │ │
- Varennes │S. │Georgia │17, 18 and │3.17 │ 3.17│ .010│ 8.3
- │ Carolina│ │ 19 │ │ │ │
- Varennes │Georgia │Florida │14, 15 and │3.17 │ 6.34│ .011│ 14.5
- │ │ │ 16 │ │ │ │
- Varennes │Florida │Kentucky │11, 12 and │3.17 │ 9.51│ .013│ 21
- │ │ │ 13 │ │ │ │
- Varennes │Kentucky │Tennessee │8, 9 and 10│3.17 │ 12.68│ .013│ 26
- Tennessee│Varennes │Boulevard │ 6 and 7 │2.32 │ 77.17│ .017│ 120
- Tennessee│Boulevard │Outlet │1, 2, 3, 4,│4.72 │ 81.89│ .017│ 122
- │ │ │ and 5 │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- ─────────┴──────────┴──────────┴───────────┴──────────┴───────┴───────┴──────
-
- ─────────┬──────────┬──────────┬───────────────────────────────────────────
- On Street│ From │To Street │ By Rational Method
- │ Street │ │
- │ │ │
- │ │ │
- ─────────┼──────────┼──────────┼─────┬─────┬──────────┬─────┬──────────────
- │ │ │Area,│ _I_ │Equivalent│Total│ Time of
- │ │ │Acres│ │ 100 Per │ 100 │Concentration,
- │ │ │ │ │ Cent _I_ │ Per │ Minutes
- │ │ │ │ │ Acres │Cent │
- │ │ │ │ │ │ _I_ │
- │ │ │ │ │ │Acres│
- ─────────┼──────────┼──────────┼─────┼─────┼──────────┼─────┼──────────────
- State │N. │S. │ 2.35│ 0.50│ 1.17│ 1.17│ 7.0
- │ Carolina│ Carolina│ │ │ │ │
- State │S. │Georgia │ 3.00│ .50│ 1.50│ 2.67│ 8.1
- │ Carolina│ │ │ │ │ │
- State │Georgia │Florida │ 3.00│ .50│ 1.50│ 4.17│ 9.0
- │ │ │ │ │ │ │
- State │Florida │Kentucky │ 3.00│ .50│ 1.50│ 5.67│ 9.9
- │ │ │ │ │ │ │
- State │Kentucky │Tennessee │ 3.00│ .50│ 1.50│ 7.17│ 10.7
- │ │ │ │ │ │ │
- State │Texas │Louisiana │ 3.80│ .35│ 1.33│ 1.33│ 10.0
- │ │ │ │ │ │ │
- State │Louisiana │Alabama │ 3.70│ .40│ 1.48│ 2.81│ 11.9
- │ │ │ │ │ │ │
- State │Alabama │Tennessee │ 3.00│ .45│ 1.35│ 4.16│ 12.9
- │ │ │ │ │ │ │
- Tennessee│State │Talon │ 4.30│ .50│ 2.15│13.48│ 14.5
- │ │ │ │ │ │ │
- Talon │Albemarle │Tennessee │ 2.80│ .40│ 1.12│ 1.12│ 8.0
- │ │ │ │ │ │ │
- Tennessee│Talon │Burnside │ 0.70│ .20│ 0.14│14.74│ 15.3
- │ │ │ │ │ │ │
- Burnside │N. │S. │ 2.84│ .55│ 1.56│ 1.56│ 10.0
- │ Carolina│ Carolina│ │ │ │ │
- Burnside │S. │Georgia │ 3.88│ .55│ 2.13│ 3.69│ 11.1
- │ Carolina│ │ │ │ │ │
- Burnside │Georgia │Florida │ 3.88│ .55│ 2.13│ 5.82│ 12.2
- │ │ │ │ │ │ │
- Burnside │Florida │Kentucky │ 3.88│ .55│ 2.13│ 7.95│ 13.1
- │ │ │ │ │ │ │
- Burnside │Kentucky │Tennessee │ 3.88│ .55│ 2.13│10.08│ 13.8
- │ │ │ │ │ │ │
- Tennessee│Burnside │Elm │ 2.84│ .45│ 2.28│26.10│ 15.7
- Elm │Above │Chetwood │ │ │ │ │
- │ Chetwood│ │ │ │ │ │
- Elm │Chetwood │Albemarle │ 2.75│ .40│ 1.10│ 1.10│ 8.0
- │ │ │ │ │ │ │
- Elm │Albemarle │Tennessee │ 5.75│ .45│ 2.59│ 3.69│ 9.5
- │ │ │ │ │ │ │
- Tennessee│Elm │Varennes │ 2.62│ .50│ 1.31│30.00│ 16.2
- │ │ │ │ │ │ │
- Varennes │S. │Georgia │ 3.17│ .55│ 1.74│ 1.74│ 9.0
- │ Carolina│ │ │ │ │ │
- Varennes │Georgia │Florida │ 3.17│ .55│ 1.74│ 3.48│ 9.9
- │ │ │ │ │ │ │
- Varennes │Florida │Kentucky │ 3.17│ .55│ 1.74│ 5.22│ 10.8
- │ │ │ │ │ │ │
- Varennes │Kentucky │Tennessee │ 3.17│ .55│ 1.74│ 6.96│ 11.4
- Tennessee│Varennes │Boulevard │ 2.32│ .55│ 1.28│32.84│ 16.5
- Tennessee│Boulevard │Outlet │ 0.18│ .80│ 0.14│ Area No. 1
- │ │ │ │ │ │
- │ │ │ 1.38│ .50│ 0.69│ Area No. 2
- │ │ │ 2.80│ .55│ 1.54│ Areas No. 3 and 4
- │ │ │ 0.36│ .75│ 0.27│35.48│ 16.9
- │ │ │ │ │ │ │
- ─────────┴──────────┴──────────┴─────┴─────┴──────────┴─────┴──────────────
-
- ─────────┬──────────┬──────────┬─────────────────────────────────┬──────
- On Street│ From │To Street │ By Rational Method │ Line
- │ Street │ │ │Number
- │ │ │ │
- │ │ │ │
- ─────────┼──────────┼──────────┼───┬────┬─────┬────┬───────┬─────┼──────
- │ │ │_R_│_Q_ │ _S_ │_V_ │ Sewer │Time │
- │ │ │ │ │ │ │Length,│ in │
- │ │ │ │ │ │ │ Feet │Sewer│
- │ │ │ │ │ │ │ │ │
- │ │ │ │ │ │ │ │ │
- │ │ │ │ │ │ │ │ │
- ─────────┼──────────┼──────────┼───┼────┼─────┼────┼───────┼─────┼──────
- State │N. │S. │4.8│ 5.6│0.011│ 4.6│ 300│ 1.1│ 1
- │ Carolina│ Carolina│ │ │ │ │ │ │
- State │S. │Georgia │4.6│12.2│ .010│ 5.5│ 300│ 0.9│ 2
- │ Carolina│ │ │ │ │ │ │ │
- State │Georgia │Florida │4.4│18.3│ .012│ 5.8│ 300│ 0.9│ 3
- │ │ │ │ │ │ │ │ │
- State │Florida │Kentucky │4.2│23.9│ .009│ 6.0│ 300│ 0.8│ 4
- │ │ │ │ │ │ │ │ │
- State │Kentucky │Tennessee │4.1│29.3│ .009│ 6.2│ 300│ 0.8│ 5
- │ │ │ │ │ │ │ │ │
- State │Texas │Louisiana │4.2│ 5.6│ .009│ 3.2│ 370│ 1.9│ 6
- │ │ │ │ │ │ │ │ │
- State │Louisiana │Alabama │3.9│11.0│ .011│ 5.2│ 300│ 1.0│ 7
- │ │ │ │ │ │ │ │ │
- State │Alabama │Tennessee │3.8│15.8│ .002│ 3.2│ 300│ 1.6│ 8
- │ │ │ │ │ │ │ │ │
- Tennessee│State │Talon │3.6│48.5│ .019│ 9.8│ 450│ 0.8│ 9
- │ │ │ │ │ │ │ │ │
- Talon │Albemarle │Tennessee │4.6│ 5.2│ .004│ 3.0│ 210│ 1.2│ 10
- │ │ │ │ │ │ │ │ │
- Tennessee│Talon │Burnside │3.5│51.5│ .006│ 5.0│ 120│ 0.4│ 11
- │ │ │ │ │ │ │ │ │
- Burnside │N. │S. │4.2│ 6.5│ .008│ 4.5│ 300│ 1.1│ 12
- │ Carolina│ Carolina│ │ │ │ │ │ │
- Burnside │S. │Georgia │4.0│14.8│ .007│ 4.7│ 300│ 1.1│ 13
- │ Carolina│ │ │ │ │ │ │ │
- Burnside │Georgia │Florida │3.9│22.7│ .011│ 5.8│ 300│ 0.9│ 14
- │ │ │ │ │ │ │ │ │
- Burnside │Florida │Kentucky │3.7│29.4│ .016│ 7.5│ 300│ 0.7│ 15
- │ │ │ │ │ │ │ │ │
- Burnside │Kentucky │Tennessee │3.7│37.3│ .019│ 9.2│ 300│ 0.5│ 16
- │ │ │ │ │ │ │ │ │
- Tennessee│Burnside │Elm │3.4│88.8│ .015│10.2│ 280.│ 0.5│ 17
- Elm │Above │Chetwood │ │ │ │ │ │ │ 18
- │ Chetwood│ │ │ │ │ │ │ │
- Elm │Chetwood │Albemarle │4.6│ 5.1│ .020│ 5.3│ 480│ 1.5│ 19
- │ │ │ │ │ │ │ │ │
- Elm │Albemarle │Tennessee │4.3│15.8│ .012│ 6.1│ 410│ 1.1│ 20
- │ │ │ │ │ │ │ │ │
- Tennessee│Elm │Varennes │3.4│ 102│ .012│10.2│ 180│ 0.3│ 21
- │ │ │ │ │ │ │ │ │
- Varennes │S. │Georgia │4.4│ 7.7│ .012│ 5.2│ 270│ 0.9│ 22
- │ Carolina│ │ │ │ │ │ │ │
- Varennes │Georgia │Florida │4.2│14.5│ .010│ 5.7│ 300│ 0.9│ 23
- │ │ │ │ │ │ │ │ │
- Varennes │Florida │Kentucky │4.1│21.4│ .017│ 7.7│ 300│ 0.6│ 24
- │ │ │ │ │ │ │ │ │
- Varennes │Kentucky │Tennessee │4.0│27.8│ .015│ 7.8│ 300│ 0.6│ 25
- Tennessee│Varennes │Boulevard │3.3│ 108│ .012│10.2│ 230│ 0.4│ 26
- Tennessee│Boulevard │Outlet │ │ │ │ │ │ │ 27
- │ │ │ │ │ │ │ │ │
- │ │ │ │ │ │ │ │ │ 28
- │ │ │ │ │ │ │ │ 29
- │ │ │3.3│ 117│Areas No. 1–5 inclusive │ 30
- │ │ │ │ │ │ │ │ │
- ─────────┴──────────┴──────────┴───┴────┴─────┴────┴───────┴─────┴──────
-
-The time of concentration in minutes is assumed by judgment for the
-first area. For all subsequent areas it is the sum of the time of
-concentration for the area or areas tributary to the inlet next above
-and the time of flow in the sewer from the inlet next above to the inlet
-in question. For example, in line 2 the time 8.1 minutes is the sum of
-7.0 minutes time of concentration to the inlet at the corner of State
-and North Carolina St., and the time of flow of 1.1 minute in the sewer
-on State St. from North Carolina St. to South Carolina St. Where two
-sewers are converging as at the corner of Varennes Road and Tennessee
-St. the longest time is taken. For example, the time of concentration
-down Varennes Road to Tennessee St. is shown in line 25 as 11.4 + 0.6 =
-12.0 minutes. The time to the same point down Tennessee St. is shown in
-line 21 as 16.2 + 0.3 = 16.5 minutes. This time is therefore used in
-line 26.
-
-_R_, the rate of rainfall in inches per hour is determined by Talbot’s
-formula.
-
-_Q_, is in cubic feet per second and is the product of the 8th and 10th
-columns. Since the 8th column is the sum of the products of the 5th and
-the 6th columns for the lines representing tributary areas, then the
-11th column is the product of _A_, _I_, and _R_.
-
-_S_, is the slope on which it is assumed that the sewer will be laid. It
-is usually assumed as parallel to the ground surface unless the velocity
-for this slope becomes less than 2 feet per second. In such a case the
-slope is taken as one which will cause this velocity.
-
-_V_, the velocity in feet per second, is computed from diagrams for the
-solution of Kutter’s formula. The length in feet is scaled from the map
-as the distance between inlets or groups of inlets, and the time is the
-length in feet divided by the velocity in feet per minute.
-
-Having computed the quantity of flow to be carried in the sewer, the
-design is completed by drawing the profile and computing the diameters
-and slopes by the same method as used in the design of separate sewers.
-
-
-
-
- CHAPTER VI
- APPURTENANCES
-
-
-=55. General.=—The appurtenances to a sewerage system are those devices
-which, in addition to the pipes and conduits, are essential to or are of
-assistance in the operation of the system. Under this heading are
-included such structures and devices as: manholes, lampholes,
-flush-tanks, catch-basins, street inlets, regulators, siphons,
-junctions, outlets, grease traps, foundations and underdrains.
-
-
-=56. Manholes.=—A manhole is an opening constructed in a sewer, of
-sufficient size to permit a man to gain access to the sewer. Manholes
-are the most common appurtenances to sewerage systems and are used to
-permit inspection and the removal of obstructions from the pipes. The
-details of the Baltimore standard manholes are shown in Fig. 27 and a
-manhole on a large sewer in Omaha is shown in Fig. 28. The features of
-these designs which should be noted are the size of the opening and
-working space, and the strength of the structure. Manhole openings are
-seldom made less than 20 inches in diameter and openings 24 inches in
-diameter are preferable. A man can pass through any opening that he can
-get his hips through provided he can bend his knees and twist his
-shoulders immediately on passing the hole. For this reason the manhole
-should widen out rapidly immediately below the opening, as shown in Fig.
-27 and 38.
-
-The walls of the manhole may be built either of brick or of concrete.
-Brick is more commonly used, as the forms necessary for concrete make
-the work more expensive unless they can be used a number of times. The
-walls of the manhole should be at least 8 inches thick. Greater
-thicknesses are used in treacherous soils and for deep manholes, or to
-exclude moisture. A rough expression for the thickness of the walls of a
-brick manhole more than 12 feet deep in ordinary firm material is _t_ =
-_d_⁄2 + 2, in which _t_ is the thickness in inches and _d_ is the depth
-in feet. The thickness of brick walls may be changed every 5 to 10 feet
-or so. Concrete walls may be built thinner than brick walls.
-
-[Illustration:
-
- FIG. 27.—Baltimore Standard Manhole Details.
-]
-
-The bottoms of brick manholes are frequently made of concrete as shown
-in Fig. 27. The floor slopes towards the center and is constructed so
-that the sewage flows in a half round or U-shaped channel of greater
-capacity than the tributary sewers. The sides of the channel should be
-high enough to prevent the overflow of sewage onto the sloping floor,
-which should have a pitch of about one vertical to 10 or 12 horizontal.
-In manholes where two or more sewers join at approximately the same
-level the channels in the bottom should join with smooth easy curves.
-Where the inlet and outlet pipes are not of the same diameter the tops
-of the pipes should ordinarily be placed at the same elevation to
-prevent back flow in the smaller pipes when the larger pipes are flowing
-full.
-
-The dimensions of the manhole should not be less than 3 feet wide by 4
-feet long for a height of at least 4 feet, when built in the form of an
-ellipse, or 4 feet in diameter when built circular. No standard method
-for the reduction of the diameter of the manhole near the top is
-observed, the rate being more or less dependent on the depth of the
-manhole. The use of sloping sides above the frost line is desirable as
-such a form is more resistant to heaving by frost action.
-
-For sewers up to 48 inches in diameter the manhole is usually centered
-over the intersection of the pipes and has a special foundation. For
-larger sewers the manhole walls spring from the walls of the sewer as
-shown in Fig. 28.
-
-[Illustration:
-
- FIG. 28.—Details of a Manhole and a Well Hole.
-]
-
-In the case of a decided drop in the elevation of a sewer, or of a
-tributary sewer appreciably higher than an outlet in any manhole, the
-sewage is allowed to drop vertically at the manhole, hence the name drop
-manhole. The Baltimore standard drop manhole is shown in Fig. 27. A well
-hole is an unusually deep drop manhole in which the force of the
-vertical drop of sewage is broken by a series of baffle plates, or by a
-sump at the bottom of the well hole. Fig. 28 shows a well hole at St.
-Paul, Minn. The use of drop manholes can be avoided in large sewers by
-the construction of a flight of steps or flight sewer as shown in Fig.
-29, which allows the use of a steep grade and serves to break the
-velocity of the sewage.
-
-The specifications of the Sanitary District of Chicago, covering the
-construction of manhole covers and frames are:
-
- All castings shall be of tough, close grained, gray iron, free
- from blow holes, shrinkage and cold shuts, and sound, smooth,
- clean and free from blisters and all defects.
-
- All castings shall be made accurately to dimensions to be
- furnished and shall be planed where marked or where otherwise
- necessary to secure perfectly flat and true surfaces. Allowance
- shall be made in the patterns so that the specified thickness
- shall not be reduced.
-
- All castings shall be thoroughly cleaned and painted before
- rusting begins and before leaving the shop with two coats of high
- grade asphaltum or any other varnish that the Engineer may direct.
- After the castings have been placed in a satisfactory manner, all
- foreign adhering substances shall be removed and the castings
- given one additional coat of asphaltum. No castings shall be
- accepted the weight of which shall be less than that due to its
- dimensions by more than 5 per cent.
-
-[Illustration:
-
- FIG. 29.—Flight Sewer at Baltimore.
-
- Eng. Record, Vol. 59, p. 161.
-]
-
-[Illustration:
-
- FIG. 30.—Baltimore Standard Manhole Frame and Cover.
-]
-
-The weights of frames and covers in use vary from 200 to 600 pounds, the
-weight of the frame being about 5 times that of the cover. The lightest
-weights are used where no traffic other than an occasional pedestrian
-will pass over the manhole. Frames and covers weighing about 400 pounds
-are commonly used on residential streets, whereas 600 pound frames and
-covers are desirable in streets on which the traffic is heavy. The
-frames should be so designed that the pavement will rest firmly against
-it and wear at the same rate as the surrounding street surface.
-Experience has shown that vertical sides should be used for the outside
-of the frame to approach this condition, and that the frame should not
-be less than 8 inches high. The cover should be roughened in some
-desirable pattern as shown in Fig. 30. Smooth covers become dangerously
-slippery. Where the ventilation of the sewers is not satisfactory the
-manhole covers are sometimes perforated. This is undesirable from other
-points of view as the rising odors and vapors are obnoxious at the
-surface and the entering dirt and water are detrimental to the operation
-of the sewer. The stealing and destruction of manhole covers and the
-unauthorized entering of sewers has occasionally required the locking of
-the covers to the frame when in place. The locks commonly used consist
-of a tumbler which falls into place when the manhole is closed, and
-which can be opened only by a special wrench or hook. Adjustable frames
-are sometimes used where the street grade is settling, or may be raised
-in order that the elevation of the top of the cover may be made to
-conform to that of the street surface, without reconstructing the top of
-the manhole. One type of adjustable cover is shown in Fig. 31. Manhole
-covers should be so marked that the sanitary sewer can be distinguished
-from the storm-water sewer, and both from the telephone conduit, etc.
-
-[Illustration:
-
- FIG. 31.—Adjustable Manhole Frame and Cover.
-]
-
-Iron steps are set into the walls of the manhole about 15 inches apart
-vertically to allow entrance and exit to and from the manhole.
-Galvanized iron is preferable to unprotected metal as the action of rust
-is particularly rapid in the moist air of the sewer. One type of these
-manhole steps is shown in Fig. 27. The steps should have a firm grip in
-the wall as a loose step is a source of danger.
-
-[Illustration:
-
- FIG. 32.—Baltimore Standard Lamphole.
-]
-
-
-=57. Lampholes.=—A lamphole is an opening from the surface of the ground
-into a sewer, large enough to permit the lowering of a lantern into the
-sewer. Lampholes are used in the place of manholes to permit the
-inspection or the flushing of sewers, and to avoid the expense of a
-manhole. They are located from 300 to 400 feet from the nearest manhole
-in such a manner that a lamp lowered in the lamp hole can be seen from
-the two nearest manholes.
-
-Lampholes should be constructed of 8– to 12–inch tile or cast-iron pipe.
-The lower section should be a cast-iron T on a firm foundation, but if
-constructed of tile it should be reinforced with concrete to take up the
-weight of the shaft. The details of the Baltimore standard lamphole are
-shown in Fig. 32. Lampholes are not commonly used on sewerage systems on
-account of their lack of real usefulness and the troubles encountered by
-breaking of the pipe below the shaft.
-
-
-=58. Street Inlets.=—A street inlet is an opening in the gutter through
-which storm water gains access to the sewer. The types used in different
-cities vary widely. Details of an inlet in successful use are shown in
-Fig. 33. The figure shows also a common form of connection to the sewer.
-A water-seal trap is sometimes used to prevent the escape of odors from
-the sewer. Care must be taken in design that such traps do not freeze in
-winter nor dry out in summer, although it is not always possible to
-prevent these contingencies.
-
-[Illustration:
-
- FIG. 33.—Details of an Untrapped Street Inlet, without Catch-Basin.
-]
-
-The important features to be observed in the design of a street inlet
-are: height and length of opening, character of grating, and location.
-The general location of inlets is discussed in Chapter V. The clear
-height of opening commonly used is from 5 to 6 inches, with a clear
-length of 24 to 30 inches or longer. Inlets of this size have given
-satisfaction on paved streets with moderate slopes, where the drainage
-area is not greater than 10,000 to 12,000 square feet of pavement. W. W.
-Horner states:[35]
-
- The St. Louis type of inlet “old” style was a vertical opening in
- the curb 8 inches high and 4 feet in length with a horizontal bar
- making the net opening about 5 inches. It has a broad sill
- extending under the sidewalk. The “new” style inlet is 4½ feet
- long with a clear opening of 6 inches and no bar. The sill is done
- away with and the opening drops down directly from the curb. Tests
- were made of the capacity of this inlet on pavements on different
- slopes with sumps of depths varying from 0 to 6 inches in front of
- the inlet, extending out 3 feet from the gutter, and returning to
- the elevation of the gutter at a slope of 3 inches to the foot.
- The results of these tests are shown in Table 22. The capacity of
- the inlet is expressed as the amount of water entering just before
- some water begins to lap past. If a large amount of water is
- allowed to flow past much more water will enter the inlet thus
- furnishing a factor of safety for large storms. It was noted that
- by beginning the rise in the pavement about opposite the middle of
- the inlet the capacity of the inlet was increased from 20 to 50
- per cent.
-
- TABLE 22
-
- CAPACITIES OF ST. LOUIS STREET INLETS
-
- From tests by W. W. Horner. Cubic feet per second
- ─────────┬───────────────────┬───────────────────
- Slope in │ 0.42 │ 1.5
- Per Ct. │ │
- ─────────┼────┬────┬────┬────┼────┬────┬────┬────
- Depth of │ 0.0│ 2│ 4│ 6│ 0│ 2│ 4│ 6
- Sump, │ │ │ │ │ │ │ │
- Inches │ │ │ │ │ │ │ │
- Capacity,│ │ │1.27│ │ │ │ │
- old │ │ │ │ │ │ │ │
- style │ │ │ │ │ │ │ │
- Capacity,│ 0.1│ 0.5│ 1.5│ 2.5│0.08│ 0.4│ 1.1│ 2.1
- new │ │ │ │ │ │ │ │
- style │ │ │ │ │ │ │ │
- ─────────┴────┴────┴────┴────┴────┴────┴────┴────
-
- ─────────┬───────────────────┬───────────────────
- Slope in │ 2.85 │ 4.5
- Per Ct. │ │
- ─────────┼────┬────┬────┬────┼────┬────┬────┬────
- Depth of │ 0│ 2│ 4│ 6│ 0│ 2│ 4│ 6
- Sump, │ │ │ │ │ │ │ │
- Inches │ │ │ │ │ │ │ │
- Capacity,│0.03│0.25│0.78│1.49│ │ │ │
- old │ │ │ │ │ │ │ │
- style │ │ │ │ │ │ │ │
- Capacity,│0.03│0.28│0.87│1.62│0.02│0.15│0.45│ 1.0
- new │ │ │ │ │ │ │ │
- style │ │ │ │ │ │ │ │
- ─────────┴────┴────┴────┴────┴────┴────┴────┴────
-
-Gratings with horizontal bars will admit more water than gratings with
-vertical bars, but they will also admit more rubbish such as sticks,
-papers, leaves, etc., which serve to clog the sewers. Vertical barred
-gratings and gratings in the bottom of the gutter clog more quickly than
-other types. In the selection of the type of grating to be used a
-decision must be made as to whether it is more desirable to clean the
-sewer or catch-basin, or to flood the street as a result of clogged
-inlets. Where catch-basins are used or the sewers are large, horizontal
-bars are more satisfactory. The openings between bars should be small
-enough to prevent the entrance of a horse’s hoof or objects of
-sufficient size to clog the sewer. Four inches in the clear for vertical
-openings and 6 inches for horizontal openings are reasonable sizes.
-
-The location of the inlets at the intersection of the two curb lines at
-a corner results in a lower first cost but on heavily traveled streets
-this may result in a higher maintenance cost than for other locations
-because of the concentration of traffic at street corners, hammering the
-inlet casting out of shape or position. Vehicles making short turns will
-tend to climb the curb and will intensify the wear upon the inlet. These
-objections can be overcome by the use of two inlets at each corner, set
-back far enough from the curb intersection to avoid interference with
-the cross-walks. This also makes it possible to raise the cross-walks
-without the use of gutters under them.
-
-The size of the pipe from the inlet to the catch-basin or sewer should
-be large enough to care for all of the water which may enter the inlet.
-As the capacity of the inlet is seldom known with accuracy and the
-capacity of the pipe is difficult of determination, it has become
-customary to use a 10–inch or a 12–inch connecting pipe for each
-ordinary independent inlet.
-
-
-=59. Catch-basins.=—Catch-basins are used to interrupt the velocity of
-sewage before entering the sewer, causing the deposition of suspended
-grit and sludge and the detention of floating rubbish which might enter
-and clog the sewer. A separate catch-basin may be used for each inlet,
-or to save expense, the pipes from several inlets may discharge into one
-catch-basin.
-
-[Illustration:
-
- FIG. 34.—Catch-basin.
-
- Outlets are not always trapped.
-]
-
-The types in successful use are extremely varied, but the distinguishing
-feature of all is an outlet located above the floor of the basin. A
-common form of catch-basin is shown in Fig. 34. It is constructed
-similar to a manhole with a diameter of about 4 or 4½ feet and a depth
-of retained water from 3 to 4 feet. Catch-basins of this size will care
-for the sewage from the inlets at the four corners of a street
-intersection, each draining a city block. In unusual situations it may
-be necessary to install a larger basin, but too large a catch-basin is
-less desirable than one which is too small, as the former stinks and the
-latter is useless. Traps are sometimes used to prevent the escape of
-odors from the sewer into the street, but odors are often created in the
-catch-basins themselves. Some engineers arrange the trap so that it can
-be opened for observation down the sewer as in Fig. 34, thus combining
-the advantages of a manhole with the catch-basin.
-
-The use of catch-basins is objectionable because: they furnish a
-breeding place for mosquitoes and other flying insects; the septic
-action in them produces offensive odors; if on a combined sewer they
-permit the escape of offensive odors in dry weather when the water seal
-in the trap has evaporated; and the freezing of the water seal in the
-trap prevents the entrance of water to the sewer. The sole advantage
-lies in the prevention of the clogging of the sewers, but this may be
-sufficient to overbalance all of the disadvantages. In general
-catch-basins should be provided on paved streets which are cleaned by
-flushing the material into the sewers, or where the drainage is from an
-unimproved or macadamized street, sandy country, or into sewers in which
-the velocity of flow is less than 2 feet per second.
-
-[Illustration:
-
- FIG. 35.—Diagrammatic Section through a Grease Trap.
-]
-
-
-=60. Grease Traps.=—The presence of grease in sewers results in the
-formation of incrustations which are difficult to remove and which cause
-a material loss in the capacity of the sewer. The presence of oil and
-gasoline has resulted in violent and destructive explosions as is
-described in Chapter XII. A type of grease trap used on the drains from
-hotels, restaurants, or other large grease producing industries is shown
-in Fig. 35. The trap is similar to a catch-basin except that it is too
-small for a man to enter, and the outlet is necessarily trapped in order
-to prevent the escape of grease. The details of a gasoline and oil
-separator approved by the New York City Fire Department are shown in
-Fig. 36.[36]
-
-[Illustration:
-
- FIG. 36.—Gasoline and Oil Separator.
-]
-
-
-=61. Flush-Tanks.=—These are devices to hold water used in flushing
-sewers. They are required only on sanitary and combined sewers. Their
-use tends to prevent the clogging of sewers laid on flat grades and
-permits flatter grades in construction than could otherwise be adopted.
-Flush-tanks may be operated either by hand or automatically. Automatic
-operation is more common than hand operation. The hand-operated tanks
-are similar to manholes so arranged that the inlet and outlet sewers can
-be plugged while the manhole or tank is being filled with water either
-from a hose or a special service connection. When sufficient water has
-been accumulated the outlet is opened and the sewer is flushed by the
-rush of water. A sluice gate, flap valve, or a specially fitted board is
-sufficient to fit over the mouth of the inlet and outlet during the
-filling of the tank. Such an arrangement has the advantage of being
-cheap, simple, and satisfactory, though somewhat crude. In some cases
-water is run into the tank at the same rate that it is discharged
-through the open outlet, maintaining a depth of 4 or 5 feet in the tank
-until the water passing the manhole below runs clean. The volume of
-water required by this method is large. Flushing water under a
-relatively high head is sometimes obtained by the use of tank wagons
-which are quickly emptied into the sewer through a canvas pipe dropped
-down a manhole. In all such cases if not well constructed the manhole is
-subject to caving due to the rush of water around the outlet.
-Precautions should be taken to minimize this danger by limiting the
-depth of water which may be accumulated. This can be done by
-constructing an overflow at a height of 4 or 5 feet above the bottom of
-the manhole, discharging into the sewer through an outside drain.
-
-Automatic flush-tanks are constructed similar to a manhole, but special
-care should be taken to make them water-tight. The apparatus for
-providing the automatic discharge may operate either with or without
-moving parts, the latter being preferable as they require less attention
-and are not so liable to get out of order. An automatic flush-tank of
-the Miller type is shown in Fig. 37. It is a patented device
-manufactured by the Pacific Flush Tank Company. The small pipe at the
-left is a service connection to the water main. Water is allowed to flow
-continuously into the tank at such a rate as to fill it in the required
-interval between discharges. The tanks are discharged as nearly once a
-day as it is practicable to regulate them. The rate of flow into the
-tank is determined by trial and varies to some extent with the water
-pressure. The regulator shown in the figure is desirable as the
-continuous flow through the ordinary cock soon wears it away. Some
-waters will cause deposits to form in the small passages of the cocks or
-regulators, thus cutting off the flow.
-
-[Illustration:
-
- FIG. 37.—Automatic Flush-Tank.
-
- Pacific Flush Tank Co.
-]
-
-The tank operates as follows: when the water rising in the tank reaches
-the bottom of the bell, air is trapped in the bell and prevented from
-escaping through the main trap by the water at _A_. As the water
-continues to rise in the tank the air in the bell is compressed, the
-water level at _A_ is driven down and water trickles from the siphon at
-_C_. The height of the water in the tank above the level of the water in
-the bell is equal at all times to the height of _C_ above the lowering
-position of _A_. When _A_ reaches the position of _B_ a small amount of
-air is released through the short leg of the trap and a corresponding
-volume of water enters the bell. The head of water above the bell then
-becomes greater than the head of water in the short leg of the trap,
-which results in the discharge of all of the air in the long leg of the
-trap and the rapid discharge of the water in the tank through the
-siphon. The discharge is continued until the siphonic action is broken
-by the admission of air when the water level in the tank is lowered to
-the bottom of the bell. The size of the siphons is fixed by the diameter
-of the leg of the siphon. Table 23 shows the capacity and size of sewers
-for which the different sizes of siphons are recommended by the
-manufacturers.[37]
-
- TABLE 23
-
- SIZES OF SIPHONS TO BE USED WITH AUTOMATIC FLUSH-TANKS
-
- ──────────┬───────────┬───────────┬───────────┬───────────┬────────────
- │ │ │ │ │ Height of
- │Diameter of│ Total │ │ │ the
- │Tank at the│ Discharge │ Average │ │ Discharge
- Diameter │ Discharge │ for One │ Rate of │Diameter of│ Line above
- of Siphon │ Line in │ Flush in │ Discharge │ Sewer in │the Edge of
- in Inches │ Feet │ Gallons │in Sec.-ft.│ Inches │ the Bell
- ──────────┼───────────┼───────────┼───────────┼───────────┼────────────
- 4│ 3│ 60│ 0.35│ 4 to 6│1 ft. 2 in.
- 5│ 3│ 100│ 0.73│ 6 to 8│1 ft. 11 in.
- 6│ 4│ 240│ 1.06│ 8 to 10│2 ft. 6 in.
- 8│ 4│ 280│ 2.12│ 12 to 15│2 ft. 11 in.
- ──────────┴───────────┴───────────┴───────────┴───────────┴────────────
-
-When flush-tanks are placed at the upper end of laterals provision
-should be made for inspecting and cleaning the sewer by the construction
-of a separate manhole, or by combining the features of a manhole and a
-flush-tank in the same structure. Such a combination is shown in Fig. 38
-from a design by Alexander Potter.
-
-Except under unusual conditions flush-tanks are used only on separate
-sewers. They should be placed at the upper end of laterals in which the
-velocity of flow when full is less than 2 to 4 feet per second. The
-capacity of the tank or the volume of the dose is dependent on the
-diameter and slope of the sewer. The most effective flush is obtained by
-a volume of water traveling at a high velocity and completely filling
-the sewer. A large volume allowed to run slowly through the sewer will
-have but little if any flushing action. Data on the quantity of flushing
-water needed are given in Table 24.[38] As the result of a series of
-experiments conducted by Prof. H. N. Ogden on the flushing of
-sewers,[39] the conclusion was reached that the effect of a flush of
-about 300 gallons in an 8–inch sewer on a grade less than 1 per cent
-would not be effective beyond 800 to 1,000 feet, but that on steeper
-grades much smaller quantities of water would produce equally good
-results.
-
-[Illustration:
-
- FIG. 38.—Automatic Flush-Tank and Manhole.
-
- Miller-Potter Design. Pacific Flush Tank Co.
-]
-
- TABLE 24
-
- GALLONS OF WATER NEEDED FOR FLUSHING SEWERS
-
- ─────────────────┬─────────────────────────────────────────────────────
- Slope │ Diameter of Sewer in Inches
- ─────────────────┼─────────────────┬─────────────────┬─────────────────
- │ 8│ 10│ 12
- ─────────────────┼─────────────────┼─────────────────┼─────────────────
- 0.005 │ 80│ 90│ 100
- .0075 │ 55│ 65│ 80
- .01 │ 45│ 55│ 70
- .02 │ 20│ 30│ 35
- .03 │ 15│ 20│ 24
- ─────────────────┴─────────────────┴─────────────────┴─────────────────
-
-Engineers do not agree upon the advisability of the use of automatic
-flush-tanks, some believing that they are a needless expense that can be
-avoided by hand flushing, and others feeling that a flush-tank should be
-placed at the upper end of every lateral. These diverse opinions are the
-result of different experiences in different cities.
-
-
-=62. Siphons.=—There are two forms of siphons used in sewerage practice,
-a true siphon and an inverted siphon. A true siphon is a bent tube
-through which liquid will flow at a pressure less than atmospheric,
-first upwards and then downwards, entering and leaving at atmospheric
-pressure. An inverted siphon is a bent tube through which liquid will
-flow at a pressure greater than atmospheric first downwards and then
-upwards, entering and leaving at atmospheric pressure.
-
-In sewerage practice the word siphon refers to an inverted siphon unless
-otherwise qualified. Siphons, both true and inverted, are used in
-sewerage systems to pass above or below obstacles. True siphons are
-seldom used as they must be kept constantly filled with liquid.[40]
-Accumulated gas must be removed in order to prevent the breaking of the
-siphon which results in the cessation of flow. By the breaking of a true
-siphon is meant the stoppage of siphonic action due to the accumulation
-of air or gas at the peak of the siphon. Since the rate of flow of
-sewage fluctuates widely it is extremely difficult to control the flow
-so that a true siphon may be completely filled with liquid at all times.
-
-In the design of inverted siphons care must be taken to prevent
-sedimentation, and to permit inspection and cleaning. Sedimentation is
-prevented by maintaining a velocity greater than a fixed minimum,
-usually taken at about 2 feet per second. This minimum is attained by
-providing a number of channels. The smallest channel is designed to
-convey the least expected flow at the minimum velocity. Each of the
-other channels is made as small as possible, within the limits of
-economy and simplicity, in order that the minimum velocity shall be
-exceeded quickly after flow has commenced in them. The last channel or
-channels to be filled are made somewhat larger, because the sewage
-conveyed in them contains less settleable matter than is contained in
-the more concentrated dry weather flow. The type of siphon used in New
-York to pass under the subway is shown in Fig. 39. Note should be taken
-of the clean-out manhole provided on the 14–inch pipe. The other pipes
-are large enough for a man to enter and clean.
-
-[Illustration:
-
- FIG. 39.—Sewer Siphon under New York Subway.
-
- Eng. News Vol. 76, p. 443.
-]
-
-The computations involved in the design of a siphon are illustrated in
-the following example, in which it is desired to construct a siphon to
-pass under the railway cut shown in Fig. 40. The first step is to
-determine the limiting diameter and slope of the smallest pipe in the
-siphon. One-sixth of the capacity of the 6–foot approach sewer or 19
-cubic feet per second will be assumed as the minimum flow. The diameter
-of the pipe necessary to carry 19 cubic feet per second at a velocity of
-2 feet per second is 42 inches. The hydraulic gradient should have a
-slope of 0.0005 if the material used has a roughness coefficient
-of .015. This is the minimum permissible slope of the siphon. The
-selection of a steeper slope will necessitate the laying of the sewer at
-a greater depth, and will permit the use of smaller pipes for the
-siphon. The selection of the exact slope must then be based on judgment
-with the minimum limitation above placed. The slope will be arbitrarily
-selected as 0.001, the same as that of the approach sewer. The diameter
-of the dry weather pipe will therefore be 36 inches, with a capacity of
-18 second-feet, which is approximately the assumed dry weather flow. The
-velocity of flow will be 2.5 feet per second. The length of flow along
-the siphon is 150 feet.
-
-[Illustration:
-
- FIG. 40.—Diagram for the Design of an Inverted Siphon.
-]
-
-The next step should be the determination of the elevation at the lower
-end of the 36–inch pipe. This is done by multiplying the assumed grade
-by the equivalent length of straight pipe, and subtracting the product
-from the elevation at the upper end. The length of straight pipe which
-will give the same loss of head as the siphon is called the equivalent
-pipe. It is determined as follows:
-
-First, determine the head loss at entrance. This will vary between
-nothing and one velocity head, dependent on the arrangement at the
-entrance.[41] The length of straight pipe which will give this same loss
-can be computed from the expression _l_ = _h_⁄_S_, using for _S_ the
-assumed slope of the hydraulic gradient.
-
-Second, determine the head loss due to the bends, This is determined
-from the expression
-
- _h_ = (_fl_)⁄(_d_) (_V_^2)⁄(2_g_)
-
- in which _h_ = the head loss in the bend;
-
- _l_ = the length of the bend;
-
- _d_ = the diameter of the pipe;
-
- _v_ = the average velocity of flow;
-
- _g_ = the acceleration due to gravity;
-
- _f_ = a factor dependent on the radius (_R_) of the bend and
- _d_.
-
-The relation between _f_, _R_, and _d_, for 90° bends is shown as
-follows:[42]
-
- _R_⁄_d_ 24 16 10 6 4 2.4
-
- _f_ 0.036 0.037 0.047 0.060 0.062 0.072
-
-After the head loss has been determined, the equivalent length of
-straight pipe is determined as above.
-
-Third. The equivalent length of pipe will be the sum of the actual
-length of pipe and the equivalent lengths as found above.
-
-In the problem in hand the head lost at the entrance will be assumed as
-one-third of a velocity head, or 0.0324 foot. With the assumed slope of
-0.001 this is equivalent to 32 feet of pipe. The radius of the bend is
-about 20 feet and the length for a 45° central angle is about 16 feet.
-The head loss for this angle will probably be a little more than
-one-half that for a 90° angle. The expression will therefore be taken as
-about 0.2(_V_^2)⁄(2_g_) and for two bends is equivalent to about 40 feet
-of pipe. The equivalent length of pipe is therefore 150 + 32 + 40 = 222
-feet. The elevation at the lower end should therefore be: the elevation
-at the upper end, 92.07 − 222 × .001 = 91.85.
-
-The diameters of the remaining pipes in the siphon are determined so
-that the sewage in the approach sewer is backed up as little as is
-consistent with good judgment before each pipe comes into action. This
-is done satisfactorily by a method of cut and try. Let it be assumed
-that the siphon will be composed of three pipes: the dry weather pipe
-taking 18 second-feet, the second pipe taking 28 second-feet, and the
-third pipe taking the remaining 70 second-feet. The diameters of the two
-larger pipes on the assumed slope of 0.001 will therefore be 42 inches
-and 60 inches respectively. Other combinations might be used which would
-be equally satisfactory. There are many methods by which the sewage can
-be diverted into the different channels of the siphon. For example, the
-openings into the different pipes may be placed at the same elevation,
-and the sewage allowed to enter them in turn through automatically or
-hand-controlled gates, or in another method of control the openings may
-be placed at such elevations that when the capacity of one pipe has been
-exceeded the sewage will flow into the next largest pipe as shown in
-Fig. 40. The outlets from the different pipes are ordinarily placed at
-the same elevation, thus leaving each pipe standing full of sewage. Stop
-planks should be provided at the outlet in order that the pipes may be
-pumped out for cleaning. The objection to this arrangement is that the
-larger pipes may operate at a velocity less than 2 feet per second, and
-they will be standing full of sewage which might become septic. However,
-as they will take nothing but the storm flow near the top of the sewer
-no difficulty should be encountered from sedimentation in them, and all
-are large enough for a man to enter for inspection or cleaning.
-
-[Illustration:
-
- FIG. 41.—Coffin Sewer Regulator.
-]
-
-
-=63. Regulators.=—Regulators are commonly used to divert the direction
-of flow of sewage in order to prevent the overcharging of a sewer or to
-regulate the flow to a treatment plant. Sewer regulators are of two
-types, those with moving parts and those without moving parts. An
-example of the moving part type is shown in Fig. 41. In this type as the
-sewage rises the float closes the gate to the inlet sewer, thus
-preventing the entrance of sewage under head from the larger sewer.
-There are many variations in the details of float controlled regulators,
-but the principle of operation is similar in all. These regulators can
-be adjusted to fix the maximum rate of flow to a relief channel or
-sewage treatment plant, or during times of storm to cut off the outlet
-to the dry weather channel. Another form of the moving part type is
-shown in Fig. 42.[43] It has been used extensively by the Milwaukee
-Sewerage Commission. In its operation the dry weather flow is diverted
-by the dam into the intercepter. It passes under the movable gate on its
-way to the treatment plant. As the flow increases the dam is overtopped
-and flood waters are discharged down the storm channel. The movable gate
-is hung on a pivot placed below center. As the water rises in the
-intercepter, the pressure against the upper portion of the gate becomes
-greater than that against the lower portion, and the gate closes. An
-opening is left at the bottom to allow an amount of sewage equal to the
-dry weather flow to escape beneath the gate to prevent clogging or
-sedimentation in the intercepter channel.
-
-Objections to all moving part regulators are their need of attention and
-liability to become clogged.
-
-[Illustration:
-
- FIG. 42.—Moving Part Regulator without Float.
-]
-
-[Illustration:
-
- FIG. 43.—Leaping Weir at Danville, Illinois.
-]
-
-[Illustration:
-
- FIG. 44.—Overflow Weir at San Francisco.
-
- Eng. News, Vol. 73, p. 307.
-]
-
-[Illustration:
-
- FIG. 45.—Overflow Weir in Action.
-
- Shadow of steel knife edge which forms the lip of the weir can be seen
- through the falling sewage.
-]
-
-The overflow weir and the leaping weir have no moving parts and are used
-for the regulation of the flow in sewers. A leaping weir is formed by a
-gap in the invert of a sewer through which the dry weather flow will
-fall and over which a portion or all of the storm flow will leap. One
-form of leaping weir is shown in Fig. 43. An overflow weir is formed by
-an opening in the side of a sewer high enough to permit the discharge of
-excess flow into a relief channel. A weir at San Francisco is shown in
-Fig. 44. A series of tests were run on leaping weirs and overflow weirs
-in the hydraulic laboratory of the University of Illinois. The type of
-leaping weir tested was formed by the smooth spigot end of a standard
-vitrified sewer pipe. The overflow weirs were formed by a steel knife
-edge in the side of the pipe parallel to its axis as shown in Fig. 45.
-Tests were made in 18–inch and 24–inch pipes on various slopes from
-0.018 to 0.005, for both leaping weirs and overflow weirs. The overflow
-weirs were varied in length from 16 inches to 42 inches and were placed
-at various heights from 25 per cent to 50 per cent of the diameter above
-the invert of the sewer. As the result of the observations the following
-formulas were developed. For the leaping weir the expressions for the
-coordinates of the curve of the surfaces of the falling stream, are:
-
- For the outside surface _x_ = 0.53_V_^⅔ + _y_^{4⁄7}
-
- For the inside surface _x_ = 0.30_V_^{4⁄7} + _y_^¾
-
-in which _x_ and _y_ are the coordinates. The origin is in the upper
-surface of the stream vertically above the end of the invert of the
-pipe. The ordinate _y_ is measured vertically downwards. _V_ is the
-velocity of approach in feet per second. These expressions are
-applicable to any diameter of sewer up to 10 or 15 feet. They should
-_not_ be used for depths of flow greater than about 14 inches; nor for
-slopes of more than 25 per 1,000; nor for velocities less than 1 foot
-per second nor more than 10 feet per second. The expression for the
-ordinate of the inside curve is not good for less than 6 inches nor more
-than 5 feet. The expression for the ordinate of the outside curve is
-limited to values between the origin and 5 feet below it.
-
-The expression for the length of an overflow weir of the type shown in
-Fig. 45, necessary to discharge a given quantity, is in the form,
-
- _l_ = 2.3_Vd_ log _h__{1}⁄_h__{2}
-
- in which _l_ = the length of the weir in feet;
-
- _V_ = the velocity of approach in feet per second;
-
- _d_ = the diameter of the pipe in feet;
-
- _h__{1} = the head of water on the upper end of the weir;
-
- _h__{2} = the head of water on the lower end of the weir.
-
-In the design of an overflow weir by this formula the height of the weir
-above the invert of the sewer and the flow over the weir should be
-determined arbitrarily. The height should be subtracted from the
-computed depth of water above the weir to determine the value of
-_h__{1}. The difference between the flow over the weir and the flow
-above the weir will represent the rate of flow in the sewer below the
-weir. The value of _h__{2} can then be computed as the difference in the
-depth of flow below the weir and the height of the weir above the
-invert. The value of _V_ is computed from Kutter’s formula. The length
-of the weir is determined by substituting these values in the formula.
-
-
-=64. Junctions.=—At the junction of two or more sewers the elevation of
-the inverts should be such that the normal flow lines are at the same
-elevation in all sewers. The sewers should approach the junction on a
-steep grade to prevent sewage backing up in one when the other is
-flowing full. The velocity of flow at the junction should not be
-decreased and turbulence should be avoided in order to prevent
-sedimentation and loss of head. The junction should be effected on
-smooth easy curves with radii at least five times the diameter of the
-sewer where possible. Curves with short radii cause backing up of sewage
-thus reducing the capacity of the sewers.
-
-The terms bellmouth or trumpet arch are sometimes applied to the
-junction of sewers large enough to be entered by a man. In small sewers
-the Y branches and special junctions are manufactured so that the center
-lines of the pipes intersect, and the junctions of mains and laterals
-are made in manholes. In the construction of a bellmouth the arch is
-carried over all the sewers. A manhole should be constructed at these
-junctions as clogging frequently occurs there, due to swirling and back
-eddies which cannot be avoided.
-
-
-=65. Outlets.=—The outlets to a sewerage system discharging into a
-swiftly running stream must be protected against wash and floating
-debris. In a stream or other body of water subject to wide variations in
-elevation the backing up of the sewage during high water should be
-avoided. Where tidal flats or low ground about the outlet may be
-alternately submerged and uncovered the discharge should always be into
-swiftly running water. In quiescent bodies of water such as lakes and
-harbors, and in rivers where the dilution is low, and in many other
-cases, the sewer outlet should be submerged.
-
-[Illustration:
-
- FIG. 46.—Tide Gate.
-]
-
-Outlets are protected against wash and the impact of debris by the
-construction of deep foundations and heavy protecting walls. Although
-the construction of an outlet in a slow current or a back eddy would
-avoid danger from wash and debris, the discharge of the sewage into the
-most rapid current possible aids in the prevention of a local nuisance.
-A row of batter piles on the upstream or exposed side of the sewer is
-desirable, or it may be necessary to construct a break-water to prevent
-the wash of the current from dislodging the pipe. These break-waters are
-low dams of wood or broken stone, more or less loosely thrown together.
-The backing up of water into the sewer can be prevented by constructing
-the sewer above the outlet on a steep grade. Where this is not possible
-the use of tide gates will be helpful. A tide gate, one form of which is
-shown in Fig. 46, is a special form of check valve placed on the end of
-the sewer.
-
-[Illustration:
-
- FIG. 47.—Sewer Outlet on a Trestle.
-
- Eng. News, Vol. 49, p. 9.
-]
-
-Sewer outlets are sometimes constructed on long trestles in order to
-reach deep or running water. Such a trestle is shown in Fig. 47. In
-Boston the outlet sewers are submerged under the harbor and discharge
-through outlets well out in the tidal currents. The sewage is discharged
-under pressure and the pumps are operated at some of the stations only
-at such times as the tidal currents will carry the sewage away from the
-harbor. It is not always necessary in a combined sewerage system to
-carry the storm flow to a distant submerged outlet. A double outlet can
-be constructed as shown in Fig. 48 in which the dry weather flow is
-carried to the channel in a submerged sewer and the storm flow is
-discharged on the bank.[44] Cast-iron pipe should be used for submerged
-outlets as the sewer is subject to disturbance by the currents, anchors,
-ice, and other causes.
-
-[Illustration:
-
- FIG. 48.—Dry Weather and Storm Sewer Outlet at Minneapolis, Minnesota.
-
- Eng. Record, Vol. 63, p. 383.
-]
-
-
-=66. Foundations.=—Sewers constructed in firm dry soil require no
-special foundation to distribute the weight over the supporting medium.
-In soft materials the lower half of the sewer ring may be spread as
-shown in Fig. 22, and in rock the pressures on sewer pipes are evenly
-distributed by a cushion of sand. In wet ground such as quicksand, mud,
-swamp land, etc., a foundation must be constructed if the water cannot
-be drained off.
-
-The permissible intensities of pressure on foundations in various
-classes of material allowed by the building codes in different cities
-are given in Table 25. These figures are based on the assumption that
-the material is restrained laterally, which is generally the condition
-in sewer construction. In the softer materials it becomes necessary to
-spread the foundations not only to reduce the intensity of pressure, but
-also to care for the thrust of the sewer arch. The arch thrust may be
-found by one of the methods of arch analysis, and the haunches spread to
-care for this, or the sewer invert may be transversally reinforced to
-assist in caring for this action. Some sewer sections in hard and soft
-material are shown in Fig. 22 and 23.
-
- TABLE 25
-
- ALLOWABLE BEARING VALUE ON SOILS IN VARIOUS CITIES
-
- From Proc. Am. Soc. Civil Engrs., Vol. 46, 1920, p. 906
-
- ─────────────────────────┬─────────────────────────────────────────────
- Quicksand and alluvial │½ to 1 ton per sq. ft. for Providence, R. I.,
- soil │ ½ ton per sq. ft. for 6 cities
- ─────────────────────────┼─────────────────────────────────────────────
- Soft clay │1 ton per sq. ft. for 27 cities, ¾ ton per
- │ sq. ft. for New Orleans, 2 to 3 tons for
- │ Providence, R. I.
- ─────────────────────────┼─────────────────────────────────────────────
- Moderately dry clay and │2 tons for 7 cities, 1¾ to 2¼ for Chicago, 2½
- fine sand, clean and │ tons for Louisville, 2 to 4 tons for
- dry │ Providence, 3 tons for Grand Rapids and Los
- │ Angeles
- ─────────────────────────┼─────────────────────────────────────────────
- Clay and sand in │2 tons for 19 cities, 1¾ to 2¼ for Chicago, 3
- alternate layers │ to 5 tons for Providence
- ─────────────────────────┼─────────────────────────────────────────────
- Firm and dry loam or │3 tons for 24 cities, 2½ tons for 2 cities, 2
- clay, or hard dry clay │ to 3 tons for Atlanta, 3½ tons for
- or fine sand │ Philadelphia, 4 tons for 6 cities
- ─────────────────────────┼─────────────────────────────────────────────
- Compact coarse sand, │4 tons for 25 cities, 3½ tons for Buffalo, 3
- stiff gravel or natural│ to 4 tons for Atlanta, 4 to 5 tons for
- earth │ Cincinnati, 5 tons for Denver, 4 to 6 tons
- │ for 3 cities, 6 tons for Rochester, N. Y.
- ─────────────────────────┼─────────────────────────────────────────────
- Coarse gravel, stratified│6 tons for 3 cities, 5 tons for 2 cities, 8
- stone and clay, or rock│ tons for 1 city
- inferior to best brick │
- masonry │
- ─────────────────────────┼─────────────────────────────────────────────
- Gravel and sand well │8 tons for 5 cities, 6 tons for 2 cities, 8
- cemented │ to 10 tons for 1 city
- ─────────────────────────┼─────────────────────────────────────────────
- Good hard pan or hard │10 tons for 4 cities, 6 tons for 2 cities, 8
- shale │ tons for 1 city
- ─────────────────────────┼─────────────────────────────────────────────
- Good hard pan or hard │8 tons for 1 city, 10 to 15 tons for 1 city,
- shale unexposed to air,│ 12 to 18 tons for 1 city
- frost or water │
- ─────────────────────────┼─────────────────────────────────────────────
- Very hard native bed rock│20 tons for 5 cities, 15 tons for 1 city, 10
- │ tons for 1 city, 25 to 50 tons for 1 city
- ─────────────────────────┼─────────────────────────────────────────────
- Rock under caisson │24 tons for Baltimore, 25 tons for Cleveland
- ─────────────────────────┴─────────────────────────────────────────────
-
-On soft foundations such as swamps or for outfalls on the muck bottom of
-rivers the sewer may be carried on a platform. For small sewers 2–inch
-planks, 2 to 4 feet longer than the diameter of the pipe are laid across
-the trench, and the sewer rests directly upon them. For large sewers
-imposing a heavy concentrated load, a pile foundation should be
-constructed. The foundation may consist of piles alone, pile bents, or a
-wooden platform supported on pile bents. The load which can be carried
-by a pile is determined with accuracy only by driving a test pile and
-placing a load on it. Where piles do not penetrate to a firm stratum the
-load they will support can be determined by any one of the various
-formulas, either theoretical or empirical, which have been devised.
-Probably the best known of these formulas are the so-called Engineering
-News formulas one of which is:
-
- _P_ = 2_Wh_⁄(_S_ + 1) for a pile driven by a drop hammer,
-
- in which _P_ = the safe load on the pile in pounds. The factor of
- safety is 6;
-
- _W_ = the weight of the hammer in pounds;
-
- _h_ = the fall of the hammer in feet;
-
- _S_ = the penetration of the pile in inches at the last
- driving blow. The blow is assumed to be driven on
- sound wood without rebound of the hammer.
-
-Reference should be made to engineering handbooks for other forms of
-pile formulas. The accuracy of all of these formulas is not of a high
-degree.
-
-The piles are driven at about 2 to 4 feet centers, to a depth of from 8
-to 20 feet, unless hard bottom is struck at a lesser depth. The butt
-diameter of the piles used for the smallest sewers is about 6 to 8
-inches. If bents are used, 2 or 3 piles are driven in a row across the
-line of the sewer and are capped with a timber. For brick, block, pipe,
-and some concrete sewers, a wooden platform must be constructed between
-the pile bents for the support of the sewer.
-
-
-=67. Underdrains.=—The construction of special foundations can sometimes
-be avoided by laying drains under the sewers, thus removing the water
-held in the soil. The laying of the underdrains facilitates the
-construction of the sewer and reduces the amount of ground water
-entering the sewer. The underdrains usually consist of 6– or 8–inch
-vitrified tile laid with open joints from 1 to 2 feet below the bottom
-of the sewer as shown in Fig. 1. If the sewers are large, parallel lines
-of drains may be laid beneath them. An observation hole should be
-constructed from the bottom of the manhole to each underdrain. This hole
-usually consists of a 6– or 8–inch pipe, embedded in concrete, connected
-to the drain and open at the top. It is too small to permit effective
-cleaning of the underdrains, which are usually neglected after
-construction, and which as a result clog and cease to function. Since
-the principal period of usefulness of the drains is during construction,
-their stoppage after the work is completed is not serious. The hollow
-tile used in vitrified block sewers serve as underdrains after
-construction, but are of little or no assistance to the draining of the
-trench during construction.
-
-
-
-
- CHAPTER VII
- PUMPS AND PUMPING STATIONS
-
-
-=68. Need.=—In the design of a sewerage system it is occasionally
-necessary to concentrate the sewage of a low-lying district at some
-convenient point from which it must be lifted by pumps. In the
-construction of sewers in flat topography the grade required to cause
-proper velocity of sewage flow necessitates deep excavation. It is
-sometimes less expensive to raise the sewage by pumping than to continue
-the construction of the sewers with deep excavation.
-
-In the operation of a sewage-treatment plant a certain amount of head is
-necessary. If the sewage is delivered to the plant at a depth too great
-to make possible the utilization of gravity for the required head, pumps
-must be installed to lift the sewage. In the construction of large
-office buildings, business blocks, etc., the sub-basements are
-frequently constructed below the sewer level. The sewage and other
-drainage from the low portion of the building must therefore be removed
-by pumping. Because pumps are often an essential part of a sewerage
-system, their details should be understood by the engineer who must
-write the specifications under which they are purchased and installed.
-
-
-=69. Reliability.=—If the only outlet from a sewerage system is through
-a pumping station, the inability of the pumps to handle all of the
-sewage delivered to them may so back up the sewage as to flood streets
-and basements, endangering lives and health and destroying property.
-Such an occurrence should be guarded against by providing sufficient
-pumping capacity and machinery of the greatest reliability.
-
-
-=70. Equipment.=—The equipment of a sewage pumping station, in addition
-to pumping machinery, may include a grit chamber, a screen, and a
-receiving well. The grit chamber and screen are necessary to protect the
-pumps from wear and clogging. Grit chambers are not necessary in sewage
-devoid of gritty matter, such as the average domestic sewage, unless
-reciprocating pumps are used. Sufficient gritty matter is found in
-average domestic sewage to have an undesirable effect on reciprocating
-pumps. Receiving wells are used in small pumping stations where the
-capacity of the pumps is greater than the average rate of sewage flow.
-The pumps are then operated intermittently, the pumps standing idle
-during the time that the receiving well is filling.
-
-Except for a few types of pumps of which the valve openings are
-unsuitable, any machine capable of pumping water is capable of pumping
-sewage which has been properly screened. The principles of sewage pumps
-are then similar to principles of water pumps. The conditions under
-which these principles are applied differ but slightly in the character
-of the liquid, and a smaller range of discharge pressures. Pumps with
-large passages, discharging under low heads are more commonly found
-among sewage pumps.
-
-[Illustration:
-
- FIG. 49.—Calumet Sewage Pumping Station, Chicago, Illinois.
-]
-
-
-=71. The Building.=—The pumping station should, if possible, be of
-pleasing design and should be surrounded by attractive grounds. The
-Calumet Sewage Pumping Station in Chicago is shown in Fig. 49. Its
-architecture is pleasing particularly in contrast with its location and
-immediate surroundings. Such structures tend to remove the popular
-prejudice from sewerage and to arouse interest in sewerage questions.
-Service to the public is of value. It can be rendered more easily by
-arousing public interest and cooperation by the erection of attractive
-structures, than by feeding popular prejudice by the construction of
-miserable eyesores.
-
-
-=72. Capacity of Pumps.=—The capacity of the pumping equipment should be
-sufficient to care for the maximum quantity of sewage delivered to it,
-with the largest pumping unit shut down, and the provision of such
-additional capacity as, in the opinion of the designer, will provide the
-necessary factor of safety.
-
-Pumps can usually be operated under more or less overload. Power pumps
-and centrifugal pumps driven by constant speed electric motors have no
-overload capacity. A power pump or a centrifugal pump may be overloaded
-up to the maximum horse-power of any variable speed motor or steam
-engine driving it, provided the pump has been designed to permit it.
-Direct-acting steam pumps which are designed for proper piston speed and
-valve action at normal loads, can carry a 50 per cent overload for short
-periods, although the strain on the pump is great. They will carry a 20
-to 25 per cent overload for about eight hours with less vibration and
-strain. The use of pumps capable of working at an appreciable overload
-is somewhat of an additional factor of safety, but the overload factor
-should not be taken into consideration in determining the capacity of
-the pumping equipment.
-
-The load on a pumping station consists of the quantity of sewage to be
-pumped and the height it must be lifted. Variations in the quantity are
-discussed in Chapter III. The head against which the pumps must operate
-fluctuates with the level in the tributary sewer or pump well, and in
-the discharge conduit. For a free discharge or discharge into a short
-force main the greater the rate of sewage flow the smaller the lift, as
-the depth of flow in the tributary sewer increases more rapidly than
-that in the discharge conduit. If the discharge is into a large body of
-water or under other conditions where the discharge head is
-approximately constant, the fluctuations in total head should not exceed
-the diameter of the tributary sewer. Such fluctuations are of minor
-importance in the operation of direct-acting steam pumps, but may be of
-great importance in the operation of centrifugal pumps, as is brought
-out in Art. 78.
-
-
-=73. Capacity of Receiving Well.=—The use of receiving wells is
-restricted to small installations which require, in addition to the
-standby unit, only one pump, the capacity of which is equal to the
-maximum rate of sewage flow. When the receiving well has been pumped dry
-the pump stops, allowing the well to fill again. Although the use of a
-large receiving well, or an equalizing reservoir, for a large pumping
-station would permit the operation of the pumps under more economical
-conditions, the storage of sewage for the length of time required would
-not be feasible. The sewage would probably become septic, creating odors
-and corroding the pumps. The extra cost of the reservoir might not
-compensate for the saving in the capacity and operation of the pumps.
-
-The capacity of the receiving well should be so designed that the pump
-when operating will be working at its maximum capacity, and the period
-of rest during conditions of average rate of flow should be in the
-neighborhood of 15 to 20 minutes. For example, assume an average rate of
-flow of 2 cubic feet per second, with a maximum rate of double this
-amount. The pump should have a capacity of 4 cubic feet per second, and
-if the receiving well is to be filled in 15 minutes by the average rate
-of sewage flow its capacity should be 15 × 5 × 60 × 7.5 or 14,000
-gallons. Under these circumstances the pump will operate 15 minutes and
-rest 15 minutes, during average conditions of flow.
-
-
-=74. Types of Pumping Machinery.=—The two principal types of pumping
-machines for lifting sewage are centrifugal pumps and reciprocating
-pumps. A centrifugal pump is, in general, any pump which raises a liquid
-by the centrifugal force created by a wheel, called the impeller,
-revolving in a tight casing, as shown in Fig. 50. A reciprocating pump
-is one in which there is a periodic reversal of motion of the parts of
-the pump.
-
-Centrifugal pumps are sometimes classified as volute pumps and turbine
-pumps. A volute pump is a centrifugal pump with a spiral casing into
-which the water is discharged from the impeller with the same velocity
-at all points around the circumference, as shown in Fig. 51. A turbine
-pump is a centrifugal pump in which the water is discharged from the
-impeller through guide passages into a collecting chamber, in such a
-manner as to prevent loss of energy in changing from kinetic head to
-pressure head. A turbine pump is shown in section in Fig. 51.
-Centrifugal pumps are sometimes classified as single stage and
-multi-stage. A centrifugal pump from which the water is discharged at
-the pressure created by a single impeller is called a single-stage pump.
-If the water in the pump is discharged from one impeller into the
-suction of another impeller the pump is known as a multi-stage pump. The
-number of impellers operating at different pressures determines the
-number of stages of the pump. A three-stage pump is shown in Fig. 52.
-
-[Illustration:
-
- FIG. 50.—Section through de Laval Single-Stage, Double Suction
- Centrifugal Pump.
-]
-
- 375 Lubricating ring.
-
- 380 Oil hole cap.
-
- 383 Oil drain tube.
-
- 404 Shaft sleeve lock nut.
-
- 440 Driving coupling.
-
- 441 Driven coupling.
-
- 443 Coupling check nut.
-
- 450 Coupling bolt.
-
- 451 Coupling bolt nut.
-
- 452 Coupling rubber.
-
- 453 Coupling rubber steel tube.
-
- 500 Pump case.
-
- 550 Bearing bracket cap.
-
- 551 Bearing.
-
- 552 Shaft.
-
- 553 Shaft sleeve, right hand thread.
-
- PW Impeller.
-
- 554 Shaft sleeve, left hand thread.
-
- 555 Shaft stop collar, inner.
-
- 555–1 Shaft stop collar, outer.
-
- 556 Guide ring.
-
- 560 Packing gland.
-
- 563 Bearing.
-
- 567R Impeller protecting ring, right hand thread.
-
- 567L Impeller protecting ring, left hand thread.
-
- 583 Pump case protecting ring.
-
- 567 Labyrinth packing.
-
- 583 Labyrinth packing.
-
- 600 Pump case cover.
-
- 692 Impeller key.
-
- 815 Bearing bracket, outer.
-
- 815–1 Bearing bracket, inner.
-
-[Illustration:
-
- FIG. 51.—Types of Centrifugal Pumps.
-]
-
-[Illustration:
-
- FIG. 52.—Section of a Multi-Stage Centrifugal Pump.
-
- Courtesy DeLaval Steam Turbine Co.
-]
-
-Reciprocating pumps are generally driven by steam and are either
-direct-acting, or of the crank-and-fly-wheel type. Power pumps are
-reciprocating machines which may be driven by any form of motor, to
-which they are connected by belt, chain or shaft. A Deming triplex
-power pump is shown in Fig. 53. Power pumps can be used only where the
-character of the sewage will not clog the valves nor corrode the pump.
-A direct-acting steam pump is one in which the steam and water
-cylinders are in the same straight line and the steam is used at full
-boiler pressure throughout the full length of the stroke. The
-crank-and-fly-wheel type of pumping engine permits the use of steam
-expansively during a part of the stroke, the energy stored in the
-flywheel carrying the machine through the remainder of the stroke.
-Reciprocating pumps are sometimes classified as plunger pumps and
-piston pumps. In the action of a plunger pump the water is expelled
-from the water cylinder, by the action of a plunger which only partly
-fills the water cylinder, as shown in Figs. 54 and 55. In a piston
-pump the water is expelled from the water cylinder by the action of a
-piston which completely fills the water cylinder, as shown in Fig. 63,
-which illustrates a direct-acting piston pump.
-
-[Illustration:
-
- FIG. 53.—Triplex Power Pump.
-
- Courtesy, The Deming Co.
-]
-
-Plungers are better than pistons for pumping sewage as the wear between
-the pistons and the inside face of the cylinder soon reduces the
-efficiency of the pump. Outside packed plungers are better than the
-inside packed type because the packing can be taken up without stopping
-the pump and the leakage from the pump is visible at all times. Outside
-packed pumps are more expensive in first cost, but are easier to
-maintain and have a longer life than piston pumps.
-
-[Illustration:
-
- FIG. 54.—Water End of Inside Center-Packed Plunger Pump.
-]
-
-In selecting a pump to perform certain work the size of the water
-cylinder and the speed of the travel of the piston should be
-investigated to insure proper capacity. The average linear travel of the
-piston for slow speed pumps is estimated at about 100 feet per minute,
-dependent on the length of stroke and the valve area. For short strokes
-and small valve areas the speed may be as low as 40 feet per minute, and
-for long stroke fire pumps with large valves the piston can be operated
-at a speed of 200 feet per minute.[45] Vertical, triple-expansion,
-crank-and-fly-wheel, outside packed plunger pumps with flap valves can
-be operated at speeds of 200 feet per minute when lifting sewage, and
-when equipped with mechanically operated valves and lifting water they
-can be run at speeds of 400 to 500 feet per minute. The speed of travel
-multiplied by the volume of piston or plunger displacement, with proper
-allowance for slippage, will give the capacity of the pump. The slippage
-allowance may be from 3 to 8 per cent for the best pumps, and for pumps
-in poor conditions it may be a high as 30 to 40 per cent.
-
-[Illustration:
-
- FIG. 55—Water End of Outside Center-Packed Plunger Pump.
-
- Courtesy Allis-Chalmers Co.
-]
-
-There are two types of ejector pumps used for lifting sewage. One of
-these depends on the vacuum created by the velocity of a stream of water
-or steam passing through a small nozzle. The operation of this pump is
-described in Art. 139 and it is illustrated in Fig. 97. The other type
-of ejector pump is known as the compressed-air ejector. It is operated
-by means of compressed air which is turned into a receptacle containing
-sewage. The details of this type are explained in Art. 83 and are
-illustrated in Fig. 68.
-
-
-=75. Sizes and Description of Pumps.=—The size of a centrifugal pump is
-expressed as the diameter of the discharge pipe in inches. It has
-nothing to do with the head for which the pump is suited. On the
-assumption of a velocity of flow of 10 feet per second through the
-discharge pipe the capacity of the pump can be approximated.
-
-The size of a reciprocating pump involves the expression of the
-diameters of the steam cylinders, the water cylinder, and the length of
-the stroke in inches, in the order named, beginning with the steam
-cylinder with the highest pressure. A complete description of a steam
-pumping engine might be; compound, duplex, horizontal, condensing,
-crank-and-fly-wheel, outside-center-packed, 12″ × 24″ × 18″ × 24″ pump.
-The word compound means that there are a high-pressure and a
-low-pressure steam cylinder; the word duplex means that there are two of
-each of these cylinders; the word horizontal means that the axes of
-these cylinders are in a horizontal plane; the word condensing means
-that the steam is discharged from the low-pressure cylinders into a
-condenser; the name crank-and-fly-wheel is self-explanatory; the name
-outside-center-packed means that the water cylinder is divided into two
-portions between which the plunger is exposed to the atmosphere, and
-that the packing rings are on the outside of the two portions of the
-cylinder as shown in Fig. 55; the figures shown mean that the
-high-pressure steam cylinder is 12 inches in diameter, the low-pressure
-24 inches in diameter, the water cylinder is 18 inches in diameter, and
-the stroke of the pump is 24 inches.
-
-
-=76. Definitions of Duty and Efficiency.=—The duty of a pump is the
-number of foot-pounds of work done by the pump per million B.T.U., per
-thousand pounds of steam, or per hundred pounds of coal, consumed in
-performing the work. These units are only approximately equal as 100
-pounds of coal or 1,000 pounds of steam do not always contain the same
-number of B.T.U. and may only approximately equal 1,000,000 B.T.U.
-
-Since 1,000,000 B.T.U. are equal to 778,000,000 foot-pounds of work, a
-pump with a duty of 778,000,000 will have an efficiency of 100 per cent.
-The efficiency of a pump is therefore its duty based on B.T.U. divided
-by 778,000,000. The efficiencies or duties of various types of pumps are
-given in Table 26.[46]
-
- TABLE 26
-
- APPROXIMATE DUTIES OF STEAM PUMPS
-
- Small duplex, non-condensing 10,000,000
- Large duplex, non-condensing 25,000,000
- Small simple, flywheel, condensing 50,000,000
- Large simple, flywheel, condensing 65,000,000
- Small compound, flywheel, condensing 65,000,000
- Large compound, flywheel, condensing 120,000,000
- Small triple, flywheel, condensing 150,000,000
- Large triple, flywheel, condensing 165,000,000
-
-
-=77. Details of Centrifugal Pumps.=—A section of a centrifugal pump with
-the names of the parts marked thereon is shown in Fig. 50. Among the
-important parts which require the attention of the purchaser are: the
-impeller (_PW_), the impeller packing rings (567 _R_ & _L_), the
-bearings (551, 563), the thrust bearings (555–1), the shaft (552), and
-the shaft coupling (440).
-
-The impeller should be of bronze, gun metal, or other alloy, because
-there is no rusting or roughening of the surface, and the efficiency
-does not fall with age. Normal fresh sewage is not corrosive, but septic
-sewage and sludge are usually so corrosive that iron parts cannot be
-used with success in contact with them. The impeller should be machined
-and polished to reduce the friction with the liquid. Impellers are made
-either closed or open, i.e., either with or without plates on the sides
-connecting the blades to avoid the friction of the liquid against the
-side of the casing. The closed type of impeller is shown in Fig. 50.
-Closed impellers are slightly more expensive, but generally give better
-service and higher efficiencies than the open type. Single impeller
-pumps should have an inlet on each side of the impeller to aid in
-balancing the machine, unless the plane of the impeller is to be
-horizontal when operating. Multi-impeller pumps usually have single
-inlet openings for each impeller. Vibration in the pump is sometimes
-caused by an unbalanced impeller. The moving parts may be balanced at
-one speed and unbalanced at another. To determine if the moving parts
-are balanced the pump should be run free at different speeds and the
-amount of vibration observed. If the impeller is removed from the pump
-its balance when at rest can be studied by resting it on horizontal
-knife edges. If there is a tendency to rotate in any direction from any
-position the impeller is not perfectly balanced.
-
-Packing rings are used to prevent the escape of water from the discharge
-chamber back into the suction chamber. These rings should be made of the
-same material as the impeller. Labyrinth type rings, as shown in Fig.
-50, are sometimes used as the long tortuous passages are efficient in
-preventing leakage.
-
-The bearings must be carefully made because of the high speed of the
-pump. They are usually made of cast iron with babbitt lining. They
-should be placed on the ends of the shaft on the outside of the pump
-casing, as shown in Fig. 50, and should be split horizontally so as to
-be easily renewed. Exterior bearings are oil lubricated by means of ring
-or chain oilers with deep oil wells. Where interior bearings are
-necessary, because of the length of the shaft, they should be made of
-hard brass and should be water lubricated.
-
-[Illustration:
-
- FIG. 56.—Marine Type Thrust Bearing.
-
- Courtesy, DeLaval Steam Turbine Co.
-]
-
-Thrust bearings or thrust balancing devices are used to take up the end
-thrust which occurs in even the best designed pumps. To overcome this
-pumps are designed with double suction, opposed impellers, or two pumps
-with their impellers opposed may be placed on the same shaft. Due to
-inequalities in wear, workmanship or other conditions, end thrust will
-occur and must be cared for. Various types of thrust bearings are in
-successful use, such as: the piston, ball, roller or marine types. The
-marine type thrust bearing is shown in Fig. 56. The piston type of
-hydraulic balancing device is shown in Fig. 57. In the figure _A_
-represents the impeller, and _B_ a piston fixed to the shaft and
-revolving with it. There is a passage for water through the openings
-(1), (2), and (3) leading from the impeller chamber to the atmosphere or
-to the suction of the pump. If the impeller tends to move to the right
-opening (1) is closed resulting in pressure on the right of the impeller
-forcing it to the left. If the impeller moves to the left (1) is opened
-thus transmitting pressure to the piston _B_ forcing the impeller to the
-right. The flange _C_ is not essential, but is advantageous in pumps
-handling gritty matter. As the channel (2) wears larger the pressure
-against the piston decreases allowing it to move to the left. This
-partially closes (3) building up the pressure again.
-
-[Illustration:
-
- FIG. 57.—Piston Type of Thrust Balancing Device.
-]
-
-Flexible shaft couplings should be used if the shaft of the driving
-motor and the pump are in the same line, as direct alignment is
-difficult to obtain or to maintain. Where connected to steam turbines,
-reduction gearing and rigid couplings are usually used on sewage pumps
-to obtain slow speed and permit large passages. Flexible couplings are
-of various types, one of which is shown in Fig. 50. A rigid coupling
-would be formed by bolting the flanges firmly together. Shaft couplings
-are usually not necessary where the pump is driven by belt connection to
-the engine or motor, or where the pump and pulley rest on only two
-bearings.
-
-The stuffing box shown in Fig. 50 is packed loosely with two layers of
-hemp between which is a lantern gland, in order to permit a small amount
-of leakage. A drip box is placed below this gland to catch the leakage
-and return it to the pump. The leakage is permitted as it aids in
-lubrication and the tightening of the gland will cause binding of the
-shaft. The gland on the suction side of the pump should be connected by
-a small pipe to the discharge chamber in order to keep a constant supply
-of water for lubrication and to prevent the entrance of air to the
-suction end of the pump.
-
-
-=78. Centrifugal Pump Characteristics.=—The capacity of a centrifugal
-pump is fixed by the size and type of its impeller and by the speed of
-revolution. Roughly, the capacity of a pump, for maximum efficiency,
-varies directly as the speed of revolution, the discharge pressure
-varies as the square of the speed, and the power varies as the cube of
-the speed. These relations are found not to hold exactly in tests
-because of internal hydraulic friction in the pump.
-
-The characteristic curves for a centrifugal pump, or the so-called pump
-characteristics, are represented graphically by the relation between
-quantity and efficiency, quantity and power necessary to drive, and
-quantity and head, all at the same speed. The quantities are plotted as
-abscissas in every case. The curve whose ordinates are head and whose
-abscissas are quantities is known as “the characteristic.” The curve
-showing the relation between quantities and speeds is sometimes included
-among the characteristics. Characteristics of pumps with different
-styles of impellers are shown in Fig. 58. Fig. 59 shows the
-characteristics of a pump run at different speeds, the efficiencies at
-these speeds when pumping at different rates, and the maximum efficiency
-at different speeds. It is to be noted that the information given in
-this figure is more extensive than that in Fig. 58. The operating
-conditions under any head, rate of discharge, and speed are given. The
-curves of constant speed are parallel, and their distances apart vary as
-the square of the speed. The line of maximum efficiency is approximately
-a parabola.
-
-[Illustration:
-
- FIG. 58.—Characteristics of Centrifugal Pumps with Different Styles of
- Impellers at Constant Speed.
-]
-
-A study of the characteristics of any particular pump should be made
-with a view to its selection for the load and conditions under which it
-is to be used. Among the important things to be considered in the
-selection of a centrifugal pump for the expected conditions of load are:
-the capacity required, the maximum and minimum total head to be pumped
-against, the maximum variations in suction and discharge heads, and the
-nature of the drive. For example, the pump, whose characteristics are
-shown in Fig. 59, should be operated at about 800 revolutions per
-minute. Under total heads between 40 and 50 feet, the discharge for the
-best efficiency will vary between 600 and 670 gallons per minute.
-
-[Illustration:
-
- FIG. 59.—Efficiency and Characteristic Curves of a Centrifugal Pump at
- Different Speeds.
-]
-
-[Illustration:
-
- FIG. 60.—Efficiencies of Centrifugal Pumps.
-]
-
-The efficiencies of centrifugal pumps increase with their capacities as
-is shown approximately in Fig. 60.
-
-
-=79. Setting of Centrifugal Pumps.=—In setting a centrifugal pump, care
-should be taken to provide a firm foundation to hold the shafts of the
-pump and the electric motor or the reduction gearing in good alignment,
-or to prevent the pump from being displaced by the pull of a belt. It is
-desirable that the foundation be level. Centrifugal pumps should be set
-submerged for small pumping stations automatically controlled. Sludge
-pumps must be set submerged as otherwise they will not prime
-successfully. Provision should be made by which the pump can be lifted
-from the sewage, or sludge, for inspection and repair. In many cases the
-pump can be made self-priming by setting it in a dry, water-tight vault
-below the low level of sewage flow. Where possible it is desirable not
-to set the pump submerged as it will receive better care when easily
-accessible.
-
-[Illustration:
-
- FIG. 61.—Centrifugal Pump in Manhole at Duluth, Minn.
-
- Eng. Contracting, Vol. 43, 1915, p. 310.
-]
-
-The suction pipe should be free from vertical bends where air might
-collect and should be straight for at least 18 to 24 inches from the
-pump casing. An elbow on the suction pipe, attached directly to the
-casing of the pump gives a lower efficiency than a suction pipe with a
-short straight run. Centrifugal pumps will operate with as high a
-suction lift as reciprocating pumps, but at the start they must be
-primed and some provision must be made for priming them. The suction
-pipe should be equipped with foot valves to hold the priming, or some
-method may be provided for exhausting the air from the suction pipe. The
-foot valves should be so installed as to form no appreciable obstruction
-to the flow of water. They should have an area of opening at least 50
-per cent greater than the cross-section of the suction pipe. A strainer
-on the suction pipe is undesirable as it becomes clogged and is usually
-in an inaccessible position for cleaning. A screen should be placed at
-the entrance to the suction well to prevent the entrance of objects that
-are likely to clog the pump. A gate-valve and a check-valve should be
-provided on the discharge pipe, the former to assist in controlling the
-rate of discharge and the latter to prevent back flow into the pump when
-it is not operating.
-
-Centrifugal pumps are well adapted to service in either large or small
-units. An installation in a manhole at Park Point, Duluth, is shown in
-Fig. 61. This station is controlled by an automatic electric device
-which is operated by a float in the suction pit. Such automatic control
-is an added advantage of the use of electrically driven centrifugal
-pumps. The Calumet Pumping Station in Chicago, shown in Fig. 49, has a
-capacity of approximately 1,000 cubic feet per second. The simplicity of
-the layout of this station is shown in Fig. 62.
-
-[Illustration:
-
- FIG. 62.—Interior Arrangement of the Calumet Sewage Pumping Station,
- Chicago.
-
- Eng. News-Record, Vol. 85, 1920, p. 872.
-]
-
-
-=80. Steam Pumps and Pumping Engines.=—The direct-acting steam pump, one
-type of which is shown in Fig. 63, is adapted to pumping sewage the
-character of which will not corrode or clog the valves. In this form of
-pump it is necessary to utilize the steam at full pressure throughout
-the entire length of the stroke, which results in high steam
-consumption. A flywheel permits the use of steam expansively during a
-part of the stroke, thus increasing the economy of operation. Other
-devices used for the same purpose are known as compensators. They are
-not in general use.
-
-Steam engines are classified in many different ways, for example;
-according to the type of valve gear, as, plain slide valve, Corliss,
-Lentz, etc.; or according to the number of steam expansions, as, simple,
-compound, triple-expansion, etc.; or according to the efficiency of the
-machine as low duty or high duty; or as
-
-[Illustration:
-
- FIG. 63.—Section of Duplex Piston Steam Pump.
-
- Courtesy, The John H. McGowan Co.
-]
-
- STEAM END
-
- 2 Steam cylinder and housing combined.
-
- 8 Steam piston head.
-
- 9 Steam piston follower.
-
- 10 Steam piston inside ring.
-
- 11 Steam piston outside ring (2).
-
- 12 Steam cylinder head.
-
- 14 Steam chest.
-
- 16 Steam chest cover.
-
- 17 Steam slide valve.
-
- 18 Steam valve rod.
-
- 20 Steam valve rod, pin and nut.
-
- 22 Steam valve rod, collar and set screw.
-
- 23 Steam valve rod, stuffing box.
-
- 24 Steam valve rod, stuffing box, nut and gland.
-
- 38 Piston rod.
-
- 47 Piston rod stuffing box.
-
- 48 Piston rod, stuffing box, nut and gland.
-
- 49 Valve gear stand.
-
- 51 Long valve crank and shaft.
-
- 52 Short valve crank and shaft.
-
- PUMP END
-
- 115 Pump body.
-
- 127 Brass liner.
-
- 129 Water piston head.
-
- 130 Water piston follower.
-
- 137 Cylinder head.
-
- 139 Valve plate.
-
- 140 Cap.
-
- 152 Suction flange.
-
- 161 Discharge flange.
-
- 162 Valve seat, suction or discharge.
-
- 163 Valve, suction or discharge.
-
- 164 Suction valve spring.
-
- 167 Discharge valve spring.
-
- 168 Valve plate, suction or discharge.
-
- 169 Valve stem, suction or discharge.
-
- STEAM END
-
- 55 Crank pin.
-
- 56 Valve rod link.
-
- 61 Long rocker arm.
-
- 62 Short rocker arm.
-
- 63 Rocker arm wiper.
-
- 69 Cross head.
-
-condensing or non-condensing, etc. Throttling engines or automatic
-engines refer to the method of control of the steam by the governor. In
-throttling engines the governor controls the amount of opening of the
-throttle valve, in automatic engines the governor controls the position
-of the cut-off.
-
-The simple slide valve, low-duty, non-condensing, throttling engine, is
-the lowest in first cost and the most expensive in the consumption of
-fuel. The triple-expansion Corliss, or the non-releasing Corliss,
-high-duty pumping engine is the most expensive in first cost but
-consumes less steam for the power delivered than any other form of
-reciprocating engine. For pumps of very small capacity the cost of fuel
-is not so important an item as the first cost of the machine. For this
-reason and because of the lower cost of attendance low-duty pumps are
-more frequently found in small pumping stations.
-
-[Illustration:
-
- FIG. 64.—Diagram Showing Rates of Steam Consumption for Different Size
- Units under Different Loads.
-]
-
- TABLE 27
-
- WATER RATES OF PRIME MOVERS AT FULL AND PART LOADS
-
- ───────────────────────────────┬──────┬─────────────────────────┬──────
- Type of Engine │ │ │Boiler
- │Power,│ │Press.
- │ K.W. │ Per Cent of Full Load │ Lbs.
- ───────────────────────────────┼──────┼────┬────┬────┬─────┬────┼──────
- │ │ 25 │ 50 │ 75 │ 100 │125 │
- ───────────────────────────────┼──────┼────┼────┼────┼─────┼────┼──────
- Single cylinder, high speed, │ │ │ │ │ │ │100 to
- non-condensing │ 25│ 33│ 27│26.3│ 27.0│27.5│ 150
- │ 250│ 42│37.5│ 35│ 34.0│34.0│
- │ │ │ │ │ │ │
- Automatic, flat four valve, │ │ │ │ │ │ │100 to
- high speed │ 150│ │ 32│ 30│ 26.5│29.0│ 125
- │ 250│ │ 33│ 31│ 28│30.0│
- │ │ │ │ │ │ │
- Tandem compound condensing, │ │ │ │ │ │ │100 to
- high speed │ 125│ │ 23│ 19│ 17│ 18│ 150
- │ │ │ 25│ 20│ 19.5│ 21│
- │ │ │ │ │ │ │
- Cross compound, condensing, │ │ │ │ │ │ │ 125
- high speed │ │ 30│ 26│ 24│ 23│23.5│
- │ │ │ │ │ │ │
- Cross compound, non-condensing,│ │ │ │ │ │ │ 125
- high speed │ │ 39│ 31│ 27│ 26│27.5│
- │ │ │ │ │ │ │
- Single cylinder Corliss, │ │ │ │ │ │ │ 100
- condensing │ 120│23.7│20.4│ 19│ 18.5│19.0│
- │ 500│26.3│22.8│21.3│ 20.8│21.3│ 125
- │ │ │ │ │ │ │
- Compound Corliss, condensing │ │16.5│ 14│12.5│ 12.1│12.5│ 100
- │ │22.2│ 19│17.0│ 16.5│17.0│ 150
- │ │ │ │ │ │ │
- Single cylinder, rotary four │ │ │ │ │ │ │ 100
- valve, non-condensing │ 75│26.2│22.3│21.3│ 21.6│22.8│
- │ 400│35.0│27.2│26.4│ 26.0│26.8│ 180
- │ │ │ │ │ │ │
- Rotary four valve, tandem │ │ │ │ │ │ │ 100
- compound non-condensing │ 125│32.0│22.0│ 20│18.25│18.5│
- │ 600│40.0│28.3│23.2│ 22.5│22.7│ 150
- │ │ │ │ │ │ │
- Cross compound, non-condensing │ │ │ │ │ │ │ 100
- rotary four valve │ 125│ 25│ 21│19.1│ 18.5│19.0│
- │ 600│39.4│ 28│22.3│ 20.6│20.7│ 150
- │ │ │ │ │ │ │
- Single cylinder, poppett valve,│ │ │ │ │ │ │ 100
- non-condensing │ 120│22.7│20.5│19.7│ 19.1│20.1│
- │ 600│28.5│26.0│25.0│ 24.3│25.5│ 150
- │ │ │ │ │ │ │
- Single cylinder, poppett valve,│ │ │ │ │ │ │ 100
- condensing │ 120│18.5│16.7│16.1│ 15.6│16.4│
- │ 600│24.6│22.3│21.4│ 20.8│21.9│ 150
- │ │ │ │ │ │ │
- Compound condensing, poppett │ │ │ │ │ │ │ 100
- valve │ 200│14.2│13.0│12.5│ 12.2│12.9│
- │ 1200│18.4│16.9│16.3│ 15.9│16.8│ 150
- │ │ │ │ │ │ │
- Uniflow │ 125│14.6│13.7│13.4│ 13.4│13.3│ 150
- │ 600│15.0│14.3│13.7│ 13.5│14.0│
- │ │ │ │ │ │ │
- Steam turbines, condensing, │ │ │ │ │ │ │ 125
- Allis-Chalmers │ 300│ │ 24│ 17│ 160│16.5│
- │ 2000│ │31.9│26.3│ 23.8│23.0│ 175
- │ │ │ │ │ │ │
- Steam turbines, condensing, │ │ │ │ │ │ │ 125
- Westinghouse │ 300│ │13.7│12.8│ 12.2│12.6│
- │ 2000│ │18.2│16.9│ 16.2│16.8│ 175
- │ │ │ │ │ │ │
- Steam turbines, high pressure, │ │ │ │ │ │ │
- non-con., 12″ to 36″ wheel, │4 to 8│ │ │ │ │ │
- 1000 to 3600 R.P.M. │stages│ │ │ │ 28 5│ │
- │ │ │ │ │116.5│ │
- │ │ │ │ │ │ │
- Ditto. Condensing, 26–inch │ │ │ │ │ 17 3│ │
- │ │ │ │ │112.0│ │
- │ │ │ │ │ │ │
- ───────────────────────────────┴──────┴────┴────┴────┴─────┴────┴──────
-
-The steam consumption per indicated horse-power, better known as the
-water rate of the engine, for various types of engines at full and at
-part load is shown in Fig. 64. The steam consumption of other types at
-full load is shown in Table 27. The indicated horse-power (I.H.P.) of a
-steam engine is the product of the mean effective pressure (M.E.P.), the
-area of the steam pistons, the length of the stroke, and the number of
-strokes per unit of time. A common form of this expression is,
-
- I.H.P = _PLAN_⁄33,000,
-
- in which _P_ = the M.E.P. in pounds per square inch;
-
- _L_ = the length of the stroke in inches;
-
- _A_ = the sum of the areas of the pistons in square inches;
-
- _N_ = the number of revolutions per minute.
-
-The I.H.P. multiplied by the mechanical efficiency of the machine will
-give the brake or water horse-power, that is, the horse-power delivered
-by the machine. The product of the M.E.P., the sum of the areas of the
-steam pistons and the mechanical efficiency of the machine, should equal
-the product of the total head of water pumped against expressed in
-pounds per square inch and the sum of the areas of the water pistons or
-plungers. The M.E.P. is determined from indicator cards taken from the
-steam cylinders during operation. These cards show the steam pressure on
-the head and crank ends of each cylinder at all points during the
-stroke.
-
-
-=81. Steam Turbines.=—Among the advantages in the use of steam turbines
-as compared with reciprocating steam engines for driving centrifugal
-pumps are their simplicity of operation, the small floor space needed,
-their freedom from vibration requiring a relatively light foundation,
-and their ability to operate successfully and economically either
-condensing or non-condensing under varying steam pressure. They can be
-operated with steam at atmospheric or low pressure, thus taking the
-exhaust from other engines. The greatest economy of operation for the
-turbine alone will be obtained by operating with high pressure,
-superheated steam and with a vacuum of 28 inches. In large units the
-economy of operation of steam turbines is equal to that of the best type
-of reciprocating engines. In order to develop the highest economy
-turbines are operated at speeds from about 3,600 to 10,000 r.p.m. or
-greater, the smaller turbines operating at the higher speeds. As these
-speeds are usually too great for the operation of centrifugal pumps for
-lifting sewage, reduction gears must be introduced between the turbine
-and the pump. Although the best form of spiral-cut reduction gears may
-obtain efficiencies of 95 to 98 per cent, or even higher, their use,
-particularly in small units, is an undesirable feature of the steam
-turbine for driving pumps.
-
-The steam consumption of DeLaval turbines of different powers, and the
-steam consumption of a 450 horse-power DeLaval turbine at different
-loads are shown in Fig. 64. Some steam consumptions of other turbines
-are recorded in Table 27. It is to be noted that the steam consumption
-of the 450 horse-power turbine at part loads is not markedly greater
-than that at full loads. This is an advantage of steam turbines as
-compared with reciprocating engines. The steam consumption of any
-turbine is dependent on the conditions of operation and is lower the
-higher the vacuum into which the exhaust takes place.
-
-[Illustration:
-
- FIG. 65.—The DeLaval Trade Mark, Illustrating the Principle of the
- DeLaval Steam Turbine.
-
- Courtesy, DeLaval Steam Turbine Co.
-]
-
-There are two types of turbines in general use, the single stage or
-impulse machines, and the compound or reaction type. The DeLaval is a
-well-known make of the single stage or impulse type. The principle of
-its operation is indicated in Fig. 65, which is the trade mark of the
-DeLaval Steam Turbine Co. The energy of the steam is transmitted to the
-wheel due to the high velocity of the steam impinging against the vanes.
-In the compound or reaction type of machine the steam expands from one
-stage to the next imparting its energy to the wheel by virtue of its
-expansion in the passages of the turbine. For this reason the
-single-stage or impulse type is operated at higher speeds than the
-compound or reaction machines.
-
-
-=82. Steam Boilers.=—Among the important points to be considered in the
-selection of a steam boiler for a sewage pumping station are: the
-necessary power; the quality of the feed water; the available floor
-space; the steam pressure to be carried; and the quality and character
-of the fuel. Tubular boilers of the type shown in Fig. 66, are lower in
-first cost than other types of boilers. They are not ordinarily built in
-units larger than 250 to 300 horse-power and where more power is desired
-a number of units must be used. They are objectionable because of the
-relatively large floor space required, and because of their relatively
-poor economy of operation. The efficiencies of water-tube boilers of
-different types are given in Table 28. Large power units of the
-water-tube type, as shown in Fig. 67, although more expensive in first
-cost, require less floor space. Almost any desired steam pressure can be
-obtained from either type but water-tube boilers are more commonly used
-for high pressures. The grate or stoker can be arranged to burn almost
-any kind of fuel under either water-tube or fire-tube boilers. The use
-of poor quality of water in water-tube boilers is undesirable as the
-tubes are more likely to become clogged than the larger passages of the
-fire-tube boilers. If necessary, a feed-water purification plant should
-be installed, as it is usually cheaper to take the impurities out of the
-water than to take the scale out of the boiler.
-
-[Illustration:
-
- FIG. 66.—Horizontal Fire-tube Boiler.
-]
-
-[Illustration:
-
- FIG. 67.—Babcock and Wilcox Water-tube Boiler.
-]
-
-Not less than two boiler units should be used in any power station,
-regardless of the demands for power, and if the feed water is bad, three
-or even four units should be provided, as two units may be down at any
-time. An appreciable factor of safety is provided by the ability of a
-boiler to be operated at 30 to 50 per cent overload, if sufficient draft
-is available, but with resulting reduction in the economy of operation.
-The number of units provided should be such that the maximum load on the
-pumping station can be carried with at least one in every 6 units or
-less, out of service for repairs or other cause.
-
- TABLE 28
-
- EFFICIENCIES OF STEAM BOILERS
-
- From Marks’ Mechanical Engineer’s Handbook
- ────────┬───────────┬──────────┬──────┬────────┬──────┬──────┬──────────
- Type │Horse-power│ Furnace │ │ │ │Evap. │
- │ │ │ │ │ │ from │
- │ │ │ │ │ │and at│
- │ │ │ │ │B.T.U.│ 212° │ Combined
- │ │ │ Sq. │Per Cent│ per │ per │Efficiency
- │ │ │ Ft. │of Rated│ Lb. │ Lb. │of Boiler
- │ │ │Grate │Capacity│ Dry │ Dry │ and
- │ │ │ Area │D’v’l’d │ Coal │ Coal │ Furnace
- ────────┼───────────┼──────────┼──────┼────────┼──────┼──────┼──────────
- Babcock │ 300│Hand-fired│ │ │ │ │
- & │ │ │ │ │ │ │
- Wilcox│ │ │ 84│ 118.7│11,912│ 8.81│ 71.8
- Babcock │ 640│Hand-fired│ │ │ │ │
- & │ │ │ │ │ │ │
- Wilcox│ │ │ 118│ 121.5│14,602│ 10.83│ 72.0
- Stirling│ 1128│B. & W. │ │ │ │ │
- │ │ chain │ │ │ │ │
- │ │ grate │ 187│ 198.3│12,130│ 9.51│ 76.1
- Rust │ 335│Hand-fired│ 68│ 210.5│13,202│ 9.42│ 68.9
- Heine │ 400│Green │ │ │ │ │
- │ │ chain │ │ │ │ │
- │ │ grate │ 83.5│ 123.8│11,608│ 8.79│ 73.5
- Maximum efficiency recorded │ │ │ │ │ 83
- ───────────────────────────────┴──────┴────────┴──────┴──────┴──────────
-
-The steam delivered by a boiler is the basis of the measurement of its
-capacity or power. A boiler horse-power is the delivery of 33,320 B.T.U.
-per hour. It is approximately equal to the raising of 30 pounds of water
-per hour from a temperature of 100° Fahrenheit, to steam at a pressure
-of 70 pounds per square inch, or to 34 pounds of water per hour changed
-to steam from and at 212° Fahrenheit, at atmospheric pressure. The
-horse-power of a boiler is sometimes approximated by the area of its
-grate or heating surface. Such a method of measuring has a low degree of
-accuracy on account of the variations in the quality of the fuel, and
-the rate of combustion. For example, the rate of combustion under a
-locomotive boiler is high and there is less than ⅒th of a square foot of
-grate area and about 4.5 square feet of heating surface per boiler
-horse-power. The Scotch Marine type of boiler used on steam ships, has
-slightly more grate area and slightly less heating surface than the
-locomotive type of boiler, because the rate of combustion is lower.
-Stationary water-tube boilers may have 2 to 3 times as much grate area
-and heating surface per horse-power as is found in locomotive boilers.
-If a poor type of fuel is to be used the area of the grate should be
-increased about inversely as the heat content of the fuel. The
-approximate heat content of various types of fuels is shown in Table 29.
-
- TABLE 29
-
- APPROXIMATE HEAT VALUE OF FUELS
-
- ─────────────────────────────────────┬────────────────┬────────────────
- Fuel │ │Pounds of Water
- │ │Evaporated from
- │ │ and at 212° F.
- │ │ All heat
- │B.T.U. per Pound│ utilized
- ─────────────────────────────────────┼────────────────┼────────────────
- Anthracite │ 13,500│ 14.0
- Semi-bituminous, Pennsylvania │ 15,000│ 15.5
- Semi-bituminous, best, West Virginia │ 15,000│ 15.8
- Bituminous, best, Pennsylvania │ 14,450│ 15.0
- Bituminous, poor, Illinois │ 10,500│ 10.9
- Lignite, best, Utah │ 11,000│ 11.4
- Lignite, poor, Oregon │ 8,500│ 8.8
- Wood, best oak │ 9,300│ 9.6
- Wood, poor ash │ 8,500│ 8.8
- ─────────────────────────────────────┴────────────────┴────────────────
-
-
-=83. Air Ejectors.=—The Ansonia compressed-air sewage ejector is shown
-in Fig. 68. In its operation, sewage enters the reservoir through the
-inlet pipe at the right, the air displaced being expelled slowly through
-the air valve marked B. The rising sewage lifts the float which actuates
-the balanced piston valve in the pipe above the reservoir when the
-reservoir fills. The lifting of the valve admits compressed air to the
-reservoir. The air pressure closes valve A and the inlet valve at the
-right, and ejects the sewage through the discharge pipe at the left. As
-the float drops with the descending sewage it shuts off the air supply
-and opens the air exhaust through the small pipe at the top center.
-Sewage is prevented from flowing back into the reservoir by the check
-valve in the discharge pipe. Other ejectors operating on a similar
-principle are the Ellis, the Pacific, the Priestmann and the Shone.
-
-
-=84. Electric Motors.=—The most common form of alternating current
-electric motor used for driving sewage pumps where continuous operation
-and steady loads are met is the squirrel-cage polyphase induction motor.
-These motors operate at a nearly constant speed which should be selected
-to develop the maximum efficiency of the pump and motor set. While Fig.
-59 shows the best efficiency under varying heads to be obtained with
-variable speed, the advantages of cost, attention, and availability make
-the use of a constant speed motor common.[47] This type of motor is
-undesirable where stopping and starting are frequent because it has a
-relatively small starting torque and it requires a large starting
-current. Such motors can be constructed in small sizes for high starting
-torques by increasing the resistance of the rotor, but at the expense of
-the efficiency of operation.
-
-[Illustration:
-
- FIG. 68.—Ansonia Compressed-Air Sewage Ejector.
-]
-
-Alternating current motors are more generally used than direct-current
-motors because of the greater economy of transmission of alternating
-current, but where direct current is available constant speed shunt
-wound motors should be adopted.
-
-In the selection of a motor to drive a centrifugal pump it is important
-that the motor have not only the requisite power, but that its speed
-will develop the maximum efficiency from the pump and motor combined. If
-the pump and motor operate on the same shaft the speed of the two
-machines must be the same. If the two are belt connected, the size of
-the pulleys may be selected so as to give the required speed. If the
-motor is to be connected to a power pump an adequate automatic pressure
-relief valve should be provided on the discharge pipe from the pump, to
-prevent the overloading of the motor or bursting of the pump in case of
-a sudden stoppage in the pipe. The motor must be selected to suit the
-conditions of voltage, cycle, and phase on the line. Transformers are
-available to step the voltage up or down to practically any value.
-Rotary converters are used to change direct to alternating current or
-vice versa.
-
-
-=85. Internal Combustion Engines.=—Internal combustion engines are used
-for driving pumps. Units are available in size from fractions of 1
-horse-power to 2,000 horse-power or more, although the use of the larger
-sizes is exceptional. These engines are not commonly used for sewage
-pumping but when used they are ordinarily belt connected to a
-centrifugal pump, or to an electric generator which in turn drives
-electric motors which operate centrifugal pumps. This type of engine is
-more commonly adapted to small loads, although not entirely confined to
-this field, as they serve admirably as emergency units to supplement an
-electrically equipped pumping station. The fuel efficiency of internal
-combustion engines is higher than for steam engines as is indicated in
-Table 30, but the fuel is more expensive.
-
-The four-cycle gas engine shown in Fig. 69 is the type most commonly
-used. Its horse-power is the product of: the mean effective pressure,
-the length of the stroke, the area of the piston, and the number of
-explosions per second divided by 550. The M.E.P. is dependent on the
-character of the fuel used and the compression of the gas before
-ignition. Producer gas will furnish mean effective pressures between 60
-and 70 pounds per square inch, natural gas and gasoline, 85 to 90 pounds
-per square inch, and alcohol from 95 to 110 pounds per square inch.
-
- TABLE 30
-
- COMPARATIVE FUEL COSTS FOR PRIME MOVERS
-
- ───────────────────────────────────────┬───────────────┬───────────────
- Type of Engine │ Quantity of │Cost of Fuel in
- │ Fuel per H.P. │ Cents per
- │ Hour │ Horse-power
- │ │ Hour
- ───────────────────────────────────────┼───────────────┼───────────────
- Reciprocating steam engines, simple, │ 21 to 8 lb. │ 4.2 to 1.6
- non-condensing, 25 to 200 H.P. │ coal │
- Triple condensing, 2000 to 10,000 │2.3 to 1.9 lb. │ 0.46 to 0.37
- H.P. │ coal │
- ───────────────────────────────────────┼───────────────┼───────────────
- Steam turbines, high pressure, │ │
- non-condensing, │ │
- 200 to 500 K.W. │6.5 to 4.2 lb. │ 1.3 to 0.86
- │ coal │
- 500 to 3000 K.W. │2.6 to 1.9 lb. │ 0.52 to 0.37
- │ coal │
- Condensing 5000 to 20,000 K.W. │1.8 to 1.43 lb.│ 0.36 to 0.28
- │ coal │
- ───────────────────────────────────────┼───────────────┼───────────────
- Gas engines │ │
- Natural gas, 50 to 200 H.P. │ 19 to 11 cu. │
- │ ft. │
- Producer gas, 50 to 200 H.P. │ 2 to 1.5 cu. │
- │ ft. │
- Illuminating gas, 10 to 75 H.P. │ 26 to 19 cu. │ 2.1 to 1.5
- │ ft. │
- Gasoline, 10 to 75 H.P. │ 1.5 to 0.8 │ 5.6 to 3.0
- │ pints │
- ───────────────────────────────────────┼───────────────┼───────────────
- Oil engines, 100 to 500 H.P. │1.1 to 0.75 lb.│
- │ oil │
- ───────────────────────────────────────┴───────────────┴───────────────
- NOTE.—Coal assumed at $4.00 per ton, illuminating gas at 80 cents per
- thousand cubic feet, and gasoline at 30 cents per gallon.
-
-[Illustration:
-
- FIG. 69.—Bessemer Oil Engine. Twin Cylinder, Valve Side.
-]
-
-The Diesel Engine is the most efficient of internal combustion engines.
-The original aim of the inventor, Dr. Rudolph Diesel, was to avoid the
-explosive effect of the ordinary internal combustion engine by injecting
-a fuel into air so highly compressed that its heat would ignite the
-fuel, causing slow combustion of the fuel thus utilizing its energy to a
-greater extent. The fuel and air were to be so proportioned as to
-require no cooling. Although the ideal condition has not been attained,
-the heat efficiency of Diesel engines is high. They will consume from
-0.3 to 0.5 of a pound of oil (containing 18,000 B.T.U. per pound) per
-brake horse-power hour, giving an effective heat efficiency of 25 to 30
-per cent. Although not now in extensive use in the United States it is
-probable that this engine will be more generally adopted for conditions
-suitable for internal combustion engines.
-
-
-=86. Selection of Pumping Machinery.=—Centrifugal pumps are particularly
-adapted to the lifting of sewage because of their large passages, and
-their lack of valves. The low lifts, nearly constant head, and the
-possibility of equalizing the load by means of reservoirs are
-particularly suited to efficient operation of centrifugal pumps. They
-require less floor space than reciprocating pumps of the same capacity,
-and because of their freedom from vibration they do not demand so heavy
-a foundation. The discharge from the pump is continuous thus relieving
-the piping from vibration. In case of emergency the discharge valve can
-be shut off without shutting down the pump, an important point in “fool
-proof” operation.
-
-Volute pumps are better adapted to pumping sewage as their passages are
-more free and they are better suited to the low lifts met. Gritty and
-solid matter will cause wear on the diffusion vanes of turbine pumps in
-spite of the most careful design. Although turbine pumps can possibly be
-built with higher efficiency than volute pumps, their efficiency at part
-load falls rapidly and the fluctuations of sewage flow are sufficient to
-affect the economy of operation. Turbine pumps are more expensive and
-heavier than volute pumps on account of the increased size necessitated
-by the diffusion vanes.
-
-Multi-stage pumps are used for high lifts and are seldom if ever
-required in sewage pumping. As ordinarily manufactured, each stage is
-good for an additional 40 to 100 pounds pressure, but wide variations in
-the limiting pressures between stages are to be found.
-
-Reciprocating plunger pumps are sometimes used for sewage pumping where
-the character of the sewage is such that the valves will not be clogged
-nor parts of the pump corroded. These pumps are seldom used in small
-installations or for low lifts. They are not adapted to automatic or
-long distance control as are electrically driven centrifugal pumps. The
-use of reciprocating pumps for sewage pumping is practically restricted
-to very large pumping stations with capacities in the neighborhood of
-50,000,000 gallons per day or more. Steam-driven pumps are the most
-common of the reciprocating type, but power pumps are sometimes used in
-special cases for small installations and may be driven by either a
-steam or gas engine or an electric motor.
-
-Compressed air ejectors, as described in Art. 83 are used for lifting
-sewage and other drainage from the basement of buildings below the sewer
-level.
-
-Centrifugal pumps electrically driven are, as a rule, the most
-satisfactory for sewage pumping. Electric drive lends itself to control
-by automatic devices, which are particularly convenient in small pumping
-stations. The control can be arranged so that the pump is operated only
-at full load and high efficiency, and when not operating no power is
-being consumed, as is not the case with a steam pump where steam
-pressure must be maintained at all times. The electric driven pump is
-thrown into operation by a float controlled switch which is closed when
-the reservoir fills, and opens when the pump has emptied the reservoir.
-The choice between steam and electric power for large pumping stations
-is a matter of relative reliability and economy.
-
-The selection of the proper type of pump, whether reciprocating or
-otherwise, requires some experience in the consideration of the factors
-involved. Fig. 70 is of some assistance. In discussing this figure,
-Chester states:
-
- “Fig. 70 attempts to represent graphically, the writer’s ideas
- under general conditions, of the machines that should be selected
- for certain capacities for both principal engine and alternate and
- the station duty they may be expected to produce, but you must
- realize that this intends the principal engine doing at least 90
- per cent of the work and that the head, the cost of coal, the load
- factor, the cost of real estate ... the boiler pressure, and the
- space available, and finally ... the funds available, are factors
- which may shift both the horizontal and curved lines. In the field
- of low service pumps of 10,000,000 capacity or over, the
- centrifugal pump reigns supreme, and for constant low heads of
- 20,000,000 capacity or over the turbine driven centrifugal usurps
- the field.”
-
-A reciprocating pump of any type would have to be specially built for
-pumping sewage not carefully screened or otherwise treated, as the
-valves, ordinarily used in such pumps for lifting water, would clog. The
-vertical triple-expansion pumping engine with special valves and for
-large installations, and the centrifugal pump for large or small
-installations are the only suitable types for pumping sewage. With steam
-turbine or electric drive the centrifugal has the field to itself.
-
-[Illustration:
-
- FIG. 70.—Expectancy Curves for Pumping Engines Working against a
- Pressure of 100 Pounds per Square Inch.
-
- J. N. Chester, Journal Am. Water Works Ass’n, Vol. 3, 1916, p. 493.
-]
-
-
-=87. Costs of Pumping Machinery.=—The cost of pumping machinery can not
-be stated accurately as the many factors involved vary with the
-fluctuations in the prices of raw materials, transportation, labor, etc.
-The actual purchase price of machinery can be found accurately only from
-the seller. The costs given in this chapter are useful principally for
-comparative purposes and for exercise in the making of estimates. The
-costs of complete pumping stations are shown in Table 31.[48] These
-figures represent costs in 1911.
-
- TABLE 31
-
- COSTS OF COMPLETE PUMPING STATIONS
-
- These costs include the best type of triple-expansion engines,
- high-pressure boilers, brick or inexpensive stone building with slate
- roof, chimney and intake. Cost of land is not included.
- ─────────────────┬─────────────────┬─────────────────┬─────────────────
- Discharge │ Horse-power per │ │
- Pressure, Lbs. │ Million Gals. │Cost, Dollars per│Cost, Dollars per
- per Sq. In. │ Pumped │ Horse-power │ Million Gallons
- ─────────────────┼─────────────────┼─────────────────┼─────────────────
- 30│ 12│ 562│ 6,750
- 40│ 16│ 438│ 7,000
- 50│ 20│ 362│ 7,250
- 60│ 24│ 312│ 7,500
- 70│ 28│ 277│ 7,750
- 80│ 32│ 250│ 8,000
- 90│ 36│ 229│ 8,250
- 100│ 40│ 213│ 8,500
- 110│ 44│ 200│ 8,750
- 120│ 48│ 187│ 9,000
- 130│ 52│ 192│ 10,000
- │ │ │
- ─────────────────┴─────────────────┴─────────────────┴─────────────────
-
-
-=88. Cost Comparisons of Different Designs.=—In the design of a pumping
-station and its equipment the relative costs of different designs should
-be compared, and the least expensive design selected, due consideration
-being given to serviceability, reliability, and other factors without
-definite financial value. In comparing the costs of different types of
-machinery, all items in connection with the pumping station should be
-considered. For example, the cost of an electrically driven centrifugal
-pump and equipment may be less than the total cost of a steam driven
-reciprocating pump and equipment because of the saving in the cost of
-boilers, boiler house, etc., but a comparison of the capitalized cost of
-the two might show in favor of the reciprocating steam pump because of
-the lower cost of operation.
-
-The total cost of a plant, or any portion thereof, may be considered as
-made up of three parts: (1) The first cost, (2) operation and
-maintenance and, (3) renewal. The total cost S can be expressed as
-
- _S_ = _C_ + _O_⁄_r_ + _R_,
-
- in which _C_ = the first cost;
-
- _O_ = the annual expenditure for operation and maintenance;
-
- _R_ = the amount set aside to cover renewal;
-
- _r_ = the rate of interest.
-
-_S_ is called the capitalized cost of a plant. The annual payment
-necessary to perpetuate a plant is
-
- _A_ = _Sr_ = _Cr_ + _O_ + _Rr_.
-
-The value of _R_ is useful when expressed in terms of the life of the
-plant or machine and the current rate of interest. It is sometimes
-called the depreciation factor or capitalized depreciation. If it is
-borne in mind that _R_ is the amount to be set aside at compound
-interest for the life of the plant, at the end of which time the accrued
-interest should be sufficient to renew the plant, it is evident that
-
- _R_(1 + _R_)^n − _R_ = _C_
-
- or _R_ = _C_⁄((1+_r_)^n − 1)
-
-in which _n_ is the period of usefulness, or life of the plant,
-expressed in years, no allowance being made for scrap value.
-
-A comparison of the annual expense of three different plants is shown in
-Table 32. It is evident from this comparison that the machinery with the
-least first cost is not always the least expensive when all items are
-considered.
-
-A sinking fund is a sum of money to which additions are made annually
-for the purpose of renewing a plant at the expiration of its period of
-usefulness. The annual payment into the sinking fund is equivalent to
-the term _Rr_ in the expression for annual cost, or in terms of _C_,
-_r_, and _n_, the annual payment is
-
- _Cr_⁄((1 + _r_)^n − 1).
-
-It is the same as the capitalized depreciation multiplied by the rate of
-interest. The expression _r_⁄((1 + _r_)^n − 1) is sometimes called the
-rate of depreciation.
-
-The present worth of a machine is the difference between its first cost
-and the present value of the sinking fund. If _m_ represents the present
-age of a plant in years, then the present worth is
-
- _P_ = _C_(1 – ((1 + _r_)^n − 1)⁄((1 + _r_)^m − 1)).
-
- TABLE 32
-
- COMPARISON OF COSTS OF THREE DIFFERENT PUMPING STATIONS. NOMINAL
- CAPACITY THIRTY MILLION GALLONS PER DAY RAISED THIRTY FEET
-
- ────────────────┬──────────────────────────────────
- Equipment │ Plant A
- ────────────────┼──────────────────────────────────
- │One Acre of Land. Brick Building,
- │ Steel Trussed Roof, Slate
- │ Covered. Cross Compound
- │ Condensing Horizontal Pumping
- │ Engine
- ────────────────┼───────┬──────────┬───────┬───────
- │Annual │ Years of │Sinking│ Total
- │Payment│Usefulness│ Fund │
- │ on │ │Payment│
- │ First │ │ │
- │ Cost │ │ │
- ────────────────┼───────┼──────────┼───────┼───────
- Land │ 100│ │ 0│ 100
- Permanent │ 1188│ 50│ 1080│ 2,260
- Structures[49]│ │ │ │
- Pumps and │ 440│ 15│ 435│ 875
- Machinery │ │ │ │
- Boilers │ 280│ 10│ 446│ 726
- Labor │ │ │ │ 14,000
- Fuel │ │ │ │ 5,500
- Repairs, etc. │ │ │ │ 480
- ────────────────┼───────┼──────────┼───────┼───────
- Total │ │ │ │ 23,941
- ────────────────┴───────┴──────────┴───────┴───────
-
- ────────────────┬──────────────────────────────────
- Equipment │ Plant B
- ────────────────┼──────────────────────────────────
- │One Acre of Land. Brick Building.
- │ Steel Trussed Roof, Slate
- │ Covered. Compound Condensing Low
- │ Duty Horizontal Pumping Engine
- │
- ────────────────┼───────┬──────────┬───────┬───────
- │Annual │ Years of │Sinking│ Total
- │Payment│Usefulness│ Fund │
- │ on │ │Payment│
- │ First │ │ │
- │ Cost │ │ │
- ────────────────┼───────┼──────────┼───────┼───────
- Land │ 100│ │ 0│ 100
- Permanent │ 1180│ 50│ 1080│ 2,260
- Structures[49]│ │ │ │
- Pumps and │ 390│ 15│ 395│ 785
- Machinery │ │ │ │
- Boilers │ 252│ 10│ 400│ 652
- Labor │ │ │ │ 14,000
- Fuel │ │ │ │ 7,200
- Repairs, etc. │ │ │ │ 400
- ────────────────┼───────┼──────────┼───────┼───────
- Total │ │ │ │ 25,497
- ────────────────┴───────┴──────────┴───────┴───────
-
- ────────────────┬──────────────────────────────────
- Equipment │ Plant C
- ────────────────┼──────────────────────────────────
- │One Acre of Land. Frame Building,
- │ Shingle Roof. Compound Duplex
- │ Non-Condensing Pumping Engine.
- │
- │
- ────────────────┼───────┬──────────┬───────┬───────
- │Annual │ Years of │Sinking│ Total
- │Payment│Usefulness│ Fund │
- │ on │ │Payment│
- │ First │ │ │
- │ Cost │ │ │
- ────────────────┼───────┼──────────┼───────┼───────
- Land │ 100│ │ 0│ 100
- Permanent │ 810│ 50│ 775│ 1,585
- Structures[49]│ │ │ │
- Pumps and │ 360│ 15│ 352│ 712
- Machinery │ │ │ │
- Boilers │ 308│ 10│ 490│ 798
- Labor │ │ │ │ 14,000
- Fuel │ │ │ │ 8,200
- Repairs, etc. │ │ │ │ 550
- ────────────────┼───────┼──────────┼───────┼───────
- Total │ │ │ │ 25,945
- ────────────────┴───────┴──────────┴───────┴───────
-
-Where straight-line depreciation is spoken of it is assumed that the
-worth of a machine depreciates an equal part of its first cost each
-year. For example, if the life of a plant is assumed to be 20 years,
-straight-line depreciation will assume that the plant loses 1/20 of its
-original value annually. The present worth of a plant under this
-assumption would be the product of its first cost and the ratio between
-its remaining life and its total life. This method of estimating
-depreciation and worth is frequently used, particularly for short-lived
-plants and for simplicity in bookkeeping, but it is less logical than
-the method given above.
-
-
-=89. Number and Capacity of Pumping Units.=—In order to select the
-number and capacity of pumping units for the best economy, a comparison
-of the costs of different combinations of units should be made and the
-most economical combination determined by trial. The principles outlined
-in the preceding articles should be observed in making these
-comparisons. In a steam pumping station, when the number of units
-operating is less than the average daily maximum for the period, steam
-must nevertheless be kept on a sufficient number of boilers to operate
-the maximum number of pumps. This, and corresponding standby losses must
-not be overlooked, as they may show that a smaller number of larger
-units is ultimately more economical.
-
- TABLE 33
-
- SUMMARY OF FLUCTUATIONS OF SEWAGE FLOW AT A PROPOSED PUMPING STATION
-
- ─────────────────┬─────────────────┬─────────────────┬─────────────────
- Number of Days │Flow in Thousand │ │
- Loads Occurred in│ Gallons per │ │
- One Year │ Minute │ Lift in Feet │ Horse-power
- ─────────────────┼─────────────────┼─────────────────┼─────────────────
- 1│ 293│ 6.0│ 450
- 8│ 163│ 8.6│ 354
- 15│ 119│ 10.0│ 300
- 18│ 106│ 10.6│ 284
- 23│ 88│ 11.2│ 249
- 31│ 69│ 12.2│ 211
- 32│ 65│ 12.4│ 204
- 45│ 51│ 13.4│ 173
- 41│ 50│ 13.5│ 169
- 30│ 45│ 13.8│ 158
- 28│ 44│ 13.9│ 154
- 23│ 40│ 14.2│ 143
- 21│ 38│ 14.4│ 137
- 18│ 35│ 14.6│ 129
- 12│ 29│ 15.0│ 111
- 8│ 24│ 15.6│ 95
- 5│ 20│ 16.0│ 79
- 3│ 16│ 16.5│ 65
- 2│ 14│ 16.8│ 58
- 1│ 6.5│ 18.0│ 29
- ─────────────────┴─────────────────┴─────────────────┴─────────────────
- Total horse-power days for one year, 102,000.
- Average load in horse-power, 280.
-
- TABLE 34
-
-POSSIBLE COMBINATIONS OF FIVE PUMPING UNITS TO CARE FOR THE LOADS SHOWN
- IN TABLE 33[50]
-
- ──────────────────────────────────┬───────────────
- 40 Horse-power │ Load
- Type 1[51] │
- ────────┬──────┬───────────┬──────┼───────┬───────
- Per Cent│Pounds│ Load in │Pounds│Number │ Total
- of Rated│Steam │Horse-power│Steam,│of Days│ Load
- Capacity│ per │ │Units │Load is│Carried
- │ H.P. │ │10,000│Carried│ on
- │ Hour │ │Pounds│in Year│ these
- │ │ │ │ │Days in
- │ │ │ │ │ H.P.
- ────────┼──────┼───────────┼──────┼───────┼───────
- 151│ 45│ 60.4│ 6.5│ 1│ 681
- 120│ 44│ 48│ 40.5│ 8│ 542
- 102│ 45│ 40.8│ 66.1│ 15│ 458
- 96│ 45│ 38.4│ 74.8│ 18│ 434
- 98│ 45│ 39.2│ 97.5│ 23│ 381
- │ │ │ │ 31│ 322
- │ │ │ │ 32│ 312
- │ │ │ │ 45│ 264
- │ │ │ │ 41│ 258
- 101│ 45│ 40.4│ 131│ 30│ 242
- 98│ 45│ 39.2│ 119│ 28│ 235
- │ │ │ │ 23│ 218
- │ │ │ │ 21│ 210
- │ │ │ │ 18│ 198
- │ │ │ │ 12│ 170
- 104│ 45│ 41.6│ 20.9│ 8│ 145
- │ │ │ │ 5│ 121
- │ │ │ │ 3│ 100
- 99│ 45│ 39.6│ 8.5│ 2│ 89
- 113│ 44│ 45.2│ 4.8│ 1│ 45
- │ │ │ ————│ │
- Sub-total │ 596.6│ │
- Grand total in pounds, 65,700,000
- ──────────────────────────────────────────────────
-
- ──────────────────────────────────┬───────────────
- 50 Horse-power │ Load
- Type 1[51] │
- ────────┬──────┬───────────┬──────┼───────┬───────
- Per Cent│Pounds│ Load in │Pounds│Number │ Total
- of Rated│Steam │Horse-power│Steam,│of Days│ Load
- Capacity│ per │ │Units │Load is│Carried
- │ H.P. │ │10,000│Carried│ on
- │ Hour │ │Pounds│in Year│ these
- │ │ │ │ │Days in
- │ │ │ │ │ H.P.
- ────────┼──────┼───────────┼──────┼───────┼───────
- 151│ 45│ 75.5│ 8.2│ 1│ 681
- 120│ 44│ 60.0│ 50.7│ 8│ 542
- 102│ 45│ 51.0│ 82.7│ 15│ 458
- 90│ 45│ 48.0│ 93.5│ 18│ 434
- 98│ 45│ 49.0│ 122.0│ 23│ 381
- 104│ 45│ 52.0│ 174.5│ 31│ 322
- 101│ 45│ 50.5│ 174.8│ 32│ 312
- │ │ │ │ 45│ 264
- 103│ 45│ 51.5│ 228│ 41│ 258
- │ │ │ │ 30│ 242
- │ │ │ │ 28│ 235
- │ │ │ │ 23│ 218
- │ │ │ │ 21│ 210
- │ │ │ │ 18│ 198
- │ │ │ │ 12│ 170
- │ │ │ │ 8│ 145
- 109│ 44│ 54.5│ 28.8│ 5│ 121
- │ │ │ │ 3│ 100
- 99│ 45│ 49.5│ 10.7│ 2│ 89
- │ │ │ │ 1│ 45
- │ │ │ ————│ │
- │ 973.9│ │
-
- ──────────────────────────────────────────────────
-
- ──────────────────────────────────┬───────────────
- 60 Horse-power │ Load
- Type 1[51] │
- ────────┬──────┬───────────┬──────┼───────┬───────
- Per Cent│Pounds│ Load in │Pounds│Number │ Total
- of Rated│Steam │Horse-power│Steam,│of Days│ Load
- Capacity│ per │ │Units │Load is│Carried
- │ H.P. │ │10,000│Carried│ on
- │ Hour │ │Pounds│in Year│ these
- │ │ │ │ │Days in
- │ │ │ │ │ H.P.
- ────────┼──────┼───────────┼──────┼───────┼───────
- 151│ 45│ 90.6│ 9.8│ 1│ 681
- 120│ 44│ 72.0│ 60.8│ 8│ 542
- 102│ 45│ 61.2│ 99.2│ 15│ 458
- 96│ 45│ 57.6│ 112│ 18│ 434
- │ │ │ │ 23│ 381
- 104│ 45│ 62.4│ 209.0│ 31│ 322
- 101│ 45│ 60.6│ 210│ 32│ 312
- 102│ 45│ 61.2│ 325│ 45│ 264
- │ │ │ │ 41│ 258
- │ │ │ │ 30│ 242
- │ │ │ │ 28│ 235
- │ │ │ │ 23│ 218
- │ │ │ │ 21│ 210
- │ │ │ │ 18│ 198
- 106│ 45│ 63.6│ 137│ 12│ 170
- │ │ │ │ 8│ 145
- 109│ 44│ 65.4│ 34.5│ 5│ 121
- │ │ │ │ 3│ 100
- │ │ │ │ 2│ 89
- │ │ │ │ 1│ 45
- │ │ │ ————│ │
- │1197.3│ │
-
- ──────────────────────────────────────────────────
-
- ──────────────────────────────────┬───────────────
- 100 Horse-power │ Load
- Type 4[51] │
- ────────┬──────┬───────────┬──────┼───────┬───────
- Per Cent│Pounds│ Load in │Pounds│Number │ Total
- of Rated│Steam │Horse-power│Steam,│of Days│ Load
- Capacity│ per │ │Units │Load is│Carried
- │ H.P. │ │10,000│Carried│ on
- │ Hour │ │Pounds│in Year│ these
- │ │ │ │ │Days in
- │ │ │ │ │ H.P.
- ────────┼──────┼───────────┼──────┼───────┼───────
- 151│ 28│ 151│ 10.2│ 1│ 681
- 120│ 25│ 120│ 57.5│ 8│ 542
- 102│ 25│ 102│ 62.5│ 15│ 458
- 96│ 25│ 96│ 103.8│ 18│ 434
- 98│ 25│ 98│ 135.1│ 23│ 381
- │ │ │ │ 31│ 322
- │ │ │ │ 32│ 312
- │ │ │ │ 45│ 264
- │ │ │ │ 41│ 258
- │ │ │ │ 30│ 242
- │ │ │ │ 28│ 235
- │ │ │ │ 23│ 218
- │ │ │ │ 21│ 210
- │ │ │ │ 18│ 198
- 106│ 25│ 106│ 76.5│ 12│ 170
- 104│ 25│ 104│ 29.1│ 8│ 145
- │ │ │ │ 5│ 121
- 100│ 25│ 100│ 32.4│ 3│ 100
- │ │ │ │ 2│ 89
- │ │ │ │ 1│ 45
- │ │ │ ————│ │
- │ 507.1│ │
-
- ──────────────────────────────────────────────────
-
- ──────────────────────────────────┬───────────────
- 200 Horse-power │ Load
- Type 5[51] │
- ────────┬──────┬───────────┬──────┼───────┬───────
- Per Cent│Pounds│ Load in │Pounds│Number │ Total
- of Rated│Steam │Horse-power│Steam,│of Days│ Load
- Capacity│ per │ │Units │Load is│Carried
- │ H.P. │ │10,000│Carried│ on
- │ Hour │ │Pounds│in Year│ these
- │ │ │ │ │Days in
- │ │ │ │ │ H.P.
- ────────┼──────┼───────────┼──────┼───────┼───────
- 151│ 23│ 302│ 16.7│ 1│ 681
- 120│ 20│ 240│ 92.0│ 8│ 542
- 102│ 20│ 204│ 147│ 15│ 458
- 96│ 20│ 192│ 166│ 18│ 434
- 98│ 20│ 196│ 216│ 23│ 381
- 104│ 20│ 208│ 309.5│ 31│ 322
- 101│ 20│ 202│ 310│ 32│ 312
- 102│ 20│ 204│ 481│ 45│ 264
- 103│ 20│ 206│ 405│ 41│ 258
- 101│ 20│ 202│ 291│ 30│ 242
- 98│ 20│ 196│ 264│ 28│ 235
- 109│ 20│ 218│ 241│ 23│ 218
- 105│ 20│ 210│ 212│ 21│ 210
- 99│ 20│ 198│ 171│ 18│ 198
- │ │ │ │ 12│ 170
- │ │ │ │ 8│ 145
- │ │ │ │ 5│ 121
- │ │ │ │ 3│ 100
- │ │ │ │ 2│ 89
- │ │ │ │ 1│ 45
- │ │ │ ————│ │
- │3322.2│ │
-
- ──────────────────────────────────────────────────
-
- TABLE 35
-
- FINANCIAL COMPARISON OF PUMPING EQUIPMENTS
-
- The loads to be cared for are shown in Table 34. An emergency unit is
- supplied to bring the overload capacity of the plant, less the largest
- unit, equal to the maximum load on the plant. No unit will be
- overloaded more than fifty per cent of its rated capacity.
-
- ───────────┬───────────┬───────────┬───────────┬───────────┬───────────
- Number of │ │ │ │ │
- Units │ │ │ │ │
- Exclusive │ │ │ │ │
- of │ │ │ │ │
- Emergency │ │ │ │ │
- Unit │ 5 │ 4 │ 3 │ 2 │ 1
- ───────────┼───────────┼───────────┼───────────┼───────────┼───────────
- Capacity │ 40 h.p.,│ │ │ │
- and Type of│ Type 1│ │ │ │
- Units │ 50 h.p.,│ 50 h.p.,│ │ │
- │ Type 1│ Type 1│ │ │
- │ 60 h.p.,│ 100 h.p.,│ 50 h.p.,│ │
- │ Type 1│ Type 4│ Type 1│ │
- │ 100 h.p.,│ 125 h.p.,│ 150 h.p.,│ 200 h.p.,│
- │ Type 4│ Type 4│ Type 5│ Type 5│
- │ 200 h.p.,│ 175 h.p.,│ 250 h.p.,│ 250 h.p.,│ 450 h.p.,
- │ Type 5│ Type 5│ Type 6│ Type 6│ Type 7
- ───────────┼───────────┼───────────┼───────────┼───────────┼───────────
- Emergency │ │ │ │ │
- Unit, │ │ │ │ │
- Capacity │ 200 h.p.,│ 175 h.p.,│ 250 h.p.,│ 250 h.p.,│ 450 h.p.,
- and Type │ Type 5│ Type 5│ Type 6│ Type 6│ Type 7
- ───────────┼───────────┼───────────┼───────────┼───────────┼───────────
- Annual │ │ │ │ │
- payments,│ │ │ │ │
- Dollars │ │ │ │ │
- First │ │ │ │ │
- cost of│ │ │ │ │
- pumps │ 1,560│ 1,660│ 1,480│ 1,440│ 1,500
- Renewal │ │ │ │ │
- of │ │ │ │ │
- pumps │ 1,340│ 1,430│ 1,270│ 1,240│ 1,290
- First │ │ │ │ │
- cost, │ │ │ │ │
- boilers│ 1,024│ 1,089│ 1,125│ 1,115│ 1,410
- Renewal, │ │ │ │ │
- boilers│ 800│ 935│ 966│ 958│ 1,210
- Fuel │ 13,140│ 11,860│ 10,490│ 9,420│ 9,400
- Repairs, │ │ │ │ │
- oil, │ │ │ │ │
- etc. │ 2,000│ 1,800│ 1,500│ 1,300│ 1,200
- Labor │ 35,000│ 31,500│ 29,500│ 27,000│ 27,000
- Emergency│ │ │ │ │
- unit. │ │ │ │ │
- First │ │ │ │ │
- cost │ 640│ 560│ 800│ 800│ 1,500
- Emergency│ │ │ │ │
- unit. │ │ │ │ │
- Renewal│ 550│ 480│ 690│ 690│ 1,290
- ───────────┼───────────┼───────────┼───────────┼───────────┼───────────
- Total │ 56,134│ 51,314│ 47,821│ 43,963│ 45,800
- ───────────┴───────────┴───────────┴───────────┴───────────┴───────────
-
- Type 1. Simple duplex, non-condensing, horizontal.
-
- Type 4. Compound condensing low duty horizontal.
-
- Type 5. Low duty, triple, condensing, horizontal.
-
- Type 6. Cross compound, condensing, horizontal.
-
- Type 7. High duty, triple, condensing, vertical.
-
-For example, the sewage flow expected at a proposed pumping station is
-shown in Table 33. The steps involved in the selection of the number and
-capacity of pumping units to care for these quantities are as follows:
-(1) Determine the rated capacity of the equipment to be provided. In
-this case the capacity will be taken as 450 horse-power, which is the
-maximum load to be placed on the pumps. (2) Select any number of units
-of such different types and capacities as are available for comparison,
-and arrange them in different combinations so that each unit will
-operate as nearly as possible at its rated capacity. The work involved
-in such a study for 5 units is shown in Table 34. The weight of steam
-consumed per indicated horse-power hour corresponding to the per cent of
-the rated capacity at which the unit is operating is read from Fig. 64
-or other data. (3) Repeat this step for other numbers and types of
-units. (4) Prepare a table showing the annual costs of combinations of
-different numbers and types of units as shown for this example in Table
-35. The figures in Table 35 show that the least expensive of the
-combinations of the units studied is one 200 horse-power unit, and one
-250 horse-power unit, with a 250 horse-power unit in reserve. It is to
-be noted that a reserve unit has been provided in each combination, the
-capacity of which is equal to that of the largest unit of the
-combination.
-
-
-
-
- CHAPTER VIII
- MATERIALS FOR SEWERS
-
-
-=90. Materials.=—The materials most commonly used for the manufacture of
-sewer pipe are vitrified clay and concrete. Cast iron, steel, and wood
-are also used, but only under special conditions. For pipes built in the
-trench, concrete, concrete blocks, brick, and vitrified clay blocks are
-used. Concrete is being used to-day more than bricks or blocks because
-it is cheaper. A decade or more ago all large sewers were built of
-bricks. Vitrified clay and concrete are used for manufactured pipe 42
-inches and less in diameter. Concrete is used almost exclusively for
-larger sizes of pipe, particularly for pipe constructed in place,
-although a brick invert lining is advisable when high velocities of flow
-are expected.
-
-The character of the external load, the velocity of flow and the quality
-of sewage are important factors in determining the material to be used
-in the construction of sewers. Reinforced concrete should be used for
-large sewers near the surface subjected to heavy moving loads. A high
-velocity of flow with erosive suspended matter demand a brick wearing
-surface on the invert. Many engineers consider concrete less suitable
-than vitrified clay or brick for conveying septic sewage or acid
-industrial wastes, as concrete deteriorates more rapidly under such
-conditions. Concrete should be used on soft yielding foundations,
-whereas a hard compact earth, which can be cut to the form of the sewer,
-is suitable to the use of brick or concrete.
-
-Cast-iron pipe with lead joints is used for sewers flowing under
-pressure, or where movements of the soil are to be expected. If the
-sewage is not flowing under pressure, cement joints are sometimes used
-in the cast-iron pipe. Movements of the soil are to be expected on side
-hills, under railroad tracks, etc. Steel pipe is used on long outfalls
-or under other conditions where external loads are light and the cost is
-less than for other materials. Because of the thin plates used and the
-liability to corrosion steel is not frequently used. It should never be
-deeply buried nor externally loaded because of its weakness in resisting
-such forces. Like wood pipe, its lightness is favorable to use on
-bridges, but the greater heat conductivity of steel than wood
-necessitates protection against freezing in exposed positions. Wood is
-preferable only where the economy of its use is pronounced and the pipe
-is running full at all times. It is desirable that the wood pipe should
-be always submerged as the life of alternately wet and dry wood is
-short.
-
-Corrugated galvanized iron and unglazed tile have been used for sewers,
-but usually only in emergencies or as a makeshift. Corrugated iron is
-not suitable on account of its roughness and liability to corrosion, and
-unglazed tile because of its lack of strength.
-
-[Illustration:
-
- FIG. 71.—Diagrammatic Section through Clay-pipe Press.
-]
-
-
-=91. Vitrified Clay Pipe.=—In general the physical and chemical
-qualities of clays before burning are not sufficient to cause their
-condemnation or approval by the engineer, as their behavior in the
-furnace is quite individual and depends greatly on the manner in which
-they are fired. The engineer is interested in the result and writes his
-specifications accordingly.
-
-In the manufacture of clay pipe, the clay as excavated is taken to a
-mill and ground while dry, to as fine a condition as possible. It is
-then sent to storage bins from which it is taken for wet grinding and
-tempering. In this process the clay is mixed with water to the proper
-degree of plasticity. A variation of 1 to 1½ per cent in the moisture
-content will mean failure. Too wet a mixture will not have sufficient
-strength to maintain its shape in the kiln. Too dry a mixture will show
-laminations as it is pressed through the discs.
-
-A press used in the manufacture of clay pipe is shown in cross-section
-in Fig. 71. With the piston heads in the steam and mud cylinders at
-their extreme upward positions, the mud cylinder is filled with clay of
-the proper consistency. Steam is then turned into the steam cylinder
-under pressure and the clay is squeezed into the space between the inner
-and outer shells of the die and mandrel to form the hub of the pipe. The
-pressure on the clay may be from 250 to 600 pounds per square inch. When
-clay appears at the holes, marked _hh_ at the bottom of the mud
-cylinder, the bottom plate and the center portion of the die are removed
-and the remainder or straight portion of the pipe is formed by squeezing
-the clay between the mandrel and the outer wall of the die. A completely
-formed pipe can be seen issuing from the press in Fig. 72. Any sized
-pipe that is desired can be formed from the same press by changing the
-size of the dies and mandrel.
-
-[Illustration:
-
- FIG. 72.—Clay-pipe Press.
-
- Courtesy, Blackmer and Post Manufacturing Co.
-]
-
-Curved pipes are made in two ways—by bending directly as they issue from
-the press, or by shaping by hand in plaster of paris molds. Junctions
-are made by cutting the branch pipe to the shape of the outside of the
-main pipe, fastening the branch in place with soft clay and then cutting
-out the wall of the main pipe the size of the branch. Special fittings
-are usually made by hand in plaster molds.
-
-After being pressed into shape the pipes are taken to a steam-heated
-drying room where a constant temperature is maintained in order to
-prevent cracking of the pipes. They remain in the drying room from 3 to
-10 days until dry, when they are taken to the kilns. If taken to the
-kilns when moist blisters will be produced.
-
-The dried pipes are piled carefully in the kiln so that heat and weight
-may be as evenly distributed as possible, and the fire is then started
-in the kiln. The process of burning can be roughly divided into five
-stages:
-
-1st. Water smoking, which lasts about 72 hours during which the
-temperature is raised gradually to 350 degrees Fahrenheit.
-
-2nd. Heating, during which the temperature is raised to 800 degrees
-Fahrenheit in 24 hours.
-
-3rd. Oxidation, during which the temperature is raised to 1,400 degrees
-Fahrenheit in 84 hours.
-
-4th. Vitrification, in which the temperature is raised to 2,100 degrees
-Fahrenheit in 48 hours, and finally,
-
-5th. Glazing, during which the temperature is unchanged but salt (NaCl)
-is thrown in and allowed to burn.
-
-Oxidation must be complete before vitrification is started as otherwise
-blisters will be raised due to imprisoned carbon dioxide. The important
-points in vitrification are to make the required temperature within a
-reasonable time and to maintain a uniform distribution of heat
-throughout the kiln. When vitrification is complete as shown by a glassy
-fracture of a broken sample taken from the kiln, glazing is accomplished
-by throwing a shovelful of salt on the hottest part of the fire. About
-five to six applications of salt from two to three hours apart may be
-needed. The kiln is then allowed to cool and the manufacture of the pipe
-is complete. The completeness of vitrification is indicated by the
-amount of water that the finished pipe will absorb. Completely vitrified
-pipe will absorb no moisture. Soft-burned pipe may absorb as much as 15
-per cent moisture.
-
-Vitrified clay blocks are made of the same material and in the same
-manner as vitrified clay pipe.
-
-The following data on vitrified pipe have been abstracted from the
-specifications for vitrified pipe adopted by the American Society for
-Testing Materials.
-
-Pipes shall be subject to rejection on account of the following:
-
- (_a_) Variation in any dimension exceeding the permissible
- variations given in Table 36.
-
- (_b_) Fracture or cracks passing through the shell or hub, except
- that a single crack at either end of a pipe not exceeding 2 inches
- in length or a single fracture in the hub not exceeding 3 inches
- in width nor 2 inches in length will not be deemed cause for
- rejection unless these defects exist in more than 5 per cent of
- the entire shipment or delivery.
-
- (_c_) Blisters or where the glazing is broken or which exceed 3
- inches in diameter, or which project more than ⅛ inch above the
- surface.
-
- (_d_) Laminations which indicate extended voids in the pipe
- material.
-
- (_e_) Fire cracks or hair cracks sufficient to impair the
- strength, durability or serviceability of the pipe.
-
- (_f_) Variations of more than ⅛ inch per linear foot in alignment
- of a pipe intended to be straight.
-
- (_g_) Glaze which does not fully cover and protect all parts of
- the shell and ends except those exempted in Sect. 31. Also glaze
- which is not equal to best salt glaze.
-
- (_h_) Failure to give a clear ringing sound when placed on end and
- dry tapped with a light hammer.
-
- (_i_) Insecure attachment of branches or spurs.
-
-
- _Workmanship and Finish_
-
- (29) Pipes shall be substantially free from fractures, large or
- deep cracks and blisters, laminations and surface roughness.
-
- (31) The glaze shall consist of a continuous layer of bright or
- semi-bright glass substantially free from coarse blisters and
- pimples.... Not more than 10 per cent of the inner surface of any
- pipe barrel shall be bare of glaze except the hub, where it may be
- entirely absent. Glazing will not be required on the outer surface
- of the barrel at the spigot end for a distance from the end equal
- to ⅔ the specified depth of the socket for the corresponding size
- of pipe. Where glazing is required there shall be absence of any
- well defined network of crazing lines or hair cracks.
-
- (32) The ends of the pipe shall be square with their longitudinal
- axis.
-
- (33) Special shapes shall have a plain spigot end and a hub end
- corresponding in all respects with the dimensions specified for
- pipes of the corresponding internal diameter.
-
- TABLE 36
-
- PROPERTIES OF CLAY SEWER PIPE
-
- Abstracts from Tentative Specifications of the American Society for
- Testing Materials
-
- ─────────┬─────────┬───────────┬───────┬────────┬──────┬──────┬─────────
- Internal │ Minimum │ Maximum │Laying │Diameter│Depth │Taper │ Minimum
- Diameter,│Crushing │Absorption,│length,│ of │ of │ of │Thickness
- Inches │Strength,│ Per Cent │ Feet │ Inside │Socket│Socket│ of
- │ Pounds │ │ │ of │Inches│ │ Barrel.
- │ per │ │ │Socket, │ │ │ Inches
- │ Linear │ │ │ Inches │ │ │
- │ Foot. │ │ │ │ │ │
- │See Note │ │ │ │ │ │
- │ 2 │ │ │ │ │ │
- ─────────┼─────────┼───────────┼───────┼────────┼──────┼──────┼─────────
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- ─────────┼─────────┼───────────┼───────┼────────┼──────┼──────┼─────────
- │ │ │ │ │ │ │
- │ │ │ │ │ │ │
- ─────────┼─────────┼───────────┼───────┼────────┼──────┼──────┼─────────
- 6 │ 1430 │ 5 │2, 2½, │ 8¼ │ 2 │1 : 20│ ⅝
- │ │ │ 3 │ │ │ │
- 8 │ 1430 │ 5 │2, 2½, │ 10¾ │ 2¼ │1 : 20│ ¾
- │ │ │ 3 │ │ │ │
- 10 │ 1570 │ 5 │2, 2½, │ 13 │ 2½ │1 : 20│ ⅞
- │ │ │ 3 │ │ │ │
- 12 │ 1710 │ 5 │2, 2½, │ 15¼ │ 2½ │1 : 20│ 1
- │ │ │ 3 │ │ │ │
- 15 │ 1960 │ 5 │2, 2½, │ 18¾ │ 2½ │1 : 20│ 1¼
- │ │ │ 3 │ │ │ │
- 18 │ 2200 │ 5 │2, 2½, │ 22¼ │ 3 │1 : 20│ 1½
- │ │ │ 3 │ │ │ │
- 21 │ 2590 │ 5 │2, 2½, │ 26 │ 3 │1 : 20│ 1¾
- │ │ │ 3 │ │ │ │
- 24 │ 3070 │ 5 │2, 2½, │ 29½ │ 3 │1 : 20│ 2
- │ │ │ 3 │ │ │ │
- 27 │ 3370 │ 5 │ 3 │ 33¼ │ 3½ │1 : 20│ 2¼
- 30 │ 3690 │ 5 │ 3 │ 37 │ 3½ │1 : 20│ 2½
- 33 │ 3930 │ 5 │ 3 │ 40¼ │ 4 │1 : 20│ 2⅝
- 36 │ 4400 │ 5 │ 3 │ 44 │ 4 │1 : 20│ 2¾
- 39 │ 4710 │ 5 │ 3 │ 47¼ │ 4 │1 : 20│ 2⅞
- 42 │ 5030 │ 5 │ 3 │ 51 │ 4 │1 : 20│ 3
- ─────────┴─────────┴───────────┴───────┴────────┴──────┴──────┴─────────
-
- ─────────┬────────────────────────────────────────────────┬────────
- Internal │ Permissible Variations │ Number
- Diameter,│ │ of
- Inches │ │Scorings
- │ │ on
- │ │ Spigot
- │ │ and
- │ │Socket ⅛
- │ │ Inch
- │ │ Deep
- ─────────┼───────┬─────────────┬────────┬───────┬─────────┼────────
- │Length,│ Internal │ Length │ Depth │Thickness│
- │ Inches│ Diameter, │ of Two │ of │ of │
- │ (-), │ Inches │Opposite│Socket,│ Barrel, │
- │ per │ │ Sides, │Inches │ Inches │
- │ Foot │ │ Inches │ (-) │ (-) │
- ─────────┼───────┼──────┬──────┼────────┼───────┼─────────┼────────
- │ │Spigot│Socket│ │ │ │
- │ │ (±) │ (±) │ │ │ │
- ─────────┼───────┼──────┼──────┼────────┼───────┼─────────┼────────
- 6 │ ¼ │ 3/16 │ ¼ │ ⅛ │ ¼ │ 1/16 │ 2
- │ │ │ │ │ │ │
- 8 │ ¼ │ ¼ │ 5/16 │ ⅛ │ ¼ │ 1/16 │ 2
- │ │ │ │ │ │ │
- 10 │ ¼ │ ¼ │ 5/16 │ ⅛ │ ¼ │ 1/16 │ 2
- │ │ │ │ │ │ │
- 12 │ ¼ │ 5/16 │ ⅜ │ ⅛ │ ¼ │ 1/16 │ 2
- │ │ │ │ │ │ │
- 15 │ ¼ │ 5/16 │ ⅜ │ ⅛ │ ¼ │ 3/32 │ 3
- │ │ │ │ │ │ │
- 18 │ ¼ │ ⅜ │ 7/16 │ 3/16 │ ¼ │ 3/32 │ 3
- │ │ │ │ │ │ │
- 21 │ ¼ │ 7/16 │ ½ │ 3/16 │ ¼ │ ⅛ │ 3
- │ │ │ │ │ │ │
- 24 │ ⅜ │ ½ │ 9/16 │ ¼ │ ¼ │ ⅛ │ 4
- │ │ │ │ │ │ │
- 27 │ ⅜ │ ⅝ │11/16 │ ¼ │ ¼ │ ⅛ │ 4
- 30 │ ⅜ │ ⅝ │11/16 │ ¼ │ ¼ │ ⅛ │ 4
- 33 │ ⅜ │ ¾ │13/16 │ ¼ │ ¼ │ 3/16 │ 5
- 36 │ ⅜ │ ¾ │13/16 │ ⅜ │ ¼ │ 3/16 │ 5
- 39 │ ⅜ │ ¾ │13/16 │ ⅜ │ ¼ │ 3/16 │ 5
- 42 │ ⅜ │ ¾ │13/16 │ ⅜ │ ¼ │ 3/16 │ 5
- ─────────┴───────┴──────┴──────┴────────┴───────┴─────────┴────────
-
- NOTE 1. For methods of making tests see Proc. Am. Soc. for Testing
- Materials.
-
- NOTE 2. Concentrated load at end of vertical diameter.
-
- (_a_) Slants shall have their spigot ends cut at an angle of
- approximately 45 degrees with the longitudinal axis.
-
- (_b_) Curves shall be at angles of 90, 45, 22½, and 11¼ degrees as
- required. They shall conform substantially to the curvature
- specified.
-
- (_c_) ... All branches shall terminate in sockets.
-
-[Illustration:
-
- FIG. 73.—Standard Clay Pipe Specials.
-
- Courtesy, Blackmer and Post Manufacturing Co.
-]
-
-In Fig. 73 are shown the various forms of vitrified pipe and specials
-which are ordinarily available on the market.
-
-The life of vitrified clay sewers and some observations on the results
-of the inspection of the sewers in Manhattan are discussed in Chapter
-XII. The strength of vitrified sewer pipes is shown in Table 37.
-
- TABLE 37
-
- STRENGTH OF SEWER PIPE
-
- Strength in pounds per linear foot to carry loads from ditch filling
- material such as ordinary sand and thoroughly wet clay, with the under
- side of the pipe bedded 60° to 90° by ordinary good methods. From Proc.
- Am. Society for Testing Materials, Vol. 20, 1920, page 604.
- ────────┬──────────────────────────────────────────────────────────────
- Height │
- of Fill │
- Above │
- Top of │
- Pipe, │
- Feet │ Breadth of the Ditch a Little Below the Top of the Pipe
- ────────┼───────────┬───────────┬───────────┬────────────┬─────────────
- │ 1 Foot │ 2 Feet │ 3 Feet │ 4 Feet │ 5 Feet
- ────────┼───────────┴───────────┴───────────┴────────────┴─────────────
- │ Ditch Filling Material
- ────────┼─────┬─────┬─────┬─────┬─────┬─────┬─────┬──────┬──────┬──────
- │sand │clay │sand │clay │sand │clay │sand │ clay │ sand │ clay
- ────────┼─────┼─────┼─────┼─────┼─────┼─────┼─────┼──────┼──────┼──────
- 2│ 265│ 280│ 615│ 635│ 970│ 990│ 1330│ 1,350│ 1,690│ 1,710
- 4│ 400│ 450│ 1055│ 1125│ 1745│ 1825│ 2455│ 2,535│ 3,165│ 3,250
- 6│ 470│ 545│ 1370│ 1500│ 2370│ 2525│ 3405│ 3,575│ 4,460│ 4,740
- 8│ 505│ 605│ 1600│ 1790│ 2875│ 3115│ 4215│ 4,495│ 5,595│ 5,890
- 10│ 525│ 640│ 1765│ 2015│ 3275│ 3610│ 4900│ 5,295│ 6,590│ 7,020
- 12│ 535│ 660│ 1880│ 2185│ 3600│ 4030│ 5485│ 6,000│ 7,460│ 8,035
- 14│ 540│ 675│ 1965│ 2320│ 3855│ 4380│ 5975│ 6,620│ 8,225│ 8,950
- 16│ 545│ 680│ 2025│ 2425│ 4065│ 4675│ 6395│ 7,165│ 8,890│ 9,775
- 18│ 545│ 685│ 2070│ 2505│ 4230│ 4920│ 6750│ 7,630│ 9,480│10,520
- 20│ 545│ 690│ 2100│ 2565│ 4365│ 5130│ 7050│ 8,060│ 9,995│11,190
- 22│ 545│ 690│ 2125│ 2610│ 4470│ 5305│ 7305│ 8,425│10,445│11,795
- 24│ 545│ 690│ 2140│ 2645│ 4560│ 5445│ 7525│ 8,750│10,840│12,340
- 26│ 545│ 690│ 2150│ 2675│ 4630│ 5575│ 7705│ 9,035│11,185│12,830
- 28│ 545│ 690│ 2160│ 2695│ 4685│ 5680│ 7860│ 9,280│11,490│13,270
- 30│ 545│ 690│ 2165│ 2715│ 4725│ 5765│ 7990│ 9,500│11,755│13,670
- Very │ │ │ │ │ │ │ │ │ │
- great │ 545│ 690│ 2180│ 2770│ 4910│ 6230│ 8725│11,075│13,635│17,305
- ────────┴─────┴─────┴─────┴─────┴─────┴─────┴─────┴──────┴──────┴──────
-
-
-=92. Cement and Concrete Pipe.=—Although there is no general recognition
-of a difference between cement and concrete pipe, there is a tendency to
-term manufactured pipe of small diameter cement pipe, and large pipes or
-pipes constructed in place, concrete pipe. Cement, unlike clay, is used
-in the manufacture of pipe in the field or by more or less unskilled
-operators in “one man” plants. Great care should be used in the
-selection of cement, aggregate, and reinforcement for precast cement
-pipe since the shocks to which it is subjected in transit are more
-liable to rupture it than the heavier but steadier loads imposed on it
-in the trench.
-
-The United States Government, various scientific and engineering
-societies, and other interested organizations have collaborated in the
-preparation of specifications for cement and cement tests. These
-specifications can be found in Trans. Am. Soc. Civil Engineers, Vol. 82,
-1918, p. 166, and in other publications.
-
-The following abstracts have been taken from the proposed tentative
-specifications for Concrete Aggregates, of the Am. Society for Testing
-Materials, issued June 21, 1921:
-
- 1. Fine aggregate shall consist of sand, stone screenings, or
- other inert materials with similar characteristics, or a
- combination thereof, having clean, hard, strong, durable uncoated
- grains, free from injurious amounts of dust, lumps, soft or flaky
- particles, shale, alkali, organic matter, loam or other
- deleterious substances.
-
- 2. Fine aggregates shall preferably be graded from fine to coarse,
- with the coarser particles predominating, within the following
- limits:
-
- Passing No. 4 sieve 100 per cent
- Passing No. 50 sieve, not more than 50 per cent
- Weight removed by elutriation test, not more than 3 per cent
-
- Sieves shall conform to the U. S. Bureau of Standards
- specifications for sieves.
-
- 3. The fine aggregate shall be tested in combination with the
- coarse aggregate and the cement with which it is to be used and in
- the proportions, including water, in which they are to be used on
- the work, in accordance with the requirements specified in Section
- 6....
-
- 7. Coarse aggregate shall consist of crushed stone, gravel or
- other approved inert materials with similar characteristics, or a
- combination thereof, having clean, hard, strong, durable, uncoated
- pieces free from injurious amounts of soft, friable, thin,
- elongated or laminated pieces, alkali, organic or other
- deleterious matter.
-
- * * * * *
-
- The following Table indicates desirable gradings, in percentages,
- for coarse aggregate for certain maximum sizes.
-
- GRADINGS OF COARSE AGGREGATES
-
- ─────────┬─────────────────────────────────────────┬───────────────────
- Maximum │ Circular Openings, Inches │ Passing Screen
- Size of │ │ Having Circular
- Aggregate│ │Openings ¼ Inch in
- Inches │ │diameter, not more
- │ │ than
- ─────────┼───┬───┬───┬─────┬─────┬─────┬─────┬─────┼───────────────────
- │ 3 │2½ │ 2 │ 1½ │ 1¼ │ 1 │ ¾ │ ½ │
- ─────────┼───┼───┼───┼─────┼─────┼─────┼─────┼─────┼───────────────────
- 3 │100│ │ │40–75│ │ │ │ │ 15 per cent
- 2½ │ │100│ │ │40–75│ │ │ │ 15 per cent
- 2 │ │ │100│ │ │40–75│ │ │ 15 per cent
- 1½ │ │ │ │ 100 │ │ │40–75│ │ 15 per cent
- 1¼ │ │ │ │ │ 100 │ │ │35–70│ 15 per cent
- 1 │ │ │ │ │ │ 100 │ │40–75│ 15 per cent
- ¾ │ │ │ │ │ │ │ 100 │ │ 15 per cent
- ─────────┴───┴───┴───┴─────┴─────┴─────┴─────┴─────┴───────────────────
-
-The manufacture of small size cement pipe requires relatively more skill
-than equipment. As a result great care must be observed in the
-inspection of cement pipe and in the enforcement of specifications. For
-large size concrete pipe and reinforced concrete pipe the difficulty of
-holding the pipe together during transportation and lowering into the
-trench aid in insuring a good product.
-
-Cement pipe is made by ramming a mixture of cement, sand, and water into
-a cylindrical mold and allowing it to stand until set. The mold is then
-removed and the pipe stands for a further period of time to become
-cured. The selection and proportion of materials, the amount of water,
-the method of ramming, the period of setting, the length of time of
-curing, and the control of moisture and temperature during this period
-are of great importance in the resulting product. E. S. Hanson[52]
-states that the most conservative engineers recommend a mixture of one
-sack of cement to 2½ cubic feet of aggregate measured as loosely thrown
-into the measuring box. In making up the aggregate, clean gravel or
-broken stone up to ¼ inch in size is used. The American Concrete
-Institute recommends that 100 per cent pass a ½-inch screen, 70 per cent
-a ¼-inch screen, 50 per cent a No. 10, 40 per cent a No. 20, 30 per cent
-a No. 30, and 20 per cent a No. 40. The materials should be carefully
-graded by experiment and not guessed at, as the behavior of all
-aggregates is not the same. Too coarse an aggregate is difficult to
-handle in manufacturing. It causes loss of pipe when the jacket or mold
-is removed and results in rough pipe, stone pockets, and pin holes
-through which water spurts when pressure tests are applied. Too fine an
-aggregate causes loss of strength and with ordinary mixtures tends to
-produce a pipe which will show seepage under internal pressure tests.
-The amount of water in the mixture will vary, from 15 to 20 per cent.
-The mixture should appear dry but should ball in the hand under some
-pressure.
-
-[Illustration:
-
- FIG. 74.—Details of 24–Inch Concrete Pipe Form.
-]
-
-The mixture can be rammed into the molds by hand or machine. A
-machine-made pipe is preferable as it produces a more even and stronger
-product. There are two types of machines for this purpose. One type
-consists of a number of tamping feet which deliver about 200 blows to
-the minute with a pressure of about 800 pounds per square inch of area
-exposed. In the other type a revolving core is drawn through the pipe,
-packing and polishing the concrete as it is pulled through, with special
-provision for packing the bell of the pipe. The tamping machines can
-make 1,500 feet of small size pipe to 300 feet of 24–inch pipe in a day.
-Machines of the second type can make 750 feet of 8–inch to 200 feet of
-30–inch pipe in 30–inch lengths in 9 hours. The inside and outside forms
-for a 24–inch pipe are shown in Fig. 74 as used with the tamping
-machines. The forms are swabbed with oil before being filled in order to
-facilitate their removal. In making a Y-branch or other special, a hole
-is cut in the pipe or mold the size of the joining pipe which is then
-set in place and the joint wiped smooth with cement.
-
- TABLE 38
-
- PROPERTIES OF CEMENT CONCRETE SEWER PIPE
-
- 1917 Specifications of American Society for Testing Materials, with
- Subsequent Revisions
-
- ─────────┬───────┬────────┬───────┬───────┬──────┬─────────
- │Laying │Diameter│Normal │ Depth │Taper │ Minimum
- │Length,│ at │Annular│ of │ of │Thickness
- │ Feet │ Inside │Space, │Socket,│Socket│ of
- │ │ of │Inches │Inches │ │ Barrel,
- │ │Socket, │ │ │ │ Inches
- │ │ Inches │ │ │ │
- Internal │ │ │ │ │ │
- Diameter,│ │ │ │ │ │
- Inches │ │ │ │ │ │
- ─────────┼───────┼────────┼───────┼───────┼──────┼─────────
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- ─────────┼───────┼────────┼───────┼───────┼──────┼─────────
- │ │ │ │ │ │
- │ │ │ │ │ │
- ─────────┼───────┼────────┼───────┼───────┼──────┼─────────
- │2, 2½, │ 8¼ │ ½ │ 2 │1 : 20│ ⅝
- 6 │ 3 │ │ │ │ │
- │2, 2½, │ 11 │ ⅝ │ 2¼ │1 : 20│ ¾
- 8 │ 3 │ │ │ │ │
- │2, 2½, │ 13¼ │ ⅝ │ 2½ │1 : 20│ ⅞
- 10 │ 3 │ │ │ │ │
- │2, 2½, │ 15⅝ │ ⅝ │ 2½ │1 : 20│ 1
- 12 │ 3 │ │ │ │ │
- │2, 2½, │ 19¼ │ ⅝ │ 2½ │1 : 20│ 1¼
- 15 │ 3 │ │ │ │ │
- │2, 2½, │ 22¾ │ ⅝ │ 2¾ │1 : 20│ 1½
- 18 │ 3 │ │ │ │ │
- │2, 2½, │ 26½ │ ¾ │ 2¾ │1 : 20│ 1¾
- 21 │ 3 │ │ │ │ │
- │2, 2½, │ 30¼ │ ¾ │ 3 │1 : 20│ 2⅛
- 24 │ 3 │ │ │ │ │
- 27 │ 3 │ 34 │ ⅞ │ 3¼ │1 : 20│ 2¼
- 30 │ 3 │ 38 │ 1 │ 3½ │1 : 20│ 2½
- 33 │ 3 │ 41½ │ 1 │ 4 │1 : 20│ 2¾
- 36 │ 3 │ 45½ │ 1¼ │ 4 │1 : 20│ 3
- 39 │ 3 │ 49 │ 1¼ │ 4 │1 : 20│ 3¼
- 42 │ 3 │ 53 │ 1½ │ 4 │1 : 20│ 3½
- ─────────┴───────┴────────┴───────┴───────┴──────┴─────────
-
- ─────────┬──────────────────────────────────────┬─────────┬───────────
- │ Limits of Permissible Variations │ Minimum │ Maximum
- │ │Crushing │Absorption,
- │ │Strength,│ Per Cent
- │ │ Pounds │
- │ │ per │
- │ │ Linear │
- Internal │ │ Foot at │
- Diameter,│ │ End of │
- Inches │ │Diameter │
- ─────────┼───────┬─────────────┬──────┬─────────┼─────────┼───────────
- │Length,│ Internal │Depth │Thickness│ │
- │ Inch │ Diameter, │of Hub│of Barrel│ │
- │ per │ Inches │ (-) │ (-) │ │
- │ Foot │ │Inches│ Inches │ │
- │ (-) │ │ │ │ │
- ─────────┼───────┼──────┬──────┼──────┼─────────┼─────────┼───────────
- │ │Spigot│Socket│ │ │ │
- │ │ (±) │ (±) │ │ │ │
- ─────────┼───────┼──────┼──────┼──────┼─────────┼─────────┼───────────
- │ ¼ │ 3/16 │ 3/16 │ ¼ │ 1/16 │ 1430 │ 8
- 6 │ │ │ │ │ │ │
- │ ¼ │ ¼ │ ¼ │ ¼ │ 1/16 │ 1430 │ 8
- 8 │ │ │ │ │ │ │
- │ ¼ │ ¼ │ ¼ │ ¼ │ 1/16 │ 1570 │ 8
- 10 │ │ │ │ │ │ │
- │ ¼ │ ¼ │ ¼ │ ¼ │ 1/16 │ 1910 │ 8
- 12 │ │ │ │ │ │ │
- │ ¼ │ ¼ │ ¼ │ ¼ │ 3/32 │ 1960 │ 8
- 15 │ │ │ │ │ │ │
- │ ¼ │ ¼ │ ¼ │ ¼ │ 3/32 │ 2200 │ 8
- 18 │ │ │ │ │ │ │
- │ ¼ │ 5/16 │ 5/16 │ ¼ │ ⅛ │ 2590 │ 8
- 21 │ │ │ │ │ │ │
- │ ⅜ │ 5/16 │ 5/16 │ ¼ │ ⅛ │ 3070 │ 8
- 24 │ │ │ │ │ │ │
- 27 │ ⅜ │ 5/16 │ ⅜ │ ¼ │ ⅛ │ 3370 │ 8
- 30 │ ⅜ │ ⅜ │ ⅜ │ ¼ │ ⅛ │ 3690 │ 8
- 33 │ ⅜ │ ⅜ │ ⅜ │ ¼ │ 3/16 │ 3930 │ 8
- 36 │ ⅜ │ ½ │ ½ │ ¼ │ 3/16 │ 4400 │ 8
- 39 │ ⅜ │ ½ │ ½ │ ¼ │ 3/16 │ 4710 │ 8
- 42 │ ⅜ │ ½ │ ½ │ ¼ │ 3/16 │ 5030 │ 8
- ─────────┴───────┴──────┴──────┴──────┴─────────┴─────────┴───────────
-
-After the removal of the mold the pipe may be cured by the water or the
-steam process. Hanson states:
-
- By the former the pipe are simply set on the floor of the plant
- and as soon as they are sufficiently strong so that they can be
- sprinkled with water without falling down; sprinkling is commenced
- and continued at such intervals for 6 or 7 days that the pipe will
- be moist at all times. This is a slower process than steam curing.
- It is also less uniform and less subject to control than where the
- product is cured by steam.
-
-In the steam process the pipe is exposed to low-pressure steam with
-plenty of moisture in a closed receptacle for 24 hours, or until
-hardened. It has been found by tests that pipes sprinkled for 28 days
-are as strong as steam-cured pipes.
-
-The dimensions of cement concrete sewer pipe as recommended by the Am.
-Society for Testing Materials are shown in Table 38.
-
-The following has been abstracted from the description of the
-manufacture of one form of concrete pipe by G. C. Bartram.[53] All pipe
-are manufactured in 4–foot lengths near the site at which they are to be
-installed because of their great weight, for example, 36–inch pipe
-weighs one ton. The plant for the manufacture of the pipe consists of
-cast-iron bottom and top rings for each size to be used on the job, and
-inside and outside steel casings. There are three bases for each steel
-casing as the pipes stand on the bases for 72 hours and the steel casing
-remains on for only 24 hours after the concrete has been poured. The
-pipes are then lifted off the bases and stored for aging. The pipes are
-cast with the spigot end up.
-
-The concrete is ordinarily mixed in the proportions of 1 : 2 : 4. The
-materials are placed in the mixer in the following order: first, the
-stone, then the sand, then the cement, and finally the water. Sufficient
-water is added to make the concrete flow freely. In cold weather or for
-a hurry-up job the molds are covered with canvas and are steamed for 2
-or 3 hours immediately after the concrete is poured. The molds are then
-removed but the pipe should be steamed before use. Otherwise they are
-allowed to stand 72 hours, as explained above. In cold weather the steam
-is used to prevent freezing and not to hasten the completion of the
-pipe.
-
-[Illustration:
-
- FIG. 75.—Triangle Mesh Reinforced Concrete Pipe.
-
- As made by the Am. Concrete Pipe and Pile Co., Chicago.
-]
-
-[Illustration:
-
- FIG. 76.—Methods of Joining and Reinforcing Concrete Pipe.
-]
-
-One layer or ring of reinforcement is used for sizes from 24 to 48
-inches and two layers or rings for larger pipe. A type of reinforcement
-sometimes used is the American Steel and Wire Company’s Triangular Mesh,
-an illustration of which is shown in Fig. 75. The wire mesh is cut to
-fit and is placed in a slot in the cast-iron base. The slot is then
-filled with sand so that the concrete cannot enter, thus leaving a
-portion of the reinforcement exposed. The inside reinforcement extends
-through and out of the spigot of the completed pipe. In the trench the
-two reinforcements overlap in the key-shaped space left on the inside of
-the pipe by the design of the bell and spigot. This space is shown in
-Fig. 76 A. When the pipe is placed in the trench the key-shaped space is
-plastered with mortar and a piece is knocked out of the bell to receive
-the grout with which the joint is closed. A spring steel band is then
-put on the outside of the joint and grout poured into the hole at the
-top. The band is removed as soon as the joint materials have set.
-
-The rules for the reinforcement of concrete pipe recommended in Volume
-XV, 1919, of the Transactions of the Concrete Institute are as follows:
-
- No reinforcement is approved for pipe between 30 and 60 inches in
- diameter or in rock or hard soils. For pipe 36 inches in diameter
- or less the minimum thickness of shell shall be 5 inches. For
- 60–inch pipe the minimum thickness shall be 7 inches with
- intermediate sizes in proportion. Reinforcement for circular pipe
- shall consist of one or two rings of circular wire fabric or rods
- of the areas shown in Table 39. All sewers near the surface and
- subject to vibration should be reinforced. For sewers 6 feet or
- less in diameter the reinforcement should consist of at least ½ of
- 1 per cent of the area of the concrete. It should be placed near
- the inside at the crown and near the outside at the haunches. If
- large horizontal pressures are expected the pipe should be
- reinforced for these reverse stresses, which involves placing the
- reinforcement near the outside at the crown and near the inside at
- the haunches. The minimum thickness of the walls of sewers greater
- than 6 feet in diameter with flat bottom and arch, with or without
- side walls, should be 8 inches.
-
- TABLE 39
-
- REINFORCEMENT FOR CIRCULAR CONCRETE SEWER PIPE
-
- (See Vol. XV, Proceedings Am. Concrete Institute)
- ─────────────────┬─────────────────┬─────────────────┬─────────────────
- Diameter in │Minimum Thickness│ Number of Rings │ Cross Sectional
- Inches │ of Shell in │ │Area of Each Ring
- │ Inches │ │
- ─────────────────┼─────────────────┼─────────────────┼─────────────────
- 24 │3 │1 │.058
- 27 │3 │1 │.068
- 30 │3½ │1 │.080
- 33 │4 │1 │.107
- 36 │4 │1 │.146
- 39 │4 │1 │.146
- 42 │4½ │1 │.153
- 48 │5 │2 │.107
- 54 │5½ │2 │.123
- 60 │6 │2 │.146
- 66 │6½ │2 │.168
- 72 │7 │2 │.180
- 84 │8 │2 │.208
- 96 │9 │2 │.245
- ─────────────────┴─────────────────┴─────────────────┴─────────────────
-
-Three methods for the reinforcement of concrete sewers are shown in Fig.
-76 B.
-
-
-=93. Proportioning of Concrete.=—In the proportioning of concrete
-questions of strength, of permeability, and of workability[54] may need
-consideration. All of these qualities are affected by the amount of
-cement, the nature and gradation and relative proportions of the fine
-and the coarse aggregate, and the amount of mixing water used.
-
-Other things being equal the strength varies with the amount of cement
-put into the concrete. For the same amount of cement and the same
-consistency of the mixture, the strength increases with increased
-density of concrete (that is, with decreased voids), and the effort
-should be made so to proportion the fine and coarse aggregates as to
-produce the densest concrete (least voids) with the aggregates
-available. For the same consistency, the strength then will vary with
-the ratio of the amount of cement to the amount of the voids.
-
-So far as the mixing water is concerned, the greatest strength in the
-concrete will be attained at a rather dry mix; that which produces the
-least volume of concrete. The addition of more water results in a
-concrete of less strength; 40 per cent more water may give a concrete of
-less than half the normal strength. The reduction in strength is then
-very marked for the wetter mixes, and the water content used is a
-feature of considerable importance in the design of concrete mixtures.
-
-Permeability is affected by the same elements as strength, but the size
-and discontinuity of the pores have a greater influence.
-
-Workability is an important quality; in some respects it will have to be
-obtained at the expense of strength. Increasing the amount of mixing
-water increases the workability of the mixtures, with a resulting
-decrease in strength which may have to be accepted or else overcome by
-increasing the cement in the mix.
-
-An excess of water is often used unnecessarily through ignorance of the
-injurious results. A high proportion of coarse aggregate, up to a
-certain limit, will give concrete of high strength, but the mixture will
-be harsh-working and not easy to place. Lower proportions of coarse
-aggregate will give greater workability and better uniformity of
-product, the latter being an important matter. It is apparent that the
-degree of workability of the mixture needed will depend upon the nature
-of the construction—for a pavement where the concrete will receive
-substantial tamping or working the water content may be much less than
-that which may need to be used in placing concrete around reinforcement
-in narrow members, or where little tamping or spading can be done. The
-nature of the work will affect the standard of consistency to be
-specified.
-
-The proportioning of the concrete should then be dependent upon the
-needs of the structure and the manner of placing the concrete. The
-proportions selected should be carefully adhered to and especially
-should care be taken to see that the right quantity of mixing water is
-used.
-
-The materials are commonly measured volumetrically (by bulk). Because of
-the variations which are introduced by volumetric measurement of the
-materials by the presence of varying degrees of moisture, measurements
-by weight would be more accurate, but these would also be affected by
-differences in the specific gravity of the materials. The methods of
-measuring, the allowance for moisture, as well as the proportions of the
-materials, should be specified.
-
-The methods for proportioning concrete are:
-
- (1) Arbitrarily selected proportions.
-
- (2) Proportions based on minimum voids.
-
- (3) Proportions based on trial mixtures.
-
- (4) Proportions based on a sieve analysis curve.
-
- (5) Proportions based on the surface area of the aggregates.
-
- (6) Proportions based on the water-cement ratio and the fineness
- modulus.
-
- (7) Proportions based on mortar-voids and cement-voids ratio.
-
-Arbitrarily selected proportions are in quite general use; they are
-intended to apply to the materials most commonly used in the vicinity of
-the work. The most common practice is to use twice as great a volume of
-coarse aggregate as fine aggregate, as for instance 1 part cement, 2
-parts fine aggregate, and 4 parts coarse aggregate. Decreasing the ratio
-of coarse aggregate to fine aggregate may give a more easily worked mix
-or require relatively less water for a given workability, and in some
-cases it will be proper to increase this ratio and thus secure an
-increase of strength. Judgment and experience with given materials may
-warrant changes from a stated ratio. The proportions are now frequently
-given as one part cement to a certain number of parts of the mixed
-aggregate, leaving the proportions of the fine to coarse to be
-determined otherwise, since small variations in the relation of these
-will not greatly affect the strength. Proportions in common use are:[55]
-
- Mortar for
- Laying brick and stone masonry from 1 : 0 to 1 : 3
- Filling joints in sewer pipe 1 : 0 to 1 : 2
- Surfaces, floors, sidewalks, pavements 1 : 0 to 1 : 2
- Waterproof linings 1 : 0 to 1 : 2
- Cement, bricks, and blocks 1 : 2½ to 1 : 4
- Concrete for
- Gravity retaining walls, heavy
- foundations, structures needing mass
- more than strength from 1 : 3 : 6 to 1 : 4 : 8
- Retaining walls, piers, sewers,
- pavements, foundations, and work
- requiring strength. (Compressive
- strength in 28 days, 1,500 to 2,000
- pounds per square inch) from 1 : 2 : 4 to 1 : 3 : 6
- Floors, beams, pavements, reinforced
- concrete, arch bridges, low-pressure
- tanks. (Compressive strength in 28
- days, 2,000 to 3,000 pounds per
- square inch) from 1 : 1½ : 3 to 1 : 2½ : 4½
- Reinforced concrete columns, conduit
- pipe, impervious concrete.
- (Compressive strength in 28 days,
- 3,000 to 4,000 pounds per square
- inch) from 1 : 1 : 2 to 1 : 1½ : 3
-
-The usual method of proportioning based on minimum voids is to assume
-that the particles of fine aggregate should fill the voids in the coarse
-aggregate and that the particles of the cement will fill the voids in
-the fine aggregate. About 5 to 10 per cent additional fine aggregate is
-generally added to push the particles of the coarse aggregate apart and
-thus give a more easily worked concrete and one freer from void spaces.
-This method is inaccurate, principally because of the effect of the
-moisture on the volume of the voids, and because the effect on the
-volume by the addition of water is unknown.
-
-Trial mixtures may be made by carefully weighing each of the ingredients
-and then combining them to give a workable concrete. Using a given
-amount of cement, the proportion of ingredients, of the same total
-weight, which will give the least volume and therefore the densest
-concrete is adopted. When making the comparison the consistency of the
-mixes must be maintained constant.
-
-Proportioning may be based on an ideal sieve analysis curve of the mixed
-cement and aggregates. The sieve analysis of the aggregates is made by
-screening a predetermined weight of the sample through a series of 5 to
-8 sieves graded in size from slightly below the size of the largest
-particle to slightly above the smallest particle of the aggregate. The
-analysis is then expressed in the form of a curve. The ideal curve,
-according to Fuller,[56] is shown in Fig. 77.
-
-[Illustration:
-
- FIG. 77.—Gravel Analysis.
-
- The dotted line indicates the ideal combination of the coarse and fine
- portions. The heavy full line indicates the combination attained.
-]
-
-The method of proportioning concrete by surface areas is based on the
-theory that the strength of a concrete depends on the amount of cement
-used in proportion to the surface area of the aggregates.[57]
-
-The proportioning of concrete on the basis of a water-cement ratio and a
-fineness modulus was introduced by Prof. D. A. Abrams.[58] It is based
-on the theory that with fixed conditions of aggregate, moisture, etc.,
-the ratio of water to cement determines the strength of the concrete.
-
-A method of proportioning concrete by determining experimentally the
-voids in mortars made up with a given amount of sand and definite
-proportions of cement, and then calculating the voids in the concrete
-made up by adding a definite amount of coarse aggregate to the mixture,
-has been developed.[59] The method is based on the theory that the
-strength of the concrete is a known function of the ratio of the volume
-of cement to the volume of the voids in the concrete. The effect of
-varying the proportion of the ingredients, including an increase in the
-amount of mixing water beyond that required to give the densest mixture,
-may be found by the method, and a comparison may be made of results
-obtainable with different classes of fine and coarse aggregates.
-
-Arbitrarily selected proportions, proportions based on voids, and
-proportions based on trial mixtures are usually satisfactory for small
-jobs where the amount of materials involved is not large. Where the
-saving in materials will permit, more accurate methods should be used.
-The methods can be studied more fully by reference to the original
-articles quoted in the footnotes, or to the following texts:
-
- Materials of Construction, Johnson, 5th Edition, 1918.
- Materials of Engineering, H. F. Moore, 2d Edition, 1920.
- Masonry Construction, I. O. Baker, 10th Edition, 1912.
- Concrete Engineer’s Handbook, Hool and Johnson, 1918.
- Concrete, Plain and Reinforced, Taylor and Thompson, 1916.
-
-
-=94. Waterproofing Concrete.=—The waterproofing of concrete is most
-satisfactorily done by making dense mixtures. In practice such
-substances as hydrated lime, clay, alum and soap, and proprietary
-compounds such as Ceresit, Medusa, etc., are frequently mixed with the
-concrete under the theory that these very fine substances will fill any
-remaining voids and render the concrete impervious. The specifications
-of the Joint Committee issued on June 4, 1921, are much briefer and
-contain less detailed instruction than those issued earlier.[60] The
-earlier instructions follow.
-
- Many expedients have been resorted to for making concrete
- impervious to water. Experience shows, however, that when mortar
- or concrete is proportioned to obtain the greatest practicable
- density and is mixed to the proper consistency, the resulting
- mortar or concrete is impervious under moderate pressure.
-
- On the other hand concrete of dry consistency is more or less
- pervious to water, and, though compounds of various kinds have
- been mixed with the concrete or applied as a wash to the surface,
- in an effort to offset this defect, these expedients have
- generally been disappointing, for the reason that many of these
- compounds have at best but temporary value, and in time lose their
- power of imparting impermeability to the concrete.
-
- In the case of subways, long retaining walls, and reservoirs,
- provided the concrete itself is impervious, cracks may be so
- reduced, by horizontal and vertical reinforcement properly
- proportioned and located, that they will be too minute to permit
- leakage, or will be closed by infiltration of silt.
-
- Asphaltic or coal tar preparations applied either as a mastic or
- as a coating on felt cloth or fabric, are used for waterproofing,
- and should be proof against injury by liquids or gases.
-
- For retaining and similar walls in direct contact with the earth,
- the application of one or two coatings of hot coal tar pitch,
- following a painting with a thin wash of coal tar dissolved in
- benzol, to the thoroughly dried surface of concrete is an
- efficient method of preventing the penetration of moisture from
- the earth.
-
-Tar paper and asphaltic compounds are not often used in sewer work as
-absolute imperviousness is seldom necessary.
-
-
-=95. Mixing and Placing Concrete.=—Careful workmanship is desirable in
-the mixing and placing of concrete in sewers since water-tight
-construction is desired. Because of the difficulty of inspecting
-concrete in wet, dark and crowded excavations, and the careless habits
-of workmen experienced in concrete sewer construction, the highest class
-of concrete work cannot be expected. The situation is met by designing
-thick walls as shown in the sections illustrated in Fig. 22 and 23.
-
-In the report of the Joint Committee on Concrete and Reinforced Concrete
-in Transactions of the American Society of Civil Engineers for 1917, on
-page 1101 the recommendation is made concerning the mixing and placing
-of concrete as follows:[61]
-
- The mixing of concrete should be thorough and should continue
- until the mass is uniform in color and is homogeneous. As the
- maximum density and greatest strength of a given mixture depends
- largely on thorough and complete mixing, it is essential that this
- part of the work should receive special attention and care.
-
- Inasmuch as it is difficult to determine by visual inspection
- whether the concrete is uniformly mixed, especially where
- aggregates having the color of cement are used, it is essential
- that the mixing should occupy a definite period of time. The
- minimum time will depend on whether the mixing is done by machine
- or hand.
-
- (_a_) Measuring Ingredients: Methods of measurement of the various
- ingredients should be used which will secure at all times separate
- and uniform measurements of cement, fine aggregate, coarse
- aggregate and water.
-
- (_b_) Machine Mixing: The mixing should be done in a batch machine
- mixer of a type which will insure the uniform distribution of the
- materials throughout the mass, and should continue for the minimum
- time of 1½ minutes after all the ingredients are assembled in the
- mixer. For mixers of 2 or more cubic yards capacity, the minimum
- time of mixing should be 2 minutes. Since the strength of the
- concrete is dependent on thorough mixing, a longer time than this
- minimum is preferable. It is desirable to have the mixer equipped
- with an attachment for automatically locking the discharging
- device so as to prevent the emptying of the mixer until all the
- materials have been mixed together for the minimum time required
- after they are assembled in the mixer. Means should be provided to
- prevent aggregates being added after the mixing has commenced. The
- mixer should also be equipped with water storage, and an automatic
- measuring device which can be locked if desired. It is also
- desirable to equip the mixer with a device recording the
- revolutions of the drum. The number of revolutions should be so
- regulated as to give at the periphery of the drum a uniform speed.
- About 200 feet per minute seems to be the best speed in the
- present state of the art.
-
- (_c_) Hand Mixing: Hand mixing should be done on a water-tight
- platform and especial precautions taken after the water has been
- added, to turn all the ingredients together at least 6 times, and
- until the mass is homogeneous in appearance and color.
-
- (_d_) Consistency: The materials should be mixed wet enough to
- produce a concrete of such a consistency as will flow sluggishly
- into the forms and about the metal reinforcement when used, and
- which at the same time can be conveyed from the mixer to the forms
- without separation of the coarse aggregate from the mortar. The
- quantity of water is of the greatest importance in securing
- concrete of maximum strength and density; too much water is as
- objectionable as too little.
-
- (_e_) Retempering: The remixing of concrete and mortar that has
- partly reset should not be permitted.
-
-
- _Placing Concrete_
-
- (_a_) Methods: Concrete after the completion of the mixing should
- be conveyed rapidly to the place of final deposit; under no
- circumstances should concrete be used that has partly set.
-
- Concrete should be deposited in such a manner as will permit the
- most thorough compacting such as can be obtained by working with a
- straight shovel or slicing tool kept moving up and down until all
- the ingredients are in their proper place. Special care should be
- exercised to prevent the formation of laitance; where laitance has
- formed it should be removed, since it lacks strength and prevents
- a proper bond in the concrete.
-
- Care should be taken that the forms are substantial and thoroughly
- wetted (except in freezing weather) or oiled, and that the space
- to be occupied by the concrete is free from all debris. When the
- placing of concrete is suspended, all necessary grooves for
- joining future work should be made before the concrete has set.
-
- When work is resumed concrete previously placed should be
- roughened, cleansed of foreign material and laitance, thoroughly
- wetted and then slushed with a mortar consisting of one part
- Portland cement and not more than 2 parts of fine aggregate.
-
- The surfaces of concrete exposed to premature drying should be
- kept covered and wet for at least 7 days.
-
- Where concrete is conveyed by spouting, the plant should be of
- such a size and design as to insure a practically continuous
- stream in the spout. The angle of the spout with the horizontal
- should be such as to allow the concrete to flow without separation
- of the ingredients; in general an angle of about 27 degrees or 1
- vertical to 2 horizontal is good practice. The spout should be
- thoroughly flushed with water before and after each run. The
- delivery from the spout should be as close as possible from the
- point of deposit. Where the discharge must be intermittent, a
- hopper should be provided at the bottom. Spouting through a
- vertical pipe is satisfactory when the flow is continuous; when it
- is checked and discontinuous it is highly objectionable unless the
- flow is checked by baffle plates.
-
- (_b_) Freezing Weather: Concrete should not be mixed or deposited
- at a freezing temperature, unless special precautions are taken to
- prevent the use of materials covered with ice crystals or
- containing frost, and to prevent the concrete from freezing before
- it has set and sufficiently hardened.
-
- As the coarse aggregate forms the greater portion of the concrete,
- it is particularly important that this material be warmed to well
- above the freezing point.
-
- The enclosing of a structure and the warming of a space inside the
- enclosure is recommended, but the use of salt to lower the
- freezing point is not recommended.
-
- (_c_) Rubble Concrete: Where the concrete is to be deposited in
- massive work, its value may be improved and its cost materially
- reduced by the use of clean stones saturated with water,
- thoroughly embedded in and completely surrounded by concrete.
-
- (_d_) Under Water: In placing concrete under water, it is
- essential to maintain still water at the place of deposit. With
- careful inspection the use of tremies, properly designed and
- operated, is a satisfactory method of placing concrete through
- water. The concrete should be mixed very wet (more so than is
- ordinarily permissible) so that it will flow readily through the
- tremie and into place with practically a level surface.
-
- The coarse aggregate should be smaller than ordinarily used and
- never more than one inch in diameter. The use of gravel
- facilitates the mixing and assists the flow. The mouth of the
- tremie should be buried in the concrete so that it is at all times
- entirely sealed and the surrounding water prevented from forcing
- itself into the tremie. The concrete will then discharge without
- coming in contact with the water. The tremie should be suspended
- so that it can be lowered quickly when it is necessary either to
- choke off or to prevent too rapid flow. The lateral flow
- preferably should not be over 15 feet.
-
- The flow should be continuous in order to produce a monolithic
- mass and to prevent the formation of laitance in the interior.
-
- In case the flow is interrupted it is important that all laitance
- be removed before proceeding with the work.
-
- In large structures it may be necessary to divide the mass of
- concrete into several small compartments or units to permit the
- continuous filling of each one. With proper care it is possible in
- this manner to obtain as good results under water as in the air.
-
- A less desirable method is the use of the drop bottom bucket.
- Where this method is used the bottom of the bucket should be
- released when in contact with the surface of the place of deposit.
-
-Concrete sewers should be constructed in longitudinal sections in a
-continuous operation without interruption for the entire invert, side
-walls, or arch. In pouring the concrete it should be kept level in the
-forms and should rise evenly on each side of the sewer. All rough places
-in the concrete should be finished smooth by brushing with a grout of
-neat cement and water and honeycombs should be filled with neat cement
-or a one-to-one mortar.
-
-
-=96. Sewer Brick.=—The quality of brick used in sewers is seldom
-specified with the minute care that is taken in the specifications for
-concrete, iron, and certain other materials of construction, as inferior
-materials in brick are more easily detected. The specifications of the
-Baltimore Sewerage Commission for sewer brick are:
-
- Sewer brick shall be whole, new bricks of the best quality, of
- uniform standard size, with straight and parallel edges and square
- corners: they shall be of compact texture, burned hard and
- entirely through, free from injurious cracks and flaws, tough and
- strong, and shall have a clear ring when struck together. The
- sides, ends and faces of all bricks shall be plane surfaces at
- right angles and parallel to each other. Bricks of any one make
- shall not vary more than 1/16th of an inch in thickness, nor more
- than 1⅛th of an inch in width or length, from the average of the
- samples submitted for approval.
-
- The truest bricks shall be used in the face of the masonry and the
- exposed surfaces shall be true and smooth planes.
-
- All bricks delivered for use shall be culled by the Contractor
- when required. No brick thrown out in the culling shall be used in
- any work done under any contract of the Sewerage Commission,
- except that the best of the culls may be used in manholes, above
- the level of the top of the sewer, if permitted by the Engineer.
-
- The average amount of water absorbed by the bricks, after being
- thoroughly dried and then immersed for 24 hours, shall not exceed
- 6 per cent. All bricks shall be uniform in quality and percentage
- of absorption.
-
- Whenever vitrified bricks are required in the invert of the sewer,
- they shall be smooth, hard, tough, and of such durability as will
- fit them for this use. They shall be of standard size, well and
- uniformly burned, thoroughly vitrified throughout, and free from
- warps, cracks, and other defects. The surfaces and edges shall be
- true and straight and the corners sharp and square. They shall be
- in every respect satisfactory to the Engineer, and in all respects
- equal to the sample in the office of the Engineer.
-
-The remaining paragraphs of the specifications deal with the manner in
-which samples shall be submitted and the necessity for conformity
-between the samples submitted and the bricks used.
-
-A common size of brick in use for sewers is 2¼ × 4 × 8¼ inches, but the
-variations in size are many. The bricks in use on any one job should be
-as near the same size as possible as the extra mortar filling necessary
-to make up for small brick detracts from the strength of the sewer.
-Small brick are undesirable as the cost of laying small and large bricks
-is the same, but the thickness of the finished sewer is less. Sewer
-brick should not absorb more than 10 to 20 per cent moisture by volume,
-in 24 hours; except the special paving brick used to prevent erosion at
-the invert which should absorb less than 5 per cent moisture.
-
-
-=97. Vitrified Sewer Block.=—Blocks and bricks are manufactured in a
-manner similar to the manufacture of vitrified sewer pipe described in
-Art. 91. J. M. Egan describes two types of sewer blocks[62] as follows:
-
- There are on the market two designs of blocks, one being a
- single-ring block and the other a double-ring block. The former
- has a ship-lap joint on the ends and a tongue-and-groove joint on
- the sides. In the double block the laps and joints are made in the
- construction of the sewer and the blocks are placed one on top of
- the other as in a two ring brick sewer. The blocks are hollow
- longitudinally with web braces. They are made for sewers from 30
- inches to 108 inches in diameter and weigh from 40 to 120 pounds.
- They are 18 inches to 24 inches long, 9 to 15 inches wide, and 5
- to 10 inches thick. Short lengths are made for convenience in
- construction and for use on sharp curves. Special blocks are made
- for connections and junctions.
-
-A special block is also made for inverts, which has occasionally been
-used with brick sewers to avoid the difficulty of constructing with
-brick at this point. Such blocks are objectionable, as they leave a line
-of weakness along the longitudinal joint so formed. They are not used
-frequently in present day practice.
-
-Vitrified blocks are generally cheaper than bricks, but they do not make
-so strong a structure. In some cases it is possible to lay vitrified
-block without the expense of high-priced bricklayers, thus saving on the
-cost of the sewer and obtaining a conduit with a smoother interior
-finish.
-
-
-=98. Cast Iron, Steel, and Wood.=—Cast iron, steel, and wood pipe belong
-more to the field of waterworks than of sewerage, as they are not
-extensively used in the construction of sewers. There are, however, some
-special conditions under which these materials may be serviceable.
-
-The iron used in cast-iron pipe for sewers, and in castings for manhole
-covers, inlet frames, etc., is seldom carefully or definitely specified.
-The standard specifications of the American Water Works Association with
-regard to the quality of iron for water pipe are:
-
- All pipe and special castings shall be made of cast iron of good
- quality and of such character as shall make the metal of the
- castings strong, tough, and of even grain and soft enough to
- satisfactorily admit of drilling and cutting. The metal shall be
- made without the admixture of cinder iron or other inferior metal,
- and shall be remelted in a cupola or air furnace.
-
-The specifications of the Sanitary District of Chicago for the quality
-of iron to be used in manhole covers, etc., are given on page 101.
-
-Although sewer pipes are not ordinarily subjected to internal pressure,
-cast-iron pipe for sewers should be as heavy or heavier than water pipe
-to resist the corrosive action of the sewage and the external stresses
-that are to be imposed upon it. The sizes and details of standard
-cast-iron pipe used for both water works and sewerage can be found in
-specification of the American and New England Water Works Associations.
-
-The quality of steel used for reinforcing concrete should be carefully
-specified because of the possibility of the substitution of inferior
-material. The specifications for “Billet Steel Concrete Reinforcement
-Bars,” of the American Society for Testing Materials[63] are the
-standard for engineering practice, or the following specifications may
-be used:
-
- All reinforcement shall be free from excessive rust, scale, paint,
- or coatings of any character which will tend to destroy the bond.
- The bars shall be rolled from new billets. No rerolled material
- will be accepted. All reinforcement bars shall develop an ultimate
- tensile strength of not less than 70,000 pounds per square inch.
- The test specimen shall bend cold around a pin, whose diameter is
- two times the thickness of the bar, 180 degrees without cracking
- on the outside portion. The reinforcing bars shall in all respects
- fulfill the requirements of the standard specifications of the
- American Society for Testing Materials for Billet Steel Concrete
- Reinforcing Bars serial designation A 15–14.
-
-The steel used in pipe should be a soft, open-hearth steel with an
-ultimate tensile strength of 60,000 pounds per square inch, an elastic
-limit of 30,000 pounds per square inch, an elongation in 8 inches before
-fracture between 22 and 25 per cent, and a reduction in area before
-fracture of 50 per cent. The working strength of the steel is taken at
-16,000 to 20,000 pounds per square inch in tension, 10,000 to 12,000
-pounds per square inch in shear, and 20,000 to 24,000 pounds per square
-inch in bearing. A liberal allowance should be made for corrosion. The
-standard specifications for Open-Hearth Boiler Plate and Rivet Steel of
-the American Society for Testing Materials, Aug. 16, 1919, include
-“flange steel,” which is suitable for the manufacture of plates, and
-extra soft steel which is suitable for rivets.
-
-Steel pipe should be coated both inside and out to protect it against
-corrosion. The various proprietary coatings are mainly coal tar pitches,
-or mixtures of coal tar pitch and asphalt. A coal tar pitch is a
-distillate of coal tar from which the naphtha has been removed and to
-which about one per cent of heavy linseed oil has been added. The
-coating is applied to the pipe at a temperature of about 300 degrees
-Fahrenheit, by dipping hot pipe in the heated coating material. The pipe
-should be carefully cleaned and all rust and scale removed before it is
-dipped. In some cases the steel is pickled before dipping. This consists
-in rolling the cold plates to a short radius to loosen the scale,
-heating them to about 125 degrees, and dipping them in a warm 5 per cent
-acid solution for about 3 minutes, and finally rinsing in a weakly basic
-wash water.
-
-The woods commonly used for the manufacture of wood pipe are spruce,
-Oregon fir, Douglas fir, and California redwood. Wood pipe lines have
-been constructed of other kinds of lumber but only in more or less
-unusual conditions. The following has been abstracted from the
-specifications for California redwood given by J. F. Partridge.[64]
-
- The staves shall be of clear, air-dried, California redwood,
- seasoned at least one year in the open air, and shall be free from
- knots (except small knots appearing on one face only), sap, dry
- rot, wind shakes, pitch, pitch seams, pitch pockets, or other
- defects which would materially impair their strength or
- durability. The sides of the staves shall be milled to conform to
- the inside and outside radii of the pipe; and the edges shall be
- beveled to true radial planes. The staves shall be milled from
- stock sizes of lumber, the net finished thickness of the stave,
- for the various diameters of pipe, shall be as given in Table 40.
- The ends shall be cut square and slotted to receive the metallic
- tongues which form the butt joints. The slots shall appear in the
- same position on each stave, and shall be cut to make a tight fit
- with the tongues in all directions. The staves shall have an
- average length of at least 15 ft. 6 in. and not more than one per
- cent shall have a length of less than 9 ft. 6 in. Staves shorter
- than 8 ft. will not be accepted.
-
- The bands shall be spaced on the pipe with a factor of safety of
- at least four, and shall consist of round, mild steel rods,
- connected with malleable iron shoes. Either open-hearth or
- Bessemer steel may be used.... The ultimate strength shall be from
- 55,000 to 65,000 lb. per sq. in.
-
-The original reference should be consulted for complete details and for
-specifications for various kinds of wood and classes of pipe. The
-discussion following the specifications is of value.
-
-Machine-made wood pipe is superior to stave pipe put together in the
-field. It is seldom manufactured in sizes large enough for use in
-sewers, which results in the almost exclusive use of field constructed
-stave pipe. The steel bands used to hold the staves together should be
-coated similarly to steel plates. All lumber, except California redwood
-should receive a preservative coating of creosote[65] or other material.
-One of the best methods of preserving the wood is to keep it submerged
-and to maintain the pipe under internal pressure.
-
- TABLE 40
-
- DETAILS OF DESIGN FOR CONTINUOUS STAVE WOOD PIPE
-
- CLASSES A, B, AND C
-
- (By J. F. Partridge, Trans. A. S. C. E., Vol. 82, page 461)
- ───────────┬───────────┬───────────┬───────────┬───────────┬───────────
- │ Stave │Stock Size │ Size of │ Top Width │Spacing of
- │Thickness, │of Lumber, │ Band, │of Staves, │ Bands for
- Diameter, │ Standard, │ Inches │ Inches │ Standard, │ 100 Feet
- Inches │ Inches │ │ │ Inches │ Head
- ───────────┼───────────┼───────────┼───────────┼───────────┼───────────
- 12│ 1⅜ │ 2 × 4 │ ⅜ │ 3.56 │ 6.38
- 18│ 1–7/16 │ 2 × 4 │ 7/16 │ 3.66 │ 5.76
- 24│ 1–7/16 │ 2 × 4 │ 7/16 │ 3.70 │ 4.34
- 30│ 1½ │ 2 × 6 │ ½ │ 5.48 │ 4.53
- 36│ 1–9/16 │ 2 × 6 │ ½ │ 5.62 │ 3.77
- 42│ 1⅝ │ 2 × 6 │ ½ │ 5.51 │ 3.23
- │ 1⅝ │ 2 × 6 │ ½ or ⅝ │ 5.60 │ 2.84 or
- 48│ │ │ │ │ 4.41
- 60│ 2½ │ 3 × 6 │ ⅝ │ 5.56 │ 3.54
- │ 3½ │ 4 × 6 │ ⅝ or ¾ │ 5.69 │ 2.95 or
- 72│ │ │ │ │ 4.24
- 84│ 3½ │ 4 × 6 │ ¾ │ 5.65 │ 3.63
- 120│ 3⅝ │ 4 × 6 │ ¾ │ 5.68 │ 2.54
- │ 3⅝ │ 4 × 6 │ ¾ or ⅞ │ 5.64 │ 2.12 or
- 144│ │ │ │ │ 2.89
- ───────────┴───────────┴───────────┴───────────┴───────────┴───────────
-
-
-
-
- CHAPTER IX
- DESIGN OF THE SEWER RING
-
-
-=99. Stresses in Buried Pipe.=—The stresses which sewer pipe should be
-designed to resist are: internal bursting pressure, for sewers flowing
-under pressure; stresses due to handling, for precast pipe; temperature
-stresses; and external loads. The latter is by far the most important
-and frequently is the only stress considered in design.
-
-The thickness of a pipe to resist internal stress should be
-
- (_PR_)⁄_f__{_t_},
-
- in which _P_ = the intensity of internal pressure;
-
- _R_ = the radius of the inside of the pipe, and
-
- _f__{_t_} = the unit-strength of the material in tension
-
-The derivation of this expression is simple. The stresses due to
-handling cannot be computed and are cared for by a thickness of material
-dictated by experience. These thicknesses are given for vitrified clay
-and cement pipe in the specifications in the preceding chapter.
-Temperature stresses are not allowed for in the design of the pipe ring,
-but allowance must be made for them in long rigid pipe lines exposed to
-wide variations in temperature. Such a condition seldom exists in
-sewerage works.
-
-The external forces are ordinarily the controlling features in the
-design of sewer rings. The simplest problems arise in the design of a
-circular pipe. If the external loading is uniform about the
-circumference of the pipe the internal stresses will all be compression.
-Almost all other forms of loading will cause bending moments resulting
-in tension and compression in different parts of the pipe. The maximum
-bending is caused by two concentrated loads diametrically opposed. As
-such a condition is extreme it is not cared for in ordinary design, but
-a loading between this condition and perfect distribution is assumed, as
-explained in Art. 103.
-
-
-=100. Design of Steel Pipe.=—The stresses which may occur in steel sewer
-pipes are commonly caused by the internal or bursting pressure of the
-contained liquid. Occasionally a steel pipe may be used as a bridge or
-as a stressed member of a bridge, but steel pipes should not be used to
-withstand compression normal to the axis. In order to avoid such
-stresses the bursting tensile stresses should exceed the external
-compressive stresses. Such a condition in design requires that buried
-pipes shall never be emptied, a condition that cannot always be
-fulfilled. Precaution should be taken, by the installation of proper
-valves, to prevent the emptying of the pipe at so rapid a rate that a
-vacuum is created resulting in the collapse of the pipe.
-
-Steel pipes are ordinarily made of plates curved to the proper diameter,
-the edges being held together by rivets. The design of the pipe consists
-in the determination of the thickness of the plate and the design of the
-riveted joint. The longitudinal joint and the thickness of the plate are
-first designed. The design of the joint consists in determining the
-diameter and pitch of the rivets and the thickness of the plate so that
-the full strength of the uncut metal shall be developed as nearly as
-possible under bearing, tearing, and shearing. This is done by making
-the efficiency of the joint the same under all stresses. The efficiency
-of the joint is the ratio of the strength of the joint under any kind of
-stress to the strength in tension of the unpunched plate. Properties of
-riveted joints are given in Table 41.
-
-The diameter of the rivet holes should be computed as 1/16 of an inch
-larger than the diameter of the rivets. Rivets and plates should be
-designed for the nearest or next largest commercial size, and a generous
-allowance for corrosion should be made in determining the thickness of
-the plate. The distance from the edge of the plate to the side of the
-rivet should not be less than 1½ times the diameter of the rivet. The
-unit-strengths of the metal are given in the preceding chapter.
-
-The transverse joint must be designed empirically as the stresses in it
-are indeterminate. The common form of joint for pipes less than 48
-inches in diameter is a single-riveted lap joint, and for larger pipes
-or for pipes exposed to unusual stresses, a double riveted lap joint is
-used. The same size rivets are used as in the longitudinal joint. The
-maximum permissible distance between rivets should be used in the
-transverse joint.
-
- TABLE 41
-
- PROPERTIES OF RIVETED JOINTS
-
- (Chicago Bridge and Iron Works)
- ──────────────────────┬─────────┬────────┬────────┬──────────┬─────────
- Type of Joint │Thickness│Diameter│ Pitch, │Efficiency│Thickness
- │ Plate, │ of │ Inches │of Joint, │ Butt
- │ Inch │ Rivet, │ │ Per Cent │ Plate,
- │ │ Inch │ │ │ Inches
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Single-riveted lap │ ¼ │ ⅝ │ 1.88 │ 49 │
- │ ¼ │ ¾ │ 2.25 │ 50 │
- │ 5/16 │ ⅞ │ 2.63 │ 50 │
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Double riveted lap │ ¼ │ ⅝ │ 2.50 │ 70 │
- │ 5/16 │ ¾ │ 3.00 │ 71 │
- │ ⅜ │ ⅞ │ 3.40 │ 71 │
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Triple riveted lap │ ¼ │ ½ │ 2.39 │ 74 │
- │ 5/16 │ ⅝ │ 2.96 │ 74 │
- │ ⅜ │ ¾ │ 3.53 │ 75 │
- │ 7/16 │ ⅞ │ 4.09 │ 76 │
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Quadruple riveted lap │ ⅜ │ ⅝ │ 3.20 │ 77 │
- │ 7/16 │ ¾ │ 3.90 │ 78 │
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Double riveted butt │ ½ │ ⅞ │ 3.62 │ 72 │ ⅜
- │ 9/16 │ ⅞ │ 3.62 │ 72 │ ⅜
- │ ⅝ │ ⅞ │ 3.62 │ 72 │ ⅜
- │ 11/16 │ ⅞ │ 3.62 │ 72 │ 7/16
- │ ¾ │ 1 │ 4.12 │ 73 │ 7/16
- │ ⅞ │ 1 │ 3.82 │ 71 │ ½
- │ 1 │ 1 │ 3.48 │ 68 │ 9/16
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Triple riveted butt │ ⅝ │ ⅞ │ 4.94 │ 80 │ ½
- │ ¾ │ 1 │ 5.62 │ 80 │ 9/16
- │ ⅞ │ 1 │ 5.16 │ 78 │ 9/16
- │ 1 │ 1 │ 4.66 │ 76 │ 9/16
- ──────────────────────┼─────────┼────────┼────────┼──────────┼─────────
- Quadruple riveted butt│ ¾ │ 1 │ 7.13 │ 84 │ ¾
- │ ⅞ │ 1 │ 6.51 │ 83 │ 11/16
- │ 1 │ 1 │ 5.84 │ 81 │ ⅝
- ──────────────────────┴─────────┴────────┴────────┴──────────┴─────────
-
-Pipes used as compression members of a bridge are stiffened by riveting
-standard rolled steel sections longitudinally on the pipe.
-
-[Illustration:
-
- FIG. 78.—Lock Bar Pipe.
-]
-
-Lock Bar Pipe is a steel pipe with a special form of joint made by the
-East Jersey Pipe Corporation. It is arranged as shown in Fig. 78 and has
-the advantage of developing the full strength of the plate. It is
-equivalent to a joint with 100 per cent efficiency, which permits the
-use of thinner plates.
-
-
-=101. Design of Wood Stave Pipe.=—In the design of wood stave pipe[66]
-the entire bursting pressure is taken up by steel bands wrapped around
-the outside of wood staves which make up the shell of the pipe. The pipe
-is not designed to resist external loads except those which may be
-overcome by the internal pressure in the pipe. The thickness of the
-staves is fixed by experience. The sizes of staves and bands recommended
-by J. F. Partridge[67] are given in Table 40. The size of the steel
-bands can be determined from the expression;
-
- _S_ = _Cr_(_R_ + _t_)
-
- in which _S_ = the total stress in the band;
-
- _R_ = the radius of the inside of the pipe;
-
- _t_ = the thickness of the stave;
-
- _r_ = the area of bearing per unit length of the band on the
- wood. For circular bands it is assumed as the radius
- of the band;
-
- _C_ = the crushing strength of wood, usually taken at 650
- pounds per sq. in.
-
-The preceding expression can be derived easily by the application of the
-laws of mechanics, and from it the expression for the distance between
-bands follows logically. It is,
-
- _p_ = _S_⁄(_PR_ + _kt_)
-
- in which _S_ = the strength of the band;
-
- _p_ = the distance between bands;
-
- _P_ = the intensity of bursting pressure in the pipe;
-
- _R_ = the radius of the inside of the pipe;
-
- _t_ = the thickness of the staves;
-
- _k_ = the swelling strength of wood, usually taken at 100
- pounds per sq. in.
-
-[Illustration:
-
- FIG. 79.—Shoe for Wood Stave Pipe.
-]
-
-Transverse joints between staves are closed by inserting metal strips
-between them, or by shaping the edges irregularly so that they fit
-closely together with an irregular joint. Transverse joints between all
-staves at any one point are avoided by splitting the joints between
-staves. Longitudinal joints between staves are usually made smooth and
-are closed by steel bands which are drawn tight about the pipe by
-inserting the ends in coupling shoes as shown in Fig. 79.
-
-[Illustration:
-
- FIG. 80.—_B_ in Formula _W_ = _CwB_^2
-]
-
-
-=102. External Loads on Buried Pipe.=—Prof. Anston Marston and H. C.
-Anderson published[68] the results of a series of experiments on the
-loads on buried pipes which are of extreme value in the design of sewer
-pipe. The load on the pipe is given by the empirical expression _W_ =
-_CwB_^2, in which _w_ is the weight of the backfilling material in
-pounds per cubic foot, _B_ is the width of the trench in feet at the
-elevation of the end of a radius making an angle of 45 degrees upwards
-with the horizontal diameter of the pipe as illustrated in Fig. 80, and
-_C_ is a coefficient dependent on the character of the backfill and the
-ratio of the width to the depth of the trench. Values of _C_ are given
-in Table 42. The weights of various classes of backfilling are given in
-Table 43.
-
- TABLE 42
-
- APPROXIMATE SAFE WORKING VALUES OF _C_ IN THE EXPRESSION _W_ = _CwB_^2
-
- From Bulletin No. 31 of the Engineering Experiment Station, Iowa State
- College of Agriculture.
- ──────────────┬────────────────────────────────────────────────────────
- Ratio of Depth│ Approximate Values of _C_
- to Width │
- ──────────────┼──────────────┬─────────────┬─────────────┬─────────────
- │Damp Top Soil │Saturated Top│ Damp Yellow │ Saturated
- │ and Dry and │ Soil │ Clay │ Yellow Clay
- │ Wet Sand │ │ │
- ──────────────┼──────────────┼─────────────┼─────────────┼─────────────
- 0.5 │ 0.46 │ 0.47 │ 0.47 │ 0.48
- 1.0 │ 0.35 │ 0.86 │ 0.88 │ 0.90
- 1.6 │ 1.16 │ 1.21 │ 1.25 │ 1.27
- 3.0 │ 1.47 │ 1.51 │ 1.56 │ 1.62
- 2.6 │ 1.70 │ 1.77 │ 1.83 │ 1.91
- 3.0 │ 1.90 │ 1.99 │ 2.08 │ 2.19
- 3.6 │ 2.08 │ 2.18 │ 2.28 │ 2.43
- 4.0 │ 2.22 │ 2.35 │ 2.47 │ 2.65
- 4.6 │ 2.34 │ 2.49 │ 2.63 │ 2.85
- 6.0 │ 2.45 │ 2.61 │ 2.78 │ 3.02
- 6.5 │ 2.54 │ 2.72 │ 2.90 │ 3.18
- 6.0 │ 2.61 │ 2.81 │ 3.01 │ 3.32
- 6.6 │ 2.68 │ 2.89 │ 3.11 │ 3.44
- 7.0 │ 2.73 │ 2.95 │ 3.19 │ 3.55
- 7.5 │ 2.78 │ 3.01 │ 3.27 │ 3.66
- 8.0 │ 2.82 │ 3.06 │ 3.33 │ 3.74
- 8.5 │ 2.85 │ 3.10 │ 3.39 │ 3.82
- 9.0 │ 2.88 │ 3.14 │ 3.44 │ 3.89
- 9.5 │ 2.90 │ 3.18 │ 3.48 │ 3.96
- 10.0 │ 2.92 │ 3.20 │ 3.52 │ 4.01
- 11.0 │ 2.95 │ 3.25 │ 3.58 │ 4.11
- 12.0 │ 2.97 │ 3.28 │ 3.63 │ 4.19
- 13.0 │ 2.99 │ 3.31 │ 3.67 │ 4.25
- 14.0 │ 3.00 │ 3.33 │ 3.70 │ 4.30
- 15.0 │ 3.01 │ 3.34 │ 3.72 │ 4.34
- ∞ │ 3.03 │ 3.38 │ 3.79 │ 4.50
- ──────────────┴──────────────┴─────────────┴─────────────┴─────────────
-
- TABLE 43
-
- APPROXIMATE WEIGHTS OF DITCH FILLING MATERIAL TO BE USED IN THE
- EXPRESSION _W_ = _CwB_^2[69]
-
- ───────────────────────────────────┬───────────────────────────────────
- Ditch Filling │ Pounds per Cubic Foot
- ───────────────────────────────────┼───────────────────────────────────
- Partly compacted top soil (damp) │ 90
- Saturated top soil │ 110
- Partly compacted damp yellow clay │ 100
- Saturated yellow clay │ 130
- Dry sand │ 100
- Wet sand │ 120
- ───────────────────────────────────┴───────────────────────────────────
-
-Where surface loads are to be carried on the sewer trench the proper
-proportion of the load to be carried by the sewer is determined by the
-expression _L__{_p_} = _CL_, in which _L__{_p_} is the equivalent
-backfill load per unit length of the trench, _L_ is the surface load per
-unit length of the trench, and _C_ is a coefficient in which allowance
-is made for the character of the backfilling, the ratio of depth to
-width of trench, and the character of the load, whether long or short. A
-long load is a load extending along the length of the trench such as a
-pile of building material. A short load is one extending across the
-trench and for only a short distance along it, such as that caused by a
-street car or road roller crossing the trench. Values of _C_ are given
-in Table 44 for long loads, and in Table 45 for short loads. Values of
-long and short loads occasionally met in practice are given in Tables 46
-and 47 respectively.
-
- TABLE 44
-
- RATIO OF LOAD ON PIPE TO LONG LOAD ON TRENCH[70]
-
- ──────────────┬──────────────┬──────────────┬──────────────┬──────────────
- Ratio of Depth│Sand and Damp │Saturated Top │ Damp Yellow │ Saturated
- to Width │ Top Soil │ Soil │ Clay │ Yellow Clay
- ──────────────┼──────────────┼──────────────┼──────────────┼──────────────
- 0.0│ 1.00│ 1.00│ 1.00│ 1.00
- 0.5│ 0.85│ 0.86│ 0.88│ 0.89
- 1.0│ 0.72│ 0.75│ 0.77│ 0.80
- 1.5│ 0.61│ 0.64│ 0.67│ 0.72
- 2.0│ 0.52│ 0.53│ 0.59│ 0.64
- 2.5│ 0.44│ 0.48│ 0.52│ 0.57
- 3.0│ 0.37│ 0.41│ 0.45│ 0.51
- 4.0│ 0.27│ 0.31│ 0.35│ 0.41
- 5.0│ 0.19│ 0.23│ 0.27│ 0.33
- 6.0│ 0.14│ 0.17│ 0.20│ 0.26
- 8.0│ 0.07│ 0.09│ 0.12│ 0.17
- 10.0│ 0.04│ 0.05│ 0.07│ 0.11
- ──────────────┴──────────────┴──────────────┴──────────────┴──────────────
-
- For example, let it be desired to determine the load on a 72–inch
- concrete sewer with a 9–inch shell under the following conditions:
- depth of backfill over the top of the pipe, 15 feet; character of
- backfill, saturated yellow clay; superimposed load, pile of
- building brick 6 feet high. The ratio of the depth of backfill to
- the width of the trench is 15 ÷ 9 or 1.67. The coefficient in the
- expression _CwB_^2 is 1.39, from Table 42. The weight of saturated
- yellow clay is 130 pounds per cubic foot, from Table 43. Therefore
- the load per foot length of the sewer due to the backfill is:
-
- _W_ = _CwB_^2 = 1.39 × 130 × 81 = 14,600 pounds.
-
- TABLE 45
-
- RATIO OF LOAD ON PIPE TO SHORT LOAD ON TRENCH[71]
-
- ───────┬───────────────┬───────────────┬───────────────┬───────────────
- Ratio │ │ │ │
- of │ │ │ │
- Height │ │ │ │
- to │ │ │ │
- Width │ │ │ │
- of │ Sand and Damp │ Saturated Top │ Damp Yellow │ Saturated
- Trench │ Top Soil │ Soil │ Clay │ Yellow Clay
- ───────┼───────────────┴───────────────┴───────────────┴───────────────
- │ Length of Load Equal to
- ───────┼───────┬───────┬───────┬───────┬───────┬───────┬───────┬───────
- │ Width │⅒ Width│ Width │⅒ Width│ Width │⅒ Width│ Width │⅒ Width
- │ of │ of │ of │ of │ of │ of │ of │ of
- │Trench │Trench │Trench │Trench │Trench │Trench │Trench │Trench
- ───────┼───────┼───────┼───────┼───────┼───────┼───────┼───────┼───────
- 0.0│ 1.00│ 1.00│ 1.00│ 1.00│ 1.00│ 1.00│ 1.00│ 1.00
- 0.5│ 0.77│ 0.12│ 0.78│ 0.13│ 0.79│ 0.13│ 0.81│ 0.13
- 1.0│ 0.59│ 0.02│ 0.61│ 0.02│ 0.63│ 0.02│ 0.66│ 0.02
- 1.5│ 0.46│ │ 0.48│ │ 0.51│ │ 0.54│
- 2.0│ 0.35│ │ 0.38│ │ 0.40│ │ 0.44│
- 2.5│ 0.27│ │ 0.29│ │ 0.32│ │ 0.35│
- 3.0│ 0.21│ │ 0.23│ │ 0.25│ │ 0.29│
- 4.0│ 0 12│ │ 0.12│ │ 0.16│ │ 0.19│
- 5.0│ 0.07│ │ 0.09│ │ 0.10│ │ 0.13│
- 6.0│ 0.04│ │ 0.05│ │ 0.06│ │ 0.08│
- 8.0│ 0.02│ │ 0.02│ │ 0.03│ │ 0.04│
- 10.0│ 0.01│ │ 0.01│ │ 0.01│ │ 0.02│
- ───────┴───────┴───────┴───────┴───────┴───────┴───────┴───────┴───────
-
- TABLE 46
-
- WEIGHTS OR COMMON BUILDING MATERIAL WHEN PILED FOR STORAGE. POUNDS PER
- CUBIC FOOT
-
- ────────────────────────────────────────┬──────────────────────────────
- Brick │ 120
- Cement │ 90
- Sand │ 90
- Broken stone │ 150
- Lumber │ 35
- Granite paving │ 160
- Coal │ 50
- Pig iron │ 400
- ────────────────────────────────────────┴──────────────────────────────
-
- The pressure of the pile of brick per square foot of trench area
- is, from Table 46, 120 × 6 = 720 pounds per square foot. The value
- of _C_ from Table 44, is about 0.70. Therefore _L_{p}_ is 0.7 × 9
- × 720 = 4536 pounds. The equivalent depth of backfill weighing 130
- pounds per cubic foot is (4536)⁄130 × 9 = 3.88 foot. The total
- equivalent depth of backfill is therefore 3.88 + 15 = 18.88 feet.
- The ratio of depth to width is 18.88⁄9 = 2.98. The coefficient _C_
- in the expression _W_ = _CwB_^2 is 2.17. The total load per foot
- length of sewer is therefore _W_ = 2.17 × 130 × 81 = 22,800
- pounds.
-
- TABLE 47
-
- WEIGHTS OF SHORT LOADS ON SEWER TRENCHES
-
- (Adapted from Specifications of the American Bridge Company for
- Bridges)
- ──────────────────────────────┬────────────────────────────────────────
- Street railways, heavy │A load of 24 tons on 2 axles on 10 foot
- │ centers.
- Street railways, light │A load of 18 tons on 2 axles on 10 foot
- │ centers.
- For city streets, heavy │A load of 24 tons on 2 axles 10 feet
- traffic │ apart and 5 foot gage.
- For city streets, moderate │A load of 12 tons on 2 axles 10 feet
- traffic │ apart and 5 foot gage.
- For city streets, light │A load of 6 tons on 2 axles 10 feet
- traffic or country roads │ apart and 5 foot gage.
- │
- Road rollers │Total weight 30,000 pounds. Weight on
- │ front wheel, 12,000 pounds, and on
- │ each of two rear wheels, 9,000 pounds.
- │ Width of front wheel, 4 feet and of
- │ each of two rear wheels 20 inches.
- │ Distance between front and rear axles
- │ 11 feet. Gage of rear wheels, 5 feet,
- │ c. to c.
- ──────────────────────────────┴────────────────────────────────────────
-
-
-=103. Stresses in Circular Ring=—In Fig. 81_a_ the loads shown indicate
-the distribution ordinarily assumed in sewer design, the forces being
-uniformly distributed across the diameter. To find the bending moment in
-the pipe caused by this loading, let _ab_ in Fig. 81_b_ represent a
-section of a pipe loaded with equally distributed horizontal and
-vertical forces. Then the vertical component on a strip of differential
-length _ds_ is _wds_ cos Θ and the horizontal component is _wds_ sin Θ
-and resolving, the resultant normal to the surface is _wds_, in which
-_w_ is the intensity per unit length of the horizontal and vertical
-forces and Θ is the angle which the tangent to _ds_ makes with the
-horizontal. Thus the loading of the nature shown in Fig. 81_b_ is
-equivalent to a loading of equally distributed normal forces which give
-no moment in the ring.
-
-[Illustration:
-
- FIG. 81.—Distribution of Stresses on Buried Pipe.
-]
-
-Considering a ring subjected to vertical forces only, the moments will
-be as shown in Fig. 81_c_ and if loaded with horizontal forces only, the
-moments will be as shown in Fig. 81_d_. Because of the symmetry of the
-figure, moment (1) equals moment (4) but is opposite in direction and
-moment (2) equals moment (3) but is opposite in direction. When the
-horizontal and vertical forces are combined on the same ring as in Fig.
-81_b_ these moments cancel each other as has been proven. Therefore
-moment (1) equals moment (2) and moment (3) equals moment (4). Then in
-Fig. 81_e_, _M_{a}_ = _M_{b}_. Now ∑_M_ = _O_ for conditions of
-equilibrium, therefore _M_{a}_ + _M_{b}_ + (_W_⁄2)(_d_⁄4) = _O_ and
-solving _M_{a}_ = (_Wd_)⁄16. This moment occurs at the ends of the
-horizontal and vertical diameters and causes tension on the inside of
-the pipe at the top and on the outside at the ends of the horizontal
-diameter. There will also be compression at each end of the horizontal
-diameter equal to one-half of the total load on the pipe. If the
-material of the pipe is homogeneous, the maximum fiber stress _f_ can be
-found through the expression _f_ = (_My_)⁄_I_ ± _P_⁄_A_ in which _M_ is
-the bending moment, _y_ is the distance from the neutral axis to the
-extreme fiber of a cross-section of the shell of the pipe of unit
-length, _I_ is the moment of inertia of this cross-section about its
-neutral axis, _P_ is one-half the total load on the pipe, and _A_ is the
-area of the cross-section. For reinforced concrete, the standard
-formulas should be used with this expression for _M_. The stresses in a
-circular ring subjected to other distributions of loads are shown in
-Table 48. An exhaustive study of the stresses in circular rings was
-published by Prof. A. N. Talbot in Bulletin No. 22 of the Engineering
-Experiment Station at the University of Illinois, 1908.
-
- TABLE 48
-
- MAXIMUM STRESS IN FLEXIBLE RINGS DUE TO DIFFERENT LOADINGS
-
- (From Marston)
- ──────────────────┬───────────────┬───────────────┬───────────
- Symmetrical │Moment at Crown│ Moment at End │Compressive
- Vertical Loadings │ of Sewer │ of Horizontal │ Thrust at
- │ │ Diameter │ Crown
- │ │ │
- │ │ │
- ────────────┬─────┼───────────────┼───────────────┼───────────
- Character │Width│ │ │
- ────────────┼─────┼───────────────┼───────────────┼───────────
- Concentrated│ 0°│+ .318_R__W_/12│- .182_R__W_/12│ 0.000
- Uniform │ 60°│+ .207_R__W_/12│- .168_R__W_/12│ 0.000
- Uniform │ 90°│+ .169_R__W_/12│- .154_R__W_/12│ 0.000
- Uniform │ 180°│+ .125_R__W_/12│- .125_R__W_/12│ 0.000
- ────────────┴─────┴───────────────┴───────────────┴───────────
-
- ──────────────────┬────────────┬───────────┬──────────
- Symmetrical │Compressive │ Shear at │ Shear at
- Vertical Loadings │ Thrust at │ Crown │ End of
- │ End of │ │Horizontal
- │ Horizontal │ │ Diameter
- │ Diameter │ │
- ────────────┬─────┼────────────┼───────────┼──────────
- Character │Width│ │ │
- ────────────┼─────┼────────────┼───────────┼──────────
- Concentrated│ 0°│+ .500_W_/12│0.500_W_/12│ 0.000
- Uniform │ 60°│+ .500_W_/12│0.000_W_/12│ 0.000
- Uniform │ 90°│+ .500_W_/12│0.000_W_/12│ 0.000
- Uniform │ 180°│+ .500_W_/12│0.000_W_/12│ 0.000
- ────────────┴─────┴────────────┴───────────┴──────────
-
- _R_ = the radius of the pipe, _W_ = total weight of ditch filling and
- superimposed load plus ⅝ of the weight of the pipe itself (usually
- neglected), expressed in pounds per foot length of pipe. Moments are
- inch-pounds per inch length of pipe. Shears and thrusts are in pounds
- per inch length of pipe.
-
-
-=104. Analysis of Sewer Arches.=—The preceding method for the
-determination of the stresses in a sewer ring has referred only to a
-circular pipe uniformly loaded. Other methods must be used if the pipe
-is not circular or the load is not uniformly distributed. The simplest
-method, is the static or so-called vouissoir method. In this method the
-arch is assumed to be fixed at both ends, presumably at the springing
-line or line of intersection between the inside face of the arch and the
-abutment, and it is so designed that the resultant of all the forces
-acting on any section shall lie within the middle third of that section.
-
-[Illustration:
-
- FIG. 82.—Voussoir Arch Analysis.
-]
-
-[Illustration:
-
- FIG. 83.—Force Polygon for Voussoir Arch Analysis.
-]
-
-To design an unreinforced sewer arch by the vouissoir method, a desired
-arch is drawn to scale in apparently good proportions for the loadings
-anticipated. The arch is then divided into any number of sections of
-equal or approximately equal length called vouissoirs, and the line of
-action of the resultant load, including the weight of the vouissoir is
-drawn above each vouissoir as shown in Fig. 82. The forces are assumed
-to act as shown in the figure. In symmetrically loaded sewer arches
-there is no vertical reaction at the crown. The resultant _R_ is assumed
-to act at the lower middle third of the skewback, which is the inclined
-joint between the arch and the abutment. The upper horizontal force _H_
-is assumed to act at the upper middle third of the middle or crown
-section. The magnitude of _H_ is computed by equating the sum of the
-moments of all forces about the point of application of _R_ at the
-skewback to zero, and solving. The force polygon is then drawn as shown
-in Fig. 83, and the equilibrium polygon is completed in Fig. 82 with its
-rays parallel to the corresponding strings drawn from the end of _H_ as
-origin in Fig. 83. If the equilibrium polygon line, called the
-resistance line, lies wholly within the middle third of each vouissoir,
-the arch is satisfactory to support the assumed load without
-reinforcement. If any portion of the resistance line lies outside of the
-middle third, an attempt should be made to find a resistance line which
-lies wholly within the middle third. The true resistance line is that
-which deviates the least from the neutral axis of the arch. To
-approximate more nearly the true resistance line find two points at
-which the resistance line already drawn deviates the most from the
-neutral axis of the arch. Select points _M_ and _N_ on these joints, _M_
-being nearer the crown than _N_. Then let _W_{1}_ and _W_{2}_ be the sum
-of all the loads between the crown and _M_ and _N_ respectively, _y_
-represent the vertical distance from the crown to _N_, and _y′_
-represent the vertical distance between _M_ and _N_, and _x_{1}_ and
-_x_{2}_ represent the horizontal distance from _W_{1}_ and _W_{2}_ to
-_M_ and _N_ respectively. Then the horizontal thrust, _H_, and _a_, the
-distance from the crown to the point of application of _H_, are,
-
- _H_ = ((_W_{2}x_{2}_ − _W_{1}x_{1})_)⁄_y′_,
-
- _a_ = _y_ − (_W_{2}x_{2}_)⁄_H_.[72]
-
-A resistance line should be drawn with this new horizontal thrust. If no
-resistance line can be found lying wholly within the middle third, new
-sections should be designed until a resistance line can be drawn lying
-wholly within the middle third—unless the arch is to be reinforced. A
-number of satisfactory arches should be designed and the easiest one to
-build should be selected. This method is limited in its application to
-sewer arches with rigid side walls and it cannot be extended to include
-the invert. Although an approximate method it is accurate within less
-than 10 per cent of the true stresses and is usually quite close.
-
-[Illustration:
-
- FIG. 84.—Method for Dividing Arch into Proportion _I_⁄_S_.
-]
-
-The elastic method for the design of arches locates the true line of
-resistance without approximations and is more accurate though not so
-simple to apply as the static or vouissoir method. In this method a
-desired form of arch is drawn as in the static method and subdivided
-into vouissoirs so that the distance _S_ along the neutral axis between
-joints is such that the ratio _I_⁄_S_ shall be the same for all
-vouissoirs. _I_ is the average of the moments of inertia of the surfaces
-of the two limiting joints about the neutral axis. If the thickness of
-the arch is constant the distance between joints will be the same. The
-method for dividing the arch into sections such that the ratio _I_⁄_S_
-shall be a constant[73] is as follows: divide the half arch axis into
-any number of equal parts; measure the radial depth at each point of
-division; lay off the length of the arch axis to scale on a straight
-line; divide this line into the same number of equal parts as the half
-arch, as shown in Fig. 84; at each point erect a perpendicular equal in
-length by scale to the moment of inertia at the corresponding point on
-the arch section; draw a smooth curve through the tops of these lines;
-draw a line _ab_ at any slope from the center of the original straight
-line to the curve, and then a line _bc_ back to the straight line to
-form an isosceles triangle _abc_; continue forming these triangles in a
-similar manner thus dividing the original straight line in the required
-ratio. The distance between joints is represented by the bases of the
-triangles. By construction the altitude of the triangle represents the
-average moment of inertia between the two limiting joints. The base of
-each isosceles triangle is _S_, and _I_⁄_S_ = ½ tan α in which α is the
-base angle of all the isosceles triangles.
-
-[Illustration:
-
- FIG. 85.—Elastic Arch Analysis.
-]
-
-The following steps in the procedure are taken from the second edition
-of the American Civil Engineers Pocket Book, p. 634:
-
- In Fig. 85 let the middle points of the joints be marked 1, 2, 3,
- etc. and the coordinates _x_ and _y_ from the crown be found for
- each by computation or measurement. For a load _W_ placed at one
- of these points, let _z_ denote the distance from it, toward the
- nearest skewback, to another middle point. Let ∑_zx_ be the sum of
- the products of all the values of _z_ by the corresponding _x_,
- and ∑_zy_ be the sum of all the products of _z_ by the
- corresponding _y_; that is, each _z_ in the last two summations is
- multiplied by the _x_ or _y_ of the point back of _W_ which
- corresponds to _z_.
-
- For a single load _W_ on the left semi-arch of Fig. 85 the
- following formulas are deduced from the elastic theory, _n_ being
- the number of parts into which the semi-arch is divided.
-
- Horizontal thrust, _H_ = (_W_⁄2)(_n_∑_zy_ − ∑_y_·∑_z_)⁄(_n_∑_y_^2
- − (∑_y_)^2) (1)
-
- Moment at Crown, _M__{0} = (½_W_∑_z_ − _H_∑_y_)⁄_n_ (2)
-
- Shear at Crown, _V__{0} = (½_W_∑_zx_)⁄∑_x_^2 (3)
-
- For symmetrical loading such as _W_ on the left and _W_ on the
- right the horizontal thrust and crown moment due to both loads are
- double those found by the above formulas, while the crown shear
- _V__{0} is zero. For several loads unsymmetrically placed the
- formulas are to be applied to each in succession and the results
- added algebraically, the value of _V__{0} being taken as negative
- for the left semi-arch and positive for the right semi-arch.
-
- For any joint whose middle point is at a distance _x_ from the
- crown
-
- _M_ = _M__{0} + _Hy_ + _V__{0}_x_ − ∑_Wz_,
-
- _V_ = _V__{0} − ∑_W_,
-
- where ∑_W_ is the sum of all the loads between the joint and the
- crown and ∑_Wz_ is the sum of the moments of those loads with
- respect to the middle of the joint. The components of the
- resultant thrust normal and parallel to the joints are,
-
- _N_ = _H_ cos θ − _V_ sin θ,
-
- _F_ = _H_ sin θ + _V_ cos θ,
-
- in which θ is the angle which the plane of the joint makes with
- the vertical.
-
- The distances from the neutral axis to the resistance line are,
-
- at the crown, _e__{0} = _M__{0}⁄_H_,
-
- at the joint, _e_ = _M_⁄_N_.
-
-The resistance line should be located as in the vouissoir method and if
-not within the middle third a new design should be studied.
-
-
-=105. Reinforced Concrete Sewer Design.=—The method to be followed in
-the design of reinforced concrete arches is similar except that the
-moment of inertia should include both the concrete and the steel, that
-is,
-
- _I_ = _I_{c}_ + _nI_{s}_,
-
-in which _I_ is the moment of inertia to be employed, _I_{c}_ is the
-moment of inertia of the concrete, _I_{s}_ is the moment of inertia of
-the steel, and _n_ is the ratio of their moduli of elasticity, generally
-taken as 15. All of the moments of inertia are referred to the neutral
-axis of the beam. The reinforcement called for in precast circular pipes
-is given in Table 39. Sewers cast in place are ordinarily designed to
-avoid reinforcement, except where the depth of cover is small and the
-sewer may be subjected to superimposed loads.
-
-Concrete sewers are sometimes reinforced longitudinally, with expansion
-joints from 30 to 50 feet apart. This reinforcement is to reduce the
-size of expansion and contraction cracks by distributing them over the
-length of a section. The pipe is divided into sections to concentrate
-motion due to expansion or contraction at definite points where it can
-be cared for.
-
-The amount of longitudinal reinforcement to be used is a matter of
-judgment. It varies in practice from 0.1 to 0.4 per cent of the area of
-the section. Since the coefficients of expansion of concrete and of
-steel are nearly the same, movements of the structure are as important
-as the stresses due to changes in temperature.
-
-Because of the uncertain and difficult conditions under which concrete
-sewers are frequently constructed it is advisable to specify the best
-grade of concrete and not to stress the concrete over 450 pounds per
-square inch in compression, with no allowable stress in tension. The
-concrete covering of reinforcing steel should be thicker than is
-ordinarily used for concrete building design, because of the possibility
-of poor concrete allowing the sewage to gain access to the steel,
-resulting in more rapid deterioration than would be caused by exposure
-to the atmosphere. A minimum covering of about 2 inches is advisable,
-except in very thin sections not in contact with the sewage. A minimum
-thickness of concrete of about 9 inches is frequently used in design,
-although crown thicknesses of 4½ inches have been used with success.
-Greater thicknesses should be used near the surface, particularly in
-locations subjected to heavy or moving loads.
-
-Brick linings are often provided for the invert where moderately high
-velocities of about 10 feet per second when flowing full are to be
-expected. For velocities in the neighborhood of 20 feet per second the
-invert should be lined with the best quality vitrified brick. Although
-concrete may erode no faster than brick under the same conditions, brick
-linings are more easily replaced and at a smaller expense.
-
-
-
-
- CHAPTER X
- CONTRACTS AND SPECIFICATIONS
-
-
-=106. Importance of the Subject.=—Sewers may be constructed by day labor
-or by contract. Under the day labor plan a city official or commission
-is charged with the purchase of material, the hiring and firing of
-employees, and the management of the work. Under the contract system a
-private individual or company contracts to supply all the material and
-labor necessary for the completion of the work.
-
-Under the day labor plan all persons engaged are “working for the City.”
-There is not the same sense of individual responsibility, the same
-incentive to economize, the same feeling of loyalty that is inspired by
-work under the personality of a contractor. Under either the day labor
-or contract plan unscrupulous politics are likely to enter into the
-relations of the employees of the city and the city officials or between
-the contractor and the city officials. Neither the day labor nor the
-contract plan offer a sure cure for unscrupulous political misdealings.
-Under the contract plan the contractor is led to keep his bid as low as
-possible, realizing the competition of other bidders, and during
-construction he will obtain greater efficiency from his labor because of
-their realization of the different conditions under which they are
-working. In some states and cities it is illegal for the municipality to
-do sewer construction except under the contract method.
-
-The contract method is therefore used in the majority of cases, and it
-is to the interest of the engineer that he be acquainted with the
-essentials of contracts and specifications necessary for the proper
-prosecution of sewer construction.
-
-
-=107. Scope of Subject.=—The making of a contract is one of the most
-common episodes of every day life. The contract may be an informal
-verbal agreement to meet at a certain place at a certain time, or it may
-be a formal document hedged about by confusing legal phraseology and
-bearing varieties of penalties and dire consequences in the event of its
-breach. The purpose of this chapter is to explain only those general
-features of an engineering contract which have particular bearing upon
-sewerage construction. Only the most essential points can be touched in
-the limited space available to this subject, it being presumed that the
-engineer is previously grounded in the principles of business law.[74]
-
-
-=108. Types of Contracts.=—Contracts are known as lump sum, cost-plus,
-unit-price, and by other titles indicating the method of payment.
-
-A lump sum contract is one in which a stated amount is fixed upon,
-before the execution of the contract, to be paid for all the work to be
-done and materials to be furnished under the contract. Such an
-arrangement is not advisable for a sewer contract, as the cautious
-contractor will bid high enough to protect himself in the event of any
-probable emergency. The principal must therefore pay whether the
-emergency or unforeseen difficulty is met or not. The advantage of this
-type of payment is that the principal knows exactly the cost of the work
-to him before construction is commenced.
-
-Cost-plus contracts are those in which the cost of the work to the
-contractor is to be paid by the principal, plus, (_a_) a fixed sum of
-money, (_b_) a percentage of the cost of the work, (_c_) a percentage of
-the cost of the work but with a fixed limit, (_d_) a percentage of the
-difference between the cost of the work and some fixed sum, or other
-variations of this principle. Such contracts have the advantage that the
-principal assumes all the risk in construction and therefore pays for
-only those contingencies which actually arise. Except for the last named
-form, they have the disadvantage that there is little or no incentive
-for the contractor to keep the cost of the work down. They are most
-successful where the contractor can be selected by the principal, but
-where it is necessary to let contracts to the lowest bidder, the
-“cost-plus” contract is not easily managed. In most states a
-municipality cannot make a cost-plus contract.
-
-A unit-price contract is one in which the amount to be paid is fixed in
-proportion to the amount of work done or materials supplied. This type
-of contract is the most suitable for sewer construction for a
-municipality where the contract must be let to the lowest bidder. The
-contractor is protected in the event of many unforeseen emergencies and
-the principal is protected against a raise in bids to cover such
-emergencies and against increase in the cost of the work in order to
-increase the profits under a “cost-plus” contract.
-
-It is sometimes desirable for the principal to furnish a portion of the
-materials, the bidders being notified beforehand that this material will
-be furnished. In this manner the quality of material is assured,
-contractors with the necessary skill but small capital may be attracted
-to bid, and uncertainties in the procuring of materials is eliminated.
-
-
-=109. The Agreement.=—A contract is an agreement between two or more
-interested parties to do a certain thing. A contract for the
-construction of a sewer is an agreement between a municipality or
-individual desiring sewerage facilities and a company or individual
-engaged in the construction of sewers. The latter promises to construct
-a sewer in return for which the former promises to pay a certain amount
-of money.
-
-The various portions of the agreement which are bound together as the
-complete contract are: I. The Advertisement, II. Information and
-Instructions for Bidders, III. Proposal, IV. General Specifications, V.
-Technical Specifications, VI. Special Specifications, VII. Contract,
-VIII. Bond, and IX. Contract Drawings. These should be fastened together
-in pamphlet form and constitute the complete instrument called the
-contract. No binding contract and specifications can be drawn upon
-logical deductions alone as legal precedent and tried methods must be
-followed to insure success. To draw up an original contract requires the
-combined knowledge of an engineer and a lawyer. The engineer of to-day
-writes his specifications by copying copiously from specifications used
-on work which has been completed successfully. In order that selections
-may be made with judgment and discrimination some examples have been
-selected from existing published specifications and contracts.
-
-
-=110. The Advertisement.=—This should contain: (1) A heading indicating
-the type of work, (2) A statement as to when, where and how bids will be
-received and opened, (3) A brief description of the character and amount
-of work to be done, (4) The method of payment, (5) The conditions under
-which further information can be obtained, (6) A statement as to the
-amount of money which must be deposited with the bid, and (7) Any other
-pertinent facts concerning the work.[75] An example of an advertisement
-follows;
-
- Sewer Construction
-
- Construction Turkey Creek Sewer
-
- Kansas City, Missouri.
-
- Bids for the construction of the Turkey Creek Sewer, two sewage
- pumping stations to be used in connection therewith, and certain
- laterals and extensions of existing sewers thereto, for Kansas
- City, Missouri, will be received up to 2 p.m. August 19, 1919, at
- the office of the Board of Public Works, City Hall, Kansas City,
- Missouri.
-
- The main sewer will be about one and one-fifth miles long, and the
- laterals and extensions about three and one-half miles: the main
- sewer will be constructed of reinforced concrete, the laterals and
- extensions will consist of concrete, segment blocks, and clay
- pipe.
-
- This work is estimated to cost from $1,500,000 to $1,750,000.
- Payment for the work will be made in four year special tax bills,
- bearing 7 per cent interest, payable one-fourth each year. Time
- 600 working days, barring strikes, bad weather, etc.
-
- Bidders are required to deposit $15,000 in cash or a certified
- check with bid, to insure signing of contract when let. Same to be
- returned on execution of the contract or rejection of bid.
-
- Complete plans and specifications for the work may be had and all
- information obtained by seeing or writing to A. D. Ludlow,
- Engineer of Sewers, City Hall, Kansas City, Missouri. Twenty-five
- ($25.00) Dollars will be required to be deposited for a set of the
- plans, but $20.00 thereof will be refunded upon return of the
- plans in good condition.
-
- BOARD OF PUBLIC WORKS,
-
- Kansas City, Missouri,
-
- by F. E. McCabe, Secretary.
-
-There are usually legal restrictions which require that the
-advertisement be inserted a certain number of times in specified
-newspapers or other advertising mediums before the opening of bids. If
-the contract is of sufficient size to attract outside contractors, the
-advertisement should be inserted in engineering and contracting journals
-of wide circulation. Although the advertisement appears separately from
-the other portions of the contract, a copy is usually bound in as the
-first page of the pamphlet containing the contract and specifications
-and is made an integral part thereof.
-
-
-=111. Information and Instructions for Bidders.=—This is somewhat on the
-order of an introduction to the pamphlet in which the specifications,
-contract, and contract drawings are published. As examples of the type
-of information and instructions given to prospective bidders the
-abstracts below have been taken from the “Contract, Specifications,
-Bond, and Proposal for the North Shore Sanitary Intercepting Sewer” by
-the Sanitary District of Chicago. The information and instructions to
-bidders can be divided into the following sections: 1st. Examination of
-Site, 2nd. Character and Quantity of Work, 3rd. Qualification for
-Bidding, 4th. Instructions for Making out Proposal, 5th. Certified
-Check, and 6th. Rejection of Bids.
-
- REQUIREMENTS FOR BIDDING AND INSTRUCTIONS TO BIDDERS
-
- Bidders are required to submit their bids upon the following express
- conditions:
-
- Bidders must carefully examine the entire sites of the work
- and the adjacent premises, and the various means of approach
- to the sites, and shall make all necessary investigations to
- inform themselves thoroughly as to the facilities for
- delivering and handling materials at the sites and to inform
- themselves thoroughly as to all the difficulties that may be
- involved in the complete execution of all work under the
- attached contract in accordance with the specifications hereto
- attached.
-
- Bidders are also required to examine all maps, plans, and data
- mentioned in the specifications, contract or proposal as being
- on file in the office of the Chief Engineer, for examination
- by bidders. No plea of ignorance of conditions that exist or
- that may hereafter exist or of conditions or difficulties that
- may be encountered in the execution of the work under this
- contract, as the result of a failure to make the necessary
- examinations and investigations, will be accepted as an excuse
- for any failure or omission on the part of the Contractor to
- fulfill in every detail all of the requirements of said
- contract, specifications and plans, or will be accepted as a
- basis for any claims whatsoever for extra compensation. Upon
- application all information in the possession of the Chief
- Engineer will be shown to bidders, but the correctness of such
- information will not be guaranteed by the Sanitary District.
-
- The following schedule of quantities, although stated with as
- much accuracy as is possible in advance, is approximate only,
- and is assumed solely for the purpose of comparing bids.
-
-Then follows an itemized schedule of the quantity of work to be done
-after which comes the following:
-
- Bidders must determine for themselves the quantities of work that
- will be required, by such means as they may prefer, and shall
- assume all risks as to variations in the quantities of the
- different classes of work actually furnished under the contract.
- Bidders shall not at any time after the submission of this
- proposal, dispute or complain of the aforesaid schedules of
- quantities or assert that there was any misunderstanding in regard
- to the amount or the character of the work to be done, and shall
- not make any claims for damages or for loss of profits because of
- a difference between the quantities of the various classes of work
- assumed for comparison of bids and the quantities of work actually
- performed.
-
- Proposals that contain any omissions, erasures, or alterations,
- conditions or items not called for in the contract and plans
- attached hereto, or that contain irregularities of any kind, will
- be rejected as informal.
-
- Bids manifestly unbalanced will not be considered in awarding the
- contract.[76]
-
- No bid will be accepted unless the party making it shall furnish
- evidence satisfactory to the Board of Trustees of the Sanitary
- District of Chicago of his experience and familiarity with work of
- the character specified and of his financial ability to
- successfully and properly prosecute the proposed work to
- completion within the specified time.
-
- Each bid shall be accompanied by a certified check, or cash, to
- the amount of ten (10) per cent of the total amount of said bid
- figured on the quantities given herewith, the lowest alternative
- total being allowed. Said amounts deposited with bids, shall be
- held until all of the bids have been canvassed and the contract
- awarded and signed. The return of said check or cash to the bidder
- to whom the contract for said work is awarded will be conditioned
- upon his appearing and executing a contract for the work so
- awarded and giving bond satisfactory to said Board of Trustees,
- for the fulfillment of each contract in the amount of fifty (50)
- per cent of the amount of each contract.
-
- The said Board of Trustees reserves the right to reject any or all
- bids.
-
- Accompanying the contract form are plans which, together with the
- specifications, show the work on which said tenders are to be
- made.
-
- The proposal must not be detached herefrom or from the contract by
- any bidder when submitting a bid.
-
-
-=112. Proposal.=—The proposal is a blank printed form on which the
-bidder is required to enter the prices for which he proposes to do the
-work. The proposal blank is necessary in order that the bids may be
-sufficiently uniform for proper comparison. Sewers are often paid for,
-particularly for small sizes, per foot of completed sewer as measured
-along the center line of the pipe parallel to the surface of the ground
-with the exterior length of manholes and other structures deducted.
-Sometimes, under other conditions, a different rate is allowed for each
-additional two feet of depth of sewer, and special structures, such as
-manholes, catch-basins, flush-tanks, etc., are paid for at a unit price
-according to the depth. Water connections to flush-tanks are paid for
-per foot of length of service pipe laid. In especially large or
-difficult work, materials are paid for at a unit-price, for example, per
-cubic yard of excavation, per cubic yard of concrete, per thousand feet
-board measure of lumber, etc.
-
-The following example is taken from the contract for the North Shore
-Intercepting Sewer previously quoted, to indicate the type of Proposal
-used:
-
-
- PROPOSAL
-
-FOR THE CONSTRUCTION OF THE NORTH SHORE INTERCEPTING SEWER
-
- To the Honorable, the President and the Board of Trustees of the
- Sanitary District of Chicago:
-
- Gentlemen:__The undersigned hereby certi____ that ____ ha____
- examined the specifications and form of contract and the
- accompanying plans for the construction of the North Shore
- Intercepting sewer, and ha____ also examined the premises at and
- adjacent to the sites of the proposed work, as herein described,
- and the means of approach to the said sites.
-
- The undersigned ha____ also examined the foregoing “Requirements
- for Bidding and Instructions to Bidders” and propose ____ to do
- all the work called for in said specifications and contract, and
- shown on said plans, and to furnish all materials, tools, labor
- and all appliances and appurtenances necessary to the full
- completion of said work at the rates and prices for said work as
- follows, to_wit:
-
- (1_a_) For six (6) by nine (9) foot concrete sewer, complete in
- place, as specified, the sum of ____ Dollars and ____ cents ($
- ____ ) per linear foot.
-
- (6_a_) For manholes, concrete, complete in place, as specified the
- sum of ____ Dollars and ____ cents ($ ____ ) each.
-
- The following plans showing the work to be performed in accordance
- with the attached specifications, have been examined by the
- undersigned in preparing the foregoing proposal, to-wit: ____ ____
- In accordance with the requirements set forth in the attached
- Information and Instructions for Bidders, there is deposited
- herewith the sum of ____ ____ Dollars and ____ cents ($ ____ )
- which under the terms therein mentioned entitle ____ to bid on
- said work, the said sum to be refunded to ____ ____ upon the
- faithful performance of all conditions set forth in the
- Information and Instructions for Bidders.
-
- Name ____
- Address ____
-
-Blanks are provided for each item. No place is left at the end for a
-summary. The proposal ends with an acknowledgment that the contract has
-been examined completely and all preliminary directions therein have
-been complied with. A blank is prepared for inserting the amount of the
-required certified check, and finally for the signature of the bidders.
-
-
-=113. General Specifications.=—The specifications, both general and
-technical, are occasionally incorporated in the contract form, but more
-frequently they are printed separately and are bound in the pamphlet
-preceding the contract. The general specifications relate to the
-conditions under which all work must be performed and are as applicable
-to the construction of a pumping station as to the smallest lateral,
-unless otherwise specified. It is not possible to include a complete set
-of General Specifications in the limited space of this text, but the
-more important specifications will be emphasized by examples taken from
-specifications in use.[77]
-
-The subjects covered in General Specifications are:
-
- (1) Definitions of doubtful terms.
-
- (2) The Engineer to settle disputes.
-
- (3) Duties of the Engineer.
-
- (4) Duties of the Contractor.
-
- (5) Hours and days of work.
-
- (6) No work to be done in the absence of an inspector.
-
- (7) Contractor to be represented at all times.
-
- (8) Time of commencing and completing the work.
-
- (9) Liquidated damages for delay in completion.
-
- (10) The City may change the plans.
-
- (11) The City may increase the amount of the work.
-
- (12) Inspection and its conduct.
-
- (13) The Contractor to be acquainted with laws relating to the work.
-
- (14) Contractor responsible for damages to persons or property.
-
- (15) City to be protected against patent claims.
-
- (16) Abandonment of contract and its remedy.
-
- (17) Estimates of work done and moneys due.
-
- (18) Payments for extra work.
-
- (19) Character of workmen to be employed.
-
- (20) City may reserve a sum for repairs during stipulated term after
- completion.
-
- (21) City may use money due Contractor to pay claims for labor or
- materials used on the work and not paid for by the Contractor.
-
- (22) The Contractor shall have no claim for damages on account of delay
- or unforeseen difficulties.
-
- (23) The Contractor may not assign nor sublet the contract without the
- City’s consent.
-
- (24) Cleaning up after completion.
-
- (25) The Contractor’s relations to other contractors.
-
- (26) The portions composing the contract.
-
-The following examples cover the subjects named in the preceding titles:
-
- 1. Definitions. The word Engineer whenever not qualified shall
- mean the Chief Engineer of the Commission, acting either directly
- or through his properly authorized agents, such agents acting
- severally within the scope of the particular duties entrusted to
- them.
-
-This article may include words that may be in dispute or ambiguous such
-as: Board of Trustees, Elevation, City, Contractor, Rock, Earth, etc.,
-etc.
-
- 2. Disputes. To prevent disputes and litigations, the Engineer
- shall in all cases determine the amount, quality, and
- acceptability of the work which is to be paid for under the
- contract; shall decide all questions in relation to said work and
- the performance thereof, and shall in all cases decide every
- question which may arise relative to the fulfillment of the
- contract on the part of the Contractor. His determination,
- decision and estimate shall be final and conclusive, and in case
- any question shall arise between the parties touching the
- contract, such determination, decision, and estimate shall be a
- condition precedent to the right of the Contractor to receive any
- moneys under the contract.
-
- 3. Duties of the Engineer. The Engineer shall make all necessary
- explanations as to the meaning and intentions of the
- specifications and shall give all orders and directions, either
- contemplated therein or thereby, or in every case in which a
- difficulty or unforeseen condition shall arise in the performance
- of the work. Should there be any discrepancies in or between, or
- should any misunderstanding arise as to the import of anything
- contained in the plans and specifications, the decision of the
- Engineer shall be final and binding. Any errors or omissions in
- plans and specifications may be corrected by the Engineer, when
- such corrections are necessary for the proper fulfillment of their
- intentions as construed by him.
-
- 4. Duties of the Contractor. The Contractor shall do all the work
- and furnish all the labor, materials, tools and appliances
- necessary or proper for performing and completing the work
- required by the contract, in the manner called for by the
- specifications, and within the contract time. He shall complete
- the entire work at the prices agreed upon and fixed therefor to
- the satisfaction of the Commission and its Chief Engineer and in
- accordance with the specifications, the drawings, and such
- detailed drawings as may be furnished from time to time, together
- with such extra work as may be required for the performance of
- which written orders may be given and received as hereinafter
- provided.
-
- The Contractor shall place sufficient lights on or near the work
- and keep them burning from twilight to sunrise; shall erect
- suitable railings, fences or other protections about all open
- trenches, and provide all watchmen on the work, by day or night,
- that may be necessary for the public safety. The Contractor shall,
- upon notice from the Engineer that he has not satisfactorily
- complied with the foregoing requirements, immediately take such
- methods and provide such means and labor to comply therewith as
- the Engineer may direct, but the Contractor shall not be relieved
- of this obligation under the contract by any such notice or
- directions given by the Engineer, or by neglect, failure, or
- refusal on the part of the Engineer to give such notice and
- directions.
-
- The Contractor shall furnish such stakes and the necessary labor
- for driving them as may be required by the Engineer. He shall
- maintain the stakes when set, with reasonable diligence, and
- stakes misplaced due to the carelessness of the Contractor or his
- workmen shall be reset under the direction of the Engineer, at the
- Contractor’s expense.
-
- 5. Night, Sunday, and Holiday Work:[78] No night, Sunday, nor
- holiday work requiring the presence of an engineer or inspector
- will be permitted except in case of emergency, and then only to
- such an extent as is absolutely necessary and with the written
- permission of the Engineer; provided that this clause shall not
- operate in the case of a gang organized for regular and continuous
- night, Sunday, or holiday work.
-
- 6. Absence of Engineer or Inspector. Any work done without lines,
- levels, and instructions having been given by the Engineer or
- without the supervision of an assistant or inspector, will not be
- estimated or paid for except when such work is authorized by the
- Engineer in writing. Work so done may be ordered removed and
- replaced at the Contractor’s sole cost and expense.
-
- 7. Absence of Contractor. During the absence of the Contractor he
- shall at all times have a duly authorized representative on the
- work. The Contractor shall give written notice to the Commission
- of the name and address of said representative and shall state
- where and how such representative can be reached, at any and all
- hours, whether by day or night.
-
- Whenever the Contractor or his representative is not present at
- any place on the work where it may be necessary to give orders or
- directions, such orders or directions will be given by the
- Engineer and they shall be received and promptly obeyed by the
- superintendent or foreman who may have immediate charge of the
- particular work in relation to which the order may be given.
-
- 8. Commencing Work. The Contractor agrees to begin the work
- covered by this contract within —— days of the execution of the
- contract and to prosecute the same with all due diligence and to
- entirely complete the work within —— days.
-
- It is understood and agreed that time is of the essence of this
- contract, and that a failure on the part of the Contractor to
- complete the work herein specified within the time specified will
- result in great loss and damage to said Sanitary District and that
- on account of the peculiar nature of such loss it is difficult, if
- not impossible, to accurately ascertain and definitely determine
- the amount thereof.
-
- 9. Liquidated Damages. It is therefore covenanted and agreed that
- in case the said Contractor shall fail or neglect to complete the
- work herein specified on or before the date hereinbefore fixed for
- completion, the said Contractor shall and will pay the said
- Sanitary District the sum of —— Dollars for each and every day the
- Contractor shall be in default in the time of completion of this
- contract.
-
- Said sum of —— Dollars per day is hereby agreed upon, fixed and
- determined by the parties hereto as the liquidated damages which
- said Sanitary District will suffer by reason of such defaults, and
- not by way of a penalty.
-
- 10. Changes in Plans. The Board reserves the right to change the
- alignment, grade, form, length, dimensions or materials of the
- sewers or any of their appurtenances, whenever any condition or
- obstructions are met that render such changes desirable or
- necessary. In case the alterations thus ordered make the work less
- expensive to the Contractor a proper deduction shall be made from
- the contract prices and the Contractor shall have no claim on this
- account for damages or for anticipated profits on the work that
- may be dispensed with. In case such alterations make the work more
- expensive, a proper addition shall be made to the contract prices.
- Any deduction or addition as aforesaid shall be determined and
- fixed by the Engineer.
-
- 11. Extensions and Additions. In the event that any material
- alterations or additions are made as herein specified which in the
- opinion of the Engineer will require additional time for execution
- of all the work under this contract, then, in that case the time
- of completion of the work shall be extended by such a period or
- periods of time as may be fixed by said Engineer and his decision
- shall be final and binding upon both parties hereto, provided that
- in such case the Contractor, within four (4) days after being
- notified in writing of such alterations and additions, shall
- request in writing an extension of time, but the provisions of
- this paragraph shall not otherwise alter the provisions of this
- contract with reference to _liquidated damages_, and the said
- Contractor shall not be entitled to any damages or compensation
- from the said Sanitary District on account of such additional time
- required for the execution of the work.
-
- 12. Inspection. All materials of whatsoever kind to be used in the
- work shall be subject to the inspection and approval of the
- Engineer and shall be subject to constant inspection before
- acceptance. Any imperfect work that may be discovered before its
- final acceptance shall be corrected immediately, and any
- unsatisfactory materials used in the work or delivered at the site
- shall be rejected and removed on the requirement of the Engineer.
- The inspection of any work shall not relieve the Contractor of any
- of his obligations to perform proper and satisfactory work as
- herein specified, and all work which, during the progress and
- before the final acceptance, may become damaged from any cause,
- shall be removed and replaced by good and satisfactory work
- without extra charge therefor. The Engineer and his assistants
- shall have at all times free access to every part of the work and
- to all points where material to be used in the work is
- manufactured, procured or stored and shall be allowed to examine
- any material furnished for use in the work under this contract.
-
- All inspection of any and all material furnished for use in work
- to be performed under this contract shall be made at the site of
- the work after the delivery of the material, provided, that, if
- requested by the Contractor the Engineer may at his option
- perform, or have performed, inspection of materials at points
- other than the site of the work. In any such case the Contractor
- shall pay the Sanitary District the extra cost of such inspection,
- including the necessary expenses of the inspector for the extra
- time expended in performing any such inspection at said other
- points.
-
- 13. Legal Requirements. The Contractor shall keep himself fully
- informed of all existing and future national and state laws and
- local ordinances and regulations in any manner affecting those
- engaged or employed in the work, or the materials used in the
- work, or of all such orders and degrees of bodies or tribunals
- having any jurisdiction or authority over the same, and shall
- protect and indemnify the party of the first part against any
- claim or liability arising from or based on the violation of such
- law, ordinance, regulation, order or decree, whether by himself or
- his employees.
-
- 14. Damages. If any damage shall be done by the Contractor or by
- any person or persons in his employ to the owner or occupants of
- any land or to any real or personal property adjoining, or in the
- vicinity of the work herein contracted to be done or to the
- property of a neighboring contractor the Engineer shall have the
- right to estimate the amount of said damage and to cause the
- Sanitary District to pay the same to the said owner, occupant, or
- contractor, and the amount so paid shall be deducted from the
- money due said Contractor under this contract. Said Contractor
- covenants and agrees to pay all damages for any personal injury
- sustained by any person growing out of any act or doing of himself
- or his employees that is in the nature of a legal liability, and
- he hereby agrees to indemnify and save the Sanitary District
- harmless against all suits or actions of every name and
- description brought against said Sanitary District, for or on
- account of any such injuries, or such damages received or
- sustained by any person or persons; and the said Contractor
- further agrees that so much of the money due to him under this
- contract, as shall be considered necessary by the Board of
- Trustees of said Sanitary District, may be retained by the
- Sanitary District until such suit or claim for damages shall have
- been settled, and evidence to that effect shall have been
- furnished to the satisfaction of said Board of Trustees.
-
- 15. Patents. It is further agreed that the Contractor shall
- indemnify, keep and save harmless said Sanitary District from all
- liabilities, judgments, costs, damages and expenses which may in
- any wise come against said Sanitary District, or which may be the
- result of an infringement of any patent by reason of the use of
- any materials, machinery, devices, apparatus, or process furnished
- or used in the performance of this contract, or by reason of the
- use of designs furnished by the Contractor and accepted by the
- Sanitary District, and in the event of any claim or suit or action
- at law or in equity of any kind whatsoever being made or brought
- against said Sanitary District, then the Sanitary District shall
- have the right to retain a sufficient amount of money in the same
- manner and upon the conditions as hereinafter specified.
-
- 16. Abandonment of Contract. If the work to be done under the
- contract shall be abandoned by the Contractor, or if at any time
- the Engineer shall be of the opinion, and shall so certify, in
- writing, to the Commission, that the performance of the contract
- is unnecessarily or unreasonably delayed, or that the Contractor
- is willfully violating any of the conditions of the
- specifications, or is executing the same in bad faith, or not in
- accordance with the terms thereof, or if the work be not fully
- completed within the time named in the contract for its
- completion, the Commission may notify the Contractor to
- discontinue all work thereunder, or any part thereof, by a written
- notice served upon the Contractor, as herein provided; and
- thereupon the Contractor shall discontinue the work, or such part
- thereof, and the Commission shall thereupon have the power to
- contract for the completion of said work in the manner prescribed
- by law, or to procure and furnish all necessary materials,
- animals, machinery, tools and appliances, and to place such and so
- many persons as it may deem advisable to work at and complete the
- work described in the specifications, or such part thereof, and to
- charge the entire cost and expense thereof to the Contractor. And
- for such completion of the work or any part thereof, the
- Commission may for itself or its contractors, take possession of
- and use or cause to be used any or all such materials, animals,
- machinery, tools and implements of every description as may be
- found on the line of the said work. The cost and expense so
- charged shall be deducted from, and paid by the City out of such
- moneys as may be due or may become due to the Contractor, under
- and by virtue of the contract. In case such expense shall exceed
- the amount which would have been payable under the contract, if
- the same had been completed by the Contractor, he shall pay the
- amount of such excess to the City. When any particular part of the
- work is being carried on by the Commission, by contract or
- otherwise, under the provisions of this clause of the contract,
- the Contractor shall continue the remainder of the work in
- conformity with the terms of his contract, and in such manner as
- in no wise to hinder or interfere with the persons or workmen
- employed by the Commission by contract or otherwise as above
- provided, to do any part of the work or to complete the same under
- the provisions hereof.
-
- 17. Estimates. The Engineer shall from time to time as the work
- progresses, on or about the last day of each month, make in
- writing an estimate, such as he shall believe to be just and fair,
- of the amount and value of the work done and the materials
- incorporated into the work by the Contractor under the
- specifications, provided however that no such estimate shall be
- required to be made when, in the judgment of the Engineer the
- total value of the work done and the materials incorporated into
- the work since the last preceding estimate is less than ——
- dollars. Such estimates shall not be required to be made by strict
- measurements, but they may be approximate only.
-
- The Contractor shall not be entitled to demand from the Commission
- as a right, a detailed statement of the measurements or quantities
- entering into the several items of the monthly estimates, but he
- will be given such opportunities and facilities to verify the
- estimates as may be deemed reasonable by the Commission.
-
- When in the opinion of the Engineer, the Contractor shall have
- completely performed the contract on his part, the Engineer shall
- make a final estimate, based on actual measurements, of the whole
- amount of the work under and according to the terms of the
- contract, and shall certify to the Commission in writing, the
- amount of the final estimate at the completion of the work. After
- the completion of the work the City shall pay to the Contractor
- the amount remaining after deducting from the total amount or
- value of the work, as stated in the final estimate, all such sums
- as have theretofore been paid to the Contractor under any of the
- provisions of the contract, except such sums as may have been paid
- for extra work, and also any sum or all sums of money which by the
- terms thereof the City is or may be authorized to reserve or
- retain; provided that nothing therein contained shall affect the
- right of the City, hereby reserved, to reject the whole or any
- portion of the aforesaid work, should the said certificate be
- found or known to be inconsistent with the terms of the contract
- or otherwise improperly given. All monthly estimates upon which
- partial payments have been made, being merely estimates, shall be
- subject to correction in the final estimate, which final estimate
- may be made without notice thereof to the Contractor, or of the
- measurements upon which it is based.
-
- 18. Extra Work. The Contractor shall do any work not herein
- otherwise provided for, when and as ordered in writing by the
- Engineer or his agents specially authorized thereto in writing,
- and shall when requested by the Engineer so to do, furnish
- itemized statements of the cost of the work ordered and give the
- Engineer access to accounts, bills, vouchers, etc. relating
- thereto. If the Contractor claims compensation for extra work not
- ordered as aforesaid, or for any damages sustained, he shall
- within one week after the beginning of any such work or the
- sustaining of any such damage, make a written statement of the
- nature of the work performed or the damage sustained, to the
- Engineer, and shall, on or before the fifteenth day of the month
- succeeding that in which any such extra work shall have been done
- or any such damage shall have been sustained, file with the
- Engineer an itemized statement of the details and amount of any
- such work or damage; and unless such statement shall be made as so
- required, his claim for compensation shall be forfeited and he
- shall not be entitled to payment on account of any such work or
- damage.
-
- For all such extra work the Contractor shall receive the
- reasonable cost of said work, plus fifteen (15) per cent of said
- cost.
-
- 19. Competent Employees. The Contractor shall employ only
- competent skillful men to do the work; and whenever the Engineer
- shall notify the Contractor, in writing, that any man employed on
- the work is, in his opinion unsatisfactory, such man shall be
- discharged from the work and shall not again be employed on it,
- except with the consent of the Engineer.
-
- 20. Money Retained. Upon the completion of the work and its
- acceptance by the City, the City shall reserve and retain five (5)
- per cent of the total value of the work done under the contract as
- shown by the final estimate, over and above any and all other
- reservations which the city by the terms thereof is entitled or
- required to retain and shall hold the said five (5) per cent for a
- period of nine (9) months from and after the date of completion
- and acceptance, and the City shall be authorized to apply such
- part of said five (5) per cent so retained to any and all costs of
- repairs and renewals as may become necessary during such period of
- nine (9) months, due to improper work done or materials furnished
- by the Contractor, if the Contractor shall fail to make such
- repairs or renewals within twenty-four (24) hours after receiving
- notice from the City so to do.
-
- Upon the expiration of said nine (9) months from and after the
- completion and acceptance of the work, the City shall pay to the
- Contractor the said five (5) per cent hereby retained, less such
- sums as may have been retained hereunder.
-
- 21. Unpaid Claims against Contractor. The Contractor shall furnish
- the City with satisfactory evidence that all persons who have done
- work or furnished materials under the contract, and have given
- written notices to the City, before and within ten (10) days after
- the final completion and acceptance of the whole work under the
- contract, that any balance for such work or materials is due and
- unpaid, have been fully paid or satisfactorily secured. And in
- case such evidence is not furnished as aforesaid, such amount as
- may be necessary to meet the claims of the persons aforesaid shall
- be fully discharged or such notices withdrawn.
-
- 22. Delays and Difficulties. The Contractor shall not be entitled
- to any claims for damages on account of postponement or delay in
- the work occasioned by forces beyond the control of the City, nor
- for postponement or delay in the work where ten (10) days written
- notice has been given the Contractor of such postponement or
- delay, nor where unforeseen difficulties are encountered in the
- prosecution of the work. In the event of a postponement or delay
- ordered in writing by the City the time of completion of the
- contract shall be extended a number of days equal to the number of
- days that the work has been postponed or delayed.
-
- 23. Assignment of Contract. The Contractor shall not assign by
- power of attorney or otherwise, nor sublet the work or any part
- thereof, without the previous written consent of the party of the
- first part, and shall not either legally nor equitably assign any
- of the moneys payable under this agreement or his claim thereto
- unless by and with the consent of the party of the first part.
-
- 24. Cleaning Up. On or before the completion of the work, the
- Contractor shall, without charge therefor, tear down and remove
- all buildings and other structures built by him, shall remove all
- rubbish of all kinds from any grounds which he has occupied, and
- shall leave the line of the work in a clean and neat condition.
-
- 25. Access to Work and Other Contractors. The Commission and its
- engineers, agents and employees may at any time and for any
- purpose enter upon the work and the premises used by the
- Contractor, and the Contractor shall provide proper and safe
- facilities therefor. Other contractors of the Commission may also
- when so authorized by the Engineer, enter upon the work and the
- premises used by the Contractor for all the purposes which may be
- required by their contracts. Any differences or conflicts which
- may arise between this Contractor and other contractors of the
- Commission in regard to their work shall be adjusted and
- determined by the Engineer.
-
- 26. The Contract. It is understood and agreed by the City and the
- Contractor that the terms of this contract are embodied and
- included in the Advertisement, Information and Instructions to
- Bidders, Proposal, Specifications of every nature, the Bond and
- the contract drawings hereto attached.
-
-These few articles have been given as examples of some of the essential
-subjects to be treated in general specifications. It is to be understood
-that these examples do not represent a complete set of general
-specifications and items have been omitted the absence of which in a
-complete contract might be injurious to the successful completion of the
-work.
-
-
-=114. Technical Specifications.=—These ordinarily follow the general
-specifications and have to do with the quality of materials, the manner
-of putting them together, and the method of doing the work. The subject
-headings in the Technical Specifications on the Baltimore Sewerage
-Commission are:
-
- Excavation
- Tunneling
- Rock Excavation
- Sheeting
- Sheet Piling
- Sheeting and Bracing
- Piles
- Blasting
- Pumping and Drainage
- Foundations
- Refilling
- Repaving
- Underdrains
- Buildings
- Inlets and Catch-Basins
- Cement
- Mortar
- Concrete
- Brick
- Masonry
- Reinforced Concrete
- Vitrified Pipe
- Concrete and Brick Sewers
- Vitrified Pipe Sewers and Drains
- Manholes
- Iron Castings
- House Connections
- Obstructions
- Fences
- Flush-Tanks
-
-Each of these subjects is treated in the appropriate section of this
-book.
-
-An important part of each section of the technical specifications is the
-clause providing for the method of payment for the work specified. This
-is usually the last clause in the section. For example, the last clause
-in the Baltimore Specifications relating to Rock Excavation, is:
-
- “Payment will be made for the number of cubic yards of rock
- measured and allowed as above specified at the price of four
- dollars and fifty cents ($4.50) per cu. yd., measured in place.
- Payment for rock excavation will be made in addition to the prices
- bid for excavation.”
-
-
-=115. Special Specifications.=—These have to do with problems, methods
-of construction, or materials peculiar to certain contracts or certain
-portions of the work. It frequently occurs that the construction of
-sewerage works will be let out under a number of contracts, or bids will
-be called for on different alternatives to which the entire
-Advertisement, Information and Instructions for Bidders, Proposal, and
-General Specifications are applicable. The special specifications will
-apply only to the contract in question, e.g., in some work done under
-the direction of the author, the sewer on one contract came within
-twelve inches of the surface of a highway. The special specification
-relating to this piece of construction, was:
-
- “Where crossing under the Chicago Road the pipe sewer shall be
- embedded in concrete as shown on the contract drawings. The
- concrete for this purpose shall be mixed in the proportions of one
- (1) part cement, three (3) parts fine aggregate, and six (6) parts
- coarse aggregate. Payment for the concrete so used will be made at
- the unit price stated in the accompanying Proposal.”
-
-In order to avoid confusion the special specifications are either
-incorporated directly in the Contract form, or follow the Technical
-Specifications and are grouped according to the contracts to which they
-apply.
-
-
-=116. The Contract.=—The contract is a brief instrument which includes a
-simple statement of the obligations of each party involved. The
-following is an example of a form in successful use:
-
-
- CONTRACT
-
- This agreement made and entered into this ____ day of ____ in the
- year one thousand nine hundred and ____ by and between the City of
- ____ by its duly constituted or elected authorities herein acting
- for the City of ____ without personal liability to themselves,
- party of the first part, hereinafter designated as the City, and
- ____ party of the second part hereinafter designated as the
- Contractor.
-
- WITNESSETH, that the parties to these presents each in
- consideration of the undertakings, promises and agreements on the
- part of the other herein contained, have undertaken, promised and
- agreed, and do hereby undertake, promise and agree, the party of
- the first part for itself, its successors and assigns, and the
- part ____ of the second part for ____ and ____ heirs, executors,
- administrators and assigns as follows, to-wit:
-
- Art. I. To be bounden by all the articles of the General,
- Technical, and Special Specifications applicable, and by the terms
- of the Advertisement, Information and Instructions for Bidders,
- Proposal and Contract Drawings hereto attached, and which are
- understood and acknowledged to be an integral part of this
- contract.
-
- Art. II. The work to be completed under this contract is ____
-
- Art. III. The City shall pay and the Contractor shall receive as
- full compensation for everything furnished and done by the
- Contractor under this contract, including all work required but
- not specifically mentioned in the following items, and also for
- all loss or damage arising from the nature of the work aforesaid,
- or from the action of the elements, or from any unforeseen
- obstruction or difficulty encountered in the prosecution of the
- work and for well and faithfully completing the work as herein
- provided, as follows:
-
-Then follows a copy of the Proposal with the prices bid. The contract
-closes with the final clause:
-
- In witness whereof the said City of ____, party of the first part
- have hereunto set their hands and seals, and the Contractor has
- also hereunto set his hand and seal and the party of the first
- part and the Contractor have executed this agreement in duplicate,
- one part to remain with the party of the first part and one to be
- delivered to the Contractor this ____ day of ____ in the year one
- thousand nine hundred and ____
-
- City of ____
- ____
- ____
-
- Contractor ____
- ____
- ____
-
-
-=117. The Bond.=—The bond called for in the Information and Instructions
-for Bidders is bound in the pamphlet following the Contract. No uniform
-practice is followed in the amount of the bond required. It varies from
-50 to 100 per cent of the contract price and may be stated as a lump sum
-before the contract price is known. There is a possibility that the
-Contractor may fail before he has commenced work and the City may be
-unable to procure another contractor to take up the work. The City
-should then be protected by a 100 per cent bond. Such a contingency is
-remote. The Contractor seldom fails until work is well under way, and
-other contractors are usually available, although the failure of one
-contractor tends to increase the bids of other contractors for the same
-work. In fixing the amount of the bond the judgment of the Engineer is
-called into play in order that the amount may be as low as possible in
-fairness to the Contractor, and high enough to protect the interests to
-the City. By reducing the amount of the bond the expense to the City is
-also reduced as the City ultimately must pay its cost.
-
-Upon the acceptance of the bond and the execution of the Contract, the
-Engineer’s duties take him out of the designing office and into the
-construction field.
-
-
-
-
- CHAPTER XI
- CONSTRUCTION
-
-
-=118. Elements.=—The principal elements in construction are: labor,
-materials, tools, and transportation. The lack of or inadequateness of
-any one of these detracts from the effectiveness of the others. The
-engineer should assure himself of the completeness of his plans or those
-of the contractor on each of these points. The disposition of labor and
-the handling of materials to obtain the largest amount of good with the
-least expenditure of money and effort are problems which must be solved
-by the engineer or the contractor during construction.
-
-
- WORK OF THE ENGINEER
-
-
-=119. Duties.=—The duties of the engineer during construction consist in
-giving lines and grades; inspecting materials; interpreting the
-contract, specifications and drawings; making decisions when unexpected
-conditions are encountered; making estimates of work done; collecting
-cost data; making progress reports; keeping records; and in guarding the
-interests of the City.
-
-
-=120. Inspection.=—In the inspection of workmanship and materials, the
-engineer is assisted by a corps of inspectors and assistants who act
-under his direction. The duties of the inspector are to be present at
-all times that work is in progress and to act for the engineer in
-enforcing the terms of the contract, the details of the drawings, and
-the tests applicable to the workmanship and materials that he is
-delegated to inspect. He should have a copy of the contract, or that
-portion of it which pertains to his work, available at all times. He
-should examine all materials as they are delivered on the job and see
-that rejected materials are removed at once. An ordinary recourse of
-some foremen will be to place rejected material to one side until a
-brief absence of the inspector will present the opportunity for the use
-of the rejected material. The methods to be followed in the inspection
-of materials and workmanship should be such as to discover discrepancies
-between the specifications and the materials delivered or the work done.
-Other duties of the inspector are: to record the location of house
-connections or to drive a stake over them for subsequent location by the
-engineer; to see that plugs are put in the branches left for future
-house connections; to inspect the workmanship in the making of joints in
-pipe sewers; to protect the line and grade stakes from displacement; to
-check the size, depth, and grade of sewers and elevations of special
-structures, etc.
-
-Dishonest and unscrupulous workmen have many tricks to get by the
-inspector. These tricks are best learned by experience as no academic
-list can impress them properly on the memory. The position of the
-inspector is not always enviable. He must hold the respect of the
-workmen, of the contractor, and of the engineer. To do this he must not
-be unreasonable or arbitrary in his decisions, but when a decision is
-once made he must be firm in following up its enforcement. He must be
-careful not to give directions whose fulfillment he cannot enforce, nor
-for which he cannot give adequate reason to his superiors. His integrity
-must never be questioned. He must not allow himself to become under
-obligations to the contractor by the acceptance of favors he cannot
-return except at the expense of his employer, yet at the same time he
-must not appear priggish by the refusal of all favors or social
-invitations. In brief he must be friendly without being intimate,
-independent without being aloof, and firm without being arbitrary.
-
-The engineer must support his inspectors in their decisions or discharge
-them if he cannot.
-
-
-=121. Interpretation of Contract.=—In interpreting the contract,
-specifications and drawings, the engineer is supposedly an impartial
-arbiter between the interests of the city and the contractor. His
-decisions, as to the meaning of the contract, must be founded on his
-engineering judgment, and should aim to produce the best results without
-demanding more from the contractor than, in his honest opinion, it is
-the intention of the contract to demand. However conscientiously he may
-attempt to remain impartial, and in spite of the honesty of the
-contractor, his position, as an employee of the city will almost
-invariably cause him to favor the city in his decisions on close points.
-The experienced contractor knows this and fixes his bid accordingly, the
-personality of the engineer sometimes acting as an important factor in
-the amount of the bid. The situation arises through the character of the
-contract, and not through a lack of moral integrity on the part of
-anyone concerned.
-
-
-=122. Unexpected Situations.=—When unexpected or uncertain conditions
-are encountered in construction the engineer should visit the spot at
-once and should advise or direct, according to the terms of the
-contract, the procedure to be followed. Such conditions may be the
-encountering of other pipes, quicksand, rock, etc. Each case is a
-problem in itself. Water, gas, telephone and electric wire conduits can
-be moved above or below the sewer being constructed with comparative
-ease. Other sewers, if smaller, may be permitted to flow temporarily
-across the line of the sewer under construction and finally discharge
-into the completed sewer, or one sewer must be made to pass under the
-other, either as an inverted siphon or by changing the grade of one of
-the sewers. Rock, or other material for which a special rate of payment
-is allowed, must be measured as soon as uncovered in order to avoid
-delaying the work or losing the record of the amount removed. When
-quicksand is met special precautions must be taken to safeguard the
-sewer foundation and to insure that the sewer will remain in place until
-after the backfilling is completed. These precautions are described in
-Art. 135.
-
-
-=123. Cost Data and Estimates.=—Cost account keeping and the making of
-monthly or other estimates are closely connected. Cost accounts are of
-value in estimating the amount of work done to date, and in making
-preliminary estimates of the cost of similar work. Although the engineer
-is not always required to keep such accounts, they are usually of
-sufficient value to pay for the labor of keeping them. Under some
-contracts the contractor’s accounts are open to examination by the
-engineer. Usually, however, he must depend on reports from the
-inspectors for information concerning the man-hours required on
-different pieces of work, and on his own measurements of materials used
-and his knowledge of their unit costs, in order to make up an estimate
-of total cost.
-
-The measurement of a completed structure and a summary of the materials
-used in its construction may act as a check on the use of proper
-materials as called for in the contract. For example, if it is known
-that 2,000 bricks are required for the construction of a manhole and if
-only 15,000 have been used in the construction of ten manholes, it is
-probable that some or all of the manholes have been skimped. Similar
-conditions may show in the proportions of concrete, backfilling in
-tunnels, sheeting to be left in place, etc.
-
-The statement of a few principles of cost accounting, and the
-illustration of a few blanks in use should be sufficiently suggestive to
-lead a resourceful engineer in the right direction.[79] Costs should be
-divided into four general classifications: labor, materials, equipment,
-and overhead. Labor should be subdivided under its several different
-classifications arranged in accordance with rates of pay. The number of
-laborers under each classification and the amount of work done per day
-should be recorded. Fig. 86 is an example of a form which may be used
-for such a purpose.
-
-[Illustration:
-
- FIG. 86.—Foreman’s Daily Payroll Report.
-
- From Engineering and Contracting, 1907.
-]
-
-Materials may be recorded as they are delivered on the job, as they are
-used, or in both cases. Measurements are usually easier to make at the
-time of delivery, but records made at the time materials are used are
-more serviceable. For example, 100 barrels of cement may be delivered on
-a job in November, 50 of them are used before the job freezes up and the
-other 50 are held over until spring. It would be misleading to charge
-100 barrels used in November. Fig. 87 is a form in use for an
-inspector’s report on materials. The total cost must be made up in the
-office from these records and a knowledge of unit costs.
-
-[Illustration:
-
- FIG. 87.—Foreman’s Daily Material Report.
-
- From Engineering and Contracting, 1907.
-]
-
-Equipment consists of tools, animals, machinery, and apparatus used in
-construction. Only equipment that is actually used should be charged to
-the job and a credit should be made at the completion of the job for the
-fair value of the equipment remaining after the completion of the work.
-
-Overhead charges include the expense of the office force,
-superintendence, and miscellaneous items such as insurance, rent,
-transportation, etc., which cannot be charged to any particular portion
-of the work but are equally applicable to all portions. It happens
-frequently that many jobs are handled in the same main office. The
-division of overhead becomes more difficult and is frequently arranged
-on an arbitrary basis, e.g., each job may be charged the proportion of
-overhead that its contract price bears to the total contract prices
-being performed under that office. This rule may be modified when it
-becomes evident that some job is taking distinctly more than its share
-of the overhead.
-
-Estimates of work done in any period can be made with the above data in
-hand by subtracting the total costs of the work up to the beginning of
-the period from the total costs up to the end of the period. Fig. 88
-shows a sample blank from the final estimate sheets used at Scarsdale,
-N. Y.
-
-
-=124. Progress Reports.=[80]—These are kept by the engineer in order
-that he may see that the work is progressing as called for in the
-contract, and any portion which is lagging behind without reason may be
-pushed. Such reports are most useful when the information is expressed
-graphically, as the eye quickly catches points where the work is falling
-behind schedule.
-
-
-=125. Records.=—The contract drawings are supposed to show exactly where
-and how construction is to be done. Due to unexpected contingencies
-changes occur, of which a record should be made and preserved. These
-records may be kept in a form similar to the contract drawings, or if
-the changes are not extensive, they can be recorded on the original
-contract drawings. The location of house and other connections should be
-recorded in a separate note book available for immediate consultation.
-The engineer should keep a diary of the work in which are recorded
-events of ordinary routine as well as those of special interest and
-importance. This diary should be illustrated by photographs showing the
-condition of the streets before and after construction, methods of
-construction, accidents, etc. Such accounts are of great value in
-defending subsequent litigation and their existence sometimes prevents
-litigation. A contractor may wait a year or so after the completion of a
-piece of work until the engineer and other city officials have broken
-their connection with the city. Suit is then brought against the city
-and unless good records are available the administration may be forced
-to buy the claimant off or may elect to enter court, only to be beaten.
-
-[Illustration:
-
- FIG. 88.—Samples of Cost Record Forms.
-
- From Engineering and Contracting, 1909.
-]
-
-
- Excavation
-
-
-=126. Specifications.=—The following abstracts have been taken from the
-specifications on Excavation by the Baltimore Sewerage Commission as
-illustrative of good practice. In conducting the work the contractor
-shall:
-
- ... remove all paving, or grub and clear the surface over the
- trench, whenever it may be necessary and shall remove all surface
- materials of whatever nature or kind. He shall properly classify
- the materials removed, separating them as required by the
- Engineer; and shall properly store, guard, and preserve such as
- may be required for future use in backfilling, surfacing, repaving
- or otherwise. All macadam material removed shall be separated and
- graded into such sizes as the Engineer may direct and materials of
- different sizes shall be kept separate from each other and from
- any and all other materials.
-
- All the curb, gutter, and flag-stones and all paving material
- which may be removed, together with all rock, earth and sand taken
- from the trenches shall be stored in such parts of the carriageway
- or such other suitable place, and in such manner as the Engineer
- may approve. The Contractor shall be responsible for the loss of
- or damage to curb, gutter and flag-stones and to paving material
- because of careless removal or wasteful storage, disposal, or use
- of the same.
-
- ... When so directed by the Engineer the bottom of the trench
- shall be excavated to the exact form of the lower half of the
- sewer or of the foundation under the sewer.
-
- The bottom width of the trench for a brick or concrete sewer shall
- be ... not less in any case than the overall width of the sewer,
- as shown on the plans. In case the trench is sheeted this minimum
- width will be measured between the interior faces of the sheeting
- as driven, but in no case shall bracing, stringers, or waling
- strips be left within any portion of the masonry of the sewer
- except by permission of the Engineer; and such braces, stringers
- and waling strips shall not, in any case, be allowed to remain
- within the neat lines of the masonry as shown on the plans. In
- case that the distance between faces of the sheeting is less than
- that called for by the width of the sewer to be laid in the
- trench, the Engineer may direct the sheeting to be drawn and
- redriven, or otherwise changed and altered; or he may direct that
- the sewer be reinforced in such manner and to such an extent as he
- may deem necessary without compensation to the Contractor, even
- though such narrower trench was not caused by negligence or other
- fault on the part of the Contractor.
-
- Trenches for vitrified pipe shall be at all points at least six
- inches wider in the clear on each side than the greatest external
- width of the sewer, measured over the hubs of the pipe.... Bell
- holes shall be excavated in the bottoms of trenches for vitrified
- pipe sewers wherever necessary.
-
- Not more than three hundred feet of trench shall be opened at any
- one time or place in advance of the completed building of the
- sewer, unless by written permission of the Engineer and for a
- distance therein specified....
-
- The excavation of the trench shall be fully completed at least
- twenty feet in advance of the construction of the invert, unless
- otherwise ordered.
-
- During the progress of construction the Contractor will be
- required to preserve from obstruction all fire hydrants and the
- carriageway on each side of the line of the work.
-
- The streets, cross-walks, and sidewalks shall be kept clean,
- clear, and free for the passage of carts, wagons, carriages and
- street or steam railway cars, or pedestrians, unless otherwise
- authorized by special permission in writing from the Engineer. In
- all cases a straight and continuous passageway on the sidewalks
- and over the cross walks of not less than three feet in width
- shall be preserved free from all obstruction.
-
- Where any cross walk is cut by the trench it shall be temporarily
- replaced by a timber bridge at least three feet wide, with side
- railings, at the Contractor’s expense. The placing of planks
- across the trench without proper means of connection or
- fastenings, or pipe or other material, or the using of any other
- makeshift in place of properly constructed bridges, will not be
- permitted.
-
-This is equally applicable to certain wagon bridges to be fixed upon by
-the Engineer, on the basis of traffic requirements.
-
- In streets that are important thoroughfares or in narrow streets
- the material excavated from the first one hundred feet of any
- opening or from such additional length as may be required, shall
- upon the order of the Engineer, be removed by the Contractor, as
- soon as excavated. The material subsequently excavated shall be
- used to refill the trench where the sewer has been built.
-
-The preceding specifications are applicable to open-trench excavation.
-Rigid restrictions are placed about tunneling because of the greater
-difficulty of doing good work, the greater danger to life and property
-and the possibility of later surface subsidence if the backfilling is
-done improperly. A common clause in specifications is:
-
- All excavations for sewers and their appurtenances shall be made
- in open trenches unless written permission to excavate in tunnel
- shall be given by the Engineer.
-
-
-=127. Hand Excavation.=—Earth excavation by pick and shovel is the
-simplest and most primitive mode of excavation. Only small jobs are
-handled in this manner in order to save the investment necessary in
-machines or the expense of hiring and moving one to the work. The tools
-used in the hand excavation of trenches are: picks, pickaxes,
-long-handled and short-handled pointed shovels, square-edged long- and
-short-handled shovels, scoop shovels, axes, crowbars, rock drills,
-mauls, sledges, etc. The excavating gangs are divided up into units of
-20 to 50 men under one foreman or straw boss, and among the men may be a
-few higher priced laborers who set the pace for the others. Each laborer
-on excavation should be provided with a shovel, the style being
-dependent on the character of the material being excavated and the depth
-of the trench. In stiff material and deep trenches requiring the lifting
-of the material in the shovel, long-handled pointed shovels should be
-used. In loose sandy material loaded directly into buckets
-short-handled, square pointed shovels are satisfactory. Picks are used
-in cemented gravels or where hard obstructions prevent cutting down with
-the edge of the shovel. Very stiff but not hard material can be cut out
-in chunks with a pickaxe and thrown from the trench or into a bucket
-with a scoop shovel. Scoop shovels are also useful in wet running
-quicksand. The number of picks, axes, crowbars, and other tools must be
-proportioned according to the material being excavated. Under the worst
-conditions of excavation in a hard cemented gravel it may be necessary
-to provide each man with a pick as well as a shovel, whereas in sand
-only a shovel is necessary. Two or three crowbars, axes, a length of
-chain, two or three screw jacks, etc., are provided per gang in case of
-an unexpected encounter with an obstruction in the trench, such as a
-boulder, a tree stump, a length of pipe, etc.
-
-In laying out the work the foreman marks the outlines of the trench on
-the ground by means of a scratch made with a pick, chalk marks, tape, or
-other devices. These marks are measured from offset or center stakes set
-by the engineer. Center stakes are less conducive to error but are more
-likely to be disturbed before use than are offset stakes, but careless
-foremen make more errors with offset than with center stakes. The
-inspector should assist or be present at the laying out of the trench.
-After the trench has been laid out each laborer should be given a
-certain specific portion of it to dig and this portion is marked out on
-the ground. In this way a check can be kept upon the performance of each
-laborer and the knowledge of this fact tends to a uniformly better
-performance. The amount of work that can be performed by one man with a
-pick and shovel is as shown in Table 49. Some men may exceed these
-rates, many will not attain them. The allotted task must be gaged on the
-character of the ground in order that the tasks may be equal and a
-spirit of competition fostered. The hard worker will set the pace for
-the lazy man. Some contractors have adopted the expedient of dismissing
-laborers for the day as soon as the allotted task is done.
-
- TABLE 49
-
- AMOUNT OF MATERIAL MOVED BY ONE MAN WITH A PICK AND SHOVEL
-
- (From H. P. Gillette)
- ────────────────────────────────────────┬──────────────────────────────
- Material │ Cubic Yard per hour
- ────────────────────────────────────────┼──────────────────────────────
- Hardpan │ 0.33
- Common earth │ 0.8 to 1.2
- Stiff clay │ 0.85
- Clay │ 1.00
- Sand │ 1.25
- Sandy soil │ 0.8 to 1.2
- Clayey earth │ 1.3
- Sandy soil (frozen) │ 0.75
- ────────────────────────────────────────┴──────────────────────────────
-
-The opening of the trench may be facilitated by breaking ground with a
-plow. In hard ground or on paved roads it may be necessary to cut
-through the surface crust with a hammer and drill, although in some
-cases a plow can be used successfully. Frozen ground can be thawed by
-building fires along the line of the trench, or greater economy may be
-achieved by placing steam pipes along the surface with perforations
-about every 18 inches and either boxing them on the top and sides or
-burying them in the frozen earth with a covering of sand. Another
-arrangement is to blow steam into a line of bottomless boxes in which
-each box is about 8 feet long. Holes are left in the top of the boxes
-into which the pipe is shoved, and after its withdrawal the holes are
-covered. Blasting of frozen earth is sometimes successful but cannot be
-resorted to in built up districts where it is unsafe unless properly
-controlled. Once the frost crust is broken through it can be attacked
-from below and frequently broken down by undermining.
-
-A laborer cannot dig and raise the earth much more than to the height of
-his head, and preferably not quite so high, without tiring quickly.
-After the trench has passed a depth of 4 feet he cannot throw the earth
-clear of the trench. An additional laborer is needed then at the surface
-to throw the earth back. He should shovel the earth from a board
-platform placed at the edge of the trench as a protection to the bank.
-When the trench passes the 6–foot depth a staging is put in about 4 feet
-from the top on which the lowest laborer piles his materials. It is then
-passed up to the surface by a second laborer on the staging, and a third
-laborer on the surface throws the material back clear of the trench.
-Stagings are put in about every 5 or 6 feet for the full depth of the
-trench.
-
-When the trench has come within half the diameter of the pipe of the
-final grade, if the material is sufficiently firm, the remainder of the
-trench should be cut to conform to the shape of the lower half of the
-outside of the pipe, with proper enlargements for each bell.
-
-
-=128. Machine Excavation.=—On work of moderately large magnitude
-excavation by machine is cheaper than by pick and shovel alone. In
-comparing the cost of excavation by the two methods all items such as
-sheeting, pipe laying, backfilling, etc., should be included, since
-these items will be affected by the method of excavation. The cost of
-setting up and reshipping the machine must be included as this is
-frequently the item on which the use of the machine depends. Because of
-the cost of setting up and shipping, which must be distributed over the
-total number of yards excavated, the cost per cubic yard of excavating
-by machine varies with the number of cubic yards excavated. The point of
-economy in the use of a machine is reached when the cost by hand and by
-machine are equal. For all work of greater magnitude, excavation by
-machine will prove cheaper.[81] Items favoring the use of machinery
-which may cause its adoption for small jobs are: its greater speed,
-reliability, ease in handling, economy in sheeting, economy in labor,
-and small amount of space needed making it useful in crowded streets.
-Continuous bucket machines, drag lines, and occasionally steam shovels
-are not adapted to conditions where rocks, pipes and other underground
-obstacles are frequently met.
-
-The following problem is an example of the work necessary in making a
-comparison of the relative economy of machine and hand excavation:
-
- It is assumed that a man can excavate 15 feet of trench 30 inches
- wide and 8 feet deep in 10 hours. He receives 55 cents per hour
- for his work. A machine costing $10,000 has a life of 6 years. It
- can be kept busy 150 days in the year. When operating it costs
- $1.25 per hour for the operator, fuel and repairs. It will
- excavate 800 linear feet of 30 inch trench to a depth of 8 feet in
- 10 hours. It is assumed that capital is worth 10 per cent on such
- a venture and that the sinking fund will draw 10 per cent. If the
- cost of moving and setting up the machine is $1,800, how many
- cubic yards of excavation must there be to make excavation by
- machine economical? Costs of sheeting, pumping, etc., are assumed
- to be the same for machine or hand work.
-
- _Solution._—For hand work the man excavated 1.11 cubic yard per
- hour at 55 cents. The relative cost of hand excavation is then 50
- cents per cubic yard.
-
- The cost of machine work will be divided into: interest on first
- cost; operation and repairs; and sinking fund for renewal. The
- interest on the first cost of $10,000 at 10 per cent is $1,000 per
- year. The machine works 1,500 hours in the year. Therefore the
- cost per hour is $0.67.
-
- The sinking fund payment, as found from sinking fund tables or the
- accumulation of $10,000 in. 6 years, is $1,300 per year or per
- hour for 1,500 hours is $0.87.
-
- The cost of operation per hour is given as $1.25.
-
- The total cost per hour is therefore $2.79.
-
- The machine excavated 59.3 cubic yards per hour which makes the
- cost, exclusive of moving, equal to $0.47 per cubic yard. In order
- to equalize the cost of machine and hand excavation the cost of
- moving the machine must be divided among a sufficient number of
- cubic yards so that the cost per cubic yard shall be 3 cents. The
- cost of moving is given as $1,800. This amount divided among
- 60,000 cubic yards equals 3 cents per cubic yard. Therefore the
- job must provide at least 60,000 cubic yards of excavation in
- order that the use of the machine shall be justifiable from the
- viewpoint of economy alone.
-
-
-=129. Types of Machines.=—Machines particularly adapted to the
-excavation of sewer and water pipe trenches are of four types: (1)
-continuous bucket excavators; (2) overhead cableway or track excavators;
-(3) steam shovels; and (4) boom and bucket excavators. Other types of
-excavating machinery can be used for sewer trenches under special
-conditions. Machines are ordinarily limited to a minimum width of trench
-of 22 inches. Between widths of 22 inches and 36 inches the limit of
-depth for the first class of machines is about 25 feet. For other types
-of machines there is no definite limit, though the economical depth for
-open cut work seldom exceeds 40 feet.
-
-
-=130. Continuous Bucket Excavators.=—Continuous bucket excavators are of
-the types shown in Figs. 89 and 90. The buckets which do the digging and
-raising of the earth may be supported on a wheel as in Fig. 89 or on an
-endless chain as in Fig. 90. The support of the wheel or endless chain
-can be raised or lowered at the will of the operator so as to keep the
-trench as close to grade as can be done by hand work. In some machines
-the shape of the buckets can be made such as to cut the bottom of the
-trench, in suitable material, to the shape of the sewer invert. In
-operation, the buckets are at the rear of the machine and revolve so
-that at the lowest point in their path they are traveling forward. The
-excavated material is dropped on to a continuous belt which throws it on
-the ground clear of the trench, into dump wagons, or on to another
-continuous belt running parallel with the trench to the backfiller, by
-means of which the excavated material is thrown directly into the
-backfill without rehandling. The body of the machine supporting the
-engine travels on wheels ahead of the excavation and is kept in line by
-means of the pivoted front axle. When obstacles are encountered the
-excavating wheel or chain is raised to pass over the obstacle, and
-allowed to dig itself in on the other side.
-
-[Illustration:
-
- FIG. 89.—Buckeye Wheel Excavator.
-
- Courtesy, Buckeye Traction Ditcher Co.
-]
-
-[Illustration:
-
- FIG. 90.—Buckeye Endless-chain Excavator.
-
- Courtesy, Buckeye Traction Ditcher Co.
-]
-
-[Illustration:
-
- FIG. 91.—Movable Sheeting Fastened to Traction Ditcher.
-
- From Eng. News-Record, Vol. 82, 1919, p. 740.
-]
-
-Wheel excavators are not adapted to the excavation of sewer trenches
-over 3 to 4 feet in width and 6 to 8 feet in depth. The endless-chain
-excavators are suitable for depths of 25 feet with widths from 22 to 72
-inches, and due to the arrangement permitting buckets to be moved
-sideways they will cut trenches of different widths with the same size
-buckets. This is an advantage where there are to be irregularities in
-the width of the trench such as for manholes or changes in size of pipe.
-With excavating machines pipe can be laid within 3 feet of the moving
-buckets and the trench backfilled immediately, thus making an
-appreciable saving in the amount of sheeting. In the construction of
-trenches for drain tile at Garden Prairie, Illinois, the sheeting was
-built in the form of a box or shield fastened to the rear of the machine
-and pulled along after it as is shown in Fig. 91.
-
-The performance of this type of excavating machine under suitable
-conditions is large. A remarkable record was made by Ryan and Co. in
-Chicago,[82] with an excavating machine. 1338 feet of 32–inch trench
-were excavated to an average depth of 8½ feet in 7 hours, or an average
-of 160 cubic yards per hour. More could have been accomplished if it had
-not been for delays in supplies. Another crew at Greeley, Colorado,[83]
-with a Buckeye endless-chain ditcher weighing 17 tons and costing $5200,
-averaged 232 cubic yards per day for 300 days, and the cost was 10.7
-cents per cubic yard. A 15–ton Austin excavator can be expected to
-remove 300 to 500 cubic yards per day.
-
-The cost of operation of the machines is made up of items listed in
-Table 50. The figures given are merely suggestive.
-
- TABLE 50
-
- COST OF OPERATING DITCHING MACHINE
-
- ─────────────────────────────────────────────────────────┬──────┬──────
- │ Per │
- │ Day │Total
- ─────────────────────────────────────────────────────────┼──────┼──────
- Labor: │ │
- 1 Operator at $150 per month │ $6.00│
- 1 Assistant Operator at $120 per month │ 4.00│
- 4 laborers at 4.00 per day │ 16.00│
- │——————│
- │ │$26.00
- │ │
- Fuel: │ │
- 20 Gallons of gasoline at 28 cents │ 5.60│ 5.60
- │ │
- Miscellaneous: │ │
- Oil, waste, etc. │ 1.20│
- Repairs and maintenance │ 10.00│
- Interest, 6 per cent on $10,000 for 150 days │ 4.00│
- Depreciation, 200 working days per year and an 8 year │ │
- life │ 11.11│ 26.31
- │——————│——————
- Total cost per day │ │$57.91
- ─────────────────────────────────────────────────────────┴──────┴──────
-
- TABLE 51
-
- COMPARISON OF COST OF HAND EXCAVATION AND MACHINE EXCAVATION WITH
- CONTINUOUS-BUCKET EXCAVATOR
-
- ───────────────────────────┬───────┬───────────────────────────┬───────
- Hand Work │ Per │ Machine Work │ Per
- │ Day, │ │ Day,
- │Dollars│ │Dollars
- ───────────────────────────┼───────┼───────────────────────────┼───────
- Foreman │ 4.00│Engineer │ 4.00
- Timberman │ 3.00│Fireman │ 2.50
- Helper │ 2.50│Coal │ 5.00
- 4 Laborers at $2.00 │ 80.00│Team │ 4.00
- │ │Foreman │ 4.00
- │ │Pipe layer │ 3.00
- │ │Helper │ 2.50
- │ │2 Teams backfilling │ 8.00
- │ │2 Helpers │ 4.00
- │ │Interest, depreciation and │
- │ │ repairs │ 10.00
- │ ——————│ │ ——————
- Total │ 95.00│ Total │ 54.50
- ───────────────────────────┴───────┴───────────────────────────┴───────
-
-In making a comparison of the cost of hand and machine excavation the
-figures given in Table 51 are from “Excavating Machinery” by McDaniel,
-who quotes the cost of machine excavation from the manufacturers of the
-Parsons machine issued as the result of several years’ experience with
-their excavator. In the comparison the hand crew is assumed to dig 315
-linear feet of trench 28 inches wide by 12 feet deep in a day of 10
-hours. This assumes that each man will excavate 7 cubic yards per day.
-The machine is assumed to excavate 250 feet of the same trench. The
-comparison indicates that an excavator will work at about 50 per cent of
-the cost of hand excavation, if the cost of moving the machine is not
-included.
-
-[Illustration:
-
- FIG. 92.—Carson Excavating Machine on Trench Excavation in South
- Milwaukee.
-
- Courtesy, Mr. C. F. Henning.
-]
-
-
-=131. Cableway and Trestle Excavators.=—Cableway and trestle excavators
-are most suitable for deep trenches and crowded conditions. They should
-not be used for trenches much less than 8 feet in depth. They differ
-from the continuous bucket excavators in that the actual dislodgment of
-the material is done by pick and shovel, the excavated material being
-thrown by hand into the buckets of the machine. A machine of the Carson
-type is shown in Fig. 92. The machine consists of a series of
-demountable frames held together by cross braces and struts to form a
-semirigid structure. An I beam or channel extending the length of the
-machine is hung closely below the top of the struts. The lower flange of
-this beam serves as a track for the carriages which carry the buckets.
-All the carriages are attached to each other and to an endless cable
-leading to a drum on the engine. This cable serves to move the buckets
-along the trench. The buckets are attached to another cable which is
-wound around another drum on the engine and serves to lower or raise all
-the buckets at the same time. In operation there are always at least two
-buckets for each carriage, one in the trench being filled and the other
-on the machine being dumped. There should be a surplus of buckets to
-replace those needing repairs.
-
-The machines may be from 200 to 350 feet in length, and the number of
-buckets which can be lifted at one time varies from one to a dozen or
-more. On trenches over 5 to 6 feet in width a double line of buckets is
-sometimes used. The entire machine rests on rollers and straddles the
-trench. It is moved along the trench by its own power, either by gearing
-or chains attached to the wheels, or by a cable attached to a dead-man
-ahead.
-
-The Potter trench machine differs from the Carson in that only 2 buckets
-are used at a time and these are carried on a car which travels on a
-track on top of the trestle. The movement of the buckets and the car are
-controlled by 2 dump men who ride on the car and who can raise or lower
-the buckets independently.
-
-The organization needed to operate these machines is: a lockman who
-locks and unlocks the buckets on the cable, a dumper, as many shovelers
-as there are buckets on the machine, and an engineman who is usually his
-own fireman. From 50 to 400 cubic yards of material can be excavated in
-a day with one of these machines, dependent on the character of the
-material and the depth of the trench. H. P. Gillette in his Handbook of
-Cost Data reports that about 190 cubic yards were excavated per day with
-a Potter machine. The machine was 370 feet long. Six ¾-yard buckets were
-used, 4 in the trench and 2 on the carrier. The trench was 10½ feet wide
-and 18 feet deep in wet sand and soft blue clay. The organization
-consisted of an engineman, a fireman, 2 dumpmen on the carrier, and from
-17 to 21 excavating laborers depending on the kind and the amount of the
-excavation. In general the capacity of such machines is limited by the
-amount of material which can be shoveled into them by hand.
-
-
-=132. Tower Cableways.=—These are essentially of the same class as the
-trestle cableway machines. They differ in that the carriage supporting
-the buckets travels on a cable suspended between 2 towers instead of on
-a track supported on a trestle. As a rule only one bucket is handled in
-the machine at a time. They are used in sewer work only in exceptional
-cases as the towers must be taken down and re-erected each time that
-there is an advance in the trench greater than the distance between the
-towers.
-
-
-=133. Steam Shovels.=—The use of steam shovels for the excavation of
-sewer trenches is becoming more prevalent because of their growing
-dependability and durability as compared with other machines, their
-adaptability for small trenches, and the relatively large number of
-widely different uses to which they can be put. In excavating a trench
-the shovel straddles the trench and runs on tractors, wheels, or rollers
-on either side of it. The shovel cuts the trench ahead of it. As a
-result it is difficult to set sheeting and bracing close to the end of
-the trench while the shovel is operating. Steam shovels are therefore
-not suitable for excavation in unstable material, unless the sheeting is
-driven ahead of the excavation. It is only in the softest ground that
-ordinary wood sheeting can be driven ahead of the excavation. Steel
-sheet piling is more suitable for such use. Fig. 93[84] shows a shovel
-at work on a trench in Evanston, Illinois.
-
-Shovels are equipped with extra long dipper handles to adapt them to
-trench excavation. The dipper handle in the picture is longer than the
-standard for this type of machine. The method of supporting the shovel
-can be seen in the picture under the machine and the method of bracing
-and of finishing the trench by hand work are also shown. The excavated
-material is taken out in the shovel and dropped on the bank or into
-wagons.
-
-The limiting depth to which trenches can be excavated by steam shovels
-is about 20 to 25 feet, where the trench is too narrow for the shovel to
-enter. Wider trenches are cut in steps of about 15 feet, the shovel
-working in the trench for additional depths. Shovels are now made to cut
-trenches as narrow as a man can enter to lay pipe. The greatest width
-that can be cut from one position of the shovel is from 15 to 40 feet,
-dependent on the size of the shovel. Occasionally a combination of a
-drag line and a steam shovel can be used, as on the construction of the
-Calumet sewer in Chicago. On this work the first step was cut by a steam
-shovel. It was followed by a drag line resting on the step thus
-prepared, and excavating the remaining distance to grade. The depth of
-the trench in this work averaged about 25 to 30 feet.
-
-[Illustration:
-
- FIG. 93.—Steam Shovel at Work on Sewer Trench for North Shore
- Intercepting Sewer, Evanston, Illinois.
-]
-
-Steam shovels are rated according to their tonnage and the capacity of
-the dipper in cubic yards. Both are necessary as the size of the dipper
-is varied for the same weight of machine, dependent on the character of
-the material being excavated. For rock the dipper is made smaller than
-for sand. Gillette in his Hand Book of Cost Data gives the coal and
-water consumption of steam shovels as shown in Table 52. The performance
-of steam shovels is recorded in Table 53. The conditions of the work
-have a marked effect on the output of the shovel. A shovel in a thorough
-cut, i.e., in a trench just wide enough for the shovel to turn 180
-degrees but too narrow to run cars or wagons along side of it, will
-perform less than one-half of the work that it can perform in a side
-cut, i.e., where the cars can be run along side the shovel which turns
-less than 90 degrees.
-
- TABLE 52
-
- COAL AND WATER CONSUMPTION BY STEAM SHOVELS
-
- (From Handbook of Cost Data, by H. P. Gillette)
- ───────────────────────────────────┬─────┬─────┬─────┬─────┬─────┬─────
- Weight in tons │ 35 │ 45 │ 55 │ 65 │ 75 │ 90
- Dipper, cubic yards │ 1¼ │ 1½ │ 1¾ │ 2 │ 2½ │ 3
- Coal, tons per 10 hour day │ ¾ │ 1 │ 1¼ │ 1½ │ 2 │ 2¼
- Water, gallons per 10 hour day │1500 │2000 │2500 │3000 │4000 │4500
- ───────────────────────────────────┴─────┴─────┴─────┴─────┴─────┴─────
-
- TABLE 53
-
- PERFORMANCE BY STEAM SHOVELS
-
- ──────┬──────┬──────┬───────┬───────────┬──────┬──────────────┬────────
- Weight│Dipper│Depth │ Width │ 10–Hour │ Cost │ Authority │Remarks
- in │Cubic │ of │of Cut │Performance│ in │ │
- Tons │Yards │ Cut, │ │ │Cents,│ │
- │ │ Feet │ │ │ per │ │
- │ │ │ │ │Cubic │ │
- │ │ │ │ │ Yard │ │
- ──────┼──────┼──────┼───────┼───────────┼──────┼──────────────┼────────
- 25 │ 1 │ 9 │36 in. │ 85 │ 22.6 │R. T. Dana │ 1
- │ │ │ │ │ │ Eng. Rec., │
- │ │ │ │ │ │ 69:581 │
- 25 │ 1 │ 8 │35 in. │ 96 │ 23.5 │ do. │ 2
- 70 │ 2 │ 26 │16 ft. │ 569 │ 6.7 │ do. │ 3
- 30 │ 1 │15–18 │60 in. │ 300 │ │A. B. McDaniel│ 4
- │ │ │ │ │ │ Excavating │
- │ │ │ │ │ │ Machinery │
- 15 │ ⅝ │ 14 │134 ft.│ 400 │ │Eng. Cont’r, │ 5
- │ │ │ │ │ │ 8–25–09 │
- │ 8 │ 36 │ Very │16 yd. cars│ │Marion Steam │ 6
- │ │ │ wide │ │ │ Shovel Co. │
- 55 │ │ │ │ 296 │ │H. P. │ 7
- │ │ │ │ │ │ Gillette’s │
- │ │ │ │ │ │ Cost Data │
- 65 │ 2¼ │ │ │ 280 │ │ do. │
- │ │ │Greater│ 700 │ 30.6 │G. C. D. │ 8
- │ │ │than 78│ │ │ Lenth, Eng. │
- │ │ │ in. │ │ │ News-Record,│
- │ │ │ │ │ │ 85:22 │
- ──────┴──────┴──────┴───────┴───────────┴──────┴──────────────┴────────
-
- Remarks:
-
- 1. One runner at $5.00, one fireman at $2.31, two laborers
- at $1.70 each, supplies at $4.50, and interest and
- depreciation on 200 days per year, $4.00. Total per
- day, $19.21. Material, clay and gravel.
-
- 2. Average of 11 jobs with the same shovel.
-
- 3. Cost per day, one runner at $5.00, one crane-man at $3.60,
- one fireman at $2.00, 7 roller men at $1.50 each, supplies
- $9.00 and interest and depreciation on $9000 at 200 days
- per year $8.00. Total, $38.10.
-
- 4. Hard clay.
-
- 5. Stiff clay for the basement of a building in Chicago.
-
- 6. Stripping ore. This is a maximum record. The average was
- about three hundred and twenty 16 cubic yard cars per day.
-
- 7. Blasted mica-schist.
-
- 8. General average.
-
-
-=134. Drag Line and Bucket Excavators.=—A drag line excavator is shown
-in Fig. 94. The back of the bucket is attached to a drum on the engine
-by means of a cable passing over the wheel in the end of the long boom.
-The front of the bucket is attached by another cable directly to another
-drum on the engine. In operation the bucket is raised by its rear end
-and dropped out to the extremity of the boom. It is then dragged over
-the ground towards the machine, digging itself in at the same time. When
-filled the bucket is raised by tightening up on the two cables, swung to
-one side by means of the movable boom, and dumped.
-
-[Illustration:
-
- FIG. 94.—Drag Line at Work on Trench for Drain Tile.
-]
-
-Drag line excavators will perform as much work as steam shovels under
-favorable conditions. They are less expensive in first cost and
-operation, and are equally reliable but they are not adapted to the more
-difficult situations where steam shovels can be used to advantage. Drag
-lines are suitable only for relatively wide trenches in material
-requiring no bracing, and in a locality where relatively long stretches
-of trench can be opened at one time.
-
-The bucket excavator differs from the drag line in that the bucket can
-be lifted vertically only and the types of buckets used in the two types
-of machine are different. The bucket may be self filling of the
-orange-peel or clam-shell type, or a cylindrical container which must be
-filled by hand. A drag line can be easily converted into a boom and
-bucket excavator. Boom and bucket excavators are well adapted to use in
-deep, closely braced trenches and shafts.
-
-
-=135. Excavation in Quicksand.=[85]—A sand or other granular material in
-which there is sufficient upward flow of ground water to lift it, is
-known as quicksand. Its most important property, from the viewpoint of
-sewer construction, is its inability to support any weight unless the
-sand is so confined as to prevent flowing of the sand, or unless the
-water is removed from the sand.
-
-Excavation in quicksand is troublesome and expensive and is frequently
-dangerous. The material will flow sluggishly as a liquid, it cannot be
-pumped easily, and its excavation causes the sides of the trench to fall
-in or the bottom to rise. The foundations of nearby structures may be
-undermined, causing collapse and serious damage. These conditions may
-arise even after the backfilling has been placed unless proper care has
-been taken. The greatest safeguard against such dangers is not only to
-exercise care in the backfilling to see that it is compactly tamped and
-placed, but to leave all sheeting in position after the completion of
-the work.
-
-The ordinary method of combating quicksand and in conducting work in wet
-trenches is to drive water-tight sheeting 2 or 3 feet below the bottom
-of the trench, and to dewater the sand by pumping. When dry it can be
-excavated relatively easily. A more primitive but equally successful
-method is to throw straw, brickbats, ashes, or other filling material
-into the trench in order to hold the excavation once made, or this may
-supplement the attempts at pumping, or the wet sand may be bailed out in
-buckets. Successful excavation in quicksand requires experience,
-resourcefulness. and a careful watch for unexpected developments. The
-well points described in Art. 142 are used for dewatering quicksand.
-
-
-=136. Pumping and Drainage.=—Ground water is to be expected in nearly
-all sewer construction and provision should be made for its care. Where
-geological conditions are well known or where previous excavations have
-been made and it is known that no ground water exists it may be safe to
-make no provision for encountering ground water. Where ground water is
-to be expected the amount must remain uncertain within certain rather
-wide limits until actually encountered.
-
-In order to avoid the necessity for pumping, or working in wet trenches
-it is sometimes possible to build the sewer from the low end upwards and
-to drain the trench into the new sewer. The wettest trenches are the
-most difficult to drain in this manner as the material is usually soft
-and the water so laden with sediment as to threaten the clogging of the
-sewer. It is undesirable to run water through the pipes until the cement
-in the joints has set. This necessitates damming up the trench for a
-period which may be so long as to flood the trench or delay the progress
-of the work. If it is not possible to drain the trench through the sewer
-already constructed the amount of water to be pumped can be reduced by
-the use of tight sheeting.
-
-[Illustration:
-
- FIG. 95. Improvised Trench Pump.
-]
-
-Pumps for dewatering trenches must be proof against injury by sand, mud,
-and other solids in the water. For this purpose pumps with wide passages
-and without valves or packed joints are desirable. The types of pumps
-used are: simple flap valve pumps improvised on the job, diaphragm
-pumps, jet pumps, steam vacuum pumps, centrifugal pumps, and
-reciprocating pumps. All are of the simplest of their type and little
-attention is paid to the economy of operation because of the temporary
-nature of their service.
-
-
-=137. Trench Pump.=—A simple pump which can be improvised on the job is
-shown in section in Fig. 95. Its capacity is about 20 gallons per minute
-but its operation is backaching work. It is inexpensive, quickly put
-together and may be a help in an emergency. It is to be noted that the
-passages are large and straight, that there are no packed joints, and
-that the velocity of flow is so small that it is not liable to clogging
-by picking up small objects.
-
-[Illustration:
-
- FIG. 96.—Diaphragm Pump
-
- Courtesy, Edson Manufacturing Co.
-]
-
-
-=138. Diaphragm Pump.=—The type of pump shown in Fig. 96 is the most
-common in use for draining small quantities of water from excavations.
-It is known as the diaphragm pump from the large rubber diaphragm on
-which the operation depends. The pump is made of a short cast-iron
-cylinder, divided by the rubber diaphragm or disk to the center of which
-the handle is connected. The valve is shown at the center of the disk.
-As the diaphragm is lifted the valve remains closed, creating a partial
-vacuum in the suction pipe and at the same time discharging the water
-which passed through the valve on the previous down stroke. When the
-valve is lowered the foot valve on the suction pipe closes, holding the
-water in place, and the valve in the pump opens allowing the water to
-flow out on top of the disk to be discharged on the next up stroke.
-Table 54 shows the capacities of some diaphragm pumps as rated by the
-manufacturers. The smaller sizes are the more frequently used and are
-equipped with a 3–inch suction hose with strainer and foot valve. They
-are not adapted to suction lifts over 10 to 12 feet. Where greater lifts
-are necessary one pump may discharge into a tub in which the foot valve
-of a higher pump is submerged.
-
- TABLE 54
-
- CAPACITIES OF DIAPHRAGM PUMPS
-
- ─────────────────┬─────────────────┬─────────────────┬─────────────────
- Diameter of │ Diameter of │Length of Stroke │ Capacity per
- Cylinder, Inches │ Suction, Inches │ in Inches │ Stroke, Gallons
- ─────────────────┼─────────────────┼─────────────────┼─────────────────
- 6│ 3│ 4│ 0.49
- 8½│ 4│ 6│ 1.47
- 9[86]│ 2½│ │ 0.75
- 12½[86]│ 3│ │ 1.25
- │ Power driven by 1 horse-power │
- 12½[86]│ engine │ 0.58[87]
- ─────────────────┴───────────────────────────────────┴─────────────────
-
-[Illustration:
-
- FIG. 97.—McGowan Steam Jet Pump.
-
- Courtesy, The John H. McGowan Co.
-]
-
-
-=139. Jet Pump.=—The simplicity of the parts of the jet pump is shown in
-Fig. 97. It has a distinct advantage over pumps containing valves and
-moving parts in that there are no obstructions offered to the passage of
-solids as well as liquids through the pump. It is not economical in the
-use of steam, however. It operates by means of a steam jet entering a
-pipe at high velocity through a nozzle. This action causes a vacuum
-which will lift water from 6 to 10 feet. The lower the suction lift,
-however, the greater the efficiency of the work. The sizes and
-capacities of jet pumps as manufactured by the J. H. McGowan Co. are
-shown in Table 55.
-
- TABLE 55
-
- CAPACITIES OF JET PUMPS
-
- (J. H. McGowan Co.)
- ──────────────┬─────────────┬─────────────┬─────────────┬──────────────
- Size of Pump │ │ │ Capacity, │ Approximate
- and Suction │ Discharge │ Steam Pipe, │ Gallons per │ Horse-power
- Pipe, Inches │Pipe, Inches │ Inches │ Minute │ Required
- ──────────────┼─────────────┼─────────────┼─────────────┼──────────────
- ¾│ ½│ ⅜│ 8│ 2
- 1│ ¾│ ½│ 15│ 3
- 1¼│ 1│ ½│ 20│ 4
- 1½│ 1¼│ ¾│ 30│ 6
- 2│ 1½│ ¾│ 40│ 8
- 2½│ 2│ 1│ 50│ 10
- 3│ 2½│ 1│ 60│ 15
- 4│ 3½│ 1¼│ 85│ 25
- ──────────────┴─────────────┴─────────────┴─────────────┴──────────────
-
-
-=140. Steam Vacuum Pumps.=—This type of pump depends on the condensation
-of steam in a closed chamber to create a vacuum which lifts water into
-the chamber previously occupied by the steam and from which the water is
-ejected by the admission of more steam. The best known pumps of this
-type are the Pulsometer, manufactured by the Pulsometer Steam Pump Co.,
-the Emerson, manufactured by the Emerson Pump and Valve Co., and the Nye
-Pump, manufactured by the Nye Steam Pump and Machinery Co.
-
-[Illustration:
-
- FIG. 98.—Pulsometer Steam Vacuum Pump.
-]
-
-A section of a Pulsometer is shown in Fig. 98. It consists of two
-bottle-shaped chambers _A_ and _B_ with their necks communicating at the
-top and each opening into the outlet chamber _O_ through a check valve.
-Steam is admitted at the top and enters chamber _A_ or _B_ according to
-the position of the steam valve _C_ as shown. This steam valve is a ball
-which is free to roll either to the right or left and forms a
-steam-tight joint with whichever seat it rests upon. In normal operation
-chamber _A_ would be filled with water as the steam enters the cylinder.
-At the same time a check valve at the top opens to admit a small
-quantity of air which forms a cushion insulating the steam from the
-water, reduces the condensation of the steam, and serves as a cushion
-for the incoming water on the opposite stroke. The pressure of the steam
-depresses the surface of the water without agitation and forces the
-water through the check valve _F_ into the discharge chamber _O_. When
-the water falls to the level of the discharge chamber the even surface
-is broken up and the intimate contact of the steam and water condenses
-the former instantaneously. This forms a vacuum in chamber _A_ which,
-assisted by a slight upward pressure in chamber _B_ caused by the
-incoming water, immediately pulls the ball _C_ over to the other seat
-and directs the steam into chamber _B_. The vacuum in chamber _A_ now
-draws up a new charge of water through the suction pipe into the
-chamber.
-
-[Illustration:
-
- FIG. 99.—Emerson Steam Vacuum Pump.
-]
-
-A section of the Emerson pump is shown in Fig. 99. The pump consists of
-two vertical cylinders _B_ and _C_. Each chamber has a suction valve _L_
-at the bottom, opening upward from a common chamber from which the
-discharge pipe _U_ extends. On the top of each chamber is a baffle plate
-_G_ which operates to distribute the steam evenly to the two chambers
-and to prevent it from agitating the surface of the water in the
-chambers. A condenser nozzle _F_ is connected with the bottom of the
-opposite chamber by a pipe into which a check valve opens upward. As the
-pressure in the chamber alternates water will be injected through _F_
-into the opposite chamber and condense the steam therein, promptly
-forming a vacuum. An air valve _P_ admits a small quantity of air while
-the chamber is filling with water, the air acting as an insulating
-cushion as in the Pulsometer. Valve _O_, just above the top connection
-_S_ is used to regulate the amount of steam that enters the pump. The
-top connection _S_ has two ports, one leading to each chamber. An
-oscillating valve enclosed in it admits the steam through these ports to
-the two chambers alternately. This valve is driven by a small
-three-cylinder engine, the crank shaft of which extends into the top
-connection in the center of the bearing on which the valve oscillates. A
-positive geared connection is made between the valve and the engine and
-so arranged that the engine will run faster than the valve.
-
-The action of these pumps consists of alternately filling and emptying
-the two chambers. They will continue operation without attention or
-lubrication so long as the steam is turned on. In view of the simplicity
-of their operation and make-up, their ability to handle liquids heavily
-charged with solids, and their reasonable steam consumption these pumps
-are widely used for pumping water in construction work. They have an
-added advantage that no foundation or setting is required for them as
-they can be hung by a chain from any available support.
-
-These pumps are manufactured in sizes varying from 25 to 2500 gallons
-per minute at a 25–foot head, and with a steam consumption of about 150
-pounds per horse-power hour. They reduce about 4 per cent in capacity
-for each 10 feet of additional lift. They will operate satisfactorily
-between heads of 5 to 150 feet, with a suction lift not to exceed 15
-feet. Lower suction lifts are desirable and the best operation is
-obtained when the pump is partly submerged. The steam pressure should be
-balanced against the total head. It varies from 50 to 75 pounds for
-lifts up to 50 feet, and increases proportionally for higher lifts. The
-dryer the steam the lower the necessary boiler pressure.
-
-
-=141. Centrifugal and Reciprocating Pumps.=—The details of these pumps,
-their adaptability to various conditions, and their capacities are given
-in Chapter VII. The centrifugal is better adapted to trench pumping as
-it is not so affected by water containing sand and grit, but for clear
-water, high suction lifts and fairly permanent installations,
-reciprocating pumps can be used with satisfaction.
-
-
-=142. Well Points.=—In dewatering quicksand a method frequently attended
-with success is to drive a number of well points into the sand and
-connect them all to a single pump. Figure 100 shows a well point system
-used on sewer work in Indiana. The well points are 3 feet apart and are
-connected to a 2½-inch header which in turn is connected to six Nye
-pumps, each with a capacity of 200 gallons per minute for a lift of 50
-feet. The number and size of well points and pumps to use will depend on
-conditions as met on the job. On a piece of work in Atlantic City[88]
-the equipment consisted of two complete outfits each comprising one
-hundred 1½ inch by 36–inch No. 60 well points, one hundred 6–foot
-lengths of rubber hose, about 600 feet of suction main, one hundred
-valved T connections, and a 7 × 8–inch Gould Triplex Pump with a
-capacity of 200 gallons per minute, belted to a 7½ horse-power motor.
-
-[Illustration:
-
- FIG. 100.—Well Points Pumped by Nye Steam Vacuum Pump.
-]
-
-
-=143. Rock Excavation.=—A common definition of rock used in
-specifications is: whenever the word Rock is used as the name of an
-excavated material it shall mean the ledge material removed or to be
-removed properly by channeling, wedging, barring, or blasting; boulders
-having a volume of 9 (this volume may be varied) cubic feet or more, and
-any excavated masonry. No soft disintegrated rock which can be removed
-with a pick, nor loose shale, nor previously blasted material, nor
-material which may have fallen into the trench will be measured or
-allowed as rock.
-
-Channeling consists in cutting long narrow channels in the rock to free
-the sides of large blocks of stone. The block is then loosened by
-driving in wedges or it is pried loose with bars. It is a method used
-more frequently in quarrying than in trench excavation where it is not
-necessary to preserve the stone intact. In blasting, a hole is drilled
-in the rock, and is loaded with an explosive which when fired shatters
-the rock and loosens it from its position.
-
-[Illustration:
-
- FIG. 101.—Plug and Feathers for Splitting Rock.
-]
-
-In drilling rock by hand the drill is manipulated by one man who holds
-it and turns it in the hole with one hand while striking it with a
-hammer weighing about 4 pounds held in the other hand, or one man may
-hold and turn the drill while one or two others strike it with heavier
-hammers. In churn drilling a heavy drill is raised and dropped in the
-hole, the force of the blow developing from the weight of the falling
-drill. Hand drills are steel bars of a length suitable for the depth of
-the hole, with the cutting edge widened and sharpened to an angle as
-sharp as can be used without breaking. The drill bar is usually about
-⅛th of an inch smaller than the diameter of the face of the drill.
-
-Wedges used are called plugs and feathers. They are shown in Fig. 101
-which shows also the method of their use. The feathers are wedges with
-one round and one flat face on which the flat faces of the plug slide.
-
-
-=144. Power Drilling.=—In power drilling the drill is driven by a
-reciprocating machine which either strikes and turns the drill in the
-hole, or lifts and turns it as in churn drilling, or the drill may be
-driven by a rotary machine which is revolved by compressed air, steam,
-or electricity. There are many different types of machines suitable for
-drilling in the different classes of material encountered and for
-utilizing the various forms of power available.
-
-A jack hammer drill is shown in Fig. 102. In its lightest form the drill
-weighs about 20 pounds and is capable of drilling ⅞-inch holes to a
-depth of 4 feet. Heavier machines are available for drilling larger and
-deeper holes. The same machine can be adapted to the use of steam or
-compressed air. When in use the point of the drill is placed against the
-rock and a pressure on the handle opens a valve admitting air or steam.
-The piston is caused to reciprocate in the cylinder, striking the head
-of the drill at each stroke. The drill is revolved in the hole by hand
-or by a mechanism in the machine. A hollow drill can be used by means of
-which the operator admits air or steam to the hole, thus blowing it out
-and keeping it clean. These machines have the advantage of small size,
-portability and simplicity. They can be easily and quickly set up and
-the drills can be changed rapidly. Their undesirable features are the
-vibration transmitted to the operator and the dust raised in the trench.
-
-[Illustration:
-
- FIG. 102.—Jack Hammer Rock Drill.
-]
-
-[Illustration:
-
- FIG. 103.—Tripod Drill.
-]
-
-A type of drill heavier and larger than the jack hammer drill is shown
-in Fig. 103. It requires some form of support such as a tripod, or in
-tunnel work it can be braced against the roof or sides. Some data on
-steam and air drills are given in Table 56. The effect of the length of
-the transmission pipe, temperature of the outside air, pressure at the
-boiler or compressor, etc., will have a marked effect on the amount of
-steam or air to be delivered to the drill. Compressed air is affected
-more than steam by these outside factors, but it has an advantage in
-that as it loses in pressure it increases in volume so that the loss of
-power is not so marked. Gillette states:
-
- We may assume that a cubic foot of steam will do practically the
- same work in a drill as a cubic foot of compressed air at the same
- pressure, because neither the steam nor the air acts expansively
- to any great extent in a drill cylinder, due to the late cut-off.
- This being so ... one pound of steam is equivalent to nearly 30
- cubic feet of free air ... all at the same pressure of 75 pounds
- per square inch. If a drill consumes at the rate of 100 cubic feet
- of free air per minute ... it would therefore consume 240 pounds
- of steam (at 75 pounds pressure) per hour.... Where not more than
- three or four drills are to be operated, probably no power can
- equal compressed air generated by gasoline. It will require 12
- horse-power to compress air for each drill, hence 1½ gallons of
- gasoline will be required per hour per drill while actually
- drilling.
-
- TABLE 56
-
- DATA ON ROCK DRILLS
-
- (From H. P. Gillette)
- ───────────────────────────────────┬─────┬─────┬─────┬─────┬─────┬─────
- Diameter of cylinder in inches │ 2¼│ 2½│ 2¾│ 3⅛│ 3¼│ 3⅜
- Length of stroke in inches │ 5│ 6│ 6½│ 6⅝│ 6⅝│ 7¼
- Length of drill from end of crank │ │ │ │ │ │
- to end of piston │ 36│ 43│ 50│ 50│ 50│ 52
- Depth of hole drilled without │ │ │ │ │ │
- change of bit, inches │ 15│ 20│ 24│ 24│ 24│ 24
- Diameter of supply inlet. Standard │ │ │ │ │ │
- pipe, inches │ ¾│ ¾│ ¾│ 1│ 1│ 1¼
- Approximate strokes per minute with│ │ │ │ │ │
- 60 pound pressure at the drill │ 500│ 450│ 375│ 350│ 325│ 300
- Depth of vertical hole each machine│ │ │ │ │ │
- will drill easily, feet │ 6│ 8│ 10│ 14│ 16│ 20
- Diameter of holes drilled, inches │ ¾ to 1½ as desired
- Diameter of octagon steel, inches │ ¾ to│ ⅞ to│ 1 to│1⅛ to│1⅛ to│1¼ to
- │ ⅞│ 1│ 1⅛│ 1¼│ 1¼│ 1⅜
- Best size of boiler to give plenty │ │ │ │ │ │
- of steam at high pressure, │ │ │ │ │ │
- horse-power │ 6│ 8│ 8│ 9│ 10│ 12
- Best size of supply pipe to carry │ │ │ │ │ │
- steam 100 to 200 feet, inches │ ¾│ ¾│ ¾│ 1│ 1│ 1¼
- Weight of drill unmounted, with │ │ │ │ │ │
- wrenches and fittings, hot boxed,│ │ │ │ │ │
- pounds │ 128│ 190│ 265│ 315│ 385│ 390
- Weight of tripod, without weights, │ │ │ │ │ │
- not boxed, pounds │ 80│ 160│ 160│ 160│ 210│ 275
- Weight of holding down weights, not│ │ │ │ │ │
- boxed, pounds │ 120│ 270│ 270│ 285│ 330│ 375
- Cubic feet of free air per minute │ │ │ │ │ │
- required to run one drill at 100 │ │ │ │ │ │
- pounds │ 92│ 104│ 126│ 146│ 154│ 160
- ───────────────────────────────────┴─────┴─────┴─────┴─────┴─────┴─────
- For more than one drill, multiply the value in the above line by the
- following factors: For 2 drills, 1.8; 5 by 4.1; 10 by 7.1; 15 by 9.5;
- 20 by 11.7; 30 by 15.8; 40 by 21.4; 70 by 33.2.
-
- Since gasoline air compressors are self regulating, when the drill
- is not using air very little gasoline is burned by the gasoline
- engine driving the compressor. A gasoline compressor possesses
- other very important economic advantages over a small steam-driven
- plant. First, there is the saving in wages of firemen and second,
- there is the saving in hauling and pumping of water and the
- hauling of fuel. The cost of gasoline is often less than the cost
- of coal for operating a small plant.
-
-An electric drill[89] operated on the principle of the solenoid does
-away with motor, valves, pipes, vapor, freezing, and other difficulties
-attendant on the use of steam or air.
-
-The rates of drilling in different classes of rock are shown in Table
-57. Frequent changes of drills and relocation of tripods will materially
-reduce the performance of a drill, for as much as 45 minutes may be lost
-in making a new set up. In this the jack hammer drills show their
-advantage as no time is lost in a set up.
-
- TABLE 57
-
- RATES OF ROCK DRILLING
-
- Rates in Feet per Ten-hour Shift. Vertical Holes 10–20 Feet Deep.
- (From Gillette)
-
- Hard Adirondack granite 48
- Maine and Massachusetts granite 45–50
- Mica-schist of New York City. Possible 60–70
- Mica-schist of New York City. Average 40–50
- Hard, Hudson River trap rock 40
- Soft red sand stone of Northern New Jersey 90
- Hard limestone near Rochester, N. Y 70
- Limestone of Chicago Drainage Canal 70–80
- Douglass, Indiana, syenite. Difficult set ups 36
- Canadian granite on Grand Trunk R. R 30
- Windmill point, Ontario limestone:
- 3⅝-inch drills 75
- 2¾-inch drills 60
- 2¼-inch drills 37
-
-
-=145. Steam or Air for Power=.—The choice between steam or air is
-dependent on the conditions of the work. Steam is undesirable in tunnels
-on account of the heat produced. In open cut work it is at a
-disadvantage because of the loss of power due to radiation from the hose
-or pipe. The life of the hose is not so long as when air is used,
-escaping steam causes clouds of vapor which obscure the work, and
-serious burns may occur due to hot water thrown from the exhaust. It is
-advantageous since leaks may be easily discovered and remedied, it
-requires less machinery than air, and it is sometimes less expensive.
-With compressed air, gasoline or electric motors can be used for
-operating the compressors.
-
- TABLE 58
-
- ROCK BLASTING
-
- (From Gillette)
- ────────────────────┬────────────────────┬─────────┬─────────┬─────────
- Character of │Powder Used per Hole│ │Distance │Distance
- Material │ │Depth of │ Back of │ Hole to
- │ │ Hole, │ Face, │ Hole,
- │ │ Feet │ feet │ feet
- ────────────────────┼────────────────────┼─────────┼─────────┼─────────
- Limestone of Chicago│40 per cent dynamite│ │ │
- Drainage Canal │ │ 12│ 8│ 8
- Sandstone │200 pounds black │ │ │
- │ powder │ 20│ 18│ 14
- Granite │2 pounds 60 per cent│ │ │
- │ dynamite │ 12│ 1½│ 4½ to 5
- Pit mining, │ │ │ │
- Treadwell, Mine, │ │ │ │
- Alaska │ │ 12│ 2½│ 6
- ────────────────────┴────────────────────┴─────────┴─────────┴─────────
-
-
-=146. Depth of Drill Hole.=—The depth of the hole is dependent on the
-character of the work. The deepest holes can be used in open cut work
-where the shattered rock is to be removed by steam shovel. The face can
-be made 10 to 15 feet high. The depth of the hole in center cut tunnel
-facings are from 6 to 10 or even 12 feet. In the bench the depth is
-equal to the height of the bench. In narrow trenches where the rock is
-to be removed by derrick or thrown into a bucket by hand, the hole
-should be sufficiently deep to shatter the rock to a depth of at least 6
-inches below the finished sewer. Frequently shooting to this depth at
-one shot cannot be done due to the built up condition of the
-neighborhood or other local factors. The depth of the hole in trench
-work should not much exceed the distance between holes. Deep holes are
-usually desirable as a matter of economy in saving frequent set ups, but
-the holes cannot be made much over 20 feet in depth without increasing
-the friction on the drill to a prohibitive amount.
-
-
-=147. Diameter of Drill Hole.=—The diameter of the hole should be such
-as to take the desired size of explosive cartridge. The common sizes of
-dynamite cartridges are from ⅞ inch to 2 inches in diameter. In
-drilling, the diameter of the hole is reduced about one-eighth of an
-inch at a time as the drill begins to stick. This reduction should be
-allowed for, and experience is the best guide for the size of the hole
-at the start. In general the softer or more faulty or seamy the rock,
-the more frequent the necessary reductions in size of bit.[90] For hard
-homogeneous rock the holes can be drilled 10 feet or more without
-changing the size of the drill bit.
-
-
-=148. Spacing of Drill Holes.=—The spacing of holes in open cut
-excavation is commonly equal to the depth of the hole. The character of
-the material being excavated has much to do with the spacing of the
-holes. The spacing, diameter and depth of holes used on some jobs is
-shown in Table 58. Gillette states:
-
- It is obviously impossible to lay down any hard and fast rule for
- drill holes. In stratified rock that is friable, and in traps that
- are full of natural joints and seams, it is often possible to
- space the holes a distance apart somewhat greater than their
- depth, and still break the rock to comparatively small sizes upon
- blasting. In tough granite, gneiss, syenite, and in trap where
- joints are few and far between, the holes may have to be spaced 3
- to 8 feet apart regardless of their depth for with wider spacing
- the blocks thrown down will be too large to handle with ordinary
- appliances. Since in shallow excavations the holes can seldom be
- much further apart than one to one and one-half times their depth
- we see that the cost of drilling per cubic yard increases very
- rapidly the shallower the excavation. Furthermore the cost of
- drilling a foot of hole is much increased where frequent shifting
- of the drill tripod is necessary.
-
- The common practice in placing drill holes is to put down holes in
- pairs, one hole on each side of the proposed trench; and if the
- trench is wide one or more holes are drilled between these two
- side holes[91] but in narrow trench work, such as for a 12–inch
- pipe, one hole in the middle of the trench will usually prove
- sufficient.
-
-The holes are spaced about 3 feet apart longitudinally. After the holes
-have been completed they should be plugged to keep out dirt and water.
-
-
- SHEETING AND BRACING
-
-
-=149. Purposes and Types.=—Sheeting and bracing are used in trenching to
-prevent caving of the banks and to prevent or retard the entrance of
-ground water. The different methods of placing wooden sheeting are
-called stay bracing, skeleton sheeting, poling boards, box sheeting, and
-vertical sheeting. Steel sheeting is usually driven to secure
-water-tightness and if braced the bracing is similar to the form used
-for vertical wooden sheeting.
-
-
-=150. Stay Bracing.=—This consists of boards placed vertically against
-the sides of the trench and held in position by cross braces which are
-wedged in place. The purpose of the board against the side of the trench
-is to prevent the cross brace from sinking into the earth. The boards
-should be from 1½ × 4 inches to 2 × 6 inches and 3 to 4 feet long. The
-cross braces should not be less than 2 × 4 inches for the narrowest
-trenches and larger sizes should be used for wider trenches. The spacing
-between the cross braces is dependent on the character of the trench and
-the judgment of the foreman. Stay bracing is used as a precautionary
-measure in relatively shallow trenches with sides of stiff clay or other
-cohesive material. It should not be used where a tendency towards caving
-is pronounced. Stay bracing is dangerous in trenches where sliding has
-commenced as it gives a false sense of security. The boards and cross
-braces are placed in position after the trench has been excavated.
-
-
-=151. Skeleton Sheeting.=—This consists of rangers and braces with a
-piece of vertical sheeting behind each brace. A section of skeleton
-sheeting is shown in Fig. 104 with the names of the different pieces
-marked on them. This form of sheeting is used in uncertain soils which
-apparently require only slight support, but may show a tendency to cave
-with but little warning. When the warning is given vertical sheeting can
-be quickly driven behind the rangers and additional braces placed if
-necessary. The sizes of pieces, spacing and method of placing should be
-the same as for complete vertical sheeting in order that this may be
-placed if necessary.
-
-
-=152. Poling Boards.=—These are planks placed vertically against the
-sides of the trench and held in place by rangers and braces. They differ
-from vertical sheeting in that the poling board is about 3 or 4 feet
-long. It is placed after the trench has been excavated; not driven down
-with the excavation like vertical sheeting. An arrangement of poling
-boards is shown in Fig. 105. This type of support is used in material
-that will stand unsupported for from 3 to 4 feet in height. Its
-advantages lie in that no driving is necessary, thus saving the trench
-from jarring; no sheeting is sticking above the sides of the trench to
-interfere with the excavation; and only short planks are necessary.
-
-[Illustration:
-
- FIG. 104.—Skeleton Sheeting.
-]
-
-[Illustration:
-
- FIG. 105.—Poling Boards.
-
- Showing Different Types of Cross Bracing.
-]
-
-The method of placing poling boards is as follows: Excavate the trench
-as far as the cohesion of the bank will permit. Poling boards, 1½ inch
-to 2 inch planks, 6 inches or more in width, are then stood on end at
-the desired intervals along each side of the trench for the length of
-one ranger. The poling boards may be held in place by one or two
-rangers. Two are safer than one but may not always be necessary. If one
-ranger is to be used it is placed at the center of the poling board.
-After the poling boards are in position the rangers are laid in the
-trench and the cross braces are cut to fit. If wedges are to be used for
-tightening the cross braces, the cross braces are cut about 2 inches
-short. If jacks are to be used the braces are cut short enough to
-accommodate the jacks when closed, or adjustable trench braces may be
-used as shown in Fig. 106. The use of extension braces saves the labor
-of fitting wooden braces. With everything in readiness in the trench,
-the cross brace is pressed against the ranger which is thus held in
-place. The wedge or jack is then tightened holding the poling boards and
-cross brace in position.
-
-[Illustration:
-
- FIG. 106.—Box Sheeting.
-
- Showing Different Types of Cross Bracing.
-]
-
-
-=153. Box Sheeting.=—Box sheeting is composed of horizontal planks held
-in position against the sides of the trench by vertical pieces supported
-by braces extending across the trench. The arrangement of planks and
-braces for box sheeting is shown in Fig. 106. This type of sheeting is
-used in material not sufficiently cohesive to permit the use of poling
-boards, and under such conditions that it is inadvisable to use vertical
-sheeting which protrudes above the sides of the trench while being
-driven. This sheeting is put in position as the trench is excavated. No
-more of the excavation than the width of three or four planks need be
-unsupported at any one time. In placing the sheeting the trench is
-excavated for a depth of 12 to 24 inches. Three or four planks are then
-placed against the sides of the trench and are caught in position by a
-vertical brace which is in turn supported by a horizontal cross brace.
-
-[Illustration:
-
- FIG. 107.—Vertical Sheeting.
-]
-
-
-=154. Vertical Sheeting.=—This is the most complete and the strongest of
-the methods for sheeting a trench. It consists of a system of rangers
-and cross braces so arranged as to support a solid wall of vertical
-planks against the sides of the trench. An arrangement of complete
-vertical sheeting is shown in Fig. 107. This type can be made nearly
-water-tight by the use of matched boards, Wakefield piling, steel
-piling, etc. Wakefield piling is made up of three planks of the same
-width and usually the same thickness. They are nailed together so that
-the two outside planks protrude beyond the inside one on one side, and
-the inside one protrudes beyond the two outside ones on the other side
-as shown in Fig. 108. The protruding inside plank forms a tongue which
-fits into the groove formed by the protruding outside planks of the
-adjacent pile.
-
-[Illustration:
-
- FIG. 108.—Wakefield Sheet Piling.
-]
-
-[Illustration:
-
- FIG. 109. Section through Malleable Steel Driving Cap.
-]
-
-In placing vertical sheeting the trench is excavated as far as it is
-safe below the surface. Blocks of the same thickness as the sheeting are
-then placed against the bank at the middle and at the ends of two
-rangers on opposite sides of the trench. The ranger rest against blocks,
-and are held away from the sides of the trench by them. Cross braces are
-next tightened into position opposite the blocks to hold the rangers in
-place. After the skeleton sheeting is in place the planks forming the
-vertical sheeting are put in position with a chisel edge cut on the
-lower end of the plank, with the flat side against the bank. The planks
-should be driven with a maul, the edge of the plank following closely
-behind the excavation. In relatively dry work the driving of the plank
-is facilitated by excavating beneath the edge as it is driven. The upper
-end of the sheeting should be protected by a malleable steel or iron cap
-to prevent brooming of the lumber. A cap is shown in Fig. 109. A sledge
-hammer may be used for driving when the lumber is protected. If the
-sheeting is to start at the surface and is to be driven by hand, the
-first length should not exceed 4 feet unless a platform is erected for
-the driver. Succeeding lengths may be longer, the driver standing on
-planks supported on the cross braces in the trench. Steam hammers and
-pile drivers are sometimes used for driving sheeting.
-
-The framework of the sheeting should be placed with a cross brace for
-each end of each ranger and a cross brace for the middle of each ranger.
-If the ends of two rangers rest on the same cross brace an accident
-displacing one ranger will be passed on to the next and might cause a
-progressive collapse of a length of trench, whereas the movement of an
-independently supported ranger should have no effect on another ranger.
-The cross braces should have horizontal cleats nailed on top of them as
-shown in Fig. 107 to prevent the braces from being knocked out of place
-by falling objects. In driving vertical sheeting a vacant place will be
-left behind each cross brace corresponding to the original block placed
-to hold the ranger away from the bank. This is an undesirable feature in
-the use of vertical sheeting. It is ordinarily remedied by slipping in
-planks the width of the slot and wedging or nailing them against the
-convenient cross bracing. In extremely wet trenches, after all other
-pieces of vertical sheeting are in place, the original cleat behind the
-cross brace can be knocked out and a piece of sheeting slipped into this
-opening and driven. Care must be taken in this event not to drive the
-rangers down when driving the sheeting. If the bracing begins to drop,
-it should be supported by vertical pieces between the rangers and
-resting on a sill at the bottom of the trench.
-
-[Illustration:
-
- FIG. 110.—Steel Clamp for Pulling Wood Sheeting.
-]
-
-
-=155. Pulling Wood Sheeting.=—Wood sheeting is pulled after the
-completion of the trench by a device shown in Fig. 110. In wet trenches
-where the removal of the sheeting would permit a movement of the banks,
-resulting in danger to the sewer or other structures, the sheeting
-should be left in place in the trench. If sufficient saving can be made
-the sheeting is cut off in the trench immediately above the danger line,
-usually the ground water line. The cutting is done with an axe or by a
-power driven saw devised for the purpose.
-
-
-=156. Earth Pressures.[92]=—The various theories of earth pressure are
-so conflicting in their conclusions as to be confusing. Rankine’s
-theory, the most frequently used, assumes that the pressure increases
-with the depth, whereas Meem’s theory[93] leads to an opposite
-conclusion. The discussion following Meem’s article is very
-illuminating. It indicates that no matter how good the theory, practical
-experience together with the use of generous sizes and close spacing are
-the best guides for bracing trenches and coffer dams. All are not
-possessed with the desired practical experience and some basis on which
-to commence work is essential. Another factor affecting computations of
-sizes based on theory is the tendency in practice to use the same size
-material for rangers and braces on any one job for all except very deep
-trenches and other special cases. Occasionally where there is an
-independent brace for each end of each ranger, the brace is made
-thinner, but is of the same depth as the ranger.
-
-The application of Rankine’s theory of earth pressure to the computation
-of the sizes of rangers and braces will be shown. His formula for the
-active earth pressure against a retaining wall is:
-
- _P_ = _wh_ cosθ (cos θ − √(cos^2 θ − cos^2 φ))⁄(cos θ + √(cos^2 θ −
- cos^2 φ))
-
- in which _w_ = the weight of earth in pounds per cubic foot;
-
- _h_ = depth in feet at point at which pressure is to be
- determined;
-
- θ = the angle of surcharge, or the angle which the surface
- makes with the horizontal;
-
- φ = the angle of repose of the earth. Usually taken as
- 33°–41′ = 1½ horizontal to 1 vertical;
-
- _P_ = the intensity of pressure in pounds per square foot on
- a vertical plane in a direction parallel to the
- surface of the ground.
-
-In studying the pressures for trenches the surface of the ground will be
-assumed as horizontal and the formula reduces to
-
- _P_ = (1 − sin φ)⁄(1 + sin φ)_wh_.
-
-
-=157. Design of Sheeting and Bracing=.—The trench shown in Fig. 111 is
-assumed to be constructed in moist sand weighing 110 pounds per cubic
-foot, with an angle of repose of 30 degrees. The material used for
-sheeting and bracing is yellow pine. The steps taken in the design of
-the sheeting and bracing for this trench are as follows:
-
-[Illustration:
-
- FIG. 111.—Diagram for the Design of Wood Sheeting.
-]
-
-1. _Earth Pressure._—Substituting the units given in the data, in
-Rankine’s formula for earth pressures,
-
- _P_ = 36.7_h_.
-
-Because the earth has been freshly cut and will not be kept open long
-enough to break up the cohesiveness of the banks it is customary to
-reduce the assumed pressure by dividing by 2, 3, or 4, according to the
-natural cohesiveness of the material. The cohesiveness of sand is not
-great, therefore the pressure will be assumed as one-half of the amount
-given by the formula, or
-
- _p_ = 18_h_.
-
-2. _Thickness of Sheeting and Spacing of Rangers._—It is desirable to
-use the same thickness of sheeting throughout the depth of the trench.
-Computations should therefore be commenced at the bottom of the trench
-where the pressures are the greatest and the thickest sheeting will be
-required. It is necessary to determine by trial a spacing for the
-rangers and a thickness of sheeting so that the sheeting is stressed to
-its full working strength. Having determined the thickness of the
-sheeting at the bottom, the remainder of the computations consists in
-determining the spacing of the rangers.
-
-In the example the lower ranger will be assumed as 3 feet from the
-bottom of the trench and the distance to the next ranger as 4 feet.
-
- The intensity of pressure at 22 feet 9 inches is 409.5 pounds per
- square foot.
-
- The intensity of pressure at 26 feet 9 inches is 481.5 pounds per
- square foot.
-
-The distribution of pressures is shown by the diagram on Fig. 111. The
-maximum bending moment is slightly below the point midway between the
-rangers and for a 12–inch strip is 10,500 inch-pounds.
-
-Assuming 3 inch sheeting the maximum fiber stress is:
-
- _f_ = _Mc_⁄_I_ = (10,400 × 1.5 × 12)⁄12 × 27 = 568 pounds per square
- inch.
-
-The working strength of yellow pine as given in Table 59, is 1200 pounds
-per square inch. Thinner sheeting should therefore be used.
-
- TABLE 59
-
- WORKING UNIT STRESSES FOR TIMBER
-
- The most used value in the Building Codes of Baltimore, Boston,
- Cincinnati, Chicago, District of Columbia, and New York City
- ─────────────┬────────┬───────────┬───────────┬──────────┬──────┬──────
- Wood │ │ │ │ │Shear │Shear
- │ │ │ │ │ With │Across
- │ │ │Compression│Transverse│Grain,│Grain,
- │Tension,│Compression│ Across │ Bending, │ lb. │ lb.
- │lb. sq. │With Grain,│Grain, lb. │ lb. sq. │ sq. │ sq.
- │ in. │lb. sq. in.│ sq. in. │ in. │ in. │ in.
- ─────────────┼────────┼───────────┼───────────┼──────────┼──────┼──────
- Yellow pine │ 1200│ 1000│ 600│ 1200│ 70│ 500
- White pine │ 800│ 800│ 400│ 800│ 40│ 250
- Spruce and │ │ │ │ │ │
- Va. pine. │ 800│ 800│ 400│ 800│ 50│ 320
- Oak │ 1000│ 900│ 800│ 1000│ 100│ 600
- Hemlock │ 600│ 500│ 500│ 600│ 40│ 275
- Chestnut │ 600│ 500│ 1000│ 800│ │ 150
- Locust │ │ 1200│ 1000│ 1200│ 100│ 720
- ─────────────┴────────┴───────────┴───────────┴──────────┴──────┴──────
- As published in American Civil Engineers Pocket Book.
-
-Assuming 2–inch sheeting, the fiber stress is 1,300 pounds per square
-inch. This stress is too large. By reducing the ranger spacing slightly
-the stress can be brought within the required limits.
-
-Assuming a ranger spacing of 3 feet 9 inches the depth to the upper
-ranger is changed to 23 feet and the maximum stress in the 2–inch
-sheeting becomes 1,140 pounds per square inch, a satisfactory result.
-The results for the computations for the other ranger spacings are shown
-in Table 60. The spacing of the rangers at the sheeting junctions is
-controlled by convenience and is not computed so long as it is obviously
-safe.
-
-3. _Size of Rangers._—The rangers will be assumed as 16 feet long with
-two end cross braces and one intermediate cross brace for each ranger.
-Starting as before at the bottom of the trench.
-
- The area of the panel below the ranger and between cross
- braces is 24 square feet.
-
- The average intensity of pressure is 28.25 × 18 = 508.5
- pounds per square inch.
-
- The load transmitted to the ranger is 6,000 pounds.
-
- Similarly the load transmitted to the ranger from the
- panel above is 6,890 pounds.
-
- The total distributed load on the ranger is 12,890 pounds.
-
-If _b_ is the vertical dimension of the ranger and _d_ is the horizontal
-dimension in inches, then from the beam theory, using _f_ as 1,200
-pounds per square inch, _bd_^2 = _M_⁄200, in which _M_ is expressed in
-inch-pounds. The maximum bending moment is
-
- (_Wl_)⁄8 = 12,200 × 8 × 12⁄8 = 155,000 inch-pounds
-
- Therefore, _bd_^2 = 775.
-
-An 8 × 10 inch beam will fulfill the conditions closely. Substituting
-these dimensions in the beam formula
-
- _f_ = (_Mc_)⁄_I_ = (155,000 × 5 × 12)⁄8 × 1000
-
-= 1,160 pounds per square inch tension in outer fiber. The results of
-the computations for other rangers are shown in Table 60.
-
-4. _Size of Cross Braces._—The cross braces act as columns. The
-dimensions of the cross braces are determined by trial in such a manner
-that the vertical dimension of the brace is equal to the vertical
-dimension of the ranger and the compressive stress in pounds per square
-inch is computed from the expression,
-
- _S_ ⪙ _S__{1}(1 − _l_⁄(60_d_)),[94]
-
- TABLE 60
-
- COMPUTATIONS FOR SHEETING AND BRACING FOR TRENCH SHOWN IN FIG. 111
-
- Material is moist sand weighing 110 pounds per cubic foot, with an angle of
- repose of 30°. Lumber is yellow pine, with working stress as given in Table
- 59. Working stresses for columns given as _S_(1 − _l_⁄(60_d_)).
- ──────────────────────────────┬───────────────────────────────────────────────
- Sheeting 2 inches × 12 Inches │ Cross Braces
- ──────────┬───────────┬───────┼───────────┬──────┬──────┬──────────┬──────────
- │ │Maximum│ │ │ │ │
- │ │ Fiber │ │ │ │ │
- │ │Stress,│ │ │ │ Actual │Allowable
- │ Maximum │Pounds │ │ │ │Intensity,│Intensity,
- │ Bending │ per │ │Total │ │Pounds per│Pounds per
- │ Moment, │Square │ Depth and │Load, │Size, │ Square │ Square
- Depth │Inch-Pounds│ Inch │Description│Pounds│Inches│ Inch │ Inch
- ──────────┼───────────┼───────┼───────────┼──────┼──────┼──────────┼──────────
- │ │ │end at 26′│ │ │ │
- 23′–26.75′│ 9100│ 1140│ 9″│ 6,445│ 4 × 8│ 202│ 784
- │ │ │int. at 26′│ │ │ │
- 19′–23′│ 8800│ 1100│ 9″│12,890│ 4 × 8│ 403│ 784
- │ │ │end at 23′│ │ │ │
- 13′–17.5′│ 8550│ 1070│ 0″│ 6,393│ 4 × 8│ 200│ 784
- │ │ │int. at 23′│ │ │ │
- 8′–13′│ 7160│ 900│ 0″│12,785│ 4 × 8│ 400│ 784
- │ │ │end at 19′│ │ │ │
- 0′–6′│ 3000│ 375│ 0″│ 3,930│ 4 × 8│ 123│ 784
- │ │ │int. at 19′│ │ │ │
- │ │ │ 0″│ 7,860│ 4 × 8│ 240│ 784
- │ │ │end at 17′│ │ │ │
- │ │ │ 6″│ 3,566│ 4 × 8│ 112│ 684
- │ │ │int. at 17′│ │ │ │
- │ │ │ 6″│ 7,132│ 4 × 8│ 224│ 684
- │ │ │end at 13′│ │ │ │
- │ │ │ 0″│ 4,385│ 4 × 8│ 137│ 684
- │ │ │int. at 13′│ │ │ │
- │ │ │ 0″│ 8,770│ 4 × 8│ 274│ 684
- │ │ │end at 8′│ │ │ │
- │ │ │ 0″│ 2,270│ 4 × 6│ 96│ 687
- │ │ │int. at 8′│ │ │ │
- │ │ │ 0″│ 4,540│ 4 × 6│ 189│ 667
- │ │ │end at 6′│ │ │ │
- │ │ │ 0″│ 1,344│ 4 × 6│ 60│ 584
- │ │ │int. at 6′│ │ │ │
- │ │ │ 0″│ 2,687│ 4 × 6│ 112│ 584
- │ │ │end at 0′│ │ │ │
- │ │ │ 0″│ 432│ 4 × 6│ 18│ 584
- │ │ │int. at 0′│ │ │ │
- │ │ │ 0″│ 863│ 4 × 6│ 36│ 584
- ──────────┴───────────┴───────┴───────────┴──────┴──────┴──────────┴──────────
-
- Rangers
- ──────┬──────┬─────────┬──────┬────────────────────┬──────┬───────────┬───────
- │ Area │ │ │ │ │ │
- │ of │Intensity│ │ │ │ │
- │Panel │ of │ │ │ │ │Maximum
- │Below │Pressure,│ │ │ │ Maximum │Stress
- │ this │ Pounds │Total │ │ │ Bending │Pounds
- │Depth,│ per │ Load │ │ │ Moment in │ per
- │Square│ Square │ in │Load Transmitted to │Size, │ Thousand │Square
- Depth │ Feet │ Inch │Pounds│the Ranger from the │Inches│Inch-Pounds│ Inch
- ──────┼──────┼─────────┼──────┼──────┬──────┬──────┼──────┼───────────┼───────
- │ │ │ │Panel │Panel │ Both │ │ │
- │ │ │ │Below │Above │Panels│ │ │
- ──────┼──────┼─────────┼──────┼──────┼──────┼──────┼──────┼───────────┼───────
- 26′ 9″│ 24│ 508.5│12,200│ 6000│ 6890│12,890│8 × 10│ 155│ 1160
- 23′ 0″│ 30│ 448│13,440│ 6545│ 6240│12,785│8 × 10│ 153│ 1150
- 19′ 0″│ 32│ 378│12,100│ 5860│ 2000│ 7,860│8 × 10│ 94.3│ 708
- 17′ 6″│ 12│ 328.5│ 3,942│ 1942│ 5190│ 7,132│8 × 10│ 85.6│ 636
- 13′ 0″│ 36│ 274.5│ 9,880│ 4690│ 4080│ 8,770│8 × 10│ 105│ 790
- 8′ 0″│ 40│ 189│ 7,560│ 3480│ 1060│ 4,540│6 × 8│ 54.4│ 850
- 6′ 0″│ 16│ 126│ 2,020│ 960│ 1727│ 2,687│6 × 8│ 32.2│ 503
- 0′ 0″│ 48│ 54│ 2,590│ 863│ 0│ 863│6 × 8│ 10.4│ 161
- ──────┴──────┴─────────┴──────┴──────┴──────┴──────┴──────┴───────────┴───────
-
- in which _S_ = permissible crushing across the grain in a column whose
- length is greater than 15 diameters;
-
- _S__{1} = unit working compressive strength of wood;
-
- _l_ = length of the column;
-
- _d_ = smallest dimension of the column;
-
- _l_ and _d_ are in the same units.
-
-The lower intermediate cross brace supports a length of 8 feet of the
-lower ranger on which the load has been found to be 12,890 pounds. The
-load on the end cross brace for the same ranger is one-half of this or
-6,445 pounds. The length of each brace is 4 feet 4 inches. From Table
-59, _S__{1} is 1,000 pounds per square inch. From the column formula,
-_S_ is 784 pounds per square inch.
-
-A 4 × 8 inch cross brace is the smallest that is feasible. This is
-stressed only 12,890 pounds or 403 pounds per square inch, which is well
-within the permissible limits. The results of the other computations for
-cross braces are shown in Table 60.
-
-
-=158. Steel Sheet Piling.=—This is coming into more general use with the
-increased cost of lumber and better acquaintance with its superiority
-over wood under many conditions. Although its first cost is higher than
-that of wood, the fact that with proper care it can be used almost an
-indefinite number of times renders it economical to contractors who may
-have an opportunity to make repeated use of it. The life of good yellow
-pine sheeting with the best of care may be as much as three or four
-seasons. With no particular care it will be destroyed at the first
-using. Fig. 112 shows various sections of steel piling used for trench
-sheeting. These forms are practically water-tight and aid materially in
-maintaining dry trenches. The piling can be made water tight by slipping
-a piece of soft wood between the steel sections when they are being
-driven, or by pouring in between the piles some dry material which will
-swell when wet. The piling is generally driven by a steam hammer and is
-pulled by attaching a ring through a bolt hole in the pile, or by
-grasping the pile with a clutch that tightens its grasp as the pull
-increases. An inverted steam hammer attached to the pile is sometimes
-used in pulling it. The impulses of the hammer together with a steady
-pull on the cable serve to drag out the most stubborn piece of piling.
-
-[Illustration:
-
- FIG. 112.—Sections of Lackawanna Steel Sheet Piling.
-]
-
-
- LINE AND GRADE
-
-
-=159. Locating the Trench.=—In order to locate a trench a line of stakes
-should be driven at about 50–foot intervals along the center line of the
-proposed sewer before excavation is commenced. Reference stakes or
-reference points to this line are located at some fixed offset or easily
-described point, or the stakes marking the center line of the trench may
-be driven at some constant offset distance one side of the trench, in
-order to avoid danger of loss or disturbance of the stakes. Grade or cut
-is seldom marked on the line of preliminary stakes, although the
-approximate cut may be indicated.
-
-For hand excavation the foreman lays out the trench from these stakes.
-In machine work the operator guides the machine so as to follow the line
-of the stakes.
-
-
-=160. Final Line and Grade.=—After the excavation of the trench has
-proceeded to within a foot or two of the final depth, the grade and line
-are transferred to markers supported over the center of the trench. The
-markers are horizontal boards spanning the trench and held in position
-either by nails driven into stakes at the side of the trench, by nails
-driven into the sheeting, or by weights holding the boards on the
-ground. Two stakes driven in the ground at the side of the trench as
-shown in Fig. 113 are the common method of support. If the banks are too
-weak to stand under the jarring of the driving of the stakes, or
-pavement or other causes prevent their use the horizontal cross piece
-may be weighted down by bricks or a bank of earth. The cross pieces are
-located about every 25 feet along the trench and at any convenient
-distance above the surface of the ground. The nearer the ground the
-stronger the support but the greater the interference with work in the
-trench. The center line of the sewer is marked on the cross pieces after
-they are set, and vertical struts are nailed on them with one edge of
-the strut straight, vertical, and on the center line as shown in Fig. 1.
-The corresponding edge should be used on all struts in order to avoid
-confusion. The edge is placed in a vertical position by means of a plumb
-bob or carpenter’s level.
-
-[Illustration:
-
- FIG. 113.—Methods for the Support of the Grade Line.
-]
-
-The cut to the invert of the sewer is recorded to an even number of feet
-where practicable by driving a nail in the upright strut so that the top
-edge of the nail is at the desired elevation above the sewer, or the
-upright is nailed with its top at the proper number of feet above the
-sewer invert. The cut is marked on the upright in feet, tenths, and
-hundredths from the recorded point to the elevation of the invert.
-
-The inspector should watch these grade markers with care by sighting
-back along them to see that they are in line and have not moved. In
-quicksand or caving material the marks may move during the setting of
-the pipes and the levelman should be on the job constantly.
-
-When excavation is being done by machine the depth of the excavation is
-controlled by the operator who maintains a sighting rod on the machine
-in line with the grade marks on the uprights.
-
-[Illustration:
-
- FIG. 114.—Diagram Showing the Use of the Grade Rod for Fixing the
- Elevation of a Sewer.
-]
-
-
-=161. Transferring Grade and Line to the Pipe.=—In transferring grade
-and line to the sewer a light strong string is stretched tightly from
-nail to nail on the uprights marking the line and grade. A rod with a
-right angle projection at the lower end, as shown in Fig. 114, is marked
-with chalk or a notch at such a distance from the end that when the mark
-is held on the grade cord the lower portion of the rod which projects
-into the pipe will rest on the invert. The pipe is placed in line by
-hanging a plumb bob so that the plumb bob string touches the grade and
-center line cord. These marks are taken only as frequently as may be
-necessary to keep the sewer in line. An experienced workman can maintain
-the line by eye for considerable distances. Measurements should never be
-taken to the top of the pipe in order to determine position and grade as
-the variations in the diameter of the pipe may cause appreciable errors.
-
-The position and elevation of the forms for brick, concrete, and unit
-block sewers are located by reference to the grade line, or they may be
-placed under the immediate direction of the survey party, or by
-specially located stakes. For large sewers requiring deep and wide
-excavation the grade and line stakes are driven in the bottom of the
-trench about a foot above the finished grade. This requires the constant
-presence of an engineer who is usually available on work of such
-magnitude.
-
-
-=162. Line and Grade in Tunnel.=—In tunnels, line and grade are given by
-nails driven in the roof, the progress of excavation or the shield being
-followed by eye and the forms set by direct measurement to the nails.
-
-
-
-
- TUNNELING
-
-
-=163. Depth.=—The depth at which it becomes economical to tunnel depends
-mainly upon the character of the material to be excavated and on the
-surface conditions. In soft dry material with unobstructed working space
-at the surface, open cut may be desirable to depths as great as 35 or 40
-feet. Tunnels are cut in rock at depths of 15 feet or less. In some very
-wet and running quicksand encountered in the construction of sewers for
-the Sanitary District of Chicago it was found economical to tunnel at
-depths of 20 feet and less. Crowded conditions on the surface, expensive
-pavements, or extensive underground structures near the surface may make
-it advantageous to tunnel at shallower depths than would otherwise be
-economical. Winter is the best season for tunneling as the workmen are
-protected from the elements and labor is more plentiful.
-
-
-=164. Shafts.=—In sinking a shaft in soft material, the excavation is
-usually done by hand, the material being thrown into a bucket which is
-hoisted to the surface and dumped. The size of the shaft is independent
-of the size of the sewer and depends principally on the machinery which
-it is necessary to lower into the tunnel. Ordinarily a shaft 6 feet in
-the clear is satisfactory. A method of timbering a shaft is shown in
-Fig. 115. Because of the timbering the shaft must be started
-sufficiently large at the top to finish with the desired dimensions at
-the bottom. This excess size is sometimes obviated by driving the
-sheeting at an angle to maintain the same size of shaft from top to
-bottom.
-
-In timbering a shaft as shown in Fig. 115 the upper frame is staked
-securely in position at the surface of the ground. This frame is
-composed of timbers fastened together in the form of a square with the
-ends of the timbers extending about 12 inches on all sides. The
-protruding ends are used to hold the frame in position. Excavation is
-begun inside the frame, and sheeting is driven around the outside of it
-as excavation progresses. Only two or three men can work advantageously
-at one time in these small shafts. The second frame is made up of the
-same size timbers, but all are cut off flush with the outside of the
-square. The outside dimensions of this frame are such as to allow
-sheeting to be slipped in between it and the sheeting already driven.
-The frame is lowered into position and supported from the upper frame by
-vertical struts nailed to it. The lower end of the sheeting already
-driven is held out from the lower frame by blocks of the thickness of
-the next length of sheeting. These blocks are removed as the next length
-of sheeting is placed and driven. The driving of the sheeting is
-facilitated by excavating beneath it as it descends.
-
-[Illustration:
-
- FIG. 115.—Section of Shaft Timbering.
-
- Abbot, Journal Western Society of Engineers, Vol. 22.
-]
-
-The sizes of sheeting and timbering should be computed on the same basis
-as that for trench sheeting except that for depths greater than 30 to 35
-feet Rankine’s Theory is not applicable and judgment must be relied on
-for computing the sizes for deep shafts. In stiff dry material the
-pressures will change very little as the depth increases. Sheeting is
-needed in shaft excavation in rock only to protect the workmen from
-falling fragments, but in sand, particularly in quicksand and in wet
-ground, the pressures increase directly with the depth and the sheeting
-should be computed accordingly. Care must be taken to prevent the
-formation of cavities behind the sheeting, to fill them if formed, and
-to see that all pieces of the sheeting and bracing have a firm bearing.
-It is difficult to prevent the collapse of the shaft once the movement
-of earth against the sheeting has commenced.
-
-Shafts are also sunk in soft ground by constructing a concrete or metal
-shell resting on a cutting shoe on the surface. The material inside is
-dug out and the shell sinks of its own or added weight. The first
-section of the shell may be from 5 to 10 feet long. As this section
-sinks other sections are added. This is called the caisson method. It is
-advantageous in wet ground and when the shafts are to be left as a
-permanent manhole. If a permanent shaft is to be left in an excavation
-being braced with wood, the permanent lining should follow within 20 to
-30 feet of the shaft excavation. This is done to avoid the difficulty of
-maintaining a great length of temporary wood shaft with the danger of
-collapse, or of blocks or other objects falling on the workers below.
-
-The distance between shafts is controlled by the depth and size of the
-tunnel, surface conditions, and the character of the material being
-tunneled. Except where surface conditions are crowded the shallower the
-cover to the tunnel the more frequent the shafts. The advantage of
-frequent shafts lies in the possibility of removing excavated material
-from the tunnel promptly, and in making ventilation of the tunnel
-easier. The saving made by the construction of numerous shafts must be
-balanced against the extra cost of the shafts. For the shallowest
-tunnels the shafts are seldom placed closer than every 500 feet.
-
-
-=165. Timbering.=—After the shaft has been excavated to the proper grade
-the tunnel is struck out either by cutting through the wooden sheeting
-or by removing portions of the caisson lining. Practically all tunnels
-except those in solid rock must be framed to some extent. Some of the
-types of frames used in tunnel construction are shown in Fig. 116.
-Different combinations of these may be used in different classes of
-materials. In solid rock which remains firm on exposure no timbering is
-necessary. Where the roof only need be supported and the sides are
-strong enough to be used for support, a timber “hitch” or frame
-supported on the sides of the tunnel may be used. This is suitable for
-loose rock roofs with solid rock sides. Timbering such as is shown in
-the lower left hand corner of Fig. 116 becomes necessary in extremely
-soft, wet, or swelling material, where the bottom and sides as well as
-the roof tend to push in. The remaining frame in Fig. 116 shows a form
-frequently used and lying between the two extremes indicated. In wet
-tunnels a channel may be cut in the bottom below the sill for drainage
-purposes as shown in this form. The needle beam method of timbering is
-also shown in Fig. 116. This method of timbering is used mainly near the
-heading because of the speed and ease with which it can be installed,
-but it is undesirable because of the space occupied.
-
-The distance between frames is dependent on the size of the tunnel and
-the character of the material. It is seldom greater than 6 feet and the
-frames are sometimes placed touching each other. The size of the
-timbering is a matter of experience and is generally determined by the
-judgment of the responsible person in charge of the construction as the
-result of observation during the progress of the work.
-
-The sheeting between frames is called poling boards, or spiling or
-lagging according as it is sharpened and driven ahead of the excavation
-or placed after the excavation has progressed. The horizontal strips
-placed between the frames to keep them apart are called wales.
-
-[Illustration:
-
- FIG. 116.—Types of Frames and Timbering for Tunnels.
-]
-
-In cutting out from the shaft in soft materials requiring support, where
-the width of the tunnel is the same or smaller than that of the shaft, a
-frame with a maximum width four thicknesses of sheeting less than the
-width of the tunnel is set up against the lining of the shaft. The
-vertical side pieces of the tunnel frame rest on the bottom frame of the
-shaft as a sill and are securely wedged into position. As the lining of
-the shaft at the top is cut away the top poling boards of the tunnel are
-slipped in between the cap of the first tunnel frame and the shaft frame
-immediately above it. The poling boards are driven with an upward pitch
-so that there may be room to slip the second length of boards between
-the next tunnel frame and the first length of boards. The placing of the
-side sheeting follows in a similar manner. Excavation is then started
-and the poling boards driven to keep pace with it. The next frame is
-placed in position and the previous sheeting or boards wedged out a
-sufficient distance to allow the advance lining to be slipped in when
-the wedges are removed. Waling pieces are nailed firmly between the
-frames to hold them in position. The various phases in the driving of a
-12–foot sewer tunnel in Seattle are shown in Fig. 117.
-
-[Illustration:
-
- FIG. 117.—Stages of Sewer Tunneling.
-
- Eng. Record, Vol. 69, 1914, p. 195.
-]
-
-In soft or running material it may be necessary to protect the face of
-the tunnel by horizontal boards, called breast boards, wedged back to
-the last frame placed. The excavation is performed by removing one board
-at a time, excavating behind it and then replacing it in the advance
-position. The advance is made from the top downwards. This represents
-the method pursued in the most difficult material where wooden sheeting
-without a shield is used. The timbering during the advance may be
-modified in any manner that the character of the material will permit.
-The timbering may lag behind the excavation a distance of two or more
-frames, or it may be omitted altogether. Heavier timbering may be
-necessary in soft, slipping or shattered rock.
-
-[Illustration:
-
- FIG. 118.—Shield for Driving Milwaukee Sewer Tunnel.
-
- Eng. News-Record, Vol. 80, 1918, p. 669.
-]
-
-
-=166. Shields.=—Shields are used in tunneling in soft wet material and
-are particularly suitable for work under air pressure. They are used in
-rock tunnels where water is anticipated or air pressure is used. The
-shields often save the expense and difficulty of timbering as the
-masonry of the sewer follows closely behind the shield. Fig. 118 shows
-the arrangement for a shield for tunneling in soft material in the
-construction of the Milwaukee sewers. The shield has an exterior
-diameter of 9 feet 4 inches and an overall length of 9 feet 8⅛ inches.
-The cutting edge section is 20 inches long. The shell is made of one
-inch plate to the back of the jack chambers and one-half inch plate in
-the tail. The shield is driven by ten 60–ton hydraulic jacks. The jacks
-are shown in position in the figure. These jacks rest against the
-finished tunnel lining and serve to consolidate it at the same time that
-they push the shield into the material to be excavated. The face of the
-tunnel is cut with a pick and shovel while the jacks are removed one at
-a time and a new ring of lining is put in place. The lining may be
-temporary timbering to receive the thrust of the jacks, but it is
-usually desirable that the permanent lining follow immediately behind
-the shield. Since the shield is larger than the outside of the lining
-the space left by its passage should be grouted immediately after it has
-passed.
-
-
-=167. Tunnel Machines.=—Tunnel machines have been used successfully on
-sewer tunnels in soft materials, but not in rock.[95] The machines are
-of different types, but in general consist of a revolving cutting head,
-equipped with knives, and driven by an electric motor. The bearing on
-which the shaft for the cutting head rests is supported against the
-sides of the tunnel. The muck is carried away by means of a conveyor and
-dumped into muck cars without rehandling. Rapid progress can be made
-with these machines in suitable conditions.
-
-[Illustration:
-
- FIG. 119.—Method of Drilling and Loading Rock Tunnel Face.
-
- Courtesy, Aetna Power Co.
-]
-
-
-=168. Rock Tunnels.=—Tunnels in rock are advanced by drilling into the
-face as shown in diagrammatic form in Fig. 119. The holes near the
-center are driven in at an angle towards the center and to depths from 6
-to 15 feet. The harder the rock the greater the angle with the tunnel.
-This is called the center cut. Other holes are driven near the outer
-edge of the tunnel and parallel to its axis. When fired, the wedge of
-rock between the center cut holes is thrown back into the tunnel and a
-delayed explosion then throws the sides into the hole thus made. A final
-delay thrusting shot throws the muck so formed away from the face of the
-tunnel. For tunnels up to 6 or 8 feet in height the entire bore is cut
-out in this fashion. For larger tunnels, the upper portion called the
-heading, is taken out in this way, and the remainder, called the bench,
-is taken out by drilling and blowing holes normal to the axis of the
-tunnel. The amount of powder necessary in the bench holes is much less
-than that required in the heading.
-
-
-=169. Ventilation.=—No tunnel more than 50 feet long should be built
-without ventilation. A fair amount of air for ordinary conditions is 75
-cubic feet of free air per minute per person in the tunnel, and double
-this amount for each animal. Where explosive gases are met, or under
-conditions where the tunnel is hot, five or six times as much air may be
-needed in order to cool the tunnel or to dilute the gases. In order that
-the air may be fresh and cool at the face of the tunnel where work is
-going on it should be conducted to the tunnel face in a pipe and blown
-out into the tunnel. Immediately following a blast at the face the
-current should be reversed so as to draw the poisonous gases out of the
-tunnel through the duct. The high pressure air line leading to the
-drills should be opened at the same time to create a current towards the
-face in order to accelerate the clearing of the air at the heading. The
-capacity of the air machines should be sufficient to exhaust four times
-the volume of the gases created by the explosion, in 15 minutes. This
-will ordinarily call for a capacity of about 4,000 cubic feet of free
-air per minute. If the same blower is to be used for exhausting the
-gases as for ventilation while work is going on, it should have a high
-overload capacity to care for this situation. The air line should be
-arranged to allow for reversal of flow.
-
-The diameter of the air pipe should be determined by a study of the
-saving of the cost and operation of the air equipment compared to the
-increased cost of a larger pipe line. Other factors affecting the size
-of the pipe line to be used are: the available space in the tunnel, the
-temporary character of the installation, the use of the exhaust from
-high-pressure air machines for the purpose of ventilation, etc.
-Cast-iron, spiral-riveted galvanized sheet iron, and canvas pipes have
-been used for conducting low-pressure ventilating air.
-
-Ventilation in tunnels working under air pressure is supplied from the
-compressors, and the air is delivered near the face of the heading,
-except that being used in the locks. In tunnels using air drills, the
-air for the drills is conducted through a separate pipe as it is not
-economical to compress the ventilating air to the pressure necessary to
-operate the drills.
-
-
-=170. Compressed Air.=—Compressed air is used in tunnel work to prevent
-the entrance of water into the tunnel and to keep the work dry. The
-pressure of air used is closely that of the pressure of the ground water
-but in a large tunnel or a tunnel with a weak roof the pressure may be
-somewhat lower on account of the danger of blowing through the roof. It
-is evident that the water pressure cannot be balanced at the top and the
-bottom of the tunnel. To balance it at the bottom makes a blow out near
-the top more probable. To balance the pressure at the top may leave the
-bottom wet. Judgment and care must be exercised during construction and
-if the pressure is balanced at or near the bottom the roof must be
-carefully guarded by grouting and puddling with clay, or the surface,
-particularly if under water, may be covered with a clay bank. If the
-cavities in the tunnel lining are large, sawdust can be mixed with the
-grout to advantage, the mixture being pumped through holes in the roof
-by hand or power operated force pumps. “Blows” must be carefully guarded
-against as they endanger the lives of the workmen and threaten the loss
-of the tunnel. The pressure and volume of air supplied for some large
-subaqueous tunnels is shown in Table 61.
-
-Labor under compressed air is arduous and dangerous with the best of
-safeguards.[96] Pressure more than about 43 pounds per square inch
-cannot be used and at this high pressure men cannot work more than four
-hours at a time. Little or no distress is noted at pressures less than
-15 pounds.
-
- TABLE 61
-
- VOLUME AND PRESSURE OF COMPRESSED AIR IN TUNNELS
-
- (American Civil Engineers Pocket Book)
- ──────────┬────────┬───────┬─────────┬─────────┬───────────────────────
- Tunnel │ │ │ Maximum │ Average │ Conditions and Cubic
- │Maximum │ │ Air │ Air │ Feet of Free Air per
- │Distance│ │Pressure,│Pressure,│ Minute
- │ High │ │ Pounds │ Pounds │
- │Water to│Minimum│ per │ per │
- │Invert, │ Cover │ Square │ Square │
- │ Feet │in Feet│ Inch │ Inch │
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- City and │ │ │ │ │In water bearing-sand.
- South │ │ │ │ │ 1660 cubic feet per
- London │ │ │ │ │ minute per face. When
- │ │ │ │ │ grouted 1000 to 1300
- │ │ │ │ │ cubic feet per minute
- │ 34│ 42│ 15│ │ per face
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- Blackwall │ │ │ │ │10,000 cubic feet per
- │ │ │ │ │ minute per face in
- │ │ │ │ │ open ballast for some
- │ 80│ 5│ 37│ 35│ time
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- Baker St. │ │ │ │ │In gravel, 3300 cubic
- and │ │ │ │ │ feet of air per
- Waterloo│ │ │ │ │ minute per face.
- │ │ │ │ │ Parallel tunnel 1650
- │ │ │ │ │ cubic feet per min.
- │ 70│ 18│ 35│ 28│ per face
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- Greenwich │ │ │ │ │Average 83.5 per man
- │ │ │ │ │ per minute. Never
- │ 70│ 30│ 28│ 20│ less than 66.7
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- Battery, │ │ │ │ │In sand. Two working
- East │ │ │ │ │ faces. Maximum 32,000
- River. │ │ │ │ │
- N. Y. │ 94│ 12│ 42│ 26│
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- East │ │ │ │ │Maximum for one face
- River, │ │ │ │ │ 25,000 cubic feet per
- N. Y., │ │ │ │ │ minute for 24 hours.
- Penn. │ │ │ │ │ Capacity of plant for
- R.R. │ │ │ │ │ 8 faces, 80,400 cubic
- │ 93│ 8│ 42│ 27│ feet per minute
- ──────────┼────────┼───────┼─────────┼─────────┼───────────────────────
- North │ │ │ │ │Maximum in gravel
- River, │ │ │ │ │ 10,000 cubic feet per
- N. Y., │ │ │ │ │ man per hour.
- Penn. │ │ │ │ │ Generally ranged
- R.R. │ 98│ 20│ 37│ 26│ between 1500 and 5000
- ──────────┴────────┴───────┴─────────┴─────────┴───────────────────────
-
-Entrance and exit to the tunnel are gained through air locks. These are
-sheet iron cylinders concreted into the lining of the tunnel or shaft.
-Air-tight iron doors are provided at both ends, which open inwards
-towards the tunnel. On entering the lock from the outside the door to
-the tunnel is found tightly closed. The outside door is then closed by
-hand, the air valve is opened and air is admitted to the lock until the
-pressure on the lock side of the tunnel door equalizes that on the
-tunnel side and the tunnel door is swung open by hand. When the lock is
-open to the tunnel the pressure in the tunnel keeps the outside door
-closed. In order to leave the tunnel the process is reversed. Materials
-are passed through the lock by the lock tender or tenders who pass
-through the lock with the material if the pressure is low, or who
-manipulate the air outside of the lock if the pressure is high. If
-pressures of 30 to 40 pounds are being used, two or even three locks may
-be necessary.
-
-
- EXPLOSIVES AND BLASTING[97]
-
-
-=171. Requirements.=—The desirable features in an explosive to be used
-in trenching and tunneling in rock are: (1) stability in make up so as
-not to deteriorate in strength or to become dangerous during storage,
-(2) imperviousness to ordinary variations in temperature and moisture,
-(3) insensibility to ordinary shocks received in transportation and
-handling, (4) not too difficult of detonation, (5) convenient form for
-transportation and loading and for making up charges of different
-weights, (6) the non-formation of poisonous gases when fired, (7)
-imperviousness to water and usefulness in wet holes, (8) power without
-bulk, etc.
-
-
-=172. Types of Explosives.=—Explosives which fill some or all these
-requirements can be divided into two classes, deflagrating and
-detonating. A deflagration is an explosion transmitted progressively
-from grain to grain. A detonation is a sudden disruption caused by
-synchronous vibrations of a wave-like character. The deflagrating
-explosives are represented by gun-powders and contractors’ powders. They
-must be carefully tamped in the hole to develop their full power and
-they must be ignited by a fuse or flame. They are valueless in water or
-moist holes. These powders are used mainly for loosening frozen earth,
-soft sandstone, cemented gravels and similar materials where a thrusting
-action rather than a disruption is desired. The detonating explosives
-are most commonly represented by the dynamites. These are exploded by a
-shock usually caused by another explosive which has been ignited by a
-fuse or electric spark, and which is known as the “detonator.”
-Detonating explosives are more powerful than deflagrating explosives and
-are used in all but the softest materials.
-
-_Gunpowder._—This is a mechanical mixture of sulphur, charcoal, and
-saltpeter generally in the proportions of 10 parts sulphur, 15 parts
-charcoal, and 75 parts saltpeter (sodium nitrate). It weighs about 62½
-pounds per cubic foot and produces about 280 times its own volume in gas
-at a pressure of 4.68 tons per square inch at a temperature of 32
-degrees F., which amounts to a pressure of approximately 38 tons per
-square inch at the temperature of explosion of 4,000 degrees F.
-
-_Blasting Powder._—This is a mixture of 19 parts sulphur, 15 parts
-charcoal, and 66 parts saltpeter. These powders are made in different
-size angular polished grains, from the size of a pin head to sizes just
-passing a ⅜ to ½ inch hole. The larger the grains the slower the action
-of the powder.
-
-_Nitro-Substitution Compounds._—These compounds are formed by the action
-of nitric acid on hydrocarbons. Triton, T.N.T., or trinitrotoluene, made
-famous during the war, is an example of these compounds. It is made by
-the successive nitration of toluene, a coal tar derivative. It melts at
-80 degrees C., is very stable, and is of great explosive strength. It is
-manufactured in a convenient form, being compressed into blocks about 2
-inches square by about 4 inches long with a specific gravity of about
-1.5. The blocks are usually copper plated to protect the T.N.T. from
-moisture. The more dense it is the less its sensitiveness. It is also
-put up in crystalline form in cartridges like dynamite, in which
-condition it is practically equal to 40 per cent dynamite. It can be cut
-with a knife, pounded with a hammer, and will burn freely and slowly in
-small quantities in the open air without exploding. It is suitable for
-all but the hardest rocks. It creates poisonous gases on detonation
-which are quickly dissipated in the open air but which render it
-unsuitable for use in tunnel work.
-
-_Nitro-glycerine._—This is formed by the action of nitric and sulphuric
-acids on animal compounds such as gelatine or glycerine. Nitro-glycerine
-is a yellowish, oily, highly unstable explosive liquid with a specific
-gravity of about 1.6. It will burn quietly when ignited in the open air.
-It will freeze at 41 degrees F., and will explode at 388 degrees F., or
-on concussion at a lower temperature. It develops about 1,500 times its
-volume in gas, which due to the heat of combustion is increased to about
-10,000 times its volume. It is a very dangerous explosive to handle, and
-is unsuitable for use in the liquid form.
-
-_Blasting Gelatine._—This is made by soaking guncotton in
-nitro-glycerine. Gelatine dynamite is a combination of blasting gelatine
-and an absorbent. Forcite is a gelatine dynamite in which the blasting
-gelatine, forming 50 per cent of the compound, contains 90 per cent
-nitro-glycerine and 2 per cent guncotton; and the absorbent, forming the
-other 50 per cent of the compound, contains 76 per cent of sodium
-nitrate, 3 per cent sulphur, 20 per cent of wood tar, and 1 per cent of
-wood pulp.
-
-Blasting gelatine is packed in a jelly-like mass in metal lined wooden
-boxes. It is less sensitive than straight dynamite and is one of the
-most powerful explosives known. It can be made up to equal 100 per cent
-dynamite. It is suitable for use in the hardest rocks and for subaqueous
-work as it is not affected by moisture. It is suitable for use in
-tunnels as the amount of carbon monoxide, peroxide of nitrogen, hydrogen
-sulphide and other dangerous gases is comparatively low when fully
-detonated. Gelatine dynamite[98] is sold as 30 per cent to 70 per cent
-dynamite, the actual percentage of nitro-glycerine being less than the
-nominal quantity given.
-
-_Dynamite._—The dynamites are made by soaking nitro-glycerine in some
-absorbent. If the absorbent is some neutral substance such as infusorial
-earth the combination is known as a true dynamite. The false or active
-dynamites are those in which the absorbent is also an explosive
-compound. The false dynamites form the best known contractors’
-explosives. Among the materials mixed with the nitro-glycerine are:
-magnesium carbonate, sulphur, wood meal, wood pulp, wood fiber, wood
-tar, nut galls, kieselguhr, sawdust, resin, pitch, sugar, charcoal, and
-guncotton. The strength of dynamites is noted by the per cent of
-nitro-glycerine and nitro substitutes contained. Dualin and Hercules
-powder both contain 40 per cent nitro-glycerine. Dualin contains 30 per
-cent sawdust and 30 per cent potassium nitrate, but the Hercules powder,
-which is stronger, contains 16 per cent sugar, 3 per cent potassium
-chlorate, 31 per cent potassium nitrate, and 10 per cent magnesium
-carbonate.
-
-Dynamite is the most common explosive used on construction work. It is
-supplied in cylindrical sticks wrapped in paper, the diameter of the
-sticks varying between ⅞ and 2 inches. They are about 8 inches long.
-Forty per cent dynamite is the common strength found on the market. It
-is suitable for ordinary work in all but very hard rocks or very soft
-material. Direct contact with water separates the nitro-glycerine from
-the base and is dangerous when the explosive is used in wet places
-unless it is fired immediately after the hole is loaded. It freezes at
-about 42 degrees F., or at even higher temperatures and in the frozen
-state it is highly dangerous, requiring powerful detonators for firing,
-but exploding spontaneously from a slight jar, or the breaking of the
-stick. Special low-freezing dynamites are made that will not freeze
-above 35 degrees F.
-
-_Ammonia Compounds._—Ammonia dynamite is a combination of
-nitro-glycerine, ammonium nitrate and such other ingredients as sodium
-nitrate, calcium carbonate and combustible material. This form of
-explosive is advantageous for underground work because, like gelatine
-dynamite, its explosion does not create large quantities of poisonous
-gases. It has a low freezing point and is relatively low in cost. It is
-seriously affected by moisture, however, and can not be used in wet
-places. Ammonium nitrate explosives which do not contain nitro-glycerine
-include 70 per cent to 95 per cent ammonium nitrate and some combustible
-material. Ammonal is a special type of this class formed by a mixture of
-ammonium nitrate, aluminum, and triton. All of these explosives are
-deliquescent, insensitive to shock, and are cheaper than the dynamites.
-
-
-=173. Permissible Explosives.=—As specified by the United States Bureau
-of Mines explosives whose rapidity, detonation, and temperature of
-explosion will not ignite explosive mixtures of pit gases and air are
-known as permissible explosives. They include nitrate explosives,
-ammonia dynamite, and others.
-
-Gunpowder, triton, picric acid, blasting gelatine, dynamite, guncotton,
-etc., are not classed as permissible explosives.
-
-
-=174. Strength.=—The relative weights for equal strength of various
-explosives are given in Table 62.
-
- TABLE 62
-
- RELATIVE WEIGHTS OF EXPLOSIVES WITH THE SAME STRENGTH AS A UNIT WEIGHT
- OF 40 PER CENT DYNAMITE
-
- ───────────────────────────────────────────────────────┬───────────────
- Explosive │Relative Weight
- ───────────────────────────────────────────────────────┼───────────────
- Picric acid │ 0.86
- Gun powder (well tamped) │ 3.10
- Straight dynamite, 15% │ 1.45
- Straight dynamite, 20 │ 1.33
- Straight dynamite, 25 │ 1.28
- Straight dynamite, 30 │ 1.18
- Straight dynamite, 35 │ 1.07
- Straight dynamite, 40 │ 1.00
- Straight dynamite, 45 │ 0.93
- Straight dynamite, 50 │ 0.86
- Straight dynamite, 55 │ 0.83
- Straight dynamite, 60 │ 0.78
- │
- Low-freezing dynamites are the same as straight │
- dynamites │
- Smokeless powder, well tamped │ 0.74
- │
- Triton │ 0.86
- Blasting gelatine │ 0.43
- Gelatine dynamite, 30% │ 1.28
- Gelatine dynamite, 35 │ 1.21
- Gelatine dynamite, 40 │ 1.14
- Gelatine dynamite, 50 │ 1.04
- Gelatine dynamite, 55 │ 0.97
- Gelatine dynamite, 60 │ 0.90
- Gelatine dynamite, 70 │ 0.83
- │
- Ammonia dynamites are the same as gelatine dynamites. │
- Chlorates (sprengle) Rack-a-rock │ 1.33
- Guncotton │ 0.72
- ───────────────────────────────────────────────────────┴───────────────
-
-
-=175. Fuses and Detonators.=—The explosion of gunpowder and other
-deflagrating explosives is caused by the direct application of a flame
-led to the charge by a powder fuse, or they may be fired by a blasting
-cap which is itself exploded by the heat from a fuse or an electric
-spark. The powder fuse is a cord made up of a train of powder securely
-wrapped in a number of thicknesses of woven cotton or linen threads and
-usually made waterproof. Ordinary fuse burns at about 2 feet per minute
-but there may be wide variations from this rate due to the quality of
-the fuse, moisture, temperature, or pressure. Moisture tends to retard
-the rate, pressure to increase it. Instantaneous fuse will burn at about
-120 feet per second. It is distinguished from the ordinary safety fuse
-both by eye and touch due to the rough red braid with which it is
-covered. It is used in firing a number of charges simultaneously. Powder
-fuses are lighted by the application of a flame or smoldering torch to
-the freshly cut or opened end exposing the powder grains. Cordeau
-Bickford is lead tubing filled with triton, in which the flame travels
-at about 17,000 feet per second. This is also used for igniting charges
-simultaneously.
-
-The detonation of an explosive is caused by the shock or heat of the
-explosion of a more sensitive substance which has been exploded by a
-powder fuse or electric spark. The common method of detonating explosive
-charges is by the firing of a blasting cap. These caps are copper
-cylinders, closed at one end, about 1½ inches long and ¼ to ⅜ of an inch
-in diameter, or larger. They contain a mixture of about 85 per cent
-fulminate of mercury and 15 per cent potassium chlorate held in place by
-a wad of shellac, collodion, or paper. The strength of detonators is
-based on the weight of fulminate of mercury and is designated as shown
-in Table 63.
-
- TABLE 63
-
- STRENGTH OF BLASTING CAPS
-
- ────────────────────────────────────────┬──────────────────────────────
- Blasting Cap, Commercial Grade │ Grains Fulminate of Mercury
- ────────────────────────────────────────┼──────────────────────────────
- 3X or Triple │ 8.3
- 4X or Quadruple │ 10.0
- 5X or Quintuple │ 12.3
- 6X or Sextuple │ 15.4
- 7X or Number 20 │ 23.1
- 8X or Number 30 │ 30.9
- Single strength │ 12.3
- Double strength │ 15.4
- Triple strength │ 23.1
- Quadruple strength │ 30.9
- ────────────────────────────────────────┴──────────────────────────────
-
-The force of the explosion is markedly affected by the strength of the
-caps, the effect being greater for low-grade powders. For 40 per cent
-dynamite the explosion caused by a 5X cap is 15 per cent stronger than
-that caused by a 3X cap. For 60 per cent dynamite the difference is only
-6 per cent. The deterioration of the caps will reduce the strength of an
-explosion noticeably. With straight dynamite, 3X caps are generally
-used, but with gelatine dynamite 6X or heavier caps must be used. Caps
-may be tested by exploding them in a confined space and noting the
-report and the effect on the shell. A full strength cap will tear the
-shell into minute pieces, while a deteriorated cap will merely tear it
-into three or four large pieces. An ordinary blasting cap is shown in
-Fig. 120 together with other equipment for blasting.
-
-Firing by electricity is generally safer and more satisfactory than by
-the use of ordinary caps and powder fuses. The explosion is more certain
-and its exact time is under the control of the operator. Fig. 121 shows
-a section through an electric blasting cap or detonator, commonly called
-an electric fuse. Delayed action electric detonators are made by
-inserting a slow-burning substance between the platinum bridge and the
-detonating substance. The time of delay is controlled by the depth of
-the slow-burning substance. Delayed action detonators are useful in
-tunnel work where it is desired to explode the charge in three or four
-stages in order that the debris from one charge may be out of the way of
-the following, and that the forces of the explosions may not serve to
-nullify each other.
-
-[Illustration:
-
- FIG. 120.—Blasting Supplies.
-
- Courtesy, Aetna Powder Co.
-]
-
-
-=176. Care in Handling.=—Some of the don’ts in the handling of
-explosives recommended by the U. S. Army Engineer Field Manual are: in
-the use of nitro-glycerine explosives of all kinds—
-
- (_a_) Don’t store detonators with explosives. Detonators should be
- kept by themselves.
-
- (_b_) Don’t open packages of explosives in a store house.
-
- (_c_) Don’t open packages of explosives with a nail puller, pick
- or chisel. Packages should be opened with a hard wood wedge and
- mallet, outside of the magazine and at some distance from it.
-
- (_d_) Don’t store explosives in a hot or damp place. All
- explosives spoil rapidly if so stored.
-
- (_e_) Don’t store explosives containing nitro-glycerine so that
- the cartridges stand on end. The nitro-glycerine is more likely to
- leak from the cartridges when they stand on end than it is when
- they lie on their sides.
-
- (_f_) Don’t use explosives that are frozen or partly frozen. The
- charge may not explode completely and serious accidents may
- result. If the explosion is not complete the full strength of the
- charge is not exerted and larger quantities of harmful gases are
- given off.
-
-[Illustration:
-
- FIG. 121.—Electric Fuse.
-
- Full size.
-]
-
- (_g_) Don’t thaw frozen explosives in front of an open fire, nor
- in a stove, nor over a lamp, nor near a boiler, nor near steam
- pipes, nor by placing cartridges in hot water. Use a commercial or
- improvised thawer.
-
- (_h_) Don’t put hot water or steam pipes in a magazine for thawing
- purposes.
-
- (_i_) Don’t carry detonators and explosives in the same package.
- Detonators are extremely sensitive to heat, friction, or blows of
- any kind.
-
- (_j_) Don’t handle detonators or explosives near an open flame.
-
- (_k_) Don’t expose detonators or explosives to direct sunlight for
- any length of time. Such exposure may increase the danger in their
- use.
-
- (_l_) Don’t open a package of explosives until ready to use the
- explosive, then use it promptly.
-
- (_m_) Don’t handle explosives carelessly. They are all sensitive
- to blows, friction, and fire.
-
- (_n_) Don’t crimp a detonator (blasting cap) around a fuse with
- the teeth. Use a cap crimper, which is supplied for this purpose.
-
- (_o_) Don’t economize by using a short length of fuse.
-
- (_p_) Don’t return to a charge for at least one-half hour after a
- miss fire. Hang fires are likely to happen.
-
- (_q_) Don’t attempt to draw nor to dig out the charge in case of a
- miss fire.
-
-Some of the positive rules in connection with the handling of explosives
-are: build the magazine on an earth foundation remote from any other
-structures, protect it with earth embankments that will direct the force
-of the explosion upwards, and build it of materials that will supply as
-few missiles as possible. Hollow tile brick, double-walled galvanized
-iron filled with sand, and similar constructions are satisfactory. The
-magazine may be heated by steam or hot-water pipes so located that
-explosives cannot come in contact with them, or by a cluster of
-incandescent bulbs, but if the explosives become frozen they must not be
-thawed out by turning on the steam or hot water. If powder or
-nitro-glycerine is dropped on the floor the magazine should be emptied,
-washed out with a hose and spots of nitro-glycerine scrubbed with a
-brush and a mixture of ½ gallon of wood alcohol, ½ gallon of water and 2
-pounds of sodium sulphide. Frozen explosives may be thawed by spreading
-out on special shelves in a warm thaw house—not in the magazine proper,
-by burying in a manure pile so that the explosive may not become
-moistened, or more commonly by heating slowly in a water bath. This is a
-dry kettle in which the explosives are placed and covered. The kettle is
-then put in another containing water which is heated gently to about 120
-degrees F. It should not be boiled.
-
-In case of a miss fire, instead of digging out the old charge put a new
-charge on top of the old and fire the two simultaneously.
-
-
-=177. Priming, Loading, and Firing.=—Priming is the act of placing the
-cap or detonator in the cartridge of explosive. The primer is either the
-cap or the cap and cartridge which are to be detonated by the fuse. If a
-cap and safety fuse are to be used the paper at the upper end of the
-cartridge is opened, a hole is poked in the explosive with the finger or
-a piece of wood, the cap and the attached fuse are pushed into the hole
-and gently embedded in the explosive so that the end of the cap is
-exposed sufficiently to prevent the fuse from igniting the dynamite
-directly. The paper is then folded up and tied firmly around the fuse
-with a piece of string. The result is shown in Fig. 122.
-
-[Illustration:
-
- FIG. 122.—Dynamite Cartridge, Safety Fuse, and Cap.
-]
-
-In placing the fuse in the cap the end of the fuse is cut off square,
-and inserted in the open end of the cap, care being taken not to spill
-the loose grains of powder or to grind the fuse down on top of the cap.
-When the fuse is shoved firmly into place the upper portion of the
-copper cap is pressed or crimped with the cap crimpers shown in Fig.
-120.
-
-The number of primers to be used is dependent on the size and location
-of the charge, but in practically all sewer work only one primer is used
-to each hole. In bulky charges the primer should be placed near the
-center of the charge and the fuse so protected that it will not ignite
-the charge prematurely. In drill holes the primer is put in last with
-the cap end down.
-
-In loading a hole, it is first pumped and cleaned out. This can be done
-satisfactorily with the end of a stick frayed out into a broom.
-Cartridges which very nearly fill the hole are dropped in one at a time
-and are pressed firmly together, with a light wooden tamping bar. They
-should not be pounded. After the primer is placed, a wad of clay or
-similar material is pressed gently into the hole against it and the hole
-is then filled with well-tamped clay. In tunnel work tamping is not so
-essential as an overcharge of powder is usually used and the time of
-tamping, which is worth more than two or three sticks of dynamite, is
-saved. In handling bulk explosives, such as gunpowder, they are poured
-into the hole, the fuse is set in the upper portion and the remainder of
-the hole is tamped with clay as for dynamite cartridges.
-
-[Illustration:
-
- FIG. 123.—Methods for Cutting Safety Fuse for Splicing.
-]
-
-If a large number of charges are to be fired simultaneously with a
-safety fuse, the length of the fuse to each charge should be made equal
-or a safety fuse used to a common center and approximately equal lengths
-of instantaneous fuse or Cordeau Bickford used from there to the charge.
-In splicing the fuses for such connections they are cut diagonally as
-shown in Fig. 123 and bound together firmly with tape. Electric
-connections are particularly advantageous under such conditions as they
-avoid the dangers incidental to spliced fuses and are less expensive. In
-tunnel work simultaneous electric detonation is not desirable as the
-holes should be fired progressively: 1st, the cuts; 2nd, the relievers;
-3rd, the backs; 4th, the sides; and 5th, the lifters. Different lengths
-of safety fuse, or delayed action electric fuses can be used for these
-delay shots.
-
-In igniting a safety fuse an open flame such as that furnished by a
-match or candle is the most satisfactory. For electric fuses the current
-is generated by a magneto shown in Fig. 120. Pressing vigorously down on
-the handle closes the circuit and generates an electric current which
-heats the platinum bridges and explodes the charges. For the small
-number of charges used in ordinary construction they are connected in
-series so that if there is a broken connection anywhere no charge will
-be exploded. If many charges are to be fired and a line circuit is to be
-used, the final connection should not be made until just before the
-charge is to be fired in order to obviate the danger of stray currents
-firing the charge prematurely. Care should be taken to see that all
-connections are good and that there are no broken wires on the line.
-
-
-=178. Quantity of Explosive.=—The quantity of explosive to be used can
-be determined satisfactorily only by experience on the job in question,
-as the factors affecting the necessary quantity are so diverse. The
-figures in Table 64 indicate the relative amounts needed under different
-conditions.
-
- TABLE 64
-
- QUANTITIES OF EXPLOSIVES
-
- ───────────┬──────┬────────┬─────────┬─────────────┬─────────┬──────────
- Kind of │Drift │Feet[99]│Black[99]│Dynamite[99],│Grade of │
- Rock │ in │of Hole │ Powder, │ Pounds │Dynamite,│ Remarks
- │ Feet │ │ Pounds │ │Per Cent │
- ───────────┼──────┼────────┼─────────┼─────────────┼─────────┼──────────
- Limestone, │ │ │ │ │ │
- Chicago │ 12│ 0.40│ │ 0.75│ 40│Gillette
- Drainage │ │ │ │ │ │
- Canal │ │ │ │ │ │
- Limestone │ │ │ │ │ │
- for │ 6│ 1.00│ │ 0.70│ 40│Gillette
- crushing │ │ │ │ │ │
- Limestone │ │ │ │ │ │
- for │ 20│ │ │ 0.37│ 50│Gillette
- cement │ │ │ │ │ │
- Limestone, │ │ │ │ │ │
- holes │ 15│ 0.40│ │ 0.26│ 50│Gillette
- sprung │ │ │ │ │ │
- Sandstone, │ 20│ 0.10│ 1.0│ 0.10│ 40│Gillette
- side cut │ │ │ │ │ │
- Sandstone, │ │ │ │ │ │
- thorough │ 20│ 0.20│ 2.0│ 0.20│ 40│Gillette
- cut │ │ │ │ │ │
- Shale, soft│ 24│ 0.08│ 0.7│ 0.03│ 40│Gillette.
- side cut │ │ │ │ │ │ Open cut
- Shale, hard│ │ │ │ │ │
- thorough │ 24│ 0.20│ 1.5│ 0.10│ 40│Gillette
- cut │ │ │ │ │ │
- Granite for│ 16│ 1.36│ │ 0.20│ 60│Gillette
- rubble │ │ │ │ │ │
- Gneiss, New│ 12│ 1.33│ │ 0.60│ 40│Gillette
- York City│ │ │ │ │ │
- Gneiss, New│ 14│ 0.63│ │ 0.50│ 40│Gillette
- York City│ │ │ │ │ │
- Syenite, │ │ │ │ │ │
- Treadwell│ 12│ 1.70│ │ 0.67│ 40│Gillette
- Mine │ │ │ │ │ │
- Magnetic │ 12½│ 0.32│ │ 0.44│ 52│Gillette
- iron ore │ │ │ │ │ │
- Trap, seamy│ 14│ 0.35│ │ 0.20│ 75│Gillette
- Trap, │ 17│ 1.00│ │ 0.70│ 40│Gillette
- massive │ │ │ │ │ │
- │ │ │ │ │ │50%
- Granite, │ │ │ │ │ │ dynamite
- Grand │ 25│ 0.10│ │ 0.80│ 50│ used to
- Trunk │ │ │ │ │ │ spring
- │ │ │ │ │ │ holes
- Clay, rock │ │ │ │ │ │
- and │Tunnel│ │ │ 1.00│ │
- Gypsum │ │ │ │ │ │
- │ │ │ │ │Grade │
- │ │ │ │ │ varied │
- │ │ │ │ │ ⅗ at │
- Hard shale │Tunnel│ │ │ 2.07│ 45%, ⅕ │
- │ │ │ │ │ at 60%,│
- │ │ │ │ │ some at│
- │ │ │ │ │ 100% │
- Hard rocky │Tunnel│ 1.60│ │ 3.57│ │
- slate │ │ │ │ │ │
- Hard rocky │Tunnel│ 1.46│ │ 3.57│ │
- slate │ │ │ │ │ │
- Mill Creek │ │ │ │ │ │Mun.
- sewer, │Tunnel│ │ │ 4.00│ 60│ Eng’g.
- St. Louis│ │ │ │ │ │ Vol. 52,
- │ │ │ │ │ │ p. 14
- ───────────┴──────┴────────┴─────────┴─────────────┴─────────┴──────────
-
-
- PIPE SEWERS
-
-
-=179. The Trench Bottom.=—It is customary to dig the bottom of the
-trench to conform to the shape of the lower 45 degrees to 90 degrees of
-the sewer if the character of the material will allow such construction.
-In soft material which will not hold its shape the sewer may be encased
-in concrete or a concrete cradle may be prepared for the pipe. In rock
-the trench is excavated to about 6 inches below grade and refilled with
-well-tamped earth so as to form a cradle giving bearing to 60 to 90
-degrees of the pipe circumference. For large sewers to be constructed in
-the trench special foundations are sometimes built.
-
-
-=180. Laying Pipe.=—Before the pipe is lowered into the trench the
-sections which are to be adjacent should be fitted together on the
-surface and the relative positions marked by chalk so that the same
-position can be obtained in the trench.
-
-Small pipes are lowered into the trench and swung into position on a
-hook as shown in Fig. 124. Pipes up to 15 or 18 inches in diameter can
-be handled by the pipe layer and helper in the trench without
-assistance. Heavier pipes may be lowered into the trench by passing
-ropes around each end of the pipe. One end of the rope is fastened at
-the surface and the ropes are paid out by the men at the surface as the
-pipe is lowered. If the pipes have been fitted together and marked at
-the surface it is undesirable to use this method of lowering as the
-position in which the pipes arrive in the bottom of the trench can not
-be easily predicted. A cradle may be used for shoving the pipe into
-position as is shown in Fig. 125.
-
-[Illustration:
-
- FIG. 124.—Hook for Lowering and Placing Sewer Pipe.
-]
-
-[Illustration:
-
- FIG. 125.—Cradle for Placing Sewer Pipe.
-]
-
-Pipes above 24 to 27 inches in diameter are too large to be handled from
-the side of the trench. A hook as shown in Fig. 124 is placed in the
-pipe so that it will be in the proper position when lowered. It is
-raised by a rope passing through a block at the peak of a stiff-legged
-derrick which spans the trench, or by a crane. If a derrick is used the
-rope passes to a windlass on the opposite side of the trench from the
-pipe. Mechanical power may be used for raising pipes too heavy to be
-raised by hand. The pipe is then lowered and swung into position while
-supported from the derrick. Excessive swinging is prevented by holding
-back on the guide rope as the pipe is raised and lowered.
-
-Pipes are usually laid with the bell end up grade as it is easier to fit
-the succeeding pipe into the bell so laid and to make the joint,
-particularly on steep grades. The Baltimore specifications state:
-
- The ends of the pipe shall abut against each other in such a
- manner that there shall be no shoulder or unevenness of any kind
- along the inside of the bottom half of the sewer or drain. Special
- care should be taken that the pipe are well bedded on a solid
- foundation.... The trenches where pipe laying is in progress shall
- be kept dry, and no pipe shall be laid in water or upon a wet bed
- unless especially allowed in writing by the Engineer. As the pipe
- are laid throughout the work they must be thoroughly cleaned and
- protected from dirt and water, no water being allowed to flow in
- them in any case during the construction except such as may be
- permitted in writing by the Engineer. No length of pipe shall be
- laid until the preceding length has been thoroughly embedded and
- secured in place, so as to prevent any movement or disturbance of
- the finished joint.
-
- The mouth of the pipe shall be provided with a board or stopper,
- carefully fitted to the pipe, to prevent all earth and any other
- substances from washing in.
-
-
-=181. Joints.=—Pipes may be laid with open joints, mortar joints, cement
-joints, or poured joints. Open joints are used for storm sewers in dry
-ground close to the surface. Mortar and cement joints are commonly used
-on all sewers except in special cases. Cement joints are more carefully
-made than mortar joints and result in a greater percentage of
-water-tight joints. Poured joints are used in wet trenches where it is
-necessary to exclude ground water from the sewer.
-
-A specification used in some cities for open joints is:
-
- Pipes laid with open joints are to be laid with their inverts in
- the same straight line and shall be firmly bedded throughout their
- length on the bottom of the trench. No cement or mortar is to be
- used in the joints. Not more than ⅛ inch shall be left between the
- spigot end of the pipe and the shoulder of the hub of the pipe
- into which it fits. The joints shall be surrounded with cheese
- cloth, burlap, broken pipe, gravel or broken stone.
-
-The purpose of the cheese cloth, etc., is to prevent fine earth from
-sifting into the pipe until the cheese cloth or other material has
-rotted away, by which time the earth has become arched over the opening.
-
-Mortar joints are specified by Metcalf and Eddy as follows:
-
- Before a pipe is laid the lower part of the bell of the preceding
- pipe shall be plastered on the inside with stiff mortar of equal
- parts of Portland cement and sand, of sufficient thickness to
- bring the inner bottoms of the abutting pipe flush and even. After
- the pipe is laid the remainder of the bell shall be thoroughly
- filled with similar mortar and the joint wiped inside and finished
- to a smooth bevel outside.
-
-In some work a wood block or a stone is embedded in the mortar at the
-bottom of the joint to bring the spigot in place concentric with the
-next pipe.
-
-Cement joints are specified in the Baltimore specifications as follows:
-
- Cement joints shall be made with a narrow gasket of hemp or jute
- and cement mortar, and special care shall be taken to secure tight
- joints. The gasket shall be soaked in Portland cement grout and
- then carefully inserted between the bell and the spigot, and well
- calked with suitable hardwood or iron calking tools. It shall be
- in one continuous piece for each joint, and of such thickness as
- to bring the inverts of the two pipes smooth and even. The
- remainder of the joint shall be filled with cement mortar all
- around, on the bottom, top and sides, applied by hand with rubber
- mittens, well pressed into the annular space and beveled off from
- the outer edge of the bell to a distance of two inches therefrom,
- or to an angle of 45 degrees. The inside of each joint shall be
- thoroughly cleansed of all surplus mortar that may squeeze out in
- making the joint; and to accomplish this some suitable scraper or
- follower, or form shall be provided and always used immediately
- after each joint is finished.
-
-Cement joints so made, form the most satisfactory joint for ordinary
-conditions and are the most frequently used. They are not always
-water-tight and can be penetrated by roots. Some roots are able to
-penetrate holes of almost microscopic size and to form growths in the
-sewer or to split the joints.
-
-Poured joints are made by pouring some jointing compound, while in a
-fluid state, into the joint in which it hardens, thus sealing the joint.
-Water-tightness in sewer lines to exclude ground water has also been
-attempted by using the ordinary cement joint and surrounding the pipe
-with a layer of cement or concrete. This has not always been successful
-as it is difficult to obtain the proper class of workmanship in wet
-sewer trenches.
-
-The requisite qualities of a poured jointing material are:
-
- (1) It should make a joint proof against the entrance of water and
- roots.
-
- (2) It should be inexpensive.
-
- (3) It should have a long life.
-
- (4) It should not deteriorate in sewage which may be either acid
- or alkaline.
-
- (5) It should adhere to the surface of the pipe.
-
- (6) It should run at a temperature below about 400° F., as too
- high temperatures will crack the pipe.
-
- (7) It should neither melt nor soften at temperatures below 250°
- F. in order to maintain the joint if hot liquids are poured into
- the sewer.
-
- (8) It should be elastic enough to permit slight movements of the
- pipes.
-
- (9) It should not require great skill in using as it must be
- handled ordinarily by unskilled workers.
-
-The materials used for poured joints are: cement grout; sulphur and
-sand; and asphalt or some bituminous compound made of vulcanized linseed
-oil, clay, and other substances the resulting mixture having the
-appearance of vulcanized rubber or coal tar. The bituminous materials
-most nearly approach the ideal conditions.
-
-Cement grout is made up of pure cement and water mixed into a soupy
-consistency. Its main advantages are its cheapness and ease in handling
-in wet trenches or difficult situations. The result is no better than a
-well made cement joint. There is no elasticity to the joint and a
-movement of the pipe will break it.
-
-Sulphur and sand are inexpensive, comparatively easy to handle, and make
-an absolutely water-tight and rigid joint which is stronger than the
-pipe itself. It frequently results in the cracking of the pipe and is
-objected to by some engineers on that account. In making the mixture,
-powdered sulphur and very fine sand are mixed in equal proportions. It
-is essential that the sand be fine so that it will mix well with the
-sulphur and not precipitate out when the sulphur is melted. Ninety per
-cent of the sand should pass a No. 100 sieve and 50 per cent should pass
-a No. 200 sieve. The mixture melts at about 260° F. and does not soften
-at lower temperatures. For making a joint in an 8 inch pipe about 1½
-pounds of sulphur, 1½ pounds of sand, ½ pound of jute, and 0.4 pound of
-pitch are used. The pitch is used to paint the surface of the joint
-while still hot in order to close up any possible cracks.
-
-Among the better known of the bituminous joint compounds are: “G.K.”
-Compound made by the Atlas Company, Mertztown, Pa., Jointite and
-Filtite, manufactured by the Pacific Flush Tank Co., Chicago and New
-York, and some of the products of the Warren Brothers Co., Boston. These
-compounds fill nearly all of the ideal conditions except as to cost and
-ease in handling. They are somewhat expensive and if overheated or
-heated too long become carbonized and brittle. In cold weather they do
-not stick to the pipe well unless the pipe is heated before the joint is
-poured. On some work joints have been poured under water with these
-compounds, but success is doubtful without skillful handling. An
-overheated compound will make steam in the joint causing explosions
-which will blow the joint clean, and an underheated compound will harden
-before the joint is completed.
-
-The materials should be heated in an iron kettle over a gasoline furnace
-or other controllable fire, until they just commence to bubble and are
-of the consistency of a thin sirup. Only a sufficient quantity of
-material for immediate use should be prepared and it should be used
-within 10 to 15 minutes after it has become properly heated. The ladle
-used should be large enough to pour the entire joint without refilling.
-There are other important points to be considered in pouring joints
-which can be learned best by experience.
-
-The quantity of material necessary for making these joints, as announced
-by the manufacturers, is shown in Table 65.
-
- TABLE 65
-
- QUANTITY OF COMPOUND NEEDED FOR POURED JOINTS
-
- ───────────┬───────────────────────────────────────────────────────────
- Diameter of│
- Pipe, in │ Quantity of Material in Pounds per Joint
- Inches │
- ───────────┼─────────────────────────────┬─────────────────────────────
- │ Standard Socket │ Deep and Wide Socket
- ───────────┼─────────┬─────────┬─────────┼─────────┬─────────┬─────────
- │Jointite │ Filtite │ G. K. │Jointite │ Filtite │ G. K.
- ───────────┼─────────┼─────────┼─────────┼─────────┼─────────┼─────────
- 6│ 0.82│ 0.72│ 0.42│ 1.46│ 1.28│ 0.72
- 8│ 1.06│ 0.95│ 0.73│ 1.82│ 1.60│ 1.25
- 10│ 1.30│ 1.15│ 0.89│ 2.26│ 1.98│ 1.52
- 12│ 2.08│ 1.82│ 1.42│ 2.65│ 2.32│ 1.80
- 15│ 2.52│ 2.20│ 1.74│ 3.20│ 2.80│ 2.20
- 18│ 3.02│ 2.64│ 2.58│ 3.75│ 3.29│ 3.25
- 20│ 3.44│ 3.00│ 2.86│ 4.30│ 3.78│ 3 60
- 22│ 3.62│ 3.16│ 3.13│ 4.62│ 4.07│ 3.97
- 24│ 4.03│ 3.50│ 3.41│ 4.91│ 4.31│ 4.27
- ───────────┴─────────┴─────────┴─────────┴─────────┴─────────┴─────────
-
-In making a poured joint the pipes are first lined up in position. A
-hemp or oakum gasket is forced into the joint to fill a space of about ¾
-of an inch. An asbestos or other non-combustible gasket such as a rubber
-hose smeared with clay is forced about ½ inch into the opening between
-the bell and the spigot and the compound is poured down one side of the
-pipe through a hole broken in the bell, until it appears on the other
-side, and the hole is filled. Occasionally the non-combustible gasket is
-wrapped tightly around the spigot of the pipe and pressed or tied firmly
-to the bell. In pouring cement grout joints a paper gasket is used which
-is held to the bell and spigot by draw strings. Greater speed in
-construction and economy in the use of materials are obtained by joining
-two or three lengths of pipe on the bank and lowering them into the
-trench as a unit. The pipes are set in a vertical position on the bank
-with the bell end up, one length resting in the other. The joint is
-calked with hemp and poured without the use of the gasket. The joint
-should always be poured immediately after being calked so that the hemp
-can not become water soaked. The asbestos gasket should be removed as
-soon as possible after the joint is poured in order to prevent sticking
-with resultant danger of breaking of the joint when attempting to pull
-the gasket free.
-
-One man can pour about 33 eight-inch joints, and two men can complete
-about 26 twelve-inch joints per hour on the bank where conditions are
-more or less fixed.
-
-
-=182. Labor and Progress.=—The labor required for the laying of pipe
-sewers, exclusive of excavation, bracing and backfilling, consists of
-pipe layers and helpers. For pipes 24 to 27 inches in diameter or
-smaller one pipe layer and one or more helpers are necessary, dependent
-on the size of the pipe and the depth of the trench. For larger pipes
-two pipe layers can work economically each working on one-half of the
-pipe and making half of the joint. The speed of pipe laying is
-ordinarily limited by the speed of the excavation, but on a job in
-Topeka, Kan.,[100] where the average day’s progress with a machine
-excavator was 200 to 500 feet of trench per day, the pace was limited by
-the speed of the pipe laying gang. This gang consisted of two pipe
-layers in the trench and two helpers on the surface. The sizes of pipes
-handled were from 8 to 27 inches.
-
-
- BRICK AND BLOCK SEWERS
-
-
-=183. The Invert.=—In good firm ground the excavation is cut to the
-shape of the sewer and the bricks are laid directly on the ground, being
-embedded in a thick layer of mortar. After the foundation has been
-prepared and before the bricks are laid, two wooden templates, called
-profiles, are prepared, similar to that shown in Fig. 126, to conform to
-the shape of the inside and outside of the sewer. Each course of bricks
-is represented by a row of nails in the profile and each nail
-corresponds to a joint in the row. The two profiles are set true to line
-and grade. A cord is stretched tightly between the two lowest nails on
-opposite templates and a row of bricks is laid. The bricks are laid
-radially and on edge with their long dimension parallel to the axis of
-the sewer and with one edge just touching the string. As each one or two
-or three rows are completed the guide line is moved up to the next
-nails. When the bricks are laid on the ground all but large depressions
-are filled in with tamped sand or mortar by the masons. Approximately
-the same number of rows of bricks is kept completed on either side of
-the center line. The succeeding courses follow within three to five rows
-of each other, the only bond between courses being the mortar joint.
-This is called row lock bond and with few exceptions has been used on
-all brick sewers in the United States. As the sides of the sewer become
-higher during the construction, platforms must be built for the masons.
-These platforms are built of wood and rest directly on the green
-brickwork. They should be designed to spread the load as much as
-possible. The brickwork of the invert is continued up in this way to the
-springing line. As soon as one section is completed one profile is moved
-10 to 20 feet ahead along the trench according to the standard length of
-sections, and set in position. The line is then strung from it to nails
-driven or pushed into the cement joints of the last completed section.
-Between work done on separate days the bricks are racked back in courses
-to provide a satisfactory bond.
-
-[Illustration:
-
- FIG. 126.—Profile for Brick Sewers.
-]
-
-In ground too soft to support the brickwork directly a cradle is
-prepared by placing profiles in position in the sewer and nailing 2–inch
-planks to these profiles, first firmly tamping earth under the planks.
-The bricks are laid in this cradle in a manner similar to that explained
-for sewers with a firm foundation. In still softer ground it may be
-necessary to construct a concrete cradle to support the bricks.
-
-
-=184. The Arch.=—The arch centering consists of a wooden form made up of
-wooden ribs as shown in Fig. 127. The center conforms to the shape of
-the inside of the arch with allowance for the thickness of the lagging.
-The lagging is nailed on the ribs in straight strips parallel to the
-axis of the sewer. The center is supported on triangular struts resting
-against the sides and on the bottom of the sewer and is lifted into
-position by wedges driven between it and the support. The centers may be
-placed immediately after the completion of the invert, or a day or two
-may be allowed to pass to give the invert an opportunity to set. After
-the centers are fixed in place the arch brick are carried up evenly on
-each side and are pounded firmly into place. The center is usually, but
-not always “struck” immediately, and the arch brick are cleaned and
-pointed up from the inside. The outside is covered with a layer of ¼ to
-¾ of an inch of cement mortar and may be backfilled to the top of the
-arch in order to maintain the moisture of the mortar during setting and
-to press the bricks of the arch together firmly. The centers are
-sometimes made collapsible so that they can be carried or rolled through
-the finished brickwork to the advanced position. In “striking” the
-centers the wedges are removed and the wings folded in.
-
-[Illustration:
-
- FIG. 127.—Centering for Brick Sewer.
-]
-
-In tunneling, the invert of the sewer is constructed in the same fashion
-as for open cut work. The arch centering is made in short sections and
-the bricks are put in position by reaching in over the end of the
-centering. All of the timbering of the tunnel is removed except the
-poling boards or lagging against which the bricks or mortar are tightly
-pressed, the boards being bricked in permanently.
-
-
-=185. Block Sewers.=—Sewers made of unit blocks of concrete or vitrified
-clay are constructed in a similar manner to brick sewers. Fig. 128 shows
-the construction of a block sewer at Clinton, Iowa. In this sewer there
-are two rings; an inside one of solid blocks and an outside one of
-hollow blocks. Block sewers do not demand the skill in construction that
-is demanded by brick sewers, as the blocks are so cast that the joints
-are radial, whereas only experienced masons can lay bricks radially.
-
-[Illustration:
-
- FIG. 128.—Segmental Block Sewer at Clinton, Iowa.
-]
-
-
-=186. Organization.=—The number of men employed on a brick or block
-sewer is proportioned according to the size of the sewer and the working
-conditions. The number of men working on different tasks usually bears
-the same ratio to the number of masons employed, regardless of the size
-of the work. These proportions are shown for different jobs, in Table
-66.
-
- TABLE 66
-
- ORGANIZATIONS FOR THE CONSTRUCTION OF BRICK AND BLOCK SEWERS
-
- ─────────────┬──────────────┬────────┬────────┬────────┬────────┬──────────
- │ │ │ │ │ 84– to │
- │General Ratio │15–foot,│66–inch │84–inch │108–inch│ 42–inch
- Type of Work │ on Basis of │ 5–ring │Circular│Circular│ Sewer │Lock-Joint
- │ Four Brick │ Brick, │ Brick, │ Brick, │Brick in│Tile Block
- │ Layers │Chicago │ Gary │ Gary │Detroit │
- │ │ │ │ │ Tunnel │
- ─────────────┼──────────────┼────────┼────────┼────────┼────────┼──────────
- Foreman │ 1│ 1│ 1│ 1│ 1│ 1
- Brick layers │ 4│ 12│ 6│ 6│ 5│ 2
- Helpers │ 2│ 11│ 3│ 3│ │ 1
- Scaffold men │ 2│ 21│ 3│ │ │
- Brick tossers│ 2│ 7│ │ 15│ │ 2
- Brick │ 2│ 2│ │ │ │ 2
- carriers │ │ │ │ │ │
- Cement mixers│ 2│ 6│ 6│ 5│ │ 1
- Cement │ 2│ 10│ │ 8│ │
- carriers │ │ │ │ │ │
- Form setters │ 1│ │ 3│ 3│ │
- Laborers │ 1│ 8│ 19│ 3│ 14│ 7
- │ Municipal │
- Source of │ Engineering, │ H. P. Gillette, Handbook of Cost Data
- Information│ Vol. 54, p. │
- │ 228 │
- ─────────────┴──────────────┴──────────────────────────────────────────────
-
-
-=187. Rate of Progress.=—In a general way it can be assumed that the
-laying of 1,000 bricks will require 3⅓ hours of the time of one mason,
-10 man-hours for helpers and laborers, 2 barrels of cement, 0.6 cubic
-yard of sand, and about 10 feet board measure of centering. One thousand
-bricks will make about 2 cubic yards of brickwork. To the costs, as
-estimated on the basis of materials and labor, must be added about 15
-per cent for overhead and an additional amount for the contractor’s
-profit. The number of bricks required in various size sewers is shown in
-Table 67. A mason can lay more bricks per hour in a large sewer than in
-a small one as there is a smaller percentage of face work, there is more
-room to work, and it is easier to lay the bricks radially. The number of
-bricks laid and the rate of progress on various jobs are shown in Table
-68.
-
- TABLE 67
-
- BRICK MASONRY IN CIRCULAR SEWERS. CUBIC YARDS PER LINEAR FOOT
-
- (From H. P. Gillette)
- ─────────────────┬─────────────────┬─────────────────┬─────────────────
- Diameter, │ One Ring │ Two Ring │ Three ring
- Feet and Inches │ (4½ Inches) │ (9 Inches) │ (13½ Inches)
- ─────────────────┼─────────────────┼─────────────────┼─────────────────
- 2 0│ 0.103│ 0.240│
- 2 6│ 0.125│ 0.280│
- 3 0│ 0.147│ 0.327│
- 3 6│ 0.169│ 0.371│
- 4 0│ 0.191│ 0.415│
- 4 6│ 0.213│ 0.458│
- 5 0│ 0.234│ 0.501│ 0.802
- 5 6│ 0.256│ 0.545│ 0.867
- 6 0│ 0.278│ 0.589│ 0.933
- 6 6│ │ 0.633│ 1.000
- 7 0│ │ 0.677│ 1.063
- 7 6│ │ 0.720│ 1.128
- 8 0│ │ 0.763│ 1.193
- 8 6│ │ 0.807│ 1.260
- 9 0│ │ 0.851│ 1.325
- 9 6│ │ 0.895│ 1.390
- 10 0│ │ 0.938│ 1.456
- ─────────────────┴─────────────────┴─────────────────┴─────────────────
-
-
- CONCRETE SEWERS
-
-
-=188. Construction in Open Cut.=—In the construction of sewer pipe of
-cement and concrete one of two methods may be employed; 1st, to
-manufacture the pipe in a plant at some distance from the place of final
-use, or 2nd, to manufacture the pipe in place. The methods of the
-manufacture of cement and concrete pipe which are to be transported to
-the place of use are treated in Chapter VIII. The process of
-constructing the pipes in place is ordinarily used for pipes 48 inches
-or more in diameter. For smaller sizes, brick, vitrified clay, and
-precast cement pipes are usually more economical.
-
-The preparation of the foundation of a concrete sewer is similar to that
-for a brick sewer. If the ground is suitable the trench is shaped to the
-outside form of the sewer and the concrete poured directly on it. In
-soft material which would give poor support to a sewer with a rounded
-exterior, the bottom of the trench is cut horizontal and a concrete
-cradle of poorer quality than that in the finished sewer is poured on
-the soft ground, on a board platform, on piles, or on cribbing supported
-on piles.
-
-If the invert of the sewer is so flat that the concrete will stand
-without an inside form the shape of the invert is obtained by a screed
-or straight-edge which is passed over the surface of the concrete and
-guided on two centers, or on one center and the face of the finished
-work. The construction of a flat invert sewer at Baltimore is shown in
-Fig. 1. The center for the concrete is shown in the foreground. When the
-concrete for the next section is poured it will be smoothed to shape by
-a screed or straight-edge resting on the face of the finished concrete
-and the center. The center is shaped to conform to that of the finished
-concrete. It is firmly staked in position and acts as a bulkhead for the
-concrete as it is poured, as well as a guide for the screed.
-
- TABLE 68
-
- RATE OF PROGRESS ON BRICK SEWER CONSTRUCTION
-
- (Based on 8–hour day)
- ────────┬────────┬──────┬──────┬──────┬────────
- │ │ │ │Bricks│
- Diameter│ │Number│Number│ per │ Number
- of Sewer│ Shape │Rings,│Masons│Mason │Laborers
- │ │Brick │ │ per │
- │ │ │ │ Day │
- ────────┼────────┼──────┼──────┼──────┼────────
- 7′ 0″│Circular│ │ │ │
- 8′ 11″│ and │ 2½ │ 6│ 4710│ 39
- │ Oval │ │ │ │
- │ │ │ │ │
- │ │ │ │ │
- 4′ 0″│Circular│ 2 │ 3│ 2500│
- │ │ │ │ │
- │ │3 arch│ │ │
- 6′ 8″│Circular│ 1 │ 18│ │ 62
- │ │invert│ │ │
- │ │ │ │ │
- │ │1 arch│ │ │
- 2′ 9″│Egg │ 2 │ 2│ │ 3
- │ │invert│ │ │
- │ │ │ │ │
- 5′ 6″│Circular│ 2 │ 6│ 4570│ 35
- 6′ 6″│Circular│ │ 4│ 4800│
- │ │ │ │ │
- │ │ │ │ │
- 2′ 9″│Circular│ 2 │ 2│ 2080│ 5
- │ │ │ │ │
- 16′ 0″│Circular│ 5 │ 8│ 5 cu.│
- │ │ │ │ yd.│
- 16′ 0″│Circular│ 5 │ 12│ │ 70–75
- 3′ 6″│Egg │ │ │ 2300│
- 9′ 6″│Circular│ │ │ 3000│
- │ │ │ │ │
- │ │ │ │ │
- 3′ 6″│Circular│blocks│ 2│ │ 13
- │ │ │ │ │
- │ │ │ │ │
- ────────┴────────┴──────┴──────┴──────┴────────
-
- ────────┬────────┬────────────┬─────────┬───────────
- │ │ │ │
- Diameter│ Feet │ │ │
- of Sewer│Progress│ Location │Authority│ Remarks
- │per Day │ │ │
- │ │ │ │
- ────────┼────────┼────────────┼─────────┼───────────
- 7′ 0″│ │ │ │
- 8′ 11″│ 60│Gary │Gillette │9–hour day
- │ │ │ │
- │ │ │ │
- │ │ │Metcalf │General
- 4′ 0″│ 36│ │ and │ average
- │ │ │ Eddy │
- │ │ │ │Concrete
- 6′ 8″│ │Denver │Gillette │ invert
- │ │ │ │
- │ │ │Eng. │
- │ │Springfield,│ Con., │
- 2′ 9″│ │ Mass. │ Jan. │
- │ │ │ 16, │
- │ │ │ 1907 │
- 5′ 6″│ 110│Gary │Gillette │
- 6′ 6″│ │ │Gillette │Exceptional
- │ │ │ │ speed
- │ │ │ │Tunnel
- 2′ 9″│ 13.9│Syracuse │Gillette │ 12–hour
- │ │ │ │ day
- 16′ 0″│ 22│Chicago │Gillette │First year
- │ │ │ │
- 16′ 0″│ 35│Chicago │Gillette │Second year
- 3′ 6″│ │St. Louis │Gillette │
- 9′ 6″│ 12.5│Chicago │H. R. │
- │ │ │ Abbott │
- │ │ │ │Lock joint
- 3′ 6″│ 30│ │ │ and tile.
- │ │ │ │ 10–hour
- │ │ │ │ day
- ────────┴────────┴────────────┴─────────┴───────────
-
-If inside forms are to be used they are made as units in lengths of 12
-or 16 feet for wooden forms, and 5 feet for steel forms. The inside form
-is supported by precast concrete blocks placed under it and which are
-concreted into the sewer. It is held in position by cleats nailed to the
-outside form, to the sheeting, or wedged against the outside of the
-trench. In some cases, particularly where steel forms are used, the
-inside form is hung by chains from braces across the trench as is shown
-in Fig. 129. The form is easily brought to proper grade by adjustment of
-the turnbuckles and is then wedged into position to prevent movement
-either sideways or upwards during the pouring of the concrete. It may be
-necessary to weight the forms down to prevent flotation. Cross bracing
-in the trench which interferes with the placing of the form is removed
-and the braces are placed against the form until the concrete is poured.
-They are removed immediately in advance of the rising concrete.
-
-[Illustration:
-
- FIG. 129.—Blaw Standard Half Round Sewer Form, Suspended from Overhead
- Support.
-
- Courtesy, Blaw Steel Form Co.
-]
-
-The sewer section may be built as a monolith, in two parts, or in three
-parts. In casting the sewer as a monolith the complete full round inside
-form is fixed in place by concrete blocks and wires. The full round
-outside form is completed as far as possible without interfering too
-much with the placing and tamping of the concrete. The concrete is
-poured from the top, being kept at the same height on each side of the
-form, and tamped while being poured. The remaining panels of the outside
-form are placed in position as the concrete rises to them. An opening is
-left at the top of the outside arch forms which is of such a width that
-the concrete will stand without support. The casting of sewers as a
-monolith is difficult and is usually undesirable because of the
-uncertainty of the quality of the work. It has the advantage, however,
-of eliminating longitudinal working joints in the sewers which may allow
-the entrance of water or act as a line of weakness.
-
-[Illustration:
-
- FIG. 130.—Construction Joints for Concrete Sewers.
-]
-
-If the sewer is to be cast in two sections the invert is poured to the
-springing line or higher. A triangular or rectangular timber is set in
-the top of the wet concrete as shown in Fig. 130. When the concrete has
-set the timber is removed and the groove thus left forms a working joint
-with the arch. After the invert concrete has set, the arch centering is
-placed and the arch is completed. This is the most common method for the
-construction of medium-sized circular sewers.
-
-Large sewers with relatively flat bottoms are poured in two or three
-sections. First the invert is poured without forms and is shaped with a
-screed. About 6 inches of vertical wall is poured at the same time. This
-acts as a support for the side-wall forms. The side walls reach to the
-springing line of the arch and are poured after the invert has set. At
-the third pouring the arch is completed. The sewer shown in Fig. 1 is
-being poured in two steps, as the side walls are so low that they are
-poured at the same time as the invert. A transverse working joint
-similar to one of the types used in Fig. 130 is set between each day’s
-work.
-
-The length of the form used and the capacity of the plant should be
-adjusted so that one complete unit of invert, side wall, or arch can be
-poured in one operation. The forms are left in place until the concrete
-has set. Invert and side-wall forms are generally left in position for
-at least two days, and in cold weather longer. The arch forms are left
-in place for double this time. For example if 20 feet of invert and arch
-can be poured in a day, 60 feet of invert form and 100 feet of arch form
-will be required. As the forms are released they must be moved forward
-through those in place. For this reason collapsible or demountable forms
-are necessary and steel forms are advantageous. Wooden arch forms are
-sometimes dismantled and carried forward in sections, but are preferably
-designed to collapse as shown in Fig. 131, so that they can be pulled
-through on rollers or a carriage.
-
-
-=189. Construction in Tunnels.=—In tunnels the invert and side walls are
-constructed in the same manner as for open cut work. The tunneling,
-which acts as the outside form, is concreted permanently in place. The
-concreting of a tunnel by hand is shown in Fig. 132. If the work is to
-be done by hand the concrete is thrown in between the ribs of the arch
-centering and behind the plates or lagging, which are set in advance of
-the rising concrete. The lagging plates are 5 feet long which makes it
-possible to throw the concrete in place at the arch, and to tamp it in
-place from the end. A bulkhead and a well-greased joint timber are
-placed in position as the concrete rises.
-
-[Illustration:
-
- FIG. 131.—Section through a Collapsible Wood Form.
-]
-
-Pneumatic transmission of concrete is also used for filling the arch
-forms as well as the side walls and invert forms. In using this method
-the mixer may be placed at the surface or at the bottom of the shaft or
-other convenient permanent location which may be some distance from the
-form. The mixture is discharged into a pipe line through which it is
-blown by air to the forms. The starting pressure of about 80 pounds per
-square inch can be reduced after flow has commenced. In constructing the
-St. Louis Water Works tunnel the compressor equipment for moving the
-concrete had a capacity of 1,600 cubic feet per minute at a pressure of
-110 pounds. The tunnel is horseshoe shaped, 8 feet in height and with
-walls varying from 9 to 20 inches in thickness. The extreme travel of
-the concrete was 1,100 feet in an 8 inch pipe. The amount of air
-consumed at 110 pounds varied from 1.2 to 1.7 cubic feet of free air per
-linear foot of pipe. By the time the batch had been discharged the
-pressure had reduced to 25 to 40 pounds, depending on the length of the
-pipe. It is reported that a 6–inch pipe line would probably have given
-better results.
-
-[Illustration:
-
- FIG. 132.—Ogier’s Run Intercepting Storm-Water Drain, Baltimore,
- Maryland.
-
- Placing concrete in Arch. The steel lagging of the forms is carried up
- in sections as the concrete is deposited. The drain is horseshoe
- shaped, and is 12 feet 3 inches high and 12 feet 3 inches wide.
-]
-
-The end of the concrete conveying pipe is provided with a flexible joint
-the simplest form of which can be made by slipping a section of pipe of
-larger diameter over the end of the transmission line. The concrete is
-deposited directly on the invert or into the side-wall forms and can be
-blown into the arch forms for 20 to 25 feet.
-
-
-=190. Materials for Forms.=—The materials used in forms for concrete
-sewers are: wood, wood with steel lining, and steel alone. The first
-cost of wood forms is lower than that of steel but their life is
-relatively short. If the forms are to be used a number of times steel is
-more economical. With proper care and repairs steel forms will outlast
-any other material. Because of the increasing price of lumber and
-improvements in steel forms, wood forms are not frequently used. A
-common type of specification under which forms are used is:
-
- The material of the forms shall be of sufficient thickness and the
- frames holding the forms shall be of sufficient strength so that
- the forms shall be unyielding during the process of filling. The
- face of the form next to the concrete shall be smooth. If wooden
- forms are used the planking forming the lining shall invariably be
- fastened to the studding in horizontal lines, the ends of these
- planks shall be neatly butted against each other, and the inner
- surface of the form shall be as nearly as possible perfectly
- smooth, without crevices or offsets between the ends of adjacent
- planks. Where forms are used a second time, they shall be freshly
- jointed so as to make a perfectly smooth finish to the concrete.
- All forms shall be water-tight and shall be wetted before using.
-
-Any material in contact with wet concrete should be oiled or greased
-beforehand in order to prevent adherence to the concrete.
-
-
-=191. Design of Forms.=—The design of forms for reinforced concrete work
-requires some knowledge of the strength of materials and the theories of
-beams, columns, and arches. Forms can be constructed without such
-knowledge but that they will be both economical and adequate is an
-improbability. The ordinary beam and column formulas are applicable to
-the design of forms. The maximum bending moment for sheeting and ribs is
-taken as (_wl_^2)⁄8, where _w_ is the load per unit length, and _l_ is
-the length between supports. Sanford Thompson recommends that the
-deflection be calculated as (_wl_^3)⁄(128_EI_), in which _E_ is the
-modulus of elasticity of the material, and _I_ is the moment of inertia
-of the cross-section referred to the neutral axis. The horizontal
-pressure of the concrete against the forms has been expressed
-empirically by E. B. Smith,[101] as
-
- _P_ = _H_^{0.2}_R_^{0.3} + 120_C_ − 0.3_S_
-
- in which _P_ = lateral pressure in pounds per square inch;
-
- _R_ = rate of filling forms in feet per hour;
-
- _H_ = head of fill. Ordinarily taken as ½_R_, but in cold
- weather or when continuously agitated it may be as
- high as ¾_R_;
-
- _C_ = ratio, by volume, of cement to aggregate;
-
- _S_ = consistency in inches of slump.
-
-Earlier investigators have usually concluded that the pressures were
-equal to those caused by a liquid weighing 144 pounds per cubic foot,
-but the tests of the United States Bureau of Public Roads, from which
-the above formula was devised, show the pressures to be decidedly below
-this amount under certain conditions.
-
-[Illustration:
-
- FIG. 133.—Centering for Large Forms.
-]
-
-With these units and formulas the design of the lagging becomes a matter
-of substitution in, and the solution of, the equations produced.[102]
-The forces acting on the ribs are indeterminate. No more satisfactory
-design can be made for the ribs than to follow successful practice, or
-what is seldom done, to determine the stresses in the forms by the
-application of one of the theories for the solution of arch stresses.
-The sizes of the lumber used in the ribs varies from 1½ × 6 inches to 2
-× 10 inches, depending on the size of the sewer. If vertical posts are
-used at the ends to support the arch forms they are computed as columns
-taking the full weight of the arch. If the span is so wide that radial
-supports are used as shown in Fig. 133 the load at the center is assumed
-as one-fourth of the weight of the arch.
-
-
-=192. Wooden Forms.=—Norway and Southern pine, spruce, and fir are
-satisfactory for form construction. White pine is satisfactory but is
-generally too expensive. The hard woods are too difficult to work. The
-lumber should be only partly dried as kiln-dried lumber swells too much
-when it is moistened, warping the forms out of shape or crushing the
-lagging at the joints. Green lumber must be kept moist constantly to
-prevent warping before use and when it is used it does not swell enough
-to close the cracks. The lumber should be dressed on the face next to
-the concrete and at the ends. Either beveled or matched lumber may be
-used for lagging. The joint made by beveled lumber shown in Fig. 134 is
-cheaper but less satisfactory than a tongued and grooved joint.
-
-[Illustration:
-
- FIG. 134.—Beveled Joint for Wood Fords.
-]
-
-[Illustration:
-
- FIG. 135.—Collapsible Wooden Invert Form for Concrete Sewers.
-]
-
-[Illustration:
-
- FIG. 136.—Support for Arch Centering.
-]
-
-[Illustration:
-
- FIG. 137.—Wooden Forms Used in Tunnel, North Shore Sewer, Sanitary
- District of Chicago.
-
- Journal Western Society of Engineers, Vol. 22, p. 385.
-]
-
-Types of wooden forms are shown in Figs. 135 and 136 for use in sewers
-to be built as monoliths or in two portions. Fig. 137 shows the details
-of a built-up wooden form used in tunnel work for a 42½ inch egg-shaped
-sewer.
-
-
-=193. Steel-lined Wooden Forms.=—Sheet metal linings are sometimes used
-on wooden forms. They permit the use of cheaper undressed lumber, demand
-less care in the joining of the lagging, and when in good condition give
-a smooth surface to the finished concrete. Their use has frequently been
-found unsatisfactory and more expensive than well-constructed wooden
-forms because of the difficulty of preventing warping and crinkling of
-the metal lining and in keeping the ends fastened down so that they will
-not curl. Sheet steel or iron of No. 18 or 20 gage (0.05 to 0.0375 of an
-inch) weighing 2 to 1½ pounds per square foot is ordinarily used for the
-lining.
-
-[Illustration:
-
- FIG. 138.—Blaw Standard Full Round Telescopic Sewer Forms, Showing
- Knocked-Down Sections Loaded on a Truck.
-
- Courtesy, Blaw Steel Form Co.
-]
-
-
-=194. Steel Forms.=—These are simple, light, durable, and easy to
-handle. The engineer is seldom called upon to design these forms as the
-types most frequently used are manufactured by the patentees and are
-furnished to the contractor at a fixed rental per foot of form,
-exclusive of freight and hauling from the point of manufacture. The
-forms can be made in any shape desired, the ordinary stock shapes such
-as the circular forms being the least expensive. The smaller circular
-forms are adjustable within about 3 inches to different diameters so
-that the same form can be used for two sizes of sewers. The same form
-can be used for arch and invert in circular sewers. Fig. 138 shows the
-collapsible circular forms and the manner in which they are pulled
-through those still in position. Fig. 129 shows a half round steel form
-swung in position by chains and turnbuckles from the trench bracing, and
-Fig. 139 shows the free unobstructed working space in the interior of
-some large steel forms.
-
-[Illustration:
-
- FIG. 139.—Interior of Steel Forms for Calumet Sewer, Chicago.
-
- Sewer is 16 feet wide. Note absence of obstructions. Courtesy,
- Hydraulic Steelcraft Co.
-]
-
-
-=195. Reinforcement.=—It is essential that the reinforcement be held
-firmly in place during the pouring of the concrete. A section of
-reinforcement misplaced during construction may serve no useful purpose
-and result in the collapse of the sewer. In sewer construction a few
-longitudinal bars may be laid in order that the transverse bars may be
-wired to them and held in position by notches in the centering and in
-fastenings to bars protruding from the finished work. This construction
-is shown in Fig. 1. The network of reinforcement is held up from the
-bottom of the trench by notched boards which are removed as the concrete
-reaches them, or better by stones or concrete blocks which are concreted
-in. Sometimes the reinforcement is laid on top of the freshly poured
-portion of the concrete the surface of which is at the proper distance
-from the finished face of the work. This method has the advantage of not
-requiring any special support for the reinforcement, but it is
-undesirable because of the resulting irregularity in the reinforcement
-spacing and position.
-
-In the side walls the position of the reinforcement is fixed by wires or
-metal strips which are fastened to the outside forms or to stakes driven
-into the ground. Wires are then fastened to the reinforcement bars and
-are drawn through holes in the forms and twisted tight. When the forms
-are removed the wires or strips are cut leaving a short portion
-protruding from the face of the wall. The reinforcing steel from the
-invert should protrude into the arch or the side walls for a distance of
-about 40 diameters in order to provide good bond between the sections.
-The protruding ends are used as fastenings for the new reinforcement.
-The arch steel may be supported above the forms by specially designed
-metal supports, by small stones or concrete blocks which are concreted
-into the finished work; or by notched strips of wood which are removed
-as the concrete approaches them. Strips of wood are not satisfactory
-because they are sometimes carelessly left in place in the concrete
-resulting in a line of weakness in the structure. Metal chairs are the
-most secure supports. They are fastened to the forms and the bars are
-wired to the chairs. In some instances the entire reinforcement has been
-formed of one or two bars which are fastened into position as a complete
-ring. This results in a better bond in the reinforcement, requires less
-fastening and trouble in handling, but is in the way during the pouring
-of the concrete and interferes with the handling of the forms.
-
-
-=196. Costs of Concrete Sewers.=—Under present day conditions a general
-statement of the costs of an engineering structure can not be given with
-accuracy. Only the items of labor, materials, and transportation that go
-to make up the cost can be estimated quantitively, and the total cost
-computed by multiplying the amount of each item by its proper unit cost
-obtained from the market quotations.
-
-A summary of some of the items that go to make up the cost of a concrete
-sewer and the relative amount of these items on different jobs is given
-in Tables 69 and 70.
-
- TABLE 69
-
- DIVISION OF LABOR COSTS FOR THE CONSTRUCTION OF 96–INCH CIRCULAR
- CONCRETE SEWER
-
- ─────────────────────────────────────────╥─────────────────────────────
- Classification of Labor ║ Classification of Work
- ─────────────────┬───────────┬───────────╫─────────────────┬───────────
- Task or Title │ │ Total ║ Type of Work │
- │ Number of │dollars per║ │Dollars per
- │ men │ day ║ │ foot
- ─────────────────┼───────────┼───────────╫─────────────────┼───────────
- Superintendent │ 1│ 6.00║Excavation │ 1.80
- Engineman │ │ ║Sheeting and │
- │ 1│ 3.50║ bracing │ 0.58
- Hoister │ │ ║Bottom plank │
- (engineman) │ 1│ 2.00║ │ 0.17
- Tag-men │ 2│ 3.30║Pulling sheeting │ 0.45
- Earth diggers │ 10│ 16.50║Backfilling │ 0.33
- On dump cars │ │ ║Making and │
- │ 2│ 3.30║ placing invert │ 1.17
- Carpenter on │ │ ║Making and │
- bracing │ 2│ 3.00║ placing arch │ 1.54
- Carpenters’ │ │ ║Laying brick in │
- helpers │ 2│ 3.30║ invert │ 0.29
- Laying bottom │ 2│ 3.30║ │
- Moving pumps, │ │ ║Bending and │
- etc. │ │ ║ placing steel │
- │ 2│ 3.30║ in arch │ 0.20
- Pulling sheeting │ 3│ 5.25║ │
- Mixing and │ │ ║Bending and │
- placing │ │ ║ placing steel │
- concrete │ 16│ 26.40║ in invert │ 0.09
- On steel forms │ │ ║Moving forms and │
- │ 3│ 5.25║ centers │ 0.62
- Water boy │ │ ║Watchmen, water │
- │ 1│ 1.00║ boy, etc. │ 0.62
- Coal and oil │ │ 5.00║ │
- │ │ —————║ │ —————
- Total │ │ 90.40║ Total │ 7.86
- ─────────────────┴───────────┴───────────╨─────────────────┴───────────
- NOTES.—Trench was 12½ feet wide and of various depths. At depth of 12
- feet the cost of excavation was $1.61 per foot. From Engineering and
- Contracting, Vol. 47, p. 157.
-
-
- BACKFILLING
-
-
-=197. Methods.=—Careful backfilling is necessary to prevent the
-displacement of the newly laid pipe and to avoid subsequent settlement
-at the surface resulting in uneven street surfaces and dangers to
-foundations and other structures.
-
-The backfilling should commence as soon as the cement in the joints or
-in the sewer has obtained its initial set. Clay, sand, rock dust, or
-other fine compactible material is then packed by hand under and around
-the pipe and rammed with a shovel and light tamper. This method of
-filling is continued up to the top of the pipe. The backfill should rise
-evenly on both sides of the pipe and tamping should be continuous during
-the placing of the backfill. For the next 2 feet of depth the backfill
-should be placed with a shovel so as not to disturb the pipe, and should
-be tamped while being placed, but no tamping should be done within 6
-inches of the crown of the sewer. The tamping should become
-progressively heavier as the depth of the backfill increases. Generally
-one man tamping is provided for each man shoveling.
-
- TABLE 70
-
- DIVISION OF COSTS FOR THE CONSTRUCTION OF CONCRETE SEWERS
-
- Gillette’s Handbook of Cost Data.
- ──────────────┬────────────────────────────────────────────────────────
- Item │ Location
- ──────────────┼─────────┬────────┬──────────┬──────────────────────────
- │ Fond du │ South │ │
- │ Lac │ Bend │Wilmington│ Richmond, Indiana
- ──────────────┼─────────┼────────┼──────────┼────────┬────────┬────────
- Diameter in │ │ │ │ │ │
- inches │ 30 │ 66 │ 53 │ 54 │ 48 │ 42
- Shape │circular │circular│horseshoe │circular│circular│circular
- Plain or │ │ │ │ │ │
- reinforced │ plain │ rein. │ rein. │ rein. │ rein. │ rein.
- Cubic yards │ │ │ │ │ │
- per foot │ 0.11 │ 0.594 │ 0.37 │5″ shell│5″ shell│4″ shell
- Daily │ │ │ │ │ │
- progress, │ │ │ │ │ │
- feet │ 47 │24 to 36│ │ │ │
- Cost per foot,│ │ │ │ │ │
- dollars │ 1.20 │ 4.40 │ 2.97 │ 1.35 │ 1.08 │ 0.91
- Per cent of │ │ │ │
- total cost: │ │ │ │
- Labor │39.0[103]│ 33.5 │ 33.0 │ =17.1=
- Tools │ 1.5 │ 11.5 │ │
- Sand and │ │ │ │
- gravel │ 12.4 │ 15.5 │ 18.9 │ =19.3=
- Lumber │ 0.9 │ │ │
- Water │ 0.7 │ 11.5 │ │
- Reinforcing │ 0.0 │ │ 14.5 │ =22.3=
- Cement │ 23.0 │ 20.0 │ 27.5 │ =32.0[104]=
- Frost │ │ │ │
- prevention│ 2.0 │ │ │
- Forms │ 12.5 │ 8.0 │ 6.1 │ =9.3=
- Engineering │ 8.0 │ │ │
- Length of day,│ │ │ │
- hours │ 8 │ 10 │ │
- Year of │ │ │
- construction│ 1908 │ 1906 │ Pre-war conditions
- ──────────────┴─────────┴────────┴─────────────────────────────────────
-
-Above a point 2 feet above the top of the sewer the method pursued and
-the care observed in backfilling will depend on the character of the
-backfilling material and the location of the sewer. If the sewer is in a
-paved street the backfill is spread in layers 6 inches thick and tamped
-with rammers weighing about 40 pounds with a surface of about 30 square
-inches. One man tamping for each man shoveling is frequently specified.
-If no pavement is to be laid but it is required that the finished
-surface shall be smooth, slightly less care need be taken and only one
-man tamping is specified for each two men shoveling. On paved streets a
-reinforced concrete slab with a bearing of at least 12 inches on the
-undisturbed sides of the trench may be designed to support the pavement
-and its loads. This is of great help in preventing the unsightly
-appearance and roughness due to an improperly backfilled trench. On
-unpaved streets the backfill is crowned over the trench to a depth of
-about 6 inches and then rolled smooth by a road roller. In open fields,
-in side ditches, or in locations where obstruction to traffic or
-unsightliness need not be considered, after the first 2 feet of backfill
-have been placed with proper care, the remainder is scraped or thrown
-into the trench by hand or machine, care being taken not to drop the
-material so far as to disturb the sewer.
-
-If the top of the sewer, manhole, or other structure comes close to or
-above the surface of the ground, an earth embankment should be built at
-least 3 feet thick over and around the structure. The embankment should
-have side slopes of at least 1½ on 1 and should be tamped to a smooth
-and even finish.
-
-If sheeting is to be withdrawn from the trench it should be withdrawn
-immediately ahead of the backfilling, and in trenches subject to caving
-it may be pulled as the backfilling rises.
-
-Puddling is a process of backfilling in which the trench is filled with
-water before the filling material is thrown in. It avoids the necessity
-for tamping and can be used satisfactorily with materials that will
-drain well and will not shrink on drying. Sand and gravel are suitable
-materials for puddling, heavy clay is unsatisfactory. Puddling should
-not be resorted to before the first 2 feet of backfill has been
-carefully placed. More compact work can be obtained by tamping than with
-puddling.
-
-Frozen earth, rubbish, old lumber, and similar materials should not be
-used where a permanent finished surface is desired as these will
-decompose or soften resulting in settlement. Rocks may be thrown in the
-backfill if not dropped too far and the earth is carefully tamped around
-and over them. In rock trenches fine materials such as loam, clay, sand,
-etc., must be provided for the backfilling of the first portion of the
-trench for 2 feet over the top of the pipe. More clay can generally be
-packed in an excavation than was taken out of it, but sand and gravel
-occupy more space than originally even when carefully tamped.
-
-Tamping machines have not come into general use. One type of machine
-sometimes used consists of a gasoline engine which raises and drops a
-weighted rod. The rod can be swung back and forth across the trench
-while the apparatus is being pushed along. It is claimed that two men
-operating the machine can do the work of six to ten men tamping by hand.
-The machine delivers 50 to 60 blows per minute, with a 2 foot drop of
-the 80 to 90 pound tamping head.
-
-Backfilling in tunnels is usually difficult because of the small space
-available in which to work. Ordinarily the timbering is left in place
-and concrete is thrown in from the end of the pipe between the outside
-of the pipe and the tunnel walls and roof. If vitrified pipe is used in
-the tunnel, the backfilling is done with selected clayey material which
-is packed into place around the pipe by workmen with long tamping tools.
-The backfilling should be done with care under the supervision of a
-vigilant inspector in order that subsequent settlement of the surface
-may be prevented.
-
-
-
-
- CHAPTER XII
- MAINTENANCE OF SEWERS
-
-
-=198. Work Involved.=—The principal effort in maintaining sewers is to
-keep them clean and unobstructed. A sewerage system, although buried,
-cannot be forgotten as it will not care for itself, but becoming clogged
-will force itself on the attention of the community. Besides the
-cleaning and repairing of sewers and the making of inspections for
-determining the necessity for this work, ordinances should be prepared
-and enforced for the purpose of protecting the sewers from abuse.
-Inspections to determine the amount of the depreciation of sewers with a
-view towards possible renewal, or to determine the capacity of a sewer
-in relation to the load imposed upon it are sometimes necessary. The
-valuation of the sewerage system as an item in the inventory of city
-property may be assigned to the engineer in charge of sewer maintenance.
-
-The work involved in the inspection and cleaning of sewers in New York
-City for the year ending May, 1914, included the removal of 22,687 cubic
-yards of material from catch-basins, and 14,826 catch-basin cleanings.
-This made an average of two and one-half cleanings per catch-basin per
-year, or 1½ cubic yards removed at each cleaning. The 6,432 catch-basins
-were inspected 71,890 times. There were 4,112 cubic yards of material
-removed from 517 miles of sewers, or about 8 cubic yards per mile.
-Inspection of 194 miles of brick sewers were made, 4.4 miles were
-flushed, and 27 miles were cleaned. Inspections of 198 miles of pipe
-sewers were made, 80 miles were examined more closely, 37 miles were
-flushed, and 91 miles were cleaned. The field organization for this work
-consisted of 17 foremen, 8 assistant foremen, 29 laborers, 71 cleaners,
-13 mechanics, 7 inspectors of construction, 3 inspectors of sewer
-connections, 13 horses and wagons, and 28 horses and carts.[105]
-
-
-=199. Causes of Troubles.=—The complaints most frequently received about
-sewers are caused by clogging, breakage of pipes, and bad odors. Sewers
-become clogged by the deposition of sand and other detritus which
-results in the formation of pools in which organic matter deposits,
-aggravating the clogged condition of the sewers and causing the odors
-complained of. Grease is a prolific cause of trouble. It is discharged
-into the sewer in hot wastes, and becoming cooled, deposits in thick
-layers which may effectively block the sewer if not removed. It can be
-prevented from entering the sewers by the installation of grease traps
-as described in Chapter VI. The periodic cleaning of these traps is as
-important as their installation.
-
-Tree roots are troublesome, particularly in small pipe sewers in
-residential districts. Roots of the North Carolina poplar, silver leaf
-poplar, willow, elm, and other trees will enter the sewer through minute
-holes and may fill the sewer barrel completely if not cut away in time.
-Fungus growths occasionally cause trouble in sewers by forming a network
-of tendrils that catches floating objects and builds a barricade across
-the sewer. Difficulties from fungus growths are not common, but constant
-attention must be given to the removal of grit, grease, and roots. Tarry
-deposits from gas-manufacturing plants are occasionally a cause of
-trouble, as they cement the detritus already deposited into a tough and
-gummy mass that clings tenaciously to the sewer.
-
-Broken sewers are caused by excessive superimposed loads, undermining,
-and progressive deterioration. The changing character of a district may
-result in a change of street grade, an increase in the weight of
-traffic, or in the construction of other structures causing loads upon
-the sewer for which it was not designed. The presence of corrosive acids
-or gases may cause the deterioration of the material of the sewer.
-
-
-=200. Inspection.=—The maintenance of a sewerage system is usually
-placed under the direction of a sewer department. In the organization of
-the work of this department no regular routine of inspection of all
-sewers need be followed ordinarily. Attention should be given regularly
-to those sewers that are known to give trouble, whereas the less
-troublesome sewers need not be inspected more frequently than once a
-year, preferably during the winter when labor is easier to obtain.
-
-The routine inspection of sewers too small to enter is made by an
-examination at the manhole. If the water is running as freely at one
-manhole as at the next manhole above, it is assumed that the sewer
-between the manholes is clean and no further inspection need be given
-unless there is some other reason to suspect clogging between manholes.
-If the sewage is backed up in a manhole it indicates that there is an
-obstruction in the sewer below. If the sewage in a manhole is flowing
-sluggishly and is covered with scum it is an indication of clogging,
-slow velocity and septic action in the sewer. Sludge banks on the
-sloping bottom of the manhole or signs of sewage high upon the walls
-indicate an occasional flooding of the sewer due to inadequate capacity
-or clogging.
-
-[Illustration:
-
- FIG. 140.—Inspecting Sewers with Reflected Sunlight.
-]
-
-If any of the signs observed indicate that the sewer is clogged, the
-manhole should be entered and the sewer more carefully inspected. Such
-inspection may be made with the aid of mirrors as shown in Fig. 140 or
-with a periscope device as shown in Fig. 141. Sunlight is more brilliant
-than the electric lamp shown in Fig. 141, but the mirror in the manhole
-directs the sunlight into the eyes of the observer, dazzling him and
-preventing a good view of the sides of the sewer. The observers’ eyes
-can be protected against the direct rays of the electric light, which
-can be projected against the sides of the pipe by proper shades and
-reflectors. It is possible with this device to locate house connection,
-stoppages, breaks of the pipe, and to determine fairly accurately the
-condition of the sewer without discomfort to the observers.
-
-Sewers that are large enough to enter should be inspected by walking
-through them where possible. The inspection should be conducted by
-cleaning off the sewer surface in spots with a small broom, and
-examining the brick wall for loose bricks, loose cement or cement lost
-from the joints, open joints, broken bond, eroded invert, and such other
-items as may cause trouble. An inspection in storm sewers is sometimes
-of value in detecting the presence of forbidden house connections.
-
-[Illustration:
-
- FIG. 141.—Inspecting Sewers with Periscope and Electric Light. The G-K
- System.
-]
-
-Certain precautions should be taken before entering sewers or manholes.
-If a distinct odor of gasoline is evident the sewer should be ventilated
-as well as possible by leaving a number of manhole covers open along the
-line until the odor of gasoline has disappeared. The strength of
-gasoline odor above which it is unsafe to enter a sewer is a matter of
-experience possessed by few. A slight odor of gasoline is evident in
-many sewers and indicates no special danger. A discussion of the amount
-of gasoline necessary to create explosive conditions is given in Art.
-206. In making observations of the odor it should also be noted whether
-air is entering or leaving the manhole. The presence of gasoline cannot
-be detected at a manhole into which air is entering.
-
-As soon as it is considered that the odors from a sewer indicate the
-absence of an explosive mixture, a lighted lantern or other open flame
-should be lowered into the manhole to test the presence of oxygen.
-Carbon monoxide or other asphyxiating gases may accumulate in the sewer,
-and if present will extinguish the flame. If the flame burns brilliantly
-the sewer is probably safe to enter, but if conditions are unknown or
-uncertain, the man entering should wear a life belt attached to a rope
-and tended by a man at the surface. Asphyxiating or explosive gases are
-sometimes run into without warning due to their lack of odor, or the
-presence of stronger odors in the sewer. Breathing masks and electric
-lamps are precautions against these dangers, the masks being ready for
-use only when actually needed. More deaths have occurred in sewers due
-to asphyxiating gases than by explosions, as the average sewer explosion
-is of insufficient violence to do great damage, although on occasion,
-extremely violent explosions have occurred. During inspections of sewers
-there should always be at least one man at the surface to call help in
-case of accident and the inspecting party should consist of at least two
-men.
-
-It must not be felt that entering sewers is fraught with great danger,
-as it is perfectly safe to enter the average sewer. The air is not
-unpleasant and no discomfort is felt, but conditions are such that
-unexpected situations may arise for which the man in the sewer should be
-prepared. It is therefore wise to take certain precautions. These may
-indicate to the uninitiated, a greater danger than actually exists.
-
-The inspection of sewers should include the inspection of the
-flush-tanks, control devices, grit chambers, and other appurtenances. A
-common difficulty found with flush-tanks is that the tank is “drooling,”
-that is to say the water is trickling out of the siphon as fast as it is
-entering the tank, and the intermittency of the discharge has ceased.
-If, when the tank is first inspected the water is about at the level of
-the top of the bell it is probable that the siphon is drooling. A mark
-should be made at the elevation of the water surface and the tank
-inspected again in the course of an hour or more. If the water level is
-unchanged the siphon is drooling. This may be caused by the clogging of
-the snift hole or by a rag or other obstacle hanging over the siphon
-which permits water to pass before the air has been exhausted, or a
-misplacement of the cap over the siphon, or other difficulty which may
-be recognized when the principle on which the siphon operates is
-understood. Occasionally it is discovered that an over zealous water
-department has shut off the service.
-
-Control devices, such as leaping or overflow weirs, automatic valves,
-etc., may become clogged and cease to operate satisfactorily. They
-should be inspected frequently, dependent upon their importance and the
-frequency with which they have been found to be inoperative. An
-inspection will reveal the obstacle which should be removed. Floats
-should be examined for loss of buoyancy or leaks rendering them useless.
-Grit and screen chambers should be examined for sludge deposits.
-
-Catch-basins on storm sewers are a frequent cause of trouble and need
-more or less frequent cleaning. Cleanings are more important than
-inspections for catch-basins for if they are operating properly they are
-usually in need of cleaning after every storm of any magnitude, and a
-regular schedule of cleaning should be maintained.
-
-A record should be kept of all inspections made. It should include an
-account of the inspection, its date, the conditions found, by whom made
-and the remedies taken to effect repairs.
-
-
-=201. Repairs.=—Common repairs to sewerage systems consist in replacing
-street inlets or catch-basin covers broken by traffic; raising or
-lowering catch-basin or manhole heads to compensate for the sinking of
-the manhole or the wear of the pavement; replacing of broken pipes,
-loosened bricks or mortar which has dropped out; and other miscellaneous
-repairs as the necessity may arise. Connections from private drains are
-a source of trouble because either the sewer or the drain has broken due
-to careless work or the settlement of the foundation or the backfill.
-
-
-=202. Cleaning Sewers.=—Sewers too small to enter are cleaned by
-thrusting rods or by dragging through them some one of the various
-instruments available. The common sewer rod shown in Fig. 142 is a
-hickory stick, or light metal rod, 3 or 4 feet long, on the end of which
-is a coupling which cannot come undone in the sewer. Sections of the rod
-are joined in the manhole and pushed down the sewer until the
-obstruction is reached and dislodged. Occasionally pieces of pipe
-screwed together are used with success. The end section may be fitted
-with a special cutting shoe for dislodging obstructions. In extreme
-cases these rods may be pushed 400 to 500 feet, but are more effective
-at shorter distances. Obstructions may be dislodged by shoving a fire
-hose, which is discharging water under high pressure through a small
-nozzle, down the sewer toward the obstruction. The water pressure
-stiffens the hose, which, together with the support from the sides of
-the conduit, make it possible to push the hose in for effective work 100
-feet or more from the manhole. A strip of flexible steel about ½ inch
-thick and 1½ to 2 inches wide is useful for “rodding” a short length of
-crooked sewer.
-
-[Illustration:
-
- FIG. 142.—Sewer Rods
-]
-
-Sewers are seldom so clogged that no channel whatever remains. As a
-sewer becomes more and more clogged, the passage becomes smaller,
-thereby increasing the velocity of flow of the sewage around the
-obstruction and maintaining a passageway by erosion. This phenomenon has
-been taken advantage of in the cleaning of sewers by “pills.” These
-consist of a series of light hollow balls varying in size. One of the
-smaller balls is put into the sewer at a manhole. When the ball strikes
-an obstruction it is caught and jammed against the roof of the sewer.
-The sewage is backed up and seeks an outlet around the ball, thus
-clearing a channel and washing the ball along with it. The ball is
-caught at the next manhole below. A net should be placed for catching
-the ball and a small dam to prevent the dislodged detritus from passing
-down into the next length of pipe. The feeding of the balls into the
-sewer is continued, using larger and larger sizes, until the sewer is
-clean. This method is particularly useful for the removal of sludge
-deposits, but it is not effective against roots and grease. The balls
-should be sufficiently light to float. Hollow metal balls are better
-than heavier wooden ones.
-
-[Illustration:
-
- FIG. 143.—Cable and Windlass Method of Cleaning Sewers.
-
- The cable is held to the bottom of the sewer by bracing a 2 x 4
- upright in the sewer, with a snatch block attached. A trailer is
- attached to the scoop to prevent loss of material.
-]
-
-Plows and other scraping instruments are dragged through pipe sewers to
-loosen banks of sludge and detritus and to cut roots or dislodge
-obstructions. One form of plow consists of a scoop[106] similar to a
-grocer’s sugar scoop, which is pushed or dragged up a sewer against the
-direction of flow. As fast as the scoop is filled it is drawn back and
-emptied. The method of dragging this through a sewer is indicated in
-Fig. 143. At Atlantic City the crew operating the scoop comprises five
-men, two are at work in each manhole and one on the surface to warn
-traffic and wait on the men in the manholes. The outfit of tools is
-contained in a hand-drawn tool box and includes sewer rods, metal scoops
-for all sizes of sewers, picks, shovels, hatchets, chisels, lanterns,
-grease and root cutters, etc., and two winches with from 400 to 600 feet
-of ⅜-inch wire cable.
-
-[Illustration:
-
- FIG. 144.—Sewer Cleaning Device.
-
- Eng. News, Vol. 42, 1899, p. 328.
-]
-
-[Illustration:
-
- FIG. 145.—Tools for Cleaning Sewers.
-]
-
-[Illustration:
-
- FIG. 146.—Turbine Sewer Machine Connected to Forcing Jack.
-
- The forcing jack is used when windlass and cable cannot be used.
-
- Courtesy, The Turbine Sewer Machine Co.
-]
-
-Another form of plow or drag consists of a set of hooks or teeth hinged
-to a central bar as shown in Fig. 144. A root cutter and grease scraper
-in the form of a spiral spring with sharpened edges, and other tools for
-cleaning sewers are shown in Fig. 145. A turbine sewer cleaner shown in
-Fig. 146 consists of a set of cutting blades which are revolved by a
-hydraulic motor of about 3 horse-power under an operating pressure of
-about 60 pounds per square inch. The turbine is attached to a standard
-fire hose and is pushed through the sewer by utilizing the stiffness of
-the hose, or by rods attached to a pushing jack as shown in the figure.
-This machine was invented and patented by W. A. Stevenson in 1914. Its
-performance is excellent. The blades revolve at about 600 R.P.M.,
-cutting roots and grease. The revolving blades and the escaping water
-also serve to loosen and stir up the deposits and the forward helical
-motion imparted to the water is useful in pushing the material ahead of
-the machine and in scrubbing the walls of the sewer. In Milwaukee four
-men with the machine cleaned 319 feet of 12–inch sewer in 16 hours, and
-in Kansas City 7,801 feet of sewers were cleaned in 14 days.
-
-Sewers large enough to enter may be cleaned by hand. The materials to be
-removed are shoveled into buckets which are carried or floated to
-manholes, raised to the surface and dumped. In very large sewers
-temporary tracks have been laid and small cars pushed to the manhole for
-the removal of the material. Hydraulic sand ejectors may also be used
-for the removal of deposits, similar to the steam ejector pump shown in
-Fig. 97. The water enters the apparatus at high velocity, under a
-pressure of about 60 pounds per square inch, leaps a gap in the machine
-from a nozzle to a funnel-shaped guide leading to the discharge pipe.
-The suction pipe of the machine leads to the chamber in which the leap
-is made. In leaping this gap the water creates a vacuum that is
-sufficient to remove the uncemented detritus large enough to pass
-through the machine, and will lift small stones to a height of 10 to 12
-feet. Occasionally barricades of logs, tree branches, rope, leaves, and
-other obstructions which have piled up against some inward projecting
-portion of the sewer, must be removed by hand either by cutting with an
-axe or by pulling them out. Projections from the sides of sewers are
-objectionable because of their tendency to catch obstacles and form
-barricades.
-
-Little authentic information on the cost of cleaning sewers is
-available. A permanent sewer organization is maintained by many cities.
-The division of their time between repairs, cleaning, and other duties
-is seldom made a matter of record. From data published in Public
-Works[107] it is probable that the cost varies from $3 to $15 per cubic
-yard of material removed. From the information in Vol. II of “American
-Sewerage Practice” by Metcalf and Eddy the combined cost of cleaning and
-flushing will vary between $10 and $40 per mile; the expense of either
-flushing or cleaning alone being about one-half of this.
-
-
-=203. Flushing Sewers.=—Sewers can sometimes be cleaned or kept clean by
-flushing. Flushing may be automatic and frequent, or hand flushing may
-be resorted to at intervals to remove accumulated deposits. Automatic
-flush-tanks, flushing manholes, a fire hose, a connection to a water
-main, a temporary fixed dam, a moving dam, and other methods are used in
-flushing sewers. The design, operation, and results obtained from the
-use of automatic flush-tanks and flushing manholes are discussed in
-Chapter VI.
-
-The method in use for cleaning a sewer by thrusting a fire hose down it
-can also be used for flushing sewers. It is an inexpensive and fairly
-satisfactory method. There is, however, some danger of displacing the
-sewer pipe because of the high velocity of the water. An easier and
-safer but less effective method is to allow water to enter at the
-manhole and flow down the sewer by gravity. Direct connections to the
-water mains are sometimes opened for the same purpose.
-
-Sewers are sometimes flushed by the construction of a temporary dam
-across the sewer, causing the sewage to back up. When the sewer is half
-to three-quarters full the dam is suddenly removed and the accumulated
-sewage allowed to rush down the sewer, thus flushing it out. The dam may
-be made of sand bags, boards fitted to the sewer, or a combination of
-boards and bags. The expense of equipment for flushing by this method is
-less than that by any other method, but the results obtained are not
-always desirable. Below the dam the results compare favorably with those
-obtained by other methods, but above the dam the stoppage of the flow of
-the sewage may cause depositions of greater quantities of material than
-have been flushed out below. A time should be chosen for the application
-of this method when the sewage is comparatively weak and free from
-suspended matter. The most convenient place for the construction of a
-dam is at a manhole in order that the operator may be clear of the rush
-of sewage when the dam is removed.
-
-Movable dams or scrapers are useful in cleaning sewers of a moderate
-size, but are of little value in small sewers. The scraper fits loosely
-against the sides of the sewer and is pushed forward by the pressure of
-the sewage accumulated behind it. The iron-shod sides of the dam serve
-to scrape grease and growths attached to the sewer and to stir up sand
-and sludge deposited on the bottom. The high velocity of the sewage
-escaping around the sides of the dam aids in cleaning and scrubbing the
-sewer.
-
-A natural watercourse may be diverted into the sewer if topographical
-conditions permit, or where sewers discharge into the sea below high
-tide a gate may be closed during the flood and held closed until the
-ebb. The rush of sewage on the opening of the gate serves to flush the
-sewers and stir up the sludge deposited during high tide. Other methods
-of flushing sewers may be used dependent on the local conditions and the
-ingenuity of the engineer or foreman in charge.
-
-In some sewers it is not necessary to remove the clogging material from
-the sewer. It is sufficient to flush and push it along until it is
-picked up and carried away by higher velocities caused by steeper grades
-or larger amounts of sewage.
-
-
-=204. Cleaning Catch-basins.=[108]—Catch-basins have no reason for
-existence if they are not kept clean. Their purpose is to catch
-undesirable settling solids and to prevent them from entering the
-sewers, on the theory that it is cheaper to clean a catch-basin than it
-is to clean a sewer. If the cleaning of storm sewers below some inlet to
-which no catch-basin is attached becomes burdensome, the engineer in
-charge of maintenance should install an adequate catch-basin and keep it
-clean. Catch-basins are cleaned by hand, suction pumps, and grab
-buckets. In cleaning by hand the accumulated water and sludge are
-removed by a bucket or dipper and dumped into a wagon from which the
-surplus settled water is allowed to run back into the sewer. The grit at
-the bottom of the catch-basin is removed by shoveling it into buckets
-which are then hoisted to the surface and emptied.
-
-Suction pumps in use for cleaning catch-basins are of the hydraulic
-eductor type. The eductor works on the principle of the steam pump shown
-in Fig. 97, except that water is used instead of steam. The material
-removed may be discharged into settling basins constructed in the
-street, or may be discharged directly into wagons.[109] In Chicago a
-special motor-driven apparatus is used. This consists of a 5–yard body
-on a 5–ton truck, and a centrifugal pump driven by the truck motor. In
-use, the truck, about half filled with water, drives up to the
-catch-basin, the eductor pipe is lowered and water pumped from the truck
-into the eductor and back into the truck again, together with the
-contents of the catch-basin. The surplus water drains back into the
-sewer. The Chicago Bureau of Sewers reports a truck so equipped to have
-cleaned 1013 catch-basins, removing 1763 cubic yards of material, and
-running 1380 miles, during the months of August, September and October,
-1917. The cost, including all items of depreciation, wages, repairs,
-etc., was $1,393.89. Orange-peel buckets, about 20 inches in diameter,
-operated by hand or by the motor of a 3½ to 5–ton truck with a
-water-tight body, are used for cleaning catch-basins in some cities.
-
-Catch-basins in unpaved streets and on steep sandy slopes should be
-cleaned after every storm of consequence. Basins which serve to catch
-only the grit from pavement washings require cleaning about two or three
-times per year, and from one to three cubic yards of material are
-removed at each cleaning. The cost of cleaning ordinary catch-basins by
-hand may vary from $15 to $25, but with the use of eductors or
-orange-peel buckets the cost is somewhat lower. In Seattle the cost of
-cleaning large detritus basins by hand is said[110] to vary from $45 to
-$60. With the use of eductors this cost has been reduced to one-third or
-one-fifth the cost of cleaning by hand.
-
-
-=205. Protection of Sewers.=[111]—City ordinances should be wisely drawn
-and strictly enforced for the protection of sewers against abuse and
-destruction. The requirements of some city ordinances are given in the
-following paragraphs.
-
-Washington, D. C.,[112] sewer ordinances provide that:
-
- No person shall make or maintain any connection with any public
- sewer or appurtenance thereof whereby there may be conveyed into
- the same any hot, suffocating, corrosive, inflammable or explosive
- liquid, gas, vapor, substance or material of any kind ... provided
- that the provisions of this act shall not apply to water from
- ordinary hot water boilers or residences.
-
-The following extracts from the ordinances of Indianapolis are typical
-of those from many cities:
-
- 2950. No connection shall be made with any public sewer without
- the written permission of the Committee on Sewers and the Sewerage
- Engineer.
-
- 2953. No person shall be authorized to do the work of making
- connections until he has furnished a satisfactory certificate that
- he is qualified for the duties. He shall also file bond for not
- less than $1,000 that he will indemnify the City from all loss or
- damage that may result from his work and that he will do the work
- in conformity to the rules and regulations established by the City
- Council.
-
- 2955. It shall be unlawful for any person to allow premises
- connected to the sewers or drains to remain without good fixtures
- so attached as to allow a sufficiency of water to be applied to
- keep the same unobstructed.
-
- 2956. No butcher’s offal or garbage, or dead animals, or
- obstructions of any kind shall be thrown in any receiving basin or
- sewer in penalty not greater than $100. Any person injuring,
- breaking, or removing any portion of any receiving basin, manhole
- cover, etc., shall be fined not more than $100.
-
- 2962. No person shall drain the contents of any cesspool or privy
- vault into any sewer without the permission of the Common Council.
-
-The Cleveland ordinances are similar and contain the following in
-addition:
-
- 1251. Rule 4. All connections with the main or branch sewers shall
- be made at the regular connections or junctions built into the
- same, except by special permit.
-
- Rule 16. No steam pipe, nor the exhaust, nor the blow off from any
- steam engine shall be connected with any sewer.
-
-Evanston, Illinois, protects its sewers against the additions of grease
-and other undesirable substances as follows:
-
- 1444. It is unlawful for any person to use any sewer or
- appurtenance to the sewerage system in any manner contrary to the
- orders of the Commissioner of Public Works.
-
- 1446. Wastes from any kitchen sinks, floor drains, or other
- fixtures likely to contain greasy matter from hotels, certain
- apartment houses, boarding houses, restaurants, butcher shops,
- packing houses, lard rendering establishments, bakeries,
- laundries, cleaning establishments, garages, stables, yard and
- floor drains, and drains from gravel roofs shall be made through
- intervening receiving basins constructed as prescribed in par.
- VIII of this code.
-
-Receiving basins suitable for the work required in the code are
-illustrated in Chapter VI.
-
-
-=206. Explosions in Sewers.=—Disastrous explosions in sewers were first
-recorded about 1886.[113] Up to about 1905 explosions were infrequent
-and were considered as unavoidable accidents and so rare as to be
-unworthy of study. For a decade or more after 1905 explosions occurred
-with increasing violence and frequency causing destruction of property,
-but by some freakish chance, but little loss of life. A violent and
-destructive explosion occurred in Pittsburgh on Nov. 25, 1913,[114] and
-another on March 12, 1916. The property damage amounted to $300,000 to
-$500,000 on each occasion, but there was no loss of life. Two miles of
-pavement were ripped up, gas, water, and other sewer pipes were broken,
-buildings collapsed and the streets were flooded. The streets were
-rendered unserviceable for long periods during the expensive repairs
-that were necessary. In recent years the number of explosions in sewers
-has been smaller, due probably to the gain in knowledge of the causes
-and intelligent methods of prevention.
-
-The three principal causes of explosions in sewers are: gasoline vapor,
-illuminating gas, and calcium carbide. It is probable that gasoline
-vapor is by far the most troublesome. Explosions caused by these gases
-are not so violent as those caused by dynamite or other high explosives,
-as the volume of gas and the temperature generated are much less. The
-violence of sewer explosions may be increased somewhat by the sudden
-pressures that are put upon them.
-
-Gasoline finds its way into sewers from garages and cleaning
-establishments. A mixture of 1½ per cent gasoline vapor and air may be
-explosive. It needs only the stray spark of an electric current, a
-lighted match, or a cigar thrown into the sewer to cause the explosion.
-As the result of a series of experiments on 2,706 feet of 8–foot sewer,
-Burrell and Boyd conclude.[115]
-
- One gallon of gasoline if entirely vaporized produces about 32
- cubic feet of vapor at ordinary temperature and pressure. If 1½
- per cent be adopted as the low explosive limit of mixtures of
- gasoline vapor and air, 55 gallons or a barrel of gasoline would
- produce enough vapor to render explosive the mixture in 1,900 feet
- of 9 foot sewer provided the gasoline and the air were perfectly
- mixed. Many different factors, however, govern explosibility, such
- as: size of the sewer, velocity of the sewage, temperature of the
- sewer, volatility and rate of inflow of the gasoline. Only under
- identical conditions of tests would duplicate results be obtained.
- A large amount of gasoline poured in at one time is less dangerous
- than the same amount allowed to run in slowly. With a velocity of
- flow of about 6½ feet per second it was evident that 55 gallons of
- gasoline poured all at once into a manhole rendered the air
- explosive only a few minutes (less than 10) at any particular
- point. With the same amount of gasoline run in at the rate of 5
- gallons per minute, an explosive flame would have swept along the
- sewer if ignited 15 minutes after the gasoline had been dumped.
- With a slow velocity of flow and a submerged outlet the gasoline
- vapor being heavier than air accumulated at one point and
- extremely explosive conditions could result from a small amount of
- gasoline. Comparatively rich explosive mixtures were found 5 hours
- after the gasoline had been discharged. High-test gasoline is much
- more dangerous than the naphtha used in cleaning establishments,
- yet on account of the large quantity of waste naphtha the sewage
- from cleaning establishments may be very dangerous.
-
-Illuminating gas is not so dangerous as gasoline vapor as it is lighter
-than air and it is more likely to escape from the sewer than to
-accumulate in it. It requires about one part of illuminating gas to
-seven parts of air to produce an explosive mixture.
-
-Calcium carbide is dangerous because it is self igniting. The heat of
-the generation of gas is sufficient to ignite the explosive mixture. The
-gases are highly explosive and cause a relatively powerful explosion.
-Fortunately large amounts of this material seldom reach a sewer, the gas
-being generated in garage drains or traps and escaping in the
-atmosphere.
-
-A hydrocarbon oil used by railroads in preventing the freezing of
-switches, if allowed to reach the sewers, may cause explosions
-therein.[116] The oil crystallizes and in this form it is soluble in
-water. It will thus pass traps and on volatilization will produce
-explosive mixtures.
-
-Methane, generated by the decomposition of organic matter, is a feebly
-explosive gas occasionally found in sewers. Its presence may add to the
-strength of other explosive mixtures.
-
-Sewer explosions may be prevented by the building of proper forms of
-intercepting basins to prevent the entrance of gasoline and calcium
-carbide gases, and by ventilation to dilute the explosive mixtures which
-may be made up in the sewer. There are no practical means to predict
-when an explosion is about to occur, and after an explosion has occurred
-it is difficult to determine the cause as all evidence is usually
-destroyed.
-
-
-=207. Valuation of Sewers.=—The necessity for the valuation of a
-sewerage system may arise from the legal provisions in some states
-limiting the amount of outstanding bonds which may be issued by a
-municipality to a certain percentage of the present worth of municipal
-property. The investment in the sewerage system is usually great and
-forms a large portion of the City’s tangible property. It may be
-desirable also to determine the depreciation of the sewers with a view
-towards their renewal.
-
-The most valuable work on the valuation of sewers has been done in New
-York City[117] by the engineers of the Sewer Department. The committee
-of engineers appointed to do the work recommended: (1) that the original
-cost be made the basis of valuation, and that (2), in fixing this cost
-the cost of pavement should be omitted or at most the cost of a cheap
-(cobblestone) pavement should be included. Trenches previously excavated
-in rock were considered as undepreciated assets.
-
-The present worth of sewers depends on many factors aside from the
-effects of age, such as the care exercised in the original construction,
-the material used, the kind and quantity of sewage carried, the care
-taken in maintenance, and finally the injury caused by the careless
-building of adjoining substructures. During the progress of the
-inspections the examination of brick sewers, due to their accessibility,
-yielded better results than the examination of pipe sewers. The routine
-of the examination of the brick sewers consisted in cleaning off the
-bricks with a short broom, tapping the brick with a light hammer to
-determine solidity, and testing the cement joints by scraping with a
-chisel. In addition, measurements of height and width were taken every
-30 feet. The bricks in the invert at and below the flow line were
-examined for wear.
-
-A study of the reports of these examinations disclosed that the
-following defects were noticeable:
-
- 1. Cement partly out at water line.
-
- 2. Cement partly out above water line.
-
- 3. Depressed arch and sewer slightly spread.
-
- 4. Large open joints.
-
- 5. Loose brick.
-
- 6. Bond of brick broken.
-
- 7. Distorted sides, uneven bottom, joints out of line.
-
-[Illustration:
-
- FIG. 147.—Diagrams used in Estimating Depreciation of Brick Sewers Due
- to Age, Manhattan Borough, New York City.
-
- _a._ Proportionate deterioration from various causes.
-
- _b._ Percentage of depreciation based on examination of sewers, use of
- deterioration curve (Fig. a), and age of sewers examined.
-
- Eng. News, Vol. 71, p. 84.
-]
-
-Inspection of pipe sewers from manholes, the pipe being illuminated by
-floating candles, was found to be unsatisfactory. Reliance was placed on
-the reports of men experienced in making connections and repairs to the
-sewers. Early pipe sewers in New York were laid directly on the bottom
-of the trench. Under these circumstances a small leak at a joint was
-sufficient to wash the earth away and to drop the pipe, causing serious
-conditions along the line. No wear or deterioration of pipe sewers were
-noted, the only defects being cracking of the pipes at the center line
-due to poor foundation and to defects in the pipe itself.
-
-[Illustration:
-
- FIG. 148.—Diagram Showing Rate of Depreciation of Pipe Sewers.
-
- Eng. News, Vol. 71, p. 86.
-]
-
-The depreciation of brick sewers as studied in New York, is shown
-graphically in Fig. 147. At zero the sewer is in good condition and at
-100 it is in such a state of dilapidation as to require instant
-rebuilding. Repairs are not considered economical in this condition. In
-the preparation of this diagram each condition on the list above was
-given a certain number of points, which when added together represented
-the state of depreciation of the sewer. These sums were plotted as
-ordinates and the corresponding ages of the sewer were plotted as
-abscissas. The various points were taken cumulatively, and where the
-bond of the brickwork was broken (given a value of 72) plus other
-defects gave a total of 164 the sewer was considered as valueless and
-not worth repair. The scale of 164 was later reduced to a percentage
-basis as shown on the right of the figure. Fig. 148 shows a similar
-diagram for the depreciation of pipe sewers.
-
-It was concluded that the life of a brick sewer in New York is 64 years.
-Some of the sewers examined were over 200 years old. The total original
-cost of 483 miles of brick, pipe and wood sewers was figured as
-$23,880,000 with a present worth of $18,665,000 and an average annual
-depreciation of 2.2 per cent. In figuring these amounts no account was
-taken of obsolescence. The deterioration of catch-basins proceeded at
-about the same rate as for brick sewers.
-
-
-
-
- CHAPTER XIII
- COMPOSITION AND PROPERTIES OF SEWAGE
-
-
-=208. Physical Characteristics.=—Sewage is the spent water supply of a
-community containing the wastes from domestic, industrial, or commercial
-use, and such surface and ground water as may enter the sewer.[118]
-Sewages are classed as: domestic sewage, industrial waste, storm water,
-surface water, street wash, and ground water. Domestic sewage is the
-liquid discharged from residences or institutions and contains water
-closet, laundry, and kitchen wastes. It is sometimes called sanitary
-sewage. Industrial sewage is the liquid waste resulting from processes
-employed in industrial establishments. Storm water is that part of the
-rainfall which runs over the surface of the ground during a storm and
-for such a short period following a storm as the flow exceeds the normal
-and ordinary run-off. Surface water is that part of the rainfall which
-runs over the surface of the ground some time after a storm. Street wash
-is the liquid flowing on or from the street surface. Ground water is
-water standing in or flowing through the ground below its surface.
-
-Ordinary fresh sewage is gray in color, somewhat of the appearance of
-soapy dish water. It contains particles of suspended matter which are
-visible to the naked eye. If the sewage is fresh the character of some
-of the suspended matter can be distinguished as: matches, bits of paper,
-fecal matter, rags, etc. The amount of suspended matter in sewage is
-small, so small as to have no practical effect on the specific gravity
-of the liquid nor to necessitate the modification of hydraulic formulas
-developed for application to the flow of water. The total suspended
-matter in a normal strong domestic sewage is about 500 parts per
-1,000,000. It is represented graphically in Fig. 149. The quantity of
-organic or volatile suspended matter is about 200 parts per 1,000,000.
-It is shown graphically in the smaller cube in Fig. 149.
-
-[Illustration:
-
- FIG. 149.—Graphical Representation of Relative Volumes of Liquids and
- Solids in Sewage.
-]
-
-The odor of fresh sewage is faint and not necessarily unpleasant. It has
-a slightly pungent odor, somewhat like a damp unventilated cellar.
-Occasionally the odor of gasoline, or some other predominating waste
-matter may hide all other odors. Stale sewage is black and gives off
-nauseating odors of hydrogen sulphide and other gases. If the sewage is
-so stale as to become septic, bubbles of gas will be seen breaking the
-surface and a black or gray scum may be present. Before the South Branch
-of the Chicago River was cleaned up and flushed this scum became so
-thick in places, particularly in that portion of the Stock Yards where
-the river became known as Bubbly Creek, that it is said that weeds and
-small bushes sprouted in it, and chickens and small animals ran across
-its surface.
-
-A physical analysis of sewage should include an observation of its
-appearance, and a determination of its temperature, turbidity, color,
-and odor, both hot and cold. The temperature is useful in indicating
-certain of the antecedents of the sewage, its effect on certain forms of
-bacterial life, and its effect on the possible content of dissolved
-gases. Temperatures higher than normal are indicative of the presence of
-trades wastes discharged while hot into the sewers. A low temperature
-may indicate the presence of ground water. If the temperature is much
-over 40° C. bacterial action will be inhibited and the content of
-dissolved gases will be reduced. Turbidity, color, and odor
-determinations may be of value in the control of treatment devices, or
-to indicate the presence of certain trades wastes, which give typical
-reactions. Since all normal sewages are high in color and turbidity, the
-relative amounts of these two constituents in two different sewages has
-little significance regarding the relative strengths of the two sewages
-or the proper method of treating them. A fresh domestic sewage should
-have no highly offensive odor. The presence of certain trades wastes can
-be detected sometimes in fresh sewages, and a stale sewage may sometimes
-be recognized by its odor.
-
-Sewage is a liability to the community producing it. Although some
-substances of value can be obtained from sewage[119] the cost of the
-processes usually exceed the value of the substances obtained. Where it
-becomes necessary to treat sewage the value of these substances may be
-helpful in defraying the cost of treatment.
-
-
-=209. Chemical Composition.=—Sewage is composed of mineral and organic
-compounds which are either in solution or are suspended in water. In
-making a standard chemical analysis of sewage only those chemical
-radicals and elements are determined which are indicative of certain
-important constituents. Neither a complete qualitative nor quantitative
-analysis is made. A sewage analysis will not show, therefore, the number
-of grams of sodium chloride present or any other constituent. A complete
-standard sanitary chemical analysis will report the constituents as
-named in the first column of Table 71. The quantities of these materials
-found in average strong, medium and weak sewages are also shown in this
-table. These values are not intended as fixed boundaries between sewages
-of different strengths. They are presented merely as a guide to the
-interpretation of sewage analyses.
-
-The principal objects of a chemical analysis of sewage are to determine
-its strength and its state of decomposition. The influents and effluents
-of a sewage treatment device are analyzed to aid in the control of the
-device and to gain information concerning the effect of the treatment.
-Chemical and other analyses, in connection with the desired conditions
-after disposal, will indicate the extent of treatment which may be
-required. The standard methods of water and sewage analysis adopted by
-the American Public Health Association have been generally accepted by
-sanitarians. These uniform methods make possible comparisons of the
-results obtained by laboratories working according to these standards.
-
-
- CHEMICAL ANALYSIS OF SEWAGES
-
- (Parts per million)
-
- From Report on Industrial Wastes from the Stock Yards and Packingtown,
- Chicago by the Sanitary District of Chicago in 1921, page 231.
-
- ──────────┬──────────────────┬───────┬────────┬──────────
- │ │ │ │
- │ │ │ │
- │ │ │ │
- │ │ │ │Waterbury,
- │ │Boston │Columbus│ Conn.,
- │ Typical Analyses │1905–7 │ 1904–5 │ 1905–6
- ──────────┼──────┬──────┬────┼───────┼────────┼──────────
- │Strong│Medium│Weak│ │ │
- ──────────┼──────┼──────┼────┼───────┼────────┼──────────
- Nitrogen │ │ │ │ │ │
- as │ │ │ │ │ │
- Organic │ │ │ │ │ │
- Nitrogen│ 35│ 20│ 10│ 9.1│ 9.0│ 14.8
- Free │ │ │ │ │ │
- Ammonia │ 50│ 30│ 15│ 13.9│ 11.0│ 7.8
- Nitrites │ 0.10│ 0.05│ 0.0│ 0.0│ 0.09│ 0.14
- Nitrates │ 0.40│ 0.20│ 0.1│ 0.20│ 0.20│ 1.52
- Oxygen │ │ │ │ │ │
- consumed│ 75│ 50│ 30│56[120]│ 51[121]│ 46[120]
- Oxygen │ │ │ │ │ │
- demand │ 300│ 200│ 100│ │ │
- Chlorine │ 175│ 100│ 15│ 2300│ 65│ 48
- Suspended │ │ │ │ │ │
- matter │ 500│ 300│ 150│ 135│ 209│ 165
- Volatile│ │ │ │ 91│ 79│ 115
- Fixed │ │ │ │ 44│ 130│ 50
- Alkalinity│ 200│ 100│ 50│ 125│ 350│ 41
- Fats │ 40│ 20│ │ │ 25│ 26
- ──────────┴──────┴──────┴────┴───────┴────────┴──────────
-
- ──────────┬─────────────┬──────────┬───────────┬───────────
- │ │ │ │ Chicago,
- │ │ │ │ Center
- │ │ │ Chicago, │ Avenue.
- │Gloversville,│Worcester,│ 39th St. │Industrial.
- │ N. Y. │ Mass. │Residential│Day Sewage
- │ 1908–9 │ 1908 │ 1909–12 │ 1913
- ──────────┼─────────────┼──────────┼───────────┼───────────
- │ │ │ │
- ──────────┼─────────────┼──────────┼───────────┼───────────
- Nitrogen │ │ │ │
- as │ │ │ │
- Organic │ │ │ │
- Nitrogen│ 23.0│ │ 7.8│ 79
- Free │ │ │ │
- Ammonia │ 12.0│ 22.2│ 9.1│ 22
- Nitrites │ 0.38│ │ 0.10│ 0.49
- Nitrates │ 0.88│ │ 0.33│ 3.04
- Oxygen │ │ │ │
- consumed│ 95[120]│ 117│ 43│ 268
- Oxygen │ │ │ │
- demand │ │ │ │
- Chlorine │ 158│ 57│ 40│ 1100
- Suspended │ │ │ │
- matter │ 406│ 258│ 144│ 605
- Volatile│ 229│ 166│ 90│ 46
- Fixed │ 177│ 92│ 54│ 144
- Alkalinity│ 233│ │ 212│ 291
- Fats │ 48│ │ 23[122]│ 198[123]
- ──────────┴─────────────┴──────────┴───────────┴───────────
-
-
-=210. Significance of Chemical Constituents.=—Organic nitrogen and free
-ammonia taken together are an index of the organic matter in the sewage.
-Organic nitrogen includes all of the nitrogen present with the exception
-of that in the form of ammonia, nitrites, and nitrates. Free ammonia or
-ammonia nitrogen is the result of bacterial decomposition of organic
-matter. A fresh cold sewage should be relatively high in organic
-nitrogen and low in free ammonia. A stale warm sewage should be
-relatively high in free ammonia and low in organic nitrogen. The sum of
-the two should be unchanged in the same sewage.
-
-Nitrites (RNO_{2}) and nitrates (RNO_{3})[124] are found in fresh
-sewages only in concentrations of less than one part per million. In
-well-oxidized effluents from treatment plants the concentration will
-probably be much higher. Nitrates contain one more atom of oxygen than
-nitrites. They represent the most stable form of nitrogenous matter in
-sewage. Nitrites are not stable and are reduced to ammonias or are
-oxidized to nitrates. Their presence indicates a process of change. They
-are not found in large quantities in raw sewage because their formation
-requires oxygen which must be absorbed from some other source than the
-sewage. In an ordinary sewer or sluggishly flowing open stream this
-absorption cannot take place from the atmosphere with sufficient
-rapidity to supply the necessary oxygen.
-
-Oxygen consumed is an index of the amount of carbonaceous matter readily
-oxidizable by potassium permanganate. It does not indicate the total
-quantity of any particular constituent, but it is the most useful index
-of carbonaceous matter. Carbonaceous matter is usually difficult of
-treatment and a high oxygen consumed is indicative of a sewage difficult
-to care for. The amount of oxygen consumed, as expressed in the
-analysis, is dependent on the amount of oxidizable carbonaceous matter
-present, the oxidizing agent used, and the time and temperature of
-contact of the sewage and the oxidizing agent. It is essential therefore
-that the test be conducted according to some standard method, since the
-results are of value only as compared with results obtained under
-similar conditions.
-
-Total solids (residue on evaporation) are an index of the strength of
-the sewage. They are made up of organic and inorganic substances. The
-inorganic substances include sand, clay, and oxides of iron and
-aluminum, which are usually insoluble, and chlorides, carbonates,
-sulphates and phosphates, which are usually soluble. The insoluble
-inorganic substances are undesirable in sewage because of their sediment
-forming properties which result in the clogging of sewers, treatment
-plants, pumps, and stream beds. The soluble inorganic substances are
-generally harmless and cause no nuisance, except that the presence of
-sulphur may permit the formation of hydrogen sulphide, which has a
-highly offensive odor. The organic substances are: carbohydrates, fats,
-and soaps, which are carbonaceous and are difficult of removal by
-biological processes; and the nitrogenous substances such as urea,
-proteins, amines, and amino acids. The inorganic and organic substances
-may be either in solution or suspension or in a colloidal condition.
-
-Volatile solids are used as an index of the organic matter present, as
-it is assumed that the organic matter is more easily volatilized than
-the inorganic matter. The amount of volatile inorganic matter present is
-usually so small as to be negligible.
-
-Fixed solids are reported as the difference between the total and
-volatile solids. They are therefore representative of the amount of
-inorganic matter present.
-
-Suspended matter is the undissolved portion of the total solids. High
-volatile suspended matter is an indication of offensive qualities in the
-nature of putrefying organic matter, whereas fixed suspended matter is
-indicative of inoffensive inorganic matter. It is difficult to obtain a
-sample of sewage which will represent the amount of suspended matter in
-the sewage, since a sample taken from near the surface will contain less
-inorganic matter and grit than a sample taken near the bottom.
-
-Settling solids are indicative of the sludge forming properties of the
-sewage and of the probable degree of success of treatment by plain
-sedimentation. Volatile settling solids indicate the property of the
-formation of offensive putrefying sludge banks. There is no chemical
-test which will indicate the scum-forming properties of sewage. Fixed
-settling solids indicate the presence of inorganic matter, probably
-gritty material such as sand, clay, iron oxide, etc.
-
-Colloidal matter is material which is too finely divided to be removed
-by filtration or sedimentation, yet is not held in solution. It can
-sometimes be removed by violent agitation in the presence of a
-flocculent precipitate, as in the treatment with activated sludge, or by
-the flocculent precipitate alone, as in chemical precipitation, or by
-the acidulation of the sewage so as to precipitate the colloids.
-Colloidal matter is probably the result of the constant abrasion of
-finely divided suspended matter while flowing through the sewer or other
-channel. High colloidal matter may therefore indicate a stale sewage, or
-the presence of a particular trades waste. Colloids are difficult of
-removal. For this reason, where sewage is to be treated, turbulence in
-the tributary channels should be avoided.
-
-Alkalinity may indicate the possibility of success of the biologic
-treatment of sewage, since bacterial life flourishes better in a
-slightly alkaline than in a slightly acid sewage. Within the normal
-limits of the amount of alkalinity in sewage the exact amount has little
-significance in sewage analyses. Sewages are normally slightly alkaline.
-An abnormal alkalinity or acidity may indicate the presence of certain
-trades wastes necessitating special methods of treatment. A method of
-sewage treatment may be successful without changing the amount of
-alkalinity in the sewage since the amount of alkalinity is not
-inherently an objection.
-
-Chlorine, in the form of sodium chloride, is an inorganic substance
-found in the urine of man and animals. The amount of chlorine above the
-normal chlorine content of pure waters in the district is used as an
-index of the strength of the sewage. The chlorine content may be
-affected by certain trades wastes such as ice-cream factories,
-meat-salting plants, etc., which will increase the amount of chlorine
-materially. Since chlorine is an inorganic substance which is in
-solution it is not affected by biological processes nor sedimentation.
-Its diminution in a treatment plant or in a flowing stream is indicative
-of dilution and the reduction of chlorine will be approximately
-proportional to the amount of dilution.
-
-Fats have a recoverable market value when present in sufficient quantity
-to be skimmed off the surface of the sewage. Ordinarily fats are an
-undesirable constituent of sewage as they precipitate on and clog the
-interstices in filtering material, they form objectionable scum in tanks
-and streams, and they are acted on very slowly by biological processes
-of sewage treatment. Although fats are carbonaceous matter they are not
-indicated by the oxygen consumed test because they are not easily
-oxidized. They are therefore determined in another manner; by
-evaporation of the liquid and extracting the fats from the residue by
-dissolving them in ether.
-
-Relative stability and bio-chemical oxygen demand are the most important
-tests indicating the putrefying characteristics of sewage. Since
-stability and putrescibility have opposite meanings the relative
-stability test is sometimes called the putrescibility test. The relative
-stability of a sewage is an expression for the amount of oxygen present
-in terms of the amount required for complete stability.
-
- A relative stability of 75 signifies that the sample examined
- contains a supply of available oxygen equal to 75 per cent of the
- amount of oxygen which it requires in order to become perfectly
- stable. The available oxygen is approximately equivalent to the
- dissolved oxygen plus the available oxygen of nitrate and
- nitrite.[125]
-
- TABLE 72
-
- RELATIVE STABILITY NUMBERS
-
- ──────────────────────────────────┬──────────────────────────────────
- Time Required for Decolorization │
- at 20° C. Days │ Relative Stability Number
- ──────────────────────────────────┼──────────────────────────────────
- 0.5│ 11
- 1.0│ 21
- 1.5│ 30
- 2.0│ 37
- 2.5│ 44
- 3.0│ 50
- 4.0[126]│ 60
- 5.0│ 68
- 6.0│ 75
- 7.0│ 80
- 8.0│ 84
- 9.0│ 87
- 10.0│ 90
- 11.0│ 92
- 12.0│ 94
- 13.0│ 95
- 14.0│ 96
- 16.0│ 97
- 18.0│ 98
- 20.0│ 90
- ──────────────────────────────────┴──────────────────────────────────
-
-The relative stability numbers, given in Table 72, are computed from the
-expression, _S_ = 100(1 − 0.794_t_) in which _S_ is the stability number
-and _t_ is the time in days that the sample has been incubated at 20° C.
-The bio-chemical oxygen demand is more directly an index of the
-consumption of available oxygen by the biological and chemical changes
-which take place in the decomposition of sewage or polluted water. As
-such it is a more valuable, though less easily performed test than the
-test of relative stability.
-
-The methods for the determination of the relative stability and the
-bio-chemical oxygen demand are given to show more clearly what these
-tests represent. The procedure in the relative stability test is to add
-0.4 c.c. of a standard solution of methylene blue to 150 c.c. of the
-sample. The mixture is then allowed to stand in a completely filled and
-tightly stoppered bottle at 20° C. for 20 days or until the blue fades
-out due to the exhaustion of the available oxygen. There are three
-methods in use for the determination of the bio-chemical oxygen
-demand;[127] the relative stability method, the excess nitrate method,
-and the excess oxygen method. In the relative stability method the
-sample to be treated should have a relative stability of at least 50. If
-it is lower than this the sample should be diluted with water containing
-oxygen until the relative stability has been raised to or above this
-point. The oxygen demand in parts per million is then expressed as
-
- _O′_ = ((1 − _P_)_O_)⁄_RP_,[128]
-
-in which _O′_ is the oxygen demand, _O_ is the initial oxygen in parts
-per million (p.p.m.) in the diluting water or sewage, _P_ is the
-proportion of sewage in the mixture expressed as a ratio, and _R_ is the
-relative stability of the mixture expressed as a decimal. For the
-effluents from sewage treatment plants, polluted waters, and similar
-liquids, the total available oxygen expressed as the sum of the
-dissolved oxygen, nitrites, and nitrates, divided by the relative
-stability expressed as a decimal will give the bio-chemical oxygen
-demand. The excess nitrate method requires the determination of the
-total oxygen available as dissolved oxygen, nitrites, and nitrates and
-the addition of a sufficient amount of oxygen in the form of sodium
-nitrate to prevent the exhaustion of oxygen during a 10–day period of
-incubation. At the end of the period the total available oxygen is again
-determined. The difference between the original and the final oxygen
-content represents the bio-chemical oxygen demand. The excess oxygen
-test requires the determination of the total available oxygen as before,
-and the addition of a sufficient amount of oxygen, in the form of
-dissolved oxygen in the diluting water, to prevent exhaustion of the
-oxygen in a 10–day period of incubation. The difference between the
-original and final oxygen content represents the bio-chemical oxygen
-demand. Theriault concludes as a result of his tests, that the relative
-stability and excess nitrate methods are open to objections but that the
-excess oxygen method yields very accurate and consistent results with as
-little or less labor than is required by other methods.
-
-Dissolved oxygen represents what its name implies, the amount of oxygen
-(_O__{2}) which is dissolved in the liquid. Normal sewage contains no
-dissolved oxygen unless it is unusually fresh. It is well, if possible,
-to treat a sewage before the original dissolved oxygen has been
-exhausted. Normal pure surface water contains all of the oxygen which it
-is capable of dissolving, as shown in Table 73. The presence of a
-smaller amount of oxygen than is shown in this table indicates the
-presence of organic matter in the process of oxidation, which may be in
-such quantities as ultimately to reduce the oxygen content to zero.
-Normal pure ground waters may be deficient in dissolved oxygen because
-of the absence of available oxygen for solution. The presence of certain
-oxygen-producing organisms in polluted or otherwise potable surface
-waters may cause a supersaturation with oxygen however.
-
-The dissolved-oxygen test for polluted water is probably the most
-significant of all tests. If dissolved oxygen is found in a polluted
-water it means that putrefactive odors will not occur, since
-putrefaction cannot begin in the presence of oxygen. It is possible for
-different strata in a body of water to have different quantities of
-dissolved oxygen, and putrefaction may be proceeding in the lower strata
-before the oxygen is exhausted from the upper strata. The oxygen content
-of a river water will indicate the ability of the river to receive
-sewage without resulting in a nuisance.
-
- TABLE 73
-
- SOLUBILITY OF OXYGEN IN WATER
-
- Under an atmospheric pressure of 760 mm. of mercury, the atmosphere
- containing 20.9 per cent of oxygen.
- ───────────────────────────────────┬───────────────────────────────────
- Temperature, degrees C │ Oxygen in parts per million
- ───────────────────────────────────┼───────────────────────────────────
- 0│ 14.62
- 1│ 14.23
- 2│ 13.84
- 3│ 13.48
- 4│ 13.13
- 5│ 12.8
- 6│ 12.48
- 7│ 12.17
- 8│ 11.87
- 9│ 11.59
- 10│ 11.33
- 11│ 11.08
- 12│ 10.83
- 13│ 10.6
- 14│ 10.37
- 15│ 10.15
- 16│ 9.95
- 17│ 9.74
- 18│ 9.54
- 19│ 9.35
- 20│ 9.17
- 21│ 8.99
- 22│ 8.83
- 23│ 8.68
- 24│ 8.53
- 25│ 8.38
- 26│ 8.22
- 27│ 8.07
- 28│ 7.92
- 29│ 7.77
- 30│ 7.63
- ───────────────────────────────────┴───────────────────────────────────
-
-
-=211. Sewage Bacteria.=—A slight knowledge of the nature of bacteria is
-necessary in order that the biological changes which occur in the
-treatment of sewage may be understood. Bacteria are living organisms
-which are so small that it is difficult or impossible to study them
-either with the eye alone or with the aid of powerful microscopes. They
-are studied by means of cultures, stains, and certain characteristic
-phenomena such as the production of a gas, the production of a red
-colony on litmus lactose agar, etc. Bacteria occur in three forms:
-spherical, called coccus; cylindrical, called bacillus; and spiral,
-called spirillum. In size they vary from the largest at about 1⁄10,000
-of an inch to sizes so small as to be invisible under the most powerful
-microscope. An ordinary size is 1⁄25,000 of an inch. The cylindrical or
-rod bacteria are about four times as long as they are wide. Some
-bacteria possess the power of motion due to the presence of flagella or
-hairs which can be moved and cause the cell to progress at a rate as
-high as 18 cm. per hour, but usually the rate is very much less than
-this. The composition of the bacterial cell has never been definitely
-determined.
-
-Bacteria are unicellular plants. They possess no digestive organs and
-apparently obtain their food by absorption from the surrounding media.
-Reproduction is by the division of the cell into two approximately equal
-portions. This reproduction may occur as frequently as once every half
-hour and if unchecked would quickly mount to unimaginable numbers. The
-natural cause limiting the growth of bacteria is the generation by the
-bacterium of certain substances such as the amino acids, which are
-injurious to cell life. The exhaustion of the food supply is not
-considered as an important cause of inhibition of multiplication. The
-products of growth of one species of bacteria may be helpful or harmful
-to other forms. Where the products are helpful the effect is known as
-symbiosis, and where harmful the effect is known as antibiosis. In
-sewage the presence of both aërobic and anaërobic bacteria is usually
-mutually helpful and the condition is an example of symbiosis. The
-aërobes, sometimes called obligatory aërobes, are bacteria which demand
-available oxygen for their growth. The anaërobes, or obligatory
-anaërobes, can grow only in the absence of oxygen. There are other forms
-that are known as facultative anaërobes (or aërobes) whose growth is
-independent of the presence or absence of oxygen.
-
-Spores are formed by some bacteria when they are subjected to an
-unfavorable environment such as high temperatures, the absence of food,
-the absence of moisture, etc. Spores are cells in which growth and
-animation are suspended but the life of the cell is carried on through
-the unsuitable period, somewhat similar to the condition in a plant
-seed.
-
-
-=212. Organic Life in Sewage.=—Living organisms, both plants and
-animals, exist in sewage. Bacteria are the smallest of these organisms.
-Others, which can be studied easily under the microscope or can be seen
-with difficulty by the naked eye but which do not require special
-cultures for their study, are classed as microscopic organisms or
-plankton. Organisms which are large enough to be studied without the aid
-of a microscope or special cultures are classed as macroscopic. The part
-taken in the biolysis of sewage by macroscopic organisms belonging to
-the animal kingdom, such as birds, fish, insects, rodents, etc., which
-feed upon substances in the sewage is so inconsequential as to be of no
-importance. Both plants and animals are found among the macroscopic
-organisms.
-
-Organisms in sewage may be either harmful, harmless, or beneficial. From
-the viewpoint of mankind the harmful organisms are the pathogenic
-bacteria. Their condition of life in sewage is not normal and in general
-their existence therein is of short duration. It may be of sufficient
-length, however, to permit the transmission of disease. The diseases
-which can be transmitted by sewage are only those that are contracted
-through the alimentary canal, such as typhoid fever, dysentery, cholera,
-etc. Diseases are not commonly contracted by contact of sewage with the
-skin nor by breathing the air of sewers. It is safe to work in and
-around sewage so long as the sewage is kept out of the mouth, and
-asphyxiating or toxic gases are avoided.
-
-The beneficial organisms in sewage are those on which dependence is
-placed for the success of certain methods of treatment. These organisms
-have not all been isolated or identified.
-
-The total number of bacteria in a sample of sewage has little or no
-significance. In a normal sewage the number may be between 2,000,000 and
-20,000,000 per c.c. and because of the extreme rapidity of
-multiplication of bacteria a sample showing a count of 1,000,000 per
-c.c. on the first analysis may show 4 to 5 times as many 3 or 4 hours
-later. A bacterial analysis of sewage is ordinarily of little or no
-value, since pathogenic organisms are practically certain to be present,
-there is no interest in the harmless organisms, and the helpful
-nitrifying and aërobic bacteria will not grow on ordinary laboratory
-media. Occasionally the presence of certain bacteria may indicate the
-presence of certain trades wastes. In general, the total bacterial
-count, as sometimes reported, represents only the number of bacteria
-which have grown under the conditions provided. It bears no relation to
-the total number of bacteria in the sample.
-
-The presence of bacteria in sewage is of great importance however, as
-practically all methods of treatment depend on bacterial action, and all
-sewages which do not contain deleterious trades wastes, contain or will
-support the necessary bacteria for their successful treatment, if
-properly developed.
-
-
-=213. Decomposition of Sewage.=—If a glass container be filled with
-sewage and allowed to stand, open to the air, a black sediment will
-appear after a short time, a greasy scum may rise to the surface, and
-offensive odors will be given off. This condition will persist for
-several weeks, after which the liquid will become clear and odorless.
-The sewage has been decomposed and is now in a stable condition. The
-decomposition of sewage is brought about by bacterial action the exact
-nature of which is uncertain.
-
- It[129] is well established that many of the chemical effects
- wrought by bacteria, as by other living cells, are due, not to the
- direct action of the protoplasm, but to the intervention of
- soluble ferments or enzymes.
-
-Enzymes are soluble ferments produced by the growth of the bacterial
-cell.
-
- In[130] many cases the enzymes diffuse out from the cell and exert
- their effort on the ambient substances ... in others the enzyme
- action occurs within the cell and the products pass out, (for
- example) ... the alcohol-producing enzymes of the yeast cell act
- upon sugar within the cell, the resulting alcohol and carbon
- dioxide being ejected.
-
-Other chemical effects may be brought about by the direct action of the
-living cells, but this has never been well established.
-
-Metabolism is the life process of living cells by which they absorb
-their food and convert it into energy and other products. It is the
-metabolism of bacterial growth that in itself or by the production of
-enzymes hastens the putrefactive or oxidizing stages of the organic
-cycles in sewage treatment. Bacteria can assimilate only liquid food
-since they have no digestive tract through which solid food can enter.
-The surrounding solids are dissolved by the action of the enzymes, the
-resulting solution diffusing through the chromatin or outer skin, and
-being digested throughout the interior cytoplasm.
-
-Bacteria are sometimes classified as parasites and saprophytes. The
-parasites live only on the growing cells of other plant or animal life.
-The saprophytes obtain their food only from the life products of living
-organisms and do not exist at the expense of the organisms themselves.
-Facultative saprophytes (or parasites) may exist on either living or
-dead tissue.
-
-The decomposition of sewage may be divided into anaërobic and aërobic
-stages. These conditions are usually, but not always, distinctly
-separate. The growth of certain forms of bacteria is concurrent, while
-the growth of other forms is dependent on the results of the life
-processes of other bacteria in the early stages of decomposition.
-
-When sewage is very fresh it contains some oxygen. This oxygen is
-quickly exhausted so that the first important step in the decomposition
-of sewage is carried on under anaërobic conditions. This is accompanied
-by the creation of foul odors of organic substances, ammonia, hydrogen
-sulphide, etc.; other odorless gases such as carbon dioxide, hydrogen,
-and marsh gas, the latter being inflammable and explosive; and other
-complicated compounds. An exception to the rule that putrefaction takes
-place only in the absence of oxygen is the production of other
-foul-smelling substances by the putrefactive activity of obligatory and
-facultative aërobes. Hydrogen sulphide may be produced apparently in the
-presence of oxygen the action which takes place not being thoroughly
-understood.
-
-The biolysis of sewage is the term applied to the changes through which
-its organic constituents pass due to the metabolism of bacterial life.
-Organic matter is composed almost exclusively of the four elements:
-carbon, oxygen, hydrogen, and nitrogen (COHN) and sometimes in addition
-sulphur and phosphorus. The organic constituents of sewage can be
-divided into the proteins, carbohydrates, and fats. The proteins are
-principally constituents of animal tissue, but they are also found in
-the seeds of plants. The principal distinguishing characteristic of the
-proteins is the possession of between 15 and 16 per cent of nitrogen. To
-this group belong the albumens and casein. The carbohydrates are organic
-compounds in which the ratio of hydrogen to oxygen is the same as in
-water, and the number of carbon atoms is 6 or a multiple of 6. To this
-group belong the sugars, starches and celluloses. The fats are salts
-formed, together with water, by the combination of the fatty acids with
-the tri-acid base glycerol. The more common fats are _stearin_,
-_palmatin_, _olein_, and _butyrine_. The soaps are mineral salts of the
-fatty acids formed by replacing the weak base glycerol with some of the
-stronger alkalies.
-
-The first state in the biolysis of sewage is marked by the rapid
-disappearance of the available oxygen present in the water mixed with
-organic matter to form sewage. In this state the urea, ammonia, and
-other products of digestive or putrefactive decomposition are partially
-oxidized and in this oxidation the available oxygen present is rapidly
-consumed, the conditions in the sewage becoming anaërobic. The second
-state is putrefaction in which the action is under anaërobic conditions.
-The proteins are broken down to form urea, ammonia, the foul-smelling
-mercaptans, hydrogen sulphide, etc., and fatty and aromatic acids. The
-carbohydrates are broken down into their original fatty acid, water,
-carbon dioxide, hydrogen, methane, and other substances. Cellulose is
-also broken down but much more slowly. The fats and soaps are affected
-somewhat similarly to the hydrocarbons and are broken down to form the
-original acids of their make up together with carbon dioxide, hydrogen,
-methane, etc. The bacterial action on fats and soaps is much slower than
-on the proteins, and the active biological agents in the biolysis of the
-hydrocarbons, fats, and soaps are not so closely confined to anaërobes
-as in the biolysis of the proteins. The third state in the biolysis of
-sewage is the oxidation or nitrification of the products of
-decomposition resulting from the putrefactive state. The products of
-decomposition are converted to nitrites and nitrates, which are in a
-stable condition and are available for plant food. It must be understood
-that the various states may be coexistent but that the conditions of the
-different states predominate approximately in the order stated. In the
-biolysis of sewage there is no destruction of matter. The same elements
-exist in the same amount as at the start of the biolytic action.
-
-
-=214. The Nitrogen Cycle.=—Nitrogen is an element that is found in all
-organic compounds. Its presence is necessary to all plant and animal
-life. The nitrogenous compounds are most readily attacked by bacterial
-action in sewage treatment. The non-nitrogenous substances such as soaps
-and fats, and the inorganic compounds are more slowly affected by
-bacterial action alone. The element nitrogen passes through a course of
-events from life to death and back to life again that is known as the
-Nitrogen Cycle. It is typical of the cycles through which all of the
-organic elements pass.
-
-Upon the death of a plant or animal, decomposition sets in accompanied
-by the formation of urea which is broken down into ammonia. This is
-known as the _putrefactive stage_ of the Nitrogen Cycle. The next state
-is _nitrification_ in which the compounds of ammonia are oxidized to
-nitrites and nitrates, and are thus prepared for plant food. In the
-state of _plant life_ the nitrites and nitrates are denitrified so as to
-be available as a plant or animal food. The highest state of the
-Nitrogen Cycle is _animal life_, in which nitrogen is a part of the
-living animal substance or is charged from protein to urea, ammonia,
-etc., by the functions of life in the animal. Upon the death of this
-animal organism the cycle is repeated. The Nitrogen Cycle, like the
-cycle of Life and Death, is purely an ideal condition as in nature there
-are many short circuits and back currents which prevent the continuous
-progression of the cycle. The conception of this cycle is an aid,
-however, in understanding the processes of sewage treatment.
-
-
-=215. Plankton and Macroscopic Organisms.=—In general the part played by
-these organisms in the biolysis of sewage is not sufficiently well
-understood to aid in the selection of methods of sewage treatment
-involving their activities. The presence in bodies of water receiving
-sewage, of certain plankton which are known to exist only when
-putrefaction is not imminent, indicates that the body of water into
-which the discharge of sewage is occurring is not being overtaxed. The
-control of sewage treatment plant effluents so as to avoid the poisoning
-of fish life or the contamination of shell fish is likewise important.
-The study of plankton and macroscopic life in the treatment of sewage is
-an open field for research.
-
-
-=216. Variations in the Quality of Sewage.=—The quality of sewage varies
-with the hour of the day and the season of the year. Some of the causes
-of these variations are: changes in the amount of diluting water due to
-the inflow of storm water or flushing of the streets or sewers;
-variations in domestic activities such as the suspension of
-contributions of organic wastes during the night, Monday’s wash, etc.;
-characteristics of different industries which discharge different kinds
-of wastes according to the stage of the manufacturing process, etc. In
-general night sewage is markedly weaker than day sewage in both domestic
-and industrial wastes, but in specific cases the varying strength
-depends entirely upon the characteristics of the district. Some analyses
-are given in Table 74, which emphasize these points.
-
- TABLE 74
-
- SEWAGE ANALYSES SHOWING HOURLY, DAILY, AND SEASONAL VARIATIONS IN
- QUALITY
- ────────────┬────────────┬─────┬────────┬─────────┬──────────┬─────────
- Place │ Time │ │ │Suspended│ Remarks │Reference
- │ Nitrogen │Total│Chlorine│ Matter │ │
- ────────────┼────────────┼─────┼────────┼─────────┼──────────┼─────────
- Marion, Ohio│Mid’t-noon, │ │ │ │Industrial│ 1
- │ 5–21–06. │ 45│ 53│ 190│ │
- │Noon-mid’t │ │ │ │Domestic │ 1
- │ 5–21–06. │ 37│ 94│ 133│ │
- Westerville,│Day │ │ │ │college │ 1
- Ohio │ │ 10.2│ 76│ 118│ town │
- │Night │ 2.6│ 74│ 41│ │ 1
- Columbus, │1904–1905 │ │ │ │ │
- Ohio │ │ │ │ │ │
- │Mid’t to 2 │ │ │ │ │ 2
- │ a.m. │ 4.6│ 50│ 131│ │
- │2 a.m. to 4 │ │ │ │ │ 2
- │ a.m. │ 3.0│ 52│ 95│ │
- │4 a.m. to 6 │ │ │ │ │ 2
- │ a.m. │ 2.3│ 51│ 83│ │
- │6 a.m. to 8 │ │ │ │ │ 2
- │ a.m. │ 2.7│ 48│ 83│ │
- │8 a.m. to 10│ │ │ │ │ 2
- │ a.m. │ 16.3│ 66│ 476│ │
- │10 a.m. to │ │ │ │ │ 2
- │ noon │ 11.4│ 100│ 324│ │
- │Noon to 2 │ │ │ │ │ 2
- │ p.m. │ 11.3│ 86│ 246│ │
- │2 p.m. to 4 │ │ │ │ │ 2
- │ p.m. │ 12.3│ 78│ 246│ │
- │4 p.m. to 6 │ │ │ │ │ 2
- │ p.m. │ 22.0│ 78│ 368│ │
- │6 p.m. to 8 │ │ │ │ │ 2
- │ p.m. │ 8.2│ 71│ 209│ │
- │8 p.m. to 10│ │ │ │ │ 2
- │ p.m. │ 7.8│ 80│ 120│ │
- │10 p.m. to │ │ │ │ │ 2
- │ mid’t │ 6.2│ 56│ 117│ │
- │ │ │ │ │ │
- Center Ave.,│Mid’t to 3 │ │ │ │ │ 3
- Chicago. │ a.m. │ │ │ 123│ │
- │4 a.m. to 7 │ │ │ │ │ 3
- │ p.m. │ │ │ 316│ │
- │8 a.m. to 11│ │ │ │ │ 3
- │ p.m. │ │ │ 608│ │
- │Noon to 3 │ │ │ │ │ 3
- │ p.m. │ │ │ 785│ │
- │4 p.m. to 7 │ │ │ │ │ 3
- │ p.m. │ │ │ 717│ │
- │8 p.m. to 11│ │ │ │ │ 3
- │ p.m. │ │ │ 287│ │
- │ │ │ │ │ │
- Columbus, │Sunday │ │ │ │ │ 2
- Ohio │ │ 6.7│ 55│ 858│ │
- │Monday │ 9.1│ 66│ 1048│ │ 2
- │Tuesday │ 9.4│ 69│ 1024│ │ 2
- │Wednesday │ 9.6│ 68│ 1005│ │ 2
- │Thursday │ 9.2│ 66│ 990│ │ 2
- │Friday │ 9.2│ 67│ 1018│ │ 2
- │Saturday │ 9.3│ 67│ 1016│ │ 2
- │ │ │ │ │ │
- Baltimore, │Aug. 1 to │ │ │ │ │ 4
- 1907–1908 │ Sept. 1 │ 16.0│ │ 246│ │
- │Sept. 4 to │ │ │ │ │ 4
- │ Oct. 3 │ 19.0│ │ 190│ │
- │Oct. 6 to │ │ │ │ │ 4
- │ Nov. 4 │ 20.0│ │ 188│ │
- │Nov. 15 to │ │ │ │ │ 4
- │ Nov. 29 │ 20.0│ │ 164│ │
- │Dec. 3 to │ │ │ │ │ 4
- │ Dec. 29 │ 20.0│ │ 123│ │
- │Jan. 6 to │ │ │ │ │ 4
- │ Jan. 21 │ 19.0│ │ 127│ │
- │Feb. 2 to │ │ │ │ │ 4
- │ Feb. 26 │ 20.0│ │ 149│ │
- │Feb. 29 to │ │ │ │ │ 4
- │ Mar. 24 │ 28.0│ │ 274│ │
- │Mar. 27 to │ │ │ │ │ 4
- │ April 29 │ 25.0│ │ 165│ │
- │April 30 to │ │ │ │ │ 4
- │ May 26 │ 19.0│ │ 104│ │
- │June 8 to │ │ │ │ │ 4
- │ July 11 │ 15.0│ │ 88│ │
- │July 13 to │ │ │ │ │ 4
- │ Aug. 8 │ 9.5│ │ 124│ │
- ────────────┴────────────┴─────┴────────┴─────────┴──────────┴─────────
-
- References:
-
- 1. 1908 Report of the Ohio State Board of Health.
-
- 2. Report on Sewage Purification at Columbus, Ohio, by G. A. Johnson,
- 1905.
-
- 3. Report on Industrial Wastes from the Stock Yards and Packingtown in
- Chicago, by the Sanitary District of Chicago. 1921.
-
- 4. Report of the Baltimore Sewerage Commission, 1911.
-
-
-=217. Sewage Disposal.=—Previous to the development of the
-water-carriage method for removing human excreta and other liquid wastes
-the solid matter was disposed of by burial and the liquid wastes were
-allowed to seep into the ground or to run away over its surface.
-Following the development of the water-carriage system, which
-necessitated the development of sewers, the problem of ultimate disposal
-was rendered more serious by the concentration of human excreta together
-with a large volume of water. The unthinking citizen believes the
-problem of sewage disposal is solved when the toilet is flushed or the
-bath tub is drained. The problem may more truly be said to commence at
-this point.
-
-It would appear that the simplest method of disposal of sewage would be
-to discharge it into the nearest water course. Unfortunately the nature
-of sewage is such that it may be either highly offensive to the senses
-or dangerous to health or both, when discharged in this manner. Only the
-most fortunate communities are favored with a body of water of
-sufficient size to receive sewage without creating a nuisance.
-
-The problems of sewage disposal are to prevent nuisances causing offense
-to sight and smell; to prevent the clogging of channels; to protect
-pumping machinery; to protect public water supplies; to protect fish
-life; to prevent the contamination of shell fish; to recover valuable
-constituents of the sewage; to enrich and to irrigate the soil; to
-safeguard bathing and boating; for other minor purposes; and in some
-cases to comply with the law. Sewage may be treated to attain one or
-more of these objects by methods of treatment varying as widely as the
-objects to be attained.
-
-
-=218. Methods of Sewage Treatment.=—In studying the subject of sewage
-treatment it must be borne in mind that it is impossible to destroy any
-of the elements present. They may be removed from the mixture only by
-gasification, straining or sedimentation. Their chemical combinations
-may be so changed, however, as to result in different substances than
-those introduced to the treatment plant. It is with these chemical
-changes that the student of sewage treatment is interested.
-
-The methods of sewage treatment can be classified as mechanical,
-chemical and biological. These classifications are not separated by
-rigid lines but may overlap in certain treatment devices or methods.
-Mechanical methods of treatment are exemplified by sedimentation, and
-screening. Chemical precipitation and sterilization are examples of
-chemical methods. The biological methods, the most important of all,
-include dilution, septicization, filtration, sewage farming, activated
-sludge, etc. If for any reason it is desired to treat sewage by more
-than one of these methods the procedure should follow as nearly as
-possible the order of the occurrence of the phenomena in the natural
-biolysis of sewage. For example, in one treatment plant the sewage would
-first pass through a grit chamber where the coarse sediment would be
-removed, then through a screen where the floating matter and coarse
-suspended matter would be removed, then to a sedimentation basin where
-some finer suspended matter might settle out, then to a digestive tank
-where the solid matter deposited would be worked upon by bacterial
-action and partially liquefied. Simultaneous to the liquefaction of the
-deposited solid matter the liquid effluent from the digestive tank might
-proceed to an aërating device to expedite oxidation, then to an aërobic
-filter, and finally to disposal by dilution.
-
-
-
-
- CHAPTER XIV
- DISPOSAL BY DILUTION
-
-
-=219. Definition.=—Disposal of sewage by dilution is the discharge of
-raw sewage or the effluent from a treatment plant into a body of water
-of sufficient size to prevent offense to the senses of sight and smell,
-and to avoid danger to the public health.
-
-
-=220. Conditions Required for Success.=—Among the desired conditions for
-successful disposal by dilution are: adequate currents to prevent
-sedimentation and to carry the sewage away from all habitations before
-putrefaction sets in, or sufficient diluting water high in dissolved
-oxygen to prevent putrefaction; a fresh or non-septic sewage; absence of
-floating or rapidly settling solids, grease or oil; and absence of back
-eddies or quiet pools favorable to sedimentation in the stream into
-which disposal is taking place. The conditions which should be prevented
-are: offensive odors due to sludge banks, the rise of septic gases, and
-unsightly floating or suspended matter. In some instances the pollution
-of the receiving body of water is undesirable and the sewage must be
-freed from pathogenic organisms and the danger of aftergrowths minimized
-before disposal. Such conditions are typified at Baltimore, where the
-sewage is discharged into Back Bay, an arm of Chesapeake Bay. One of the
-important industries of the state of Maryland is the cultivation of
-oysters. The pollution of the Bay was therefore so objectionable that
-careful treatment of the Baltimore sewage has been a necessary
-preliminary to final disposal by dilution. It is unwise to draw public
-water supplies, without treatment, from a stream receiving a sewage
-effluent, no matter how careful or thorough the treatment of the sewage.
-The treatment of the sewage is a safeguard, and lightens the load on the
-water purification plant, but under no considerations can it be depended
-upon to protect the community consuming the diluted effluent.
-
-The sewer outlet should be located well out in the current of the
-stream, lake, or harbor. Deeply submerged outlets are usually better
-than an outlet at the surface, as a better mixture of the sewage and
-water is obtained. The discharge of sewage into a body of water of which
-the surface level changes, alternately covering and exposing large areas
-of the bottom is unwise, as the sludge which is deposited during
-inundation will cause offensive odors when uncovered. Such conditions
-must be carefully guarded against when selecting a point of disposal in
-tidal estuaries because of the frequent fluctuations in level.
-
-
-=221. Self-Purification of Running Streams.=—The self-purification of
-running streams is due to dilution, sedimentation, and oxidation. The
-action is physical, chemical, and biological. When putrescible organic
-matter is discharged into water the offensive character of the organic
-matter is minimized by dilution. If the dilution is sufficiently great,
-it alone may be sufficient to prevent all nuisance. The oxidation of the
-organic matter commences immediately on its discharge into the diluting
-water due to the growth and activity of nitrifying and other oxidizing
-organisms and to a slight degree to direct chemical reaction. So long as
-there is sufficient oxygen present in the water septic conditions will
-not exist and offensive odors will be absent. When the organic matter is
-completely nitrified or oxidized there will be no further demand on the
-oxygen content of the stream and the stream will be said to have
-purified itself. At the same time that this oxidation is going on some
-of the organic matter will be settling due to the action of
-sedimentation. If oxidation is completed before the matter has settled
-on the bottom the result will be an inoffensive silting up of the river.
-If oxidation is not complete, however, the result will be offensive
-putrefying sludge banks which may send their stinks up through the
-superimposed layers of clean water to pollute the surrounding
-atmosphere.
-
-The most important condition for the successful self-purification of a
-stream is an initial quantity of dissolved oxygen to oxidize all of the
-organic matter contributed to it, or the addition of sufficient oxygen
-subsequent to the contribution of sewage to complete the oxidation.
-Oxygen may be added through the dilution received from tributaries,
-through aëration over falls and rapids, or by quiescent absorption from
-the atmosphere. The rapidity of self-purification is dependent on the
-character of the organic matter, the presence of available oxygen, the
-rate of reaëration, temperature, sedimentation, and the velocity of the
-current. Sluggish streams are more likely to purify themselves in a
-shorter distance and rapidly flowing turbulent streams are more likely
-to purify themselves in a shorter time, other conditions being equal.
-Although the absorption of oxygen by a stream whose surface is broken is
-more rapid than through a smooth unbroken surface, the growth of algæ,
-biological activity, the effect of sunlight, and sedimentation are more
-potent factors and have a greater effect in sluggish streams than the
-slightly more rapid absorption of oxygen in a turbulent stream. It is
-frequently more advantageous to discharge sewage into a swiftly moving
-stream, however, regardless of the conditions of self-purification, as
-the undesirable conditions which may result occur far from the point of
-disposal and may be offensive to no one.
-
-The sewage from a population of about 3,000,000 persons residing in and
-about Chicago is discharged into the Chicago Drainage Canal. It
-ultimately reaches tide water through the Des Plaines, the Illinois, and
-the Mississippi Rivers. The action occurring in these channels is one of
-the best illustrations known of the self-purification of a stream. In
-Table 75 are shown the results of analyses of samples taken at various
-points below the mouth of the Chicago River where the diluting water
-from Lake Michigan enters, to Grafton, Illinois, at the junction of the
-Illinois and Mississippi Rivers about 40 miles above St. Louis. The
-effect of the physical characteristics of the stream on its chemical
-composition is well illustrated in this table. The rise in the chlorine
-content between Lake Michigan and the entrance to the Drainage Canal is
-a measure of the addition of sewage. Since the chlorine is an inorganic
-substance which is not affected by biologic action, its loss in
-concentration in the lower reaches of the rivers is due to dilution by
-tributaries and sedimentation, e.g., between the end of the canal at
-Lockport and the sampling point at Joliet, the entrance of the Des
-Plaines River reduces the concentration of chlorine from 124.5 to 41.5
-parts per million. The entrance of the Kankakee River at Dresden Heights
-further reduces the chlorine to 24.5 p.p.m. The increase of albuminoid
-and ammonia nitrogen accompanied by a decrease in nitrites and nitrates,
-between the upper end of the canal at Bridgeport and its lower end at
-Lockport indicates the reducing action proceeding therein. The oxidizing
-action over the various dams and the effect of dilution with water
-containing oxygen is shown between miles 34 and 38, at mile 79, and at
-mile 294. The excellent effect of quiescent sedimentation and aëration
-in Peoria Lakes is shown between miles 145, 161 and 165.
-
- TABLE 75
-
- ANALYSES OF CHICAGO, DES PLAINES AND ILLINOIS RIVERS
-
- (Parts per million)
-
- ────────────┬────────┬──────────────────────────────────────────────
- Sampling │Distance│January-June, 1900, from “Sewage Disposal,” by
- Point │in Miles│ Kinnicutt, Winslow and Pratt
- │ from │
- │ Lake │
- │Michigan│
- ────────────┼────────┼────────┬────────┬──────────┬────────┬────────
- │ │Chlorine│ Ammonia│Albuminoid│Nitrates│Nitrates
- │ │ │Nitrogen│ Nitrogen│ │
- │ │ │ │ │ │
- ────────────┼────────┼────────┼────────┼──────────┼────────┼────────
- Lake │ 0│ 3.0│ 0.03│ 60.13│ 0.002│ 0.008
- Michigan │ │ │ │ │ │
- │ │ │ │ │ │
- Canal, │ 5│ 96.6│ 8.05│ 2.05│ .021│ .074
- Bridgeport│ │ │ │ │ │
- Canal, │ 34│ 124.5│ 10.90│ 2.07│ .013│ .066
- Lockport │ │ │ │ │ │
- Joliet │ 38│ 41.5│ 4.22│ 0.83│ .021│ .086
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- Dresden │ 52│ │ │ │ │
- Heights │ │ │ │ │ │
- Dresden │ 52│ │ │ │ │
- Heights │ │ │ │ │ │
- Morris │ 62│ 24.5│ 2.46│ .60│ .075│ .424
- │ │ │ │ │ │
- Marseilles │ 79│ │ │ │ │
- Marseilles │ 79│ │ │ │ │
- Ottawa │ 85│ 15.3│ 1.55│ .41│ .197│ .966
- La Salle │ 100│ 17.5│ 1.05│ .43│ .109│ .979
- Henry │ 129│ 13.3│ .92│ .38│ .102│ .800
- Chillicothe │ 145│ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- Averyville │ 161│ 13.5│ .81│ .37│ .004│ 1.150
- │ │ │ │ │ │
- │ │ │ │ │ │
- Wesley │ 165│ 12.0│ .57│ .41│ .083│ 1.03
- │ │ │ │ │ │
- Pekin │ 175│ 12.3│ .70│ .43│ .060│ .990
- Havana │ 205│ 11.2│ .60│ .36│ .065│ .570
- Beardstown │ 237│ 10.7│ .69│ .44│ .106│ .685
- La Grange │ 249│ │ │ │ │
- Kampsville │ 294│ 11.3│ .66│ .44│ .044│ .870
- Kampsville │ 294│ │ │ │ │
- Grafton │ 325│ 9.8│ .46│ .42│ .031│ 1.06
- │ │ │ │ │ │
- Grafton │ 325│ │ │ │ │
- │ │ │ │ │ │
- ────────────┴────────┴────────┴────────┴──────────┴────────┴────────
-
- ────────────┬─────────────────────┬───────────
- Sampling │ Dissolved Oxygen │ Remarks
- Point │ │
- │ │
- │ │
- │ │
- ────────────┼───────┬──────┬──────┼───────────
- │ Jan. │ July │ Nov. │
- │30–Feb.│ 8–15 │12–19,│
- │2, 1912│ 1912 │ 1912 │
- ────────────┼───────┼──────┼──────┼───────────
- Lake │ 14.1│ │ 10.8│Typical
- Michigan │ │ │ │ chemical
- │ │ │ │ analysis
- Canal, │ │ │ 6.9│Kedzie
- Bridgeport│ │ │ │ Avenue
- Canal, │ 9.9│ │ 1.7│Above dam
- Lockport │ │ │ │
- Joliet │ │ 1.4│ 5.6│Aëration
- │ │ │ │ over dam.
- │ │ │ │ Dilution
- │ │ │ │by Des
- │ │ │ │ Plaines
- │ │ │ │ River
- Dresden │ │ 1.0│ 4.1│Des Plaines
- Heights │ │ │ │ River
- Dresden │ │ │ 10.4│Kankakee
- Heights │ │ │ │ River
- Morris │ 7.8│ │ 5.7│Illinois
- │ │ │ │ River
- Marseilles │ 5.7│ 0.6│ 6.8│Above dam
- Marseilles │ 8.2│ 4.5│ 9.3│Below dam
- Ottawa │ 10.0│ │ 8.1│
- La Salle │ 5.4│ │ 7.8│
- Henry │ │ │ 7.9│
- Chillicothe │ 3.4│ 1.5│ 5.9│Above
- │ │ │ │ Peoria
- │ │ │ │ Lakes
- Averyville │ 3.3│ 8.2│ 8.9│Below
- │ │ │ │ Peoria
- │ │ │ │ Lakes
- Wesley │ │ │ 7.1│Below
- │ │ │ │ Peoria
- Pekin │ 4.9│ 3.2│ 8.9│
- Havana │ 4.8│ │ 8.8│
- Beardstown │ 6.5│ │ 9.1│
- La Grange │ │ 4.1│ 9.4│Below dam
- Kampsville │ │ 4.1│ 10.0│Above dam
- Kampsville │ │ 4.6│ 10.0│Below dam
- Grafton │ 6.6│ 4.7│ 10.4│Illinois
- │ │ │ │ River
- Grafton │ │ 7.3│ 12.0│Mississippi
- │ │ │ │ River
- ────────────┴───────┴──────┴──────┴───────────
-
-
-=222. Self-Purification of Lakes.=—Sewage may be disposed of into lakes
-with as great success as into running streams if conditions exist which
-are favorable to self-purification. Lakes and rivers purify themselves
-from the same causes; oxidation, sedimentation, etc., but in the former
-the currents are much less pronounced and may be entirely absent. In
-shallow lakes (20 feet or less in depth) dependence must be placed on
-horizontal currents and the stirring action of the wind to keep the
-water in motion in order that the sewage and the diluting water may be
-mixed. In deeper bodies of water, currents induced by the wind are
-helpful but entire dependence need not be placed upon them. Vertical
-currents, and the seasonal turnovers in the spring and fall completely
-mix the waters of the lake above those layers of water whose temperature
-never rises higher than 4° C.
-
-In the early winter the cold air cools the surface waters of a lake. The
-cooling increases the density of the surface water causing it to sink,
-and allowing the warmer layers below to rise and become cooled. After
-the temperature of the entire lake has reached 4° C. the vertical
-currents induced by temperature cease, as continued cooling decreases
-the density of the surface water maintaining the same layer at the
-surface. In the spring as the temperature of the surface water rises to
-4° C. and above it becomes heavier and drops through the colder water
-below causing vertical currents. These phenomena are known as the fall
-and spring turnovers. The former is more pronounced. These turnovers are
-effective in assisting in the self-purification of lakes.
-
-
-=223. Dilution in Salt Water.=—The oxygen content in salt water is about
-20 per cent less than in fresh water at the same temperature. The
-greater content of matter in solution in salt water reduces its capacity
-to absorb many sewage solids. This, together with the chemical reaction
-between the constituents of the salt water and those of the sewage serve
-to precipitate some of the sewage solids and to form offensive sludge
-banks. The evidence of the action which takes place in the absorption of
-oxygen from the atmosphere by salt water and its effect on dissolved
-sewage solids is conflicting, but in general fresh water is a better
-diluting medium than salt water.
-
-Black and Phelps have made valuable studies of the relative rates of
-absorption of oxygen from the air by fresh and salt water. The results
-of their experiments are published in a Report to the Board of Estimate
-and Apportionment of N. Y. City, made March 23, 1911.[131] Concerning
-these rates they conclude:
-
- Therefore there is no reason to believe that the reaëration of
- salt water follows any other laws than those we have determined
- mathematically and experimentally for fresh water. In the absence
- of fuller information on the effect of increased viscosity upon
- the diffusion coefficient, it can only be stated that the rate of
- reaëration of salt water is less than that of fresh water, in
- proportion to the respective solubilities of oxygen in the two
- waters, and still less, but to an unknown extent, by reason of the
- greater viscosity and consequent small value of the diffusion
- coefficient.
-
-
-=224. Quantity of Diluting Water Needed.=—In a large majority of the
-problems of disposal of sewage by dilution it is not necessary to add
-sufficient diluting water to oxidize completely all organic matter
-present. Ordinarily it is sufficient to prevent putrefactive conditions
-until the flow of the stream, lake, or tidal current, has reached some
-large body of diluting water or where putrefaction is no longer a
-nuisance. It is never desirable to allow the oxygen content of a stream
-to be exhausted as putrescible conditions will exist locally before
-exhaustion is complete. The exact point to which oxygen can be reduced
-in safety is in some dispute. Black and Phelps have assumed 70 per cent
-of saturation as the allowable limit; Fuller has placed it at 30 per
-cent; Kinnicutt, Winslow, and Pratt have placed it at 50 per cent. Since
-the reaction between the oxygen and the organic matter is quantitative,
-others have placed the limit in terms of parts per million of oxygen.
-Wisner,[132] has recommended a minimum of 2.5 p.p.m. as the limit for
-the sustenance of fish life, which is not far from Fuller’s limit for
-hot-weather conditions.
-
-Formulas of various types have been devised to express the rate of
-absorption of oxygen with a given quantity of diluting water which is
-mixed with a given quantity and quality of sewage. The quantity of
-sewage is sometimes expressed in terms of the tributary population or in
-other ways. Knowing the rate at which oxygen is exhausted and the
-velocity of flow of the stream, the point at which the oxygen will be
-reduced to the limit allowed is easily determined. The accuracy of none
-of these formulas has been proven, and their use, without an
-understanding of the effect of local conditions, may lead to error. They
-may be used as a check on the bio-chemical oxygen demand determinations,
-which should be conclusive.
-
-The following formula, based on the work of Black and Phelps, is a guide
-to the amount of sewage which can be added to a stream without causing a
-nuisance. It is:
-
- _C_ = (log(_O′_⁄_O_))⁄_kt_,
-
- in which _C_ = per cent of sewage allowed in the water;
-
- _O′_ = per cent of saturation or the p.p.m. of oxygen in the
- mixture at the time of dilution;
-
- _O_ = per cent of saturation or the p.p.m. of oxygen in the
- stream after period of flow to point beyond which no
- nuisance can be expected;
-
- _t_ = time in hours required for the stream to flow to this
- point;
-
- _k_ = constant determined by test determinations of the
- factors in the following expression:
-
- _k_ = (log(_O′__{1}⁄_O__{1}))⁄_C__{1}_t__{1},
-
- in which _O′__{1} = per cent of saturation or the p.p.m. of oxygen in
- the diluting water before mixing with the sewage;
-
- _O__{1} = per cent of saturation or the p.p.m. of oxygen in
- an artificial mixture made in the laboratory,
- after _t__{1} hours of incubation;
-
- _C__{1} = per cent of sewage in the mixture;
-
- _t__{1} = number of hours of incubation of the mixture of
- sewage and diluting water under laboratory
- conditions.
-
-In the solution of these formulas it is desired to determine the
-permissible amount of sewage to discharge into a given quantity of
-diluting water. This value is expressed by C in the first equation. In
-solving this equation:
-
- _O′_ is determined by laboratory tests and should represent
- the conditions to be expected during various seasons
- of the year;
-
- _O_ is determined by judgment. It may be 30 per cent or 50
- per cent or more as previously explained;
-
- _t_ is determined by float tests or other measurements of
- the stream flow;
-
- _k_ is determined by laboratory tests in which mixtures of
- various strengths are incubated for various periods
- of time. Different values of _k_ will be obtained for
- different characteristics of the sewage; but for the
- same sewage the value of _k_ should be unchanged for
- different periods of incubation.
-
-Rideal devised the formula:[133]
-
- _XO_ = _C_(_M_ − _N_)_S_
-
- in which _X_ = flow of the stream expressed in second-feet;
-
- _O_ = grams of free oxygen in one cubic foot of water;
-
- _S_ = rate of sewage discharge in second-feet;
-
- _M_ = grams of oxygen required to consume the organic matter
- in one cubic foot of diluted sewage as determined by
- the permanganate test with 4 hours boiling;
-
- _N_ = grams of oxygen available in the nitrites and nitrates
- in one cubic foot of diluted sewage;
-
- _C_ = ratio between the amount of oxygen in the stream and
- that required to prevent putrefaction. Where _C_ is
- equal to or greater than one, satisfactory conditions
- have been attained.
-
-In using this formula it is necessary to make analyses of trial mixtures
-of sewage and water until the correct mixture has been found.
-
-Hazen’s formula is:[134]
-
- _D_ = _x_⁄_S_ = 4_m_⁄_O_,
-
- in which _D_ = dilution ratio;
-
- _x_ = volume of water;
-
- _S_ = volume of sewage;
-
- _m_ = result of the oxygen consumed test expressed in p.p.m.
- after 5 minutes, boiling with potassium permanganate;
-
- _O_ = amount of dissolved oxygen in the diluting water
- expressed in p.p.m.
-
-For comparison with Rideal’s formula the factor of 7 should be used
-instead of 4 to allow for the increased time of boiling.
-
-Since the amount of oxygen needed is dependent on the amount of organic
-matter in the sewage rather than the total volume of the sewage, and
-since the amount of organic matter is closely proportional to the
-population, the amount of diluting water has sometimes been expressed in
-terms of the population. Hering’s recommendation for the quantity of
-diluting water necessary for Chicago sewage was 3.3 cubic feet of water
-per second per thousand population. Experience has proven this to be too
-small. Between a minimum limit of 2 second-feet and a maximum of 8
-second-feet of diluting water per thousand population the success of
-dilution is uncertain. Above this limit success is practically assured
-and below this limit failure can be expected.
-
-Even with these carefully devised formulas and empirical guides, the
-factors of reaëration, dilution, sedimentation, temperature, etc., may
-have so great an effect as to vitiate the conclusions. As shown in Table
-75 dilution in winter is far more successful than in summer. The lower
-temperatures so reduce the activity of the putrefying organisms that
-consumption of oxygen is greatly retarded.
-
-
-=225. Governmental Control.=—A comprehensive discussion of the legal
-principles governing the pollution of inland waters is contained in “A
-Review of the Laws Forbidding the Pollution of Inland Waters,” by E. B.
-Goodell, published by the United States Geological Survey in 1905, as
-Water Supply Paper No. 152.
-
-The disposal of sewage by dilution is subject to statutory limitations
-in many states. The enforcement of these laws is usually in the hands of
-the state board of health, which is frequently given discretionary
-powers to recommend and sometimes to enforce measures for the abatement
-of an actual or potential nuisance. Such recommendations usually take
-the form of a specification of certain forms of treatment preliminary to
-disposal by dilution. No project for the disposal of sewage by dilution
-should be consummated until the local, state, national, and in the case
-of boundary waters, international laws have been complied with. The
-attitude of the courts in different states has not been uniform. Little
-guidance can be taken from the personal feeling of the persons
-immediately interested. The opinion of the riparian owner 5 miles down
-stream may differ materially from the popular will of the voters of a
-city, and it is likely to receive a more favorable hearing from the
-court. Statutes and legal precedents are the safest guides.
-
-
-=226. Preliminary Treatment.=—If the sewage to be disposed of by
-dilution contains unsightly floating matter, oil, or grease, no amount
-of oxygen in the diluting water will prevent a nuisance to sight, or the
-formation of putrefying sludge banks. Under such conditions it will be
-necessary to introduce screens or sedimentation basins, or both, in
-order to remove the floating and the settling solids. Biologic tanks,
-filtration, or other methods of treatment may be necessary for the
-removal of other undesirable constituents.
-
-
-=227. Preliminary Investigations.=—Before adopting disposal of sewage by
-dilution without preliminary treatment, or before considering the proper
-form of treatment necessary to render disposal by dilution successful, a
-study should be made of the character of the body of water into which
-the sewage or effluent is to be discharged. This study should include:
-measurements of the quantity of water available at all seasons of the
-year; analyses of the diluting water to determine particularly the
-available dissolved oxygen; observations of the velocity and direction
-of currents, and the effect of winds thereon; a study of the effect on
-public water supplies, bathing beaches, fish life, etc. Good judgment,
-aided by the proper interpretation of such information should lead to
-the most desirable location for the sewer outlet. If preliminary
-treatment is found to be necessary tests should be made to determine the
-necessary extent and thoroughness of the treatment.
-
-
-
-
- CHAPTER XV
- SCREENING AND SEDIMENTATION
-
-
-=228. Purpose.=—The first step in the treatment of sewage is usually
-that of coarse screening in order to remove the larger particles of
-floating or suspended matter. Screens and sedimentation basins are used
-to prevent the clogging of sewers, channels, and treatment plants; to
-avoid clogging of and injuries to machinery; to overcome the
-accumulation of putrefying sludge banks; to minimize the absorption of
-oxygen in diluting water; and to intercept unsightly floating matter.
-
-By the plain sedimentation of sewage is meant the removal of suspended
-matter by quiescent subsidence unaffected by septic action or the
-addition of chemicals or other precipitants. In order to prevent septic
-action plain sedimentation tanks must be cleaned as frequently as once
-or twice a week in warm weather but not quite so often in cold weather.
-
-Fine screening may take the place of sedimentation where insufficient
-space is available for sedimentation tanks, and it is desired to remove
-only a small portion of the suspended matter. Recent American practice
-has tended to restrict the field of fine screening to treatment
-requiring less than 10 per cent removal of suspended matter, thus
-eliminating screens from the field covered by plain sedimentation tanks.
-The practice is well expressed by Potter, who states:[135]
-
- Where a high degree of purification is sought, the use of fine
- screens is of doubtful value. A modern settling tank will give
- better results and at a less cost for a given degree of
- purification. A settled liquid is also superior to a screened
- liquid for subsequent biological treatment in filters.... Again
- the storing of large quantities of screenings must necessarily be
- more objectionable than the storing of the digested sludge of a
- modern settling tank.
-
-[Illustration:
-
- FIG. 150.—Types of Moving Screens.
-
- Trans. Am. Society Civil Engineers, Vol. 78, 1915, p. 893.
-]
-
-
-=229. Types of Screens.=—The definitions of some types of screens as
-proposed by the American Public Health Association follow: A _bar
-screen_ is composed of parallel bars or rods. A _mesh screen_ is
-composed of a fabric, usually wire. A _grating_ consists of 2 sets of
-parallel bars in the same plane in sets intersecting at right angles. A
-_band screen_ consists of an endless perforated band or belt which
-passes over upper and lower rollers. A _perforated plate screen_ is made
-of an endless band of perforated plates similar to a band screen. A
-_wing screen_ has radial vanes uniformly spaced which rotate on a
-horizontal axis. A _disc screen_ consists of a circular perforated disc
-with or without a central truncated cone of similar material mounted in
-the center. The Reinsch Wurl screen is the best known type of disc
-screen. A _cage screen_[136] consists of a rectangular box made up of
-parallel bars with the upstream side of the box or cage omitted.
-Allen[137] gives the following definitions: A _drum screen_ is a
-cylinder or cone of perforated plates or wire mesh which rotates on a
-horizontal axis. A _shovel vane screen_ is similar to a wing screen with
-semicircular wings and a different method of removing the screenings.
-Examples of a band screen, a wing screen, a shovel vane screen, a drum
-screen and a disc screen are shown in Fig. 150. A bar screen is shown in
-Fig. 151 and a cage screen is shown in Fig. 152.
-
-[Illustration:
-
- FIG. 151.—Sketch of a Bar Screen.
-]
-
-[Illustration:
-
- FIG. 152.—Sketch of a Cage Screen.
-]
-
-Screens can be classed as fixed, movable, or moving. Fixed screens are
-permanently set in position and must be cleaned by rakes or teeth that
-are pulled between the bars. Movable screens are stationary when in
-operation, but are lifted from the sewage for the purpose of cleaning.
-Moving screens are in continuous motion when in operation and are
-cleaned while in motion. Fixed bar screens may be set either vertical,
-inclined, or horizontal.
-
-Movable screens with a cage or box at the bottom are sometimes used. The
-box should be of solid material to prevent the forcing of screenings
-through it when the screen is being raised for cleaning. A mesh screen
-should be used only under special circumstances because of the
-difficulty in cleaning. Screens which must be raised from the sewage for
-cleaning should be arranged in pairs in order that one may be working
-when the other is being cleaned. Movable screens are undesirable for
-small plants because the labor involved in raising and lowering is
-greater than in cleaning with a rake and the screens are more likely to
-be neglected. In a large plant rakes operated by hand are too small for
-cleaning the screens. A fixed screen is sometimes used with moving teeth
-fastened to endless chains. The teeth pass between the parallel bars and
-comb out the screenings. If the screen chamber in a small plant is too
-deep for accessibility a movable cage or box screen may be desirable.
-
-Moving screens are generally of fine mesh or perforated plates. They are
-kept moving in order to allow continuous cleaning. They are cleaned by
-brushes or by jets of air, water, or steam.
-
-
-=230. Sizes of Openings.=—The area or size of the opening of a screen is
-dependent upon the character of the sewage to be treated and upon the
-object to be attained.
-
-Large screens, with openings between 1½ inches and 6 inches are used to
-protect centrifugal pumps, tanks, automatic dosing devices, conduits,
-and gate valves from large objects such as pieces of timber, dead
-animals, etc., which are found in sewage. The quantity of material
-removed is variable, and is usually small.
-
-Medium-size screens with openings from ¼ inch to 1½ inches are used to
-prepare sewage for passage through reciprocating pumps, complex dosing
-apparatus, contact beds, and sand filters. The amount of material
-removed varies from 0.5 to 10 cubic feet per million gallons of sewage
-treated, dependent on the character of the sewage and the size of the
-screen. Screenings before drying contain 75 to 90 per cent moisture and
-weigh 40 to 50 pounds per cubic foot. At times the amount removed may
-vary widely from the limits stated. Schaetzle and Davis[138] state:
-
- Screenings differ greatly both in amount and character.... The
- amount varies with the days of the week as well as during the
- course of the day. It reaches its maximum about noon or shortly
- before and commences to disappear about midnight, reaching a
- minimum about 4 or 5 a.m. The material is almost wholly organic
- and consists of scraps of vegetables or fruit, cloth, hair, wood,
- paper and lumps of fecal matter. The amount varies so widely that
- it is impossible to state just what to expect any definite size
- screen to remove. The amount of water contained is small compared
- with that in the sludge in sedimentation basins and amounts to
- from 70 per cent to 80 per cent. On account of its organic origin
- it is highly putrescible.
-
-Medium-size screens are sometimes placed close together with the bars of
-the one opposite the openings in the other, thus approaching a fine
-screen.
-
-Fine screens vary in size of opening from ¼ inch to 50 openings per
-linear inch or 2,500 per square inch. They are used for removing solids
-preparatory to disposal by dilution, to protect sprinkling filters,
-complex dosing apparatus, sand filters, sewage farms, and to prevent the
-formation of scum in subsequent tank treatment. In general, fine screens
-will remove from 0.1 to 1 cubic yard of wet material per million gallons
-of sewage treated. The wet screenings will contain about 75 per cent
-moisture and will weigh about 60 pounds per cubic foot. The dry weight
-of the screenings will therefore be about 10 to 400 pounds per million
-gallons of sewage treated. The effect of the removal of this amount of
-material is usually not detectable by methods of chemical analysis, the
-amount of suspended matter before and after screening being found
-unchanged.
-
-In his conclusions on the discussion of the results to be expected from
-fine screens, Allen states:[139]
-
- With openings not more than 0.1 inch in size, fine screening
- should remove at least 30 per cent of the suspended solids and 20
- per cent of the suspended organic solids from ordinary domestic
- sewage, or 0.1 cubic yard of screenings, containing 75 per cent
- water per thousand population daily.
-
-The effect of the use of different size openings under the same
-conditions is shown in Fig. 153.[140] Some data covering the amount of
-material removed by screening are given in Table 76. More extensive data
-are given in Volume III of “American Sewerage Practice” by Metcalf and
-Eddy.
-
- TABLE 76
-
- DATA ON SCREENS
-
- (Trans. Am. Society Civil Engineers, Vol. 78, Page 942)
-
- ───────┬──────────┬──────────┬──────────────────────────
- Type of│ Location │ Clear │ Screenings
- Screen │ │ Opening, │
- │ │in Inches │
- │ │ │
- │ │ │
- │ │ │
- ───────┼──────────┼──────────┼────────────┬─────────────
- │ │ │Per Million │ Per 1000
- │ │ │ Gallons, │ Population
- │ │ │_y_ = Cubic │ Daily,
- │ │ │ Yard │ _y_ = Cubic
- │ │ │ _t_ = Tons │ Yard
- │ │ │ │ _t_ = Tons
- ───────┼──────────┼──────────┼────────────┼─────────────
- Band │Hamburg │ 0.6 │ 0.34_y_ │ 0.018_y_
- │Göttingen │ 0.4 │ 0.35_y_ │ 0.026_y_
- │Sutton │0.375[141]│ 0.6_y_ │
- │Chicago │ │ 2.4–3.1_t_ │
- Wing │Frankfort │ 0.40 │ 0.7_y_ │ 0.040_y_
- │Elberfeld │ 0.40 │ 1.15_y_ │ 0.053_y_
- │Stralsund │ 0.20 │ │ 0.079_y_
- │Wiesbaden │ 0.60 │ 1.1_y_ │ 0.033_y_
- Shovel │Strassburg│ 0.10 │ 1.6_y_ │ 0.043_y_
- vane │ │ │ │
- │Gleiwitz │ 0.12 │ │ 0.192_y_
- │Temesvar │ 0.12 │ 0.9–1.7_y_ │0.067–.133_y_
- Drum │Bromberg │ 0.08 │ 4.75_t_ │
- │Mainz │ Note 6 │ 0.52_y_ │
- │Trier │ 0.10 │0.39–0.42_y_│ 0.13_y_
- │Osnabruck │ 0.08 │ 3.2–4.0_y_ │ 0.08–.10_y_
- Weand │Reading, │ 36[141] │ 1.0_y_ │
- │ Pa. │ │ │
- │Brockton │ 36[141] │ 1.4_t_ │
- Reinsch│Dresden │ 0.08 │ 0.97_t_ │ 0.09_y_
- Wurl │ │ │ │
- ───────┴──────────┴──────────┴────────────┴─────────────
-
- ───────┬────────┬───────────┬─────────┬────────────
- Type of│Per Cent│Horse-Power│ Cost of │ Remarks
- Screen │Moisture│Per Screen │Operation│
- │ │ │ Per │
- │ │ │ Million │
- │ │ │Gallons, │
- │ │ │ Dollars │
- ───────┼────────┼───────────┼─────────┼────────────
- │ │ │ │
- │ │ │ │
- │ │ │ │
- │ │ │ │
- │ │ │ │
- │ │ │ │
- ───────┼────────┼───────────┼─────────┼────────────
- Band │ 87 │ 2.5 │ │Note 1
- │ │ 2.0 │ │
- │ │ │ │
- │ 79 │ │ │Stock Yard
- Wing │ │ 5.0 │ │Note 2
- │ 75 │ │ │Note 3
- │ │ 4.5 │ │
- │ │hand power │ 1.64 │Note 4
- Shovel │ 89.3 │ 3.35 │ │Note 5
- vane │ │ │ │
- │ │ │ 0.90 │
- │ 60–70 │ │ small │
- Drum │ 40–60 │ │ 2.45 │Experimental
- │ 75 │ 5.2–6.8 │0.89–3.42│
- │ 50–60 │ │ 2.41 │Experimental
- │ │ 9.00 │ │Note 7
- Weand │ 89.5 │ 2.0 │ 1.00± │
- │ │ │ │
- │ │ │ │
- Reinsch│ 84 │ 2.5 │.325–1.76│
- Wurl │ │ │ │
- ───────┴────────┴───────────┴─────────┴────────────
-
- Notes:—1. After removal of ½ this volume of grit.
-
- 2. After removal of 16 per cent by the grit chamber.
-
- 3. Including 0.6 cubic yard grit per million gallons.
-
- 4. After passing 1.6 inch bar screen.
-
- 5. After removal of 0.132 cubic yard grit and coarse
- screenings per 1000 population.
-
- 6. 0.12, 0.04–0.08.
-
- 7. Before removal of 0.4 cubic yard grit per million gallons.
-
-[Illustration:
-
- FIG. 153.—Screenings Collected on Different Sized Openings.
-
- 1921 Report on Industrial Wastes Disposal, Union Stock Yards District,
- Chicago, Illinois, to the Sanitary District of Chicago.
-]
-
-
-=231. Design of Fixed and Movable Screens.=—The determination of the
-size of the opening is the first step in the design of a sewage screen.
-This is followed by the computation of the net area of openings in the
-screen. The final steps are the determination of the overall dimensions
-of the screen; the size of the bar, wire, or support; and the dimensions
-of the screen chamber. The net area of openings is fixed by the
-permissible velocity of flow through the screen and the quantity of
-sewage to be treated. In determining the velocity of flow the general
-principle should be followed that the velocity should not be reduced
-sufficiently to allow sedimentation in the screen chamber. The velocity
-of grit bearing sewage in passing through coarse screens should not be
-reduced below 2 or 3 feet per second. If the sewage contains no grit, or
-the screen is placed below a grit chamber the velocity through a medium
-or fine screen should be from ½ to 1½ feet per minute. The velocity
-through the screen in a direction normal to the plane of the screen can
-be reduced without reducing the horizontal velocity of the sewage by
-placing the screen in a sloping position.
-
-The final steps are the design of the screen bar and the determination
-of the dimensions of the screen and of the screen chamber. The size of
-the bar in a bar screen, or as a support to a wire mesh, is dependent on
-the unsupported length of the bar. The stresses in the bars are the
-results of impact and bending, caused by cleaning, and of the load due
-to the backing up of the sewage when the screen is clogged. Allowance
-should be made for a head of 2 or 3 feet of sewage against the screen. A
-generous allowance should be made in addition for the indeterminate
-stresses due to cleaning. The screen should be supported only at the top
-and bottom, as intermediate supports in a bar screen are undesirable
-unless they are so arranged as not to interfere with the teeth of the
-cleaning devices.
-
-Fixed screens should be placed at an angle between 30° and 60° with the
-horizontal, with the direction of slope such that the screenings are
-caught on the upper portion of the screen. A small slope is desirable in
-order to obtain a low velocity through the screen. The slope is limited
-since the smaller the slope the longer the bars of the screen and the
-greater the difficulty of hand cleaning. Small slopes will tend to make
-the screens self cleaning. As the screen clogs, the increasing head of
-sewage will push the accumulated screenings up the screen. The use of
-flat screens in a vertical position is not desirable because of the
-difficulty of cleaning and the accumulation of material at inaccessible
-points. If a flat screen is placed in a horizontal position with the
-flow of sewage downward difficulties are encountered in cleaning and
-solid matter is forced through the screen as clogging increases. An
-upward flow through a horizontal screen is undesirable as the material
-is caught in a position inaccessible for cleaning. Movable screens are
-more easily handled when placed in a vertical position.
-
-In the construction of small screens, round bars are sometimes used
-where the unsupported length of the bar is less than 3 or 4 feet. They
-are not recommended, however, as the efficient area and the amount of
-material removed by the screen are diminished. Bars which produce
-openings with the larger end upstream are undesirable as particles
-become wedged in the screen, and are either forced through or become
-difficult to remove.[142] Rectangular bars are easily obtained and give
-satisfactory service except where they are of insufficient strength
-laterally. For greater lateral thickness a pear-shaped bar is sometimes
-used, with the thicker side upstream. Fine mesh screens or perforated
-plates are supported on grids or parallel bars of stronger material
-designed to take up the heavy stresses on the screen.
-
-The dimensions of the bar may be selected arbitrarily. The length and
-width of the screen are fixed to give desirable dimensions to the screen
-chamber and to give the necessary net opening in the screen. The width
-of the screen chamber and the screen should be the same. The screen
-chamber should be sufficiently long to prevent swirling and eddying
-around the screen. If the dimensions thus fixed permit an undesirable,
-velocity in the screen chamber they should be changed. A sufficient
-length of screen should be allowed to project above the sewage for the
-accumulation of screenings. The bars may be carried up and bent over at
-the top as shown in Fig. 151 to simplify the removal of screenings.
-
-Coarse screens are usually placed above all other portions of a
-treatment plant. They may be followed by grit chambers or finer screens.
-Coarse screens are occasionally placed as a protection above medium or
-fine screens. In sewage containing grit the smaller screens are
-sometimes placed below the grit chamber. It is desirable to provide some
-means of diverting the sewage from a screen chamber to allow of repairs
-to the screen and the cleaning of the chamber. Screen chambers are
-sometimes designed in duplicate to allow for the cleaning of one while
-the other is operating.
-
-
- PLAIN SEDIMENTATION
-
-
-=232. Theory of Sedimentation.=—Sedimentation takes place in sewage
-because some particles of suspended matter have a greater specific
-gravity than that of water. All particles do not settle at the same
-rate. Since the weights of particles vary as the cubes of their
-diameters, whereas the surface areas (upon which the action of the water
-takes place) vary only as the squares of the diameters, the amount of
-the skin friction on small particles is proportionally greater than that
-on large particles, because of the relatively greater surface area
-compared to their weight. As a result the smaller particles settle more
-slowly. The velocity of sedimentation of large particles has been found
-to vary about as the diameter and of small particles as the square root
-of the diameter. The change takes place at a size of about 0.01 mm.
-
-Sedimentation is accomplished by so retarding the velocity of flow of a
-liquid that the settling particles will be given the opportunity to
-settle out. The slowing down of the velocity is accomplished by passing
-the sewage through a chamber of greater cross-sectional area than the
-conduit from which it came. The time that the sewage is in this chamber
-is called the period of retention. Although the shape of a basin, the
-arrangement of the baffles and other details have a marked effect on the
-results of sedimentation, the controlling factors are the period of
-retention and the velocity of flow. Another factor affecting the
-efficiency of the process is the quality of the sewage. Usually the
-greater the amount of sediment in the sewage the greater the per cent of
-suspended matter removed. A method for the determination of the proper
-period of sedimentation has been developed by Hazen in Transactions of
-the American Society of Civil Engineers, Volume 53, 1904, page 45. The
-results of his studies are summarized in Fig. 154 which shows the per
-cent of sediment remaining in a treated water after a certain period of
-retention. This period of retention is expressed in terms of the
-hydraulic coefficient[143] of the smallest size particle to be removed.
-Table 77 shows the hydraulic coefficients of various particles. In Fig.
-154 _a_ represents the period of retention and _t_ the time that it
-would take a particle to fall to the bottom of the basin. The different
-lines of the diagram represent the results to be expected by various
-arrangements of settling basins. The meaning of these lines is given in
-Table 78.
-
- TABLE 77
-
- HYDRAULIC VALUES OF SETTLING PARTICLES IN MILLIMETERS PER SECOND
-
- ───────────────────────────────────┬───────────────────────────────────
- Diameter in mm. │ Hydraulic Value
- ───────────────────────────────────┼───────────────────────────────────
- 1.00 │ 100
- 0.80 │ 83
- 0.60 │ 63
- 0.50 │ 53
- 0.40 │ 42
- 0.30 │ 32
- 0.20 │ 21
- 0.15 │ 15
- 0.10 │ 8
- 0.08 │ 6
- 0.06 │ 3.8
- 0.05 │ 2.9
- 0.04 │ 2.1
- 0.03 │ 1.3
- 0.02 │ 0.62
- 0.015 │ 0.35
- 0.010 │ 0.154
- 0.008 │ 0.098
- 0.006 │ 0.055
- 0.005 │ 0.0385
- 0.004 │ 0.0247
- 0.003 │ 0.0138
- 0.002 │ 0.0062
- 0.0015 │ 0.0035
- 0.001 │ 0.00154
- 0.0001 │ 0.0000154
- ───────────────────────────────────┴───────────────────────────────────
-
-An example will be given to illustrate the method of using the diagram
-and tables to determine the size of a sedimentation basin to perform
-certain required work.
-
- Let it be required to determine the period of retention in a
- continuously operated sedimentation basin with good baffling,
- corresponding to two properly baffled sedimentation basins in
- series. The basins are to remove 60 per cent of the finest
- particles which are to have a size of .01 mm. The quantity to be
- treated daily is 3,000,000 gallons.
-
- 1st. Entering Table 77, we find that the hydraulic value of the
- finest particles is .154 mm. per second.
-
- 2d. Since we wish to remove 60 per cent of the finest particles,
- 40 per cent will remain. Since Fig. 154 shows the per cent
- remaining after the time _a_⁄_t_ we enter Fig. 154 at 40 per cent
- on the ordinates and run horizontally until we encounter Line 4
- corresponding to good baffling in Table 78. We then run down
- vertically from this intersection and find that the ratio of
- _a_⁄_t_ is 1.0.
-
- Then _a_ equals _t_, which means that the period of retention
- should equal the time that it takes a particle 0.01 mm. in
- diameter to drop from the top to the bottom of the basin. Since
- this depends on the depth of the basin it is necessary to
- determine the depth before the other dimensions of the basin can
- be fixed.
-
-Although this method is seldom used in practice for the final design of
-a sedimentation basin, it is a guide to judgment and can be used to
-supplement the data obtained from tests.
-
-[Illustration:
-
- FIG. 154.—Hazen’s Diagram, Showing the Relation between the Time of
- Settling and the Period of Retention in Various Types of
- Sedimentation Basins.
-
- Trans. Am. Society Civil Engineers, Vol. 53, 1904, p. 45.
-]
-
- TABLE 78
-
- COMPARISON OF DIFFERENT ARRANGEMENTS OF SETTLING BASINS
-
- (From Hazen)
- ────────────────────────────────────────┬────────────┬─────────────────
- Description of Basins │Line in Fig.│ Values of
- │ 154 │ _a_⁄_t_.
- ────────────────────────────────────────┼────────────┼─────────────────
- │ │ Per Cent of
- │ │ Matter Removed
- ────────────────────────────────────────┼────────────┼─────┬─────┬─────
- │ │ 50 │ 74 │87.5
- ────────────────────────────────────────┼────────────┼─────┼─────┼─────
- Theoretical maximum. Cannot be reached.│ A │ 0.50│ 0.75│0.875
- Surface skimming. Rockner Roth system. │ B │ 0.54│ 0.98│ 1.37
- Intermittent basins, reckoned on time of│ C │ │ │
- service only. │ │ 0.63│ 1.26│ 1.89
- Continuous basin. Theoretical limit. │ D │ 0.69│ 1.38│ 2.08
- Close approximation to the above. │ 16 │ 0.71│ 1.45│ 2.23
- Very well baffled basin. │ 8 │ 0.73│ 1.62│ 2.37
- Good baffling. │ 4 │ 0.76│ 1.66│ 2.75
- Two basins, tandem. │ 2 │ 0.82│ 2.00│ 3.70
- One long basin, well controlled. │ 1.5 │ 0.90│ 2.34│ 4.50
- Intermittent basin in service half time.│ E │ 1.26│ 2.50│ 3.80
- One basin, continuous. │ 1 │ 1.0│ 3.00│ 7.00
- ────────────────────────────────────────┴────────────┴─────┴─────┴─────
-
-The design of sedimentation basins should be based on experimental
-observations made upon the quantity of sediment removed at certain rates
-of flow and periods of retention in different types of basins. Hazen’s
-mathematical analysis is serviceable in making preliminary estimates and
-in checking the results. The shape of the tank, period of retention and
-rate of flow producing the most desirable results should be duplicated
-with the expectation of obtaining similar results or results but
-slightly modified from those obtained in the tests. This is the most
-satisfactory method of determining the proper period of retention.
-
-
-=233. Types of Sedimentation Basins.=—A sedimentation basin is a tank
-for the removal of suspended matter either by quiescent settlement or by
-continuous flow at such a velocity and time of retention as to allow
-deposition of suspended matter.[144] The difference between
-sedimentation tanks and other forms of tank treatment is that no
-chemical or biological action is depended on for the successful
-operation of the tank. Sedimentation tanks may be divided into two
-classes, grit chambers and plain sedimentation basins.
-
-A grit chamber is a chamber or enlarged channel in which the velocity of
-flow is so controlled that only heavy solids, such as grit and sand, are
-deposited while the lighter organic solids are carried forward in
-suspension. If the velocity of flow is more than about one foot per
-second, the tank is a grit chamber and below this velocity it is a plain
-sedimentation basin.
-
- There are six general types of plain sedimentation basins:
-
- 1st. Rectangular flat-bottom tanks operated on the continuous-flow
- principle.
-
- 2nd. Rectangular flat-bottom tanks operated on the fill and draw
- principle.
-
- 3rd. Rectangular or circular hopper-bottom tanks operated on the
- continuous-flow principle, with horizontal flow.
-
- 4th. Rectangular or circular hopper-bottom tanks operated on the
- fill and draw principle, with horizontal flow.
-
- 5th. Rectangular or circular hopper-bottom tanks operated on the
- continuous-flow principle with vertical flow.
-
- 6th. Circular hopper-bottom tanks operated on the continuous-flow
- principle with radial flow.
-
- TABLE 79
-
- CRITICAL VELOCITIES FOR THE TRANSPORTATION OF DEBRIS
-
- Sedimentation will not Occur at Higher Velocities
- ───────────┬───────────────────────────────────┬──────────────────────
- Diameter of│Critical Velocity, Feet per Second.│ Size of Screen or
- Particle in│ │ Number of Meshes per
- Millimeters│ │ Inch
- ───────────┼───────────────────────────────────┼──────────────────────
- │ Specific Gravity │
- ───────────┼────────┬────────┬────────┬────────┼──────────────────────
- │ 1.5 │ 2.0 │ 3.0 │ 5.0 │
- ───────────┼────────┼────────┼────────┼────────┼──────────────────────
- 0.010 │0.13 │0.20 │0.22 │0.28 │
- 0.050 │0.23 │0.34 │0.39 │0.50 │More than 200
- 0.100 │0.30 │0.42 │0.50 │0.65 │More than 150
- 0.500 │0.55 │0.73 │0.91 │1.15 │More than 28
- 1.0 │0.71 │0.92 │1.18 │1.50 │More than 14
- 1.25 │0.77 │1.00 │1.30 │1.60 │
- 2.0 │0.92 │1.20 │1.50 │1.90 │More than 10
- 5.0 │1.30 │1.70 │2.20 │2.60 │More than 4
- 10 │1.70 │2.20 │2.8 │3.4 │
- │ │ │ │ │
- Diameter in Millimeters for a Velocity of 1 Foot per Second
- │ │ │ │ │
- │2.5 │1.25 │0.65 │0.32 │
- ───────────┴────────┴────────┴────────┴────────┴──────────────────────
-
-
-=234. Limiting Velocities.=—Sand, clay, bits of metal and other
-particles of mineral matter will commence to deposit in appreciable
-quantities when the velocity of flow falls below 3 feet per second. The
-amount deposited will increase as the velocity decreases. In Table 79
-are given the approximate horizontal velocities at which certain size
-particles of mineral matter will deposit. At a velocity of about one
-foot per second organic matter will commence to deposit. It will be
-noticed by interpolation in Table 79,[145] that particles with the same
-specific gravity as sand (2.6), larger than one mm. in diameter will
-deposit at a velocity of about one foot per second or less, and that
-smaller and lighter particles will not deposit at velocity of one foot
-per second or greater. It will also be noticed that a velocity of one
-foot per minute is sufficiently slow to permit the deposit of the
-smallest and lightest particles. For this reason velocities of 1 or 2 or
-even 3 feet per second have been adopted as the velocities in grit
-chambers and velocities less than 1 foot per minute in plain
-sedimentation basins.
-
-
-=235. Quantity and Character of Grit.=—The amount of material deposited
-in grit chambers varies approximately between 0.10 and 0.50 cubic yard
-per million gallons. It is to be noted that grit chambers are used only
-for combined and storm sewage and for certain industrial wastes. They
-are unnecessary for ordinary domestic sewage. The material deposited in
-grit chambers operating with a velocity greater than one foot per second
-is non-putrescible, inorganic, and inoffensive. It can be used for
-filling, for making paths and roadways, or as a filtering material for
-sludge drying beds. An analysis of a typical grit chamber sludge is
-shown in Table 80.
-
- TABLE 80
-
- ANALYSIS OF GRIT CHAMBER SLUDGE
-
- ───────────┬───────────┬───────────┬───────────────────────────────────
- Velocity │ Specific │ Per Cent │Calculated to Dry Weight, Per Cent
- Feet per │ Gravity │ Moisture │
- Second │ │ │
- ───────────┼───────────┼───────────┼──────────┬──────────┬─────────────
- │ │ │ Nitrogen │ Fixed │Miscellaneous
- │ │ │ │ Matter │
- ───────────┼───────────┼───────────┼──────────┼──────────┼─────────────
- 1.0 │ 1.5 │ 45 │ 20 │ 78 │ 2
- ───────────┴───────────┴───────────┴──────────┴──────────┴─────────────
-
-
-=236. Dimensions of Grit Chambers.=—The quantity of sewage to be treated
-and the amount and character of the settling solids which it contains
-should be determined by measurement and analysis, and the amount of
-settling solids to be removed should be determined by a study of the
-desired conditions of disposal, in order that a grit chamber that will
-accomplish the desired results may be designed. The period of retention
-and the velocity of flow are the controlling features in the successful
-operation of any grit chamber. These should be determined by experiment
-or as the result of experience. Where neither are available, Hazen’s
-method can be followed or a decision made based on a study of other grit
-chambers. In general, the period of retention in grit chambers is from
-30 to 90 seconds, and the velocity of flow is about one foot per second.
-
-After having determined the quantity of sewage to be treated, the
-quantity of grit to be stored between cleanings, the period of
-retention, the arrangement of the chambers, and the velocity of flow to
-be used, the overall dimensions of the chambers are computed. The
-capacity of the chamber is fixed as the sum of the quantity of sewage to
-be treated during the period of retention and the required storage
-capacity for grit accumulated between cleanings. The length of the
-chamber is fixed as the product of the velocity of flow and the period
-of retention. The cross-sectional area of the portion of the chamber
-devoted to sedimentation is fixed as the quotient of the quantity of
-flow of sewage per unit time and the velocity of flow. Only the relation
-between the width and depth of the portion devoted to sedimentation and
-the portion devoted to the storage of grit remain to be determined.
-These should be so designed as to give the greatest economy of
-construction commensurate with the required results. They will be
-affected by the local conditions such as topography, available space,
-difficulties of excavation, etc. Common depths in use lie between 8 and
-12 feet, although wide variations can be found. A study of the
-proportions of existing grit chambers will be of assistance in the
-design of other basins.
-
-
-=237. Existing Grit Chambers.=—The details of some typical grit chambers
-are shown in Figs. 155 and 156. The grit chamber at the foot of 58th
-Street, in Cleveland, Ohio, is shown in Fig. 155. The special feature of
-this structure is the shape of the sedimentation basin, the bottom of
-which is formed by sloping steel plates forming a 6–inch longitudinal
-slot above the grit storage chamber. Flows between 8,000,000 and
-16,000,000 gallons per day are controlled by the outlet weir so that the
-velocity of flow remains at one foot per second. This is accomplished by
-increasing the depth of flow in the same ratio as the increase in the
-rate of flow. The bottoms of the two chambers differ, one having a
-special hopper for grit and the other a flat bottom. This is due to the
-method of cleaning the chambers, it being necessary in the one with a
-flat bottom to shut off the flow when removing the grit while in the one
-with the hopper bottom it is hoped to remove the grit by the use of sand
-ejectors without stopping the sewage flow. The details of the chamber at
-Hamilton, Ontario, are shown in Fig. 156. In studying these drawings the
-following features should be noted: 1st, the smooth curves in the
-channel to prevent eddies, undue deposition of organic matter, and
-difficulties in cleaning; 2nd, the hopper in the upper end of the grit
-storage chamber and the slope of the bottom of at least 1:20; and 3rd,
-the simplicity of the inlet and outlet devices which may be either stop
-planks or cast-iron sluice gates.
-
-[Illustration:
-
- FIG. 155.—Grit Chamber at Cleveland, Ohio.
-
- Eng. Record, Vol. 73, 1916, p. 409.
-]
-
-[Illustration:
-
- FIG. 156.—Grit Chamber at Hamilton, Ontario.
-
- Eng. News, Vol. 73, 1915, p. 425.
-]
-
-The drawings shown are merely representative of some satisfactory types.
-The number and variety of grit chambers in existence is great. In
-designing grit chambers consideration must be given to the method of
-cleaning. They are ordinarily cleaned by such methods as have been
-described for the cleaning of catch-basins in Chapter XII. Continuous
-bucket scrapers similar to excavating machines are sometimes used for
-the cleaning of large grit chambers. The period between cleanings is
-variable. The design should be such as not to require more frequent
-cleanings than twice a month under the worst conditions. The
-fluctuations in quality and quantity of grit will vary the period
-between cleanings.
-
-
-=238. Number of Grit Chambers.=—The period of retention in grit chambers
-is so short and the velocity of flow so near the maximum and minimum
-limitations that the wide fluctuations in the rate of discharge in storm
-and combined sewers necessitates the construction of a number of
-chambers which should be operated in parallel in order to maintain the
-velocity between the proper limits. Unless arrangements are made
-permitting the cleaning of grit chambers during operation, more than one
-grit chamber should be installed in order that when one is being cleaned
-the others may be in operation. The number of grit chambers must be
-determined by the desired conditions of operation and the cost of
-construction. The larger the number of basins the more nearly the flow
-in any one basin can be maintained constant, but the more expensive the
-construction. The increase in velocity of flow with increasing quantity
-is dependent on the outlet arrangements. In a shallow chamber with
-vertical sides and a standard sharp-crested rectangular weir at the
-outlet the velocity will vary approximately as the cube root of the rate
-of flow. Similarly if the outlet is a V notch the velocity will vary as
-the fifth root of the rate of flow. In all cases the deeper the basin
-the more nearly the velocity varies directly as the rate of flow. The
-outlet weir can be arranged as at Cleveland, so that the velocity
-remains constant for all rates of flow within certain limits. It is
-seldom that more than three grit chambers are necessary to care for the
-fluctuations in flow.
-
-
-=239. Quantity and Characteristics of Sludge from Plain
-Sedimentation.=—The sludge removed from plain sedimentation basins is
-slimy, offensive, not easily dried, and is highly putrescible and
-odoriferous. It contains about 90 per cent moisture and has a specific
-gravity from 1.01 to 1.05. The amount removed varies between 2 and 5
-cubic yards per million gallons of sewage. The percentage of suspended
-matter removed varies between 20 and 60. The total amount removed and
-the percentage removal depend on the character of the sewage, the type
-of basin, and the period of detention.
-
-
-=240. Dimensions of Sedimentation Basins.=—The dimensions of a
-sedimentation basin are determined by a method similar to the one given
-for the determination of the dimensions of a grit chamber in Art. 236.
-The capacity of the basin is first fixed upon to give the required
-period of sedimentation and sludge storage capacity. The length of the
-basin is the product of the velocity and the period of retention. The
-length, width, and depth of the basin are normally fixed by
-considerations of economy and the limitations of the local conditions,
-such as available area, topography, foundations, etc., and examples of
-good practice. A study of basins in use shows the relation between
-length and width to vary normally between 2:1 and 4:1. Widths greater
-than 30 to 50 feet are undesirable because of the danger of cross
-currents and back eddies which will reduce the efficiency of the
-sedimentation. Depths used in practice vary too widely to act as guides
-for any particular design. Theoretically the shallower the basin the
-better the result. Tanks abroad have been built as shallow as 3 feet and
-some in this country as deep as 16 feet. The economical dimensions can
-be determined by trial or by calculus. They will serve as a guide in the
-adoption of the final dimensions.
-
-The method to be pursued in determining the economical dimensions of any
-engineering structure are:
-
- I. Express the total cost of the structure in terms of as few
- variables as possible.
-
- II. Express all of the variables in terms of any one and rewrite
- the expression for the total cost in terms of this one variable.
-
- III. Equate the first derivative of the expression with regard to
- this variable to zero and solve for the variable. The result will
- be the economical value of the variable. The values of the other
- variables can be computed from the relations already expressed.
-
-[Illustration:
-
- FIG. 157.—Diagram for the Computation of Economical Basin Dimensions.
-]
-
-For example, let it be desired to determine the dimensions of two
-continuous-flow sedimentation basins as shown in Fig. 157, in which the
-period of retention in each is to be 2 hours, the velocity of flow is
-not to exceed one foot per second, and the sludge accumulated will be 3
-cubic yards per million gallons of sewage treated. The quantity of
-sewage to be treated is 18,000,000 gallons per day. The shortest time
-between cleanings will be 2 weeks.
-
-The capacity of each basin must be 2/24 of 18,000,000 gallons, or
-200,000 cubic feet in order to allow a period of retention of 2 hours.
-To this volume should be added sufficient capacity to allow for the 2
-weeks of sludge storage between cleanings. When a basin is being cleaned
-the load must be put on the remaining basins. Then if _Q_ represents the
-rate of accumulation of sludge per day, _n_ represents the number of
-days between cleanings, _m_ represents the number of basins, and _S_ the
-sludge capacity of one basin, then
-
- _S_ = (_Q_(_n_ − 1))⁄_m_ + _Q_⁄(_m_ − 1)
-
-The sludge storage capacity for the example given will be approximately
-11,000 cubic feet.
-
-In expressing the total cost of the basins let
-
- _h_ = the depth in feet.
- _l_ = the length in feet.
- _b_ = the width in feet.
-
- The cost of land, floor, etc., per square foot = _p_ dollars.
- The cost of wall per foot length = _qh_^2 dollars.
- The cost of pipes, valves and appurtenances = _P_ dollars.
-
- Then the total cost _C_ = (3_l_ + 4_b_)_qh_^2 + 2_plb_ + _P_.
-
- It is now necessary to express the three variables _b_, _l_, and
- _h_, in terms of one of them. From the relation _Q_ = 2_blh_ it is
- possible to rewrite the expression for the total cost as:
-
- _C_ = (3_Q_⁄(2_bh_) + 4_b_)_qh_^2 + (_pQ_)⁄_h_ + _P_.
-
- _C_ = (3_l_ + 2_Q_⁄(_lh_))_qh_^2 + (_pQ_)⁄_h_ + _P_.
-
- Holding _h_ constant and differentiating with regard to _b_ in the
- first expression and with regard to _l_ in the second expression,
- equating to zero and solving we get:
-
- _b_ = √((3_Q_)⁄(8_h_)) and _l_ = √((2_Q_)⁄(3_h_)).
-
- The economical relation between _b_ and _l_ is therefore
-
- _b_ = 0.75_l_
-
- regardless of the value of _h_.
-
- Substituting these values of _l_ and _b_ in the original
- expression for the total cost, it becomes
-
- _C_ = (3√((2_Q_)⁄(3_h_)) + 4√((3_Q_)⁄(8_h_)))_qh_^2 + (_pQ_)⁄_h_ +
- _P_.
-
- Differentiating with regard to _h_, equating to zero, and solving
-
- _h_ = 0.45((_pQ_^½)⁄_q_)^⅔.
-
- In the example given if _q_ = 0.2 and _p_ = 1.0 then
-
- _h_ = 11.6 feet, _b_ = 120 feet and _l_ = 160 feet.
-
-Since these are reasonable dimensions and in accord with good practice
-they should be used, unless other conditions are unsuitable or the
-velocity of flow is too great. A width of channel of 120 feet as
-compared to a length of 160 feet is conducive to a poor distribution of
-velocity across the basin. A ratio of width to length of about 1:4 is
-desirable. In this case, by the use of three baffles parallel to the
-length of the basin, thus dividing it into channels 40 feet wide and
-11.6 feet deep, the ratio of width to length is changed to 1:4 and the
-velocity will be increased only to 0.06 foot per second or 3.6 feet per
-minute, which is a reasonable velocity. It could be reduced by
-increasing the spacing of the baffles or the depth of the chamber.
-
-Complicated baffling is undesirable. Two or three overflow baffles may
-be used to permit quiescent sedimentation in the space thus formed, and
-hanging baffles may be placed before the inlet and outlet to break up
-surface currents, or to prevent the movement of scum. The hanging
-baffles should not extend more than 12 to 18 inches below the water
-surface. The inlet and outlet are sometimes arranged to permit the
-reversal of flow, and the connecting channels between basins to allow
-the operation of any number of basins in series or in parallel, although
-such arrangements are more important in water purification. Sewage
-should enter and leave at the top of the basin.
-
-[Illustration:
-
- FIG. 158.—Section through a Dortmund Tank.
-
- Depth 20 to 30 feet.
-]
-
-Cleaning is facilitated by the location of a central gutter in the
-bottom of the basin with the slope of the bottom of the basin towards
-the gutter from 1:25 to 1:80 or steeper. A pipe, 2 inches or larger in
-diameter, containing water under pressure with connections for hose
-placed at frequent intervals is a useful adjunct in flushing the sludge
-from the sedimentation basins. For equal capacity, deep vertical flow
-tanks are more expensive and difficult to construct than the shallower
-rectangular type. Deep tanks are advantageous, however, in that sludge
-can sometimes be removed by gravity or by pumping without stopping the
-operation of the tank. They will also operate successfully with shorter
-periods of detention and higher velocities. The upward velocity should
-not be greater than the velocity of sedimentation of the smallest
-particle to be removed. The efficiency of sedimentation in them will be
-increased by the sedimentation of the larger particles which drag some
-of the smaller particles down with them. The Dortmund tank shown in Fig.
-158 is an example of this type.
-
-Ordinarily it is not necessary to roof sedimentation basins as the odors
-created are not strong, and difficulties with ice are seldom serious.
-
-
- CHEMICAL PRECIPITATION
-
-
-=241. The Process.=—Chemical precipitation consists in adding to the
-sewage such chemicals as will, by reaction with each other and the
-constituents of the sewage, produce a flocculent precipitate and thus
-hasten sedimentation. The advantages of this process over plain
-sedimentation are a more rapid and thorough removal of suspended matter.
-Its disadvantages include the accumulation of a large amount of sludge,
-the necessity for skilled attendance, and the expense of chemicals. The
-process is not in extensive use as the conditions under which the
-advantages outweigh the disadvantages are unusual. Sewage containing
-large quantities of substances which will react with a small amount of
-an added chemical to produce the required precipitate are the most
-favorable for this method of treatment.
-
-Chemical precipitation accomplishes the same result as plain
-sedimentation, although the effluent from the chemically precipitated
-sewage may be of better quality than that from a plain sedimentation
-basin.
-
-
-=242. Chemicals.=—Lime is practically the only chemical used for the
-precipitation of the solid matter in sewage. Commercial lime used for
-precipitation consists of calcium oxide (CaO), with large quantities of
-impurities. It should be stored in a dry place and protected from undue
-exposure to the air to prevent the formation of calcium carbonate
-(CaCO_{3}), the formation of which is commonly known as air slacking.
-The active work in the formation of the precipitate is performed by the
-lime (CaO) or calcium hydroxide (Ca(OH)_{2}). The lime should therefore
-be purchased on the basis of available CaO, which may be as low as 10 to
-15 per cent in some commercial products. The amount of lime necessary
-depends on the quality of the sewage, the period of retention in the
-sedimentation basin, the method of application, the required results,
-and other less easily measured factors. Full scale tests for the amount
-of lime needed to produce certain results are the most satisfactory. In
-practice the amount of lime necessary when lime alone is used as a
-precipitant has been found to be about 15 grains per gallon. This may be
-markedly different, dependent on the quality of the sewage. For acid
-sewages, lime alone is not suitable as a precipitant since it is
-necessary to add sufficient lime to neutralize the sewage before the
-calcium carbonate will be precipitated.
-
-The use of copperas (FeSO_{4}) together with lime, leads to economy in
-the use of chemicals as the flocculent precipitate of ferrous hydroxide
-(Fe(OH)_{2}) is more voluminous than the precipitate of calcium
-carbonate. This is commonly known as the lime and iron process. The
-presence of iron in certain trade wastes may reduce the cost of chemical
-precipitation, as the necessary amount of copperas is reduced. Where 15
-grains of lime alone will be needed per gallon of sewage, the total
-amount of chemicals used will be reduced to 8 to 10 grains per gallon
-with the use of lime and iron. This combination is less expensive than
-the use of lime alone, and is even cheaper where the iron is already
-present in the sewage. Such a condition is well illustrated by the
-sewage at Worcester, Mass., where the oldest and best known chemical
-precipitation plant in the United States is located. The amount of lime
-used at this plant has varied between 6 and 10 grains per gallon of
-sewage, the normal amount being about 7 grains. No iron is added because
-of the amount already in solution.
-
-The results of a series of experiments on the chemical precipitation of
-sewage by Allen Hazen, are given in the 1890 Report of the Massachusetts
-State Board of Health, on p. 737 of the volume on the Purification of
-Water and Sewage. Hazen concludes as the result of his experiments:
-concerning lime,
-
- There is a certain definite amount of lime ... which gives as good
- or better results than either more or less. This amount is that
- which exactly suffices to form normal carbonates with all the
- carbonic acid of the sewage. This amount can be determined in a
- few minutes by simple titration.
-
-Concerning lime and iron (copperas) he states:
-
- Ordinary house sewage is not sufficiently alkaline to precipitate
- copperas, and a small amount of lime must be added to obtain good
- results. The quantity of lime required depends both upon the
- composition of the sewage and the amount of copperas used, and can
- be calculated from titration of the sewage. Very imperfect results
- are obtained from too little lime, and, when too much is used, the
- excess is wasted, the result being the same as with a smaller
- quantity.
-
- In precipitation by ferric sulphate and crude alum, the addition
- of lime was found unnecessary, as ordinary sewage contains enough
- alkali to decompose these salts. Within reasonable limits the more
- of these precipitants used the better is the result, but with very
- large quantities the improvement does not compare with the
- increased cost.
-
- Using equal values of different precipitants, applied under the
- most favorable conditions for each, upon the same sewage, the best
- results were obtained from ferric sulphate. Nearly as good results
- were obtained from copperas and lime used together, while lime and
- alum each gave somewhat inferior effluents.... When lime is used
- there is always so much lime left in solution that it is doubtful
- if its use would ever be found satisfactory except in case of an
- acid sewage.
-
- It is quite impossible to obtain effluents by chemical
- precipitation which will compare in organic purity with those
- obtained by intermittent filtration through sand.
-
- It is possible to remove from one-half to two-thirds of the
- organic matter by precipitation ... and it seems probable that ...
- a result may be obtained which will effectually prevent a public
- nuisance.
-
-
-=243. Preparation and Addition of Chemicals.=—Lime is not readily
-soluble in water. Therefore, it is not best to add the lime as a powder
-to the sewage, but to form a milk of lime, that is, a supersaturated
-solution containing from 2,000 to 4,000 grains per gallon, although dry
-slaked lime has sometimes been applied directly. The solution is
-prepared in tanks in a quantity sufficient for some part of the day’s
-run, commonly sufficient to last through one shift of 8 or 10 hours. The
-lime is prepared by placing the amount necessary to fill one storage
-tank into a slaking tank containing some cold water. Sufficient water is
-added to keep the solution just at the boiling point, or steam may be
-added to make it boil. After slaking, it is run into the milk-of-lime
-solution tank and sufficient water added to bring to the proper
-strength. The milk of lime is added in measured quantities, being
-controlled by a variable head on a fixed orifice or weir, so that it may
-be varied with the amount of sewage flowing through the plant. The
-amount of lime to be added is determined by titration with
-phenolphthalein, experience indicating the color to be obtained when the
-proper amount of lime has been added.
-
-The use of either copperas or alum has been so rare, for the
-precipitation of sewage, that a description of the methods of handling
-these chemicals as a sewage precipitant is not warranted. An excellent
-description of the methods of handling these chemicals in water
-purification will be found in “Water Purification” by Ellms.
-
- TABLE 81
-
- RESULTS OF CHEMICAL PRECIPITATION AT WORCESTER, MASSACHUSETTS[146]
-
- ──────────────────────────────────────┬──────────┬──────────┬──────────
- │ 1900 │ 1910 │ 1920
- ──────────────────────────────────────┼──────────┼──────────┼──────────
- Amount of sewage treated, million │ 4,781 │ 5,317 │ 8,893
- gallons │ │ │
- Amount of sewage chemically treated, │ 3,650 │ 3,574 │ 7,300
- million gallons │ │ │
- Gallons of wet sludge per million │ 4,450 │ 4,185 │
- gallons of sewage treated │ │ │
- Per cent of solids in sludge │ 4.42 │ 8.20 │4.64[147]
- Tons of solids │ 7,294 │ 4,182 │6,431[147]
- Pounds of lime added per million │ 999[148] │ 762[147] │ 534
- gallons of sewage pumped │ │ │
- Per cent of organic matter removed: │ │ │
- By albuminoid ammonia: │ │ │
- Total │52.7[149] │ 58.4 │ 51.9
- Suspended │90.0[149] │ 88.7 │ 83.6
- By oxygen consumed: │ │ │
- Total │62.8[149] │ 61.1 │ 62.5
- Suspended │86.6[149] │ 89.7 │ 86.2
- ──────────────────────────────────────┴──────────┴──────────┴──────────
-
-
-=244. Results.=—The results of Hazen’s experiments indicate that a
-greater amount of suspended matter can be removed in the same time by
-chemical precipitation than by plain sedimentation. The percentage of
-removal of suspended matter may be as high as 80 to 90 per cent with a
-period of retention of 6 to 8 hours and the addition of a proper amount
-of chemical. That the method is not always a success is shown by the
-results of some tests at Canton, Ohio.[150] The report states:
-
- ... lime treatment removes about 50 per cent of the suspended
- matter, and in the main about 50 per cent of the organic
- matter.... These data are instructive as indicating that the
- addition of lime to the Canton sewage in quantities as previously
- stated does not materially improve the character of the resulting
- effluent over and above that which could be produced by plain
- sedimentation alone.
-
-The plant at Worcester, Mass., is the largest in the United States and
-information from it is of value. A summary of the results at Worcester
-for 1900, 1910, and 1920 are shown in Table 81.
-
-
-
-
- CHAPTER XVI
- SEPTICIZATION
-
-
-=245. The Process.=—Septic action is a biological process caused by the
-activity of obligatory or facultative anaërobes as the result of which
-certain organic compounds are reduced from higher to lower conditions of
-oxidation, some of the solid organic substances are rendered soluble,
-and a quantity of gas is given off. Among these gases are: methane,
-hydrogen sulphide, and ammonia. The biologic process in the septic tank
-represents the downward portion of the cycle of life and death, in which
-complex organic compounds are reduced to a more simple condition
-available as food for low forms of plant life. The disposal of sewage by
-septic action, when introduced, promised the solution of all problems in
-sewage treatment. Septic action is now better understood, and it is
-known that some of the early claims were unfounded.
-
-The principal advantage of septic action in sewage treatment is the
-relatively small amount of sludge which must be cared for compared to
-that produced by a plain sedimentation tank. The sludge from a septic
-tank may be 25 to 30 per cent and in some cases 40 per cent less in
-weight, and 75 to 80 per cent less in volume than the sludge from a
-plain sedimentation tank. The most important results of septic action
-and the greatest septic activity occur in the deposited organic matter
-or sludge. The biologic changes due to septic action which occur in the
-liquid portion of the tank contents are of little or no importance. The
-installation of a septic tank, although it may fail to prevent the
-nuisance calling for abatement, has a remarkable psychological effect in
-stilling complaints. Among other advantages are the comparative
-inexpensiveness of the tanks and the small amount of attention and
-skilled attendance required. The tanks need cleaning once in 6 months to
-a year. If properly designed no other attention is necessary.
-
-The septic tank has fallen into some disrepute because of the better
-results obtainable by other methods, the occasional discharge of
-effluents worse than the influent, the occasional discharge of sludge in
-the effluent caused by too violent septic boiling, and on account of
-patent litigation. This last difficulty has been overcome as the Cameron
-patents expired in 1916. Occasionally the odors given off by the septic
-process are highly objectionable and are carried for a long distance.
-These odors can be controlled to a large extent by housing the tanks.
-Over-septicization must be guarded against as an over-septicized
-effluent is more difficult of further treatment or of disposal than a
-comparatively fresh, untreated sewage. An over-septicized or stale
-sewage is indicated by the presence of large quantities of ammonias,
-either free or albuminoid, frequently accompanied by hydrogen sulphide
-and other foul-smelling gases. The oxygen demand in an over-septicized
-sewage is greater than that in a fresh or more carefully treated sewage.
-
-
-=246. The Septic Tank.=—A septic tank is a horizontal, continuous-flow,
-one-story sedimentation tank through which sewage is allowed to flow
-slowly to permit suspended matter to settle to the bottom where it is
-retained until anaërobic decomposition is established, resulting in the
-changing of some of the suspended organic matter into liquid and gaseous
-substances, and a consequent reduction in the quantity of sludge to be
-disposed of.[151] It is to be noted that a continuous flow is essential
-to a septic tank. Small tanks containing stagnant household sewage are
-called cesspools, although sometimes erroneously spoken of as septic
-tanks.
-
-Septic and sedimentation tanks differ in their method of operation only
-in the period of storage and the frequency of cleaning. The period of
-flow in a septic tank is longer and it is cleaned less frequently. The
-results obtained by the two processes differ widely. A septic tank can
-be converted into a sedimentation tank, or vice versa, by changing the
-method of operation, no constructional features requiring alteration.
-The purpose of the tank is to store the sludge for such a period of time
-that partial liquefaction of the sludge may take place, and thus
-minimize the difficulty of sludge disposal. For this reason the sludge
-storage capacity of a septic tank is sometimes greater than would be
-necessary for a plain sedimentation tank.
-
- TABLE 82
-
- EFFICIENCIES AND PERFORMANCE OF SEPTIC TANK AT COLUMBUS, OHIO
-
- (Report of Sewage Purification, by G. A. Johnson, Nov. 10, 1905)
- ──────────────┬────┬─────┬────┬────┬────┬────┬────┬─────┬─────┬───┬────┬────
- Month, │Aug.│Sept.│Oct.│Nov.│Dec.│Jan.│Feb.│March│April│May│June│Avg.
- 1904–1905 │ │ │ │ │ │ │ │ │ │ │ │
- ──────────────┼────┼─────┼────┼────┼────┼────┼────┼─────┼─────┼───┼────┼────
- Temperature, │ │ │ │ │ │ │ │ │ │ │ │
- degrees F. │ │ │ │ │ │ │ │ │ │ │ │
- Influent │ 69 │ 70 │ 65 │ 60 │ 54 │ 51 │ 48 │ 50 │ 57 │61 │ 67 │
- Effluent │ 69 │ 68 │ 64 │ 59 │ 52 │ 48 │ 45 │ 49 │ 57 │62 │ 68 │
- Oxygen │ │ │ │ │ │ │ │ │ │ │ │
- consumed, │ │ │ │ │ │ │ │ │ │ │ │
- parts per │ │ │ │ │ │ │ │ │ │ │ │
- million: │ │ │ │ │ │ │ │ │ │ │ │
- Influent │ 49 │ 50 │ 52 │ 47 │ 43 │ 51 │ 44 │ 47 │ 53 │33 │ 40 │ 47
- Effluent │ 40 │ 36 │ 40 │ 39 │ 37 │ 35 │ 37 │ 39 │ 50 │34 │ 33 │ 38
- Per cent │ 18 │ 28 │ 23 │ 15 │ 16 │ 31 │ 16 │ 17 │ 6 │–3 │ 18 │ 19
- removal │ │ │ │ │ │ │ │ │ │ │ │
- Organic │ │ │ │ │ │ │ │ │ │ │ │
- nitrogen, │ │ │ │ │ │ │ │ │ │ │ │
- parts per │ │ │ │ │ │ │ │ │ │ │ │
- million: │ │ │ │ │ │ │ │ │ │ │ │
- Influent │6.5 │ 8.2 │9.3 │8.4 │8.8 │8.5 │6.7 │ 6.4 │ 7.9 │6.1│6.7 │7.8
- Effluent │7.3 │ 5.5 │6.0 │7.4 │8.2 │7.0 │5.4 │ 5.5 │ 5.2 │ │ │
- Per cent │–12 │ 32 │ 35 │ 12 │ 7 │ 18 │ 19 │ 14 │ 25 │30 │ 19 │ 19
- removal │ │ │ │ │ │ │ │ │ │ │ │
- Free ammonia, │ │ │ │ │ │ │ │ │ │ │ │
- parts per │ │ │ │ │ │ │ │ │ │ │ │
- million: │ │ │ │ │ │ │ │ │ │ │ │
- Influent │9.7 │12.2 │12.4│16.3│14.7│10.8│8.3 │ 9.9 │12.3 │6.9│8.3 │11.7
- Effluent │10.5│11.5 │12.4│17.2│14.3│11.1│8.9 │10.7 │14.9 │9.0│8.7 │12.1
- Per cent │ –8 │ 6 │ 0 │ –6 │ 3 │ –3 │ –7 │ –8 │ –21 │–23│ –5 │ –3
- removal │ │ │ │ │ │ │ │ │ │ │ │
- │ │ │ │ │ │ │ │ │ │ │ │
- Residue on │ │ │ │ │ │ │ │ │ │ │ │
- Evaporation,│ │ │ │ │ │ │ │ │ │ │ │
- parts per │ │ │ │ │ │ │ │ │ │ │ │
- million: │ │ │ │ │ │ │ │ │ │ │ │
- Total: │ │ │ │ │ │ │ │ │ │ │ │
- Influent │990 │ 952 │993 │961 │989 │949 │890 │ 850 │1067 │912│945 │946
- Effluent │935 │ 891 │893 │916 │925 │886 │843 │ 782 │ 895 │800│835 │873
- Per cent │ 6 │ 6 │ 10 │ 5 │ 6 │ 6 │ 5 │ 8 │ 16 │12 │ 12 │ 8
- removal │ │ │ │ │ │ │ │ │ │ │ │
- Volatile: │ │ │ │ │ │ │ │ │ │ │ │
- Influent │231 │ 184 │162 │175 │156 │167 │156 │ 168 │ 212 │122│162 │166
- Effluent │206 │ 160 │129 │148 │137 │137 │134 │ 137 │ 147 │103│144 │139
- Per cent │ 11 │ 13 │ 20 │ 15 │ 12 │ 18 │ 14 │ 18 │ 31 │16 │ 11 │ 16
- removal │ │ │ │ │ │ │ │ │ │ │ │
- Mineral: │ │ │ │ │ │ │ │ │ │ │ │
- Influent │759 │ 768 │831 │786 │833 │782 │734 │ 682 │ 855 │700│783 │780
- Effluent │729 │ 731 │764 │768 │788 │749 │709 │ 645 │ 748 │697│691 │734
- Per cent │ 4 │ 5 │ 8 │ 2 │ 5 │ 4 │ 3 │ 5 │ 11 │ 1 │ 12 │ 6
- removal │ │ │ │ │ │ │ │ │ │ │ │
- Cubic yards │ │ │0.10│1.24│1.09│1.17│0.65│0.63 │0.57 │ │1.34│
- wet sludge │ │ │ │ │ │ │ │ │ │ │ │
- per million │ │ │ │ │ │ │ │ │ │ │ │
- gallons: │ │ │ │ │ │ │ │ │ │ │ │
- Per cent │ │ │ │ │ │ │ │ │ │ │ │
- removal of │ │ │ │ │ │ │ │ │ │ │ │
- suspended │ │ │ │ │ │ │ │ │ │ │ │
- matter: │ │ │ │ │ │ │ │ │ │ │ │
- Total │ 59 │ 54 │ 56 │ 51 │ 42 │ 48 │ 32 │ 47 │ 56 │67 │ 53 │ 50
- Volatile │ 60 │ 41 │ 48 │ 52 │ 44 │ 55 │ 47 │ 47 │ 62 │80 │ 15 │ 48
- Fixed │ 75 │ 65 │ 60 │ 51 │ 40 │ 38 │ 19 │ 48 │ 53 │64 │ 67 │ 51
- Gas evolved, │ │ │ │ │ │ │ │ 29 │ 14 │41 │ 50 │
- cubic feet │ │ │ │ │ │ │ │ │ │ │ │
- per day: │ │ │ │ │ │ │ │ │ │ │ │
- ──────────────┴────┴─────┴────┴────┴────┴────┴────┴─────┴─────┴───┴────┴────
-
-
-=247. Results of Septic Action.=—The results obtained from the septic
-tanks at the Columbus Sewage Experiment Station are given in Table 82.
-The effluent is higher than the influent in free ammonia, but the
-reduction of other constituents, particularly suspended matter, is
-marked.
-
-Septic action is sensitive to temperature changes, and to certain
-constituents of the incoming sewage. Cold weather or an acid influent
-will inhibit septicization. In winter the liquefaction of sludge may
-practically cease, whereas in summer liquefaction may exceed deposition.
-The amount of gas generated is a measure of the relative amount of
-septic action. The rapid generation of gas in warm weather disturbs the
-settled sludge and may cause a deterioration of the quality of the
-effluent because of the presence of decomposed sludge. The results in
-Table 82 show the effect of cold weather on the process. In warm weather
-the violent ebullition of gas sometimes causes the discharge of sludge
-in the effluent, resulting in a liquid more difficult of disposal than
-the incoming sewage. Since septic action is dependent on the presence of
-certain forms of bacteria, where these are absent there will be no
-septic action. Sewage generally contains the forms of bacteria necessary
-for this action but it has occasionally been found necessary to seed new
-tanks in order to start septic action.
-
-The sludge from septic tanks is usually black, with a slight odor,
-though in some cases this odor may be highly offensive. The sludge will
-flow sluggishly. It can be pumped by centrifugal pumps and it will flow
-through pipes and channels. It has a moisture content of about 90 per
-cent and a specific gravity of about 1.03. It is dried with difficulty
-on open-air drying beds, and it is worthless as a fertilizer. The
-composition of some septic sludges are shown in Table 83.
-
-
-=248. Design of Septic Tanks.=—The sedimentation chambers of a septic
-tank are designed on the same principles as the sedimentation basins
-described in Art. 240. The velocity of flow should not exceed one foot
-per minute. The channels should be straight and free from obstructions
-causing back eddies. The ratio of length to width of channel should be
-between 2 : 1 to 4 : 1 with a width not exceeding 50 feet, and desirably
-narrower. The depths used vary between 5 and 10 feet, exclusive of the
-sludge storage capacity. Hanging baffles should be placed, one before
-the inlet and the other in front of the outlet, so as to distribute the
-incoming sewage over the tank, and to prevent scum from passing into the
-outlet. The baffles should hang about 12 inches below the surface of the
-sewage. Intermediate baffles are sometimes desirable to prevent the
-movement of sludge or scum towards the outlet. The placing of baffles
-must be considered carefully as injudicious baffling may lessen the
-effectiveness of a tank by so concentrating the currents as to prevent
-sedimentation or the accumulation of sludge. Baffles should be built of
-concrete or brick, as wood or metal in contact with septic sewage
-deteriorates rapidly. In designing the sludge storage chambers it may be
-assumed that one-half of the organic matter and none of the mineral
-matter will be liquefied or gasified. The net storage volume allowed is
-about 2 to 3 cubic yards per million gallons of sewage treated.
-Variations between 0.1 and 10.0 cubic yards have been recorded, however.
-If grit is carried in the sewage to be treated, it should be removed by
-the installation of a grit chamber before the sewage enters the septic
-tank.
-
- TABLE 83
-
- ANALYSIS OF TANK SLUDGES
-
- ──────────┬────────┬────────┬────────────────────────────
- Place │Specific│Per Cent│ Per Cent in Terms of Dry
- │Gravity │Moisture│ Matter
- │ │ │
- │ │ │
- │ │ │
- ──────────┼────────┼────────┼────────┬─────┬────────┬────
- │ │ │Volatile│Fixed│Nitrogen│Fat
- ──────────┼────────┼────────┼────────┼─────┼────────┼────
- Mansfield,│ 1.11│ 80.8│ │ │ │
- O. │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- Chicago, │ 1.03│ 90│ 40│ 60│ 1.9│ 7.0
- Ill. │ │ │ │ │ │
- │ │ │ │ │ │
- Columbus, │ 1.09│ 83.3│ 4.4│ 16.7│ 0.25│0.94
- O. │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- Atlanta, │ 1.02│ 87.1│ 39.1│ 60.9│ 1.25│6.11
- Ga. │ │ │ │ │ │
- │ │ │ │ │ │
- Baltimore,│ 1.02│ 91.9│ 66.2│ │ 2.45│4.02
- Md. │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- │ │ │ │ │ │
- Baltimore,│ 1.02│ 92.4│ 62.7│ │ 2.75│
- Md. │ │ │ │ │ │
- Baltimore,│ │ 79.2│ 73.8│ │ 2.64│9.00
- Md. │ │ │ │ │ │
- Baltimore,│ │ 92.4│ 58.0│ 3.19│ │
- Md. │ │ │ │ │ │
- ──────────┴────────┴────────┴────────┴─────┴────────┴────
-
- ──────────┬────────┬────────┬─────────┬────────────
- Place │ Cubic │ Pounds │ Kind of │ Reference
- │Yard per│ per │ Sludge │
- │Million │Million │ │
- │Gallons,│Gallons,│ │
- │ Wet │ Dry │ │
- ──────────┼────────┼────────┼─────────┼────────────
- │ │ │ │
- ──────────┼────────┼────────┼─────────┼────────────
- Mansfield,│ │ │Septic │1908 Report,
- O. │ │ │ │ State
- │ │ │ │ Board of
- │ │ │ │ Health
- Chicago, │ 1.0│ 200│Septic │
- Ill. │ │ │ │
- │ 1.5│ 300│ │
- Columbus, │ │ │Septic │G. A.
- O. │ │ │ │ Johnson
- │ │ │ │ 1905
- │ │ │ │ Report
- Atlanta, │ │ │Imhoff │Eng. Rec.,
- Ga. │ │ │ │ V. 72,
- │ │ │ │ 1915, p. 4
- Baltimore,│ │ │Digestion│Eng.
- Md. │ │ │ Tank │ News-Rec.,
- │ │ │ │ V. 87,
- │ │ │ │ 1921, p.
- │ │ │ │ 98
- Baltimore,│ │ │Imhoff │ do.
- Md. │ │ │ │
- Baltimore,│ │ │Raw │ do.
- Md. │ │ │ Sludge │
- Baltimore,│ │ │Settling │ do.
- Md. │ │ │ Basin │
- ──────────┴────────┴────────┴─────────┴────────────
-
-Two or more tanks should be constructed to allow for the shut down of
-one for cleaning and to increase the elasticity of the plant. The number
-of tanks to be used is dependent on the total quantity of sewage and the
-fluctuations in rate of flow. An average period of retention of about 9
-to 10 hours with a minimum period of 6 hours during maximum flow is a
-fair average to be assumed for design. The period of retention should
-not exceed about 24 hours, as the sewage may become over-septicized. The
-sludge storage period should be from 6 to 12 months.
-
-A cover is not necessary to the successful operation of a septic tank.
-Covers are sometimes used with success, however, in reducing the
-dissemination of odors from the tank. They are also useful in retaining
-the heat of the sewage in cold weather and thus aid in promoting
-bacterial activity. Types of covers vary from a building erected over
-the tank to a flat slab set close to the surface of the sewage. In the
-design of a cover, good ventilation should be provided to permit the
-escape of the gases, and easy access should be provided for cleaning.
-Tightly covered tanks or tanks with too little ventilation have resulted
-in serious explosions, as at Saratoga Springs in 1906 and at
-Florenceville, N. C., in 1915.[152]
-
-The sludge may be removed through drains in the bottom of the tank as
-described for sedimentation basins, or where such drains are not
-feasible the sludge and sewage are pumped out. For this purpose a pump
-may be installed permanently at the tank, or for small tanks portable
-pumps are sometimes used. Septic tanks should be cleaned as infrequently
-as possible without permitting the overflow of sludge into the effluent.
-The less frequent the cleaning the less the amount of sludge removed
-since digestion is continuous throughout the sludge. It is necessary to
-clean when the tank becomes so filled with sludge, that the period of
-retention is materially reduced, or sludge is being carried over into
-the effluent.
-
-The details of the septic tank at Champaign, Illinois, are shown in Fig.
-159. This tank was designed by Prof. A. N. Talbot, and was put in
-service on Nov. 1, 1897. It was among the first of such tanks to be
-installed in the United States. The tank shown in Fig. 159 is an example
-of present day practice in single-story septic tank design.
-
-[Illustration:
-
- FIG. 159.—Septic Tank at Champaign, Illinois.
-]
-
-[Illustration:
-
- FIG. 160.—Design for a Residential Septic Tank for a Family of Ten.
- Illinois State Board of Health.
-]
-
-Small septic tanks for rural homes of 5 to 15 persons, or on a slightly
-larger scale for country schools and small institutions, are little more
-than glorified cesspools. Nevertheless much attention has been given to
-the construction of such tanks by the National Government and by state
-boards of health.[153] The recommendations of some of these boards have
-been compiled in Table 84. A typical method for the construction of such
-tanks, as recommended by the Illinois State Board of Health, is shown in
-Fig. 160. A subsurface filter, into which the effluent is discharged, is
-an important adjunct where no adequate stream is available to receive
-the discharge from the tank.
-
- TABLE 84
-
- CAPACITIES OF SEPTIC TANKS FOR SMALL INSTALLATIONS
-
- ──────────────┬─────────────┬─────────┬─────────┬──────────────────────
- Rule │ Number, │Capacity,│Period of│ Remarks
- Recommended by│ Persons │ Gallons │Retention│
- State Board of│ │ per │ │
- Health │ │ Person │ │
- ──────────────┼─────────────┼─────────┼─────────┼──────────────────────
- Wisconsin │ │ 30 │24 hours │
- Ohio │ 4 to 10 │ 50 │ │Not less than 560
- │ │ │ │ gallons
- Kentucky │ │ │24 to 48 │Not more than 5 feet
- │ │ │ hours │ deep
- Texas │ │ │24 hours │
- Illinois │ │ 45 │24 hours │
- U.S. Dept. │ │ 40 │24 hours │25 per cent additional
- Agriculture.│ │ │ │
- │ │ │ │capacity for sludge
- North Carolina│Large Schools│ 15 │ │Not less than 500
- │ │ │ │ gallons
- North Carolina│ 20 pupils │ 25 │ │
- North Carolina│Medium School│ 20 │ │
- North Carolina│ Homes │25 to 30 │ │
- ──────────────┴─────────────┴─────────┴─────────┴──────────────────────
-
-
-=249. Imhoff Tanks.=—In the discussion of septic tanks it has been
-brought out that one of the objections to their use is the unloading of
-sludge into the effluent which occasionally causes a greater amount of
-suspended matter in the effluent than in the influent. The Imhoff tank
-is a form of septic tank so arranged that this difficulty is overcome.
-It combines the advantages of the septic and sedimentation tanks and
-overcomes some of their disadvantages. An Imhoff tank is a device for
-the treatment of sewage, consisting of a tank divided into 3
-compartments. The upper compartment is called the sedimentation chamber.
-In it the sedimentation of suspended solids causes them to drop through
-a slot in the bottom of the chamber to the lower compartment called the
-_digestion_ chamber. In this chamber the solid matter is humified by an
-action similar to that in a plain septic tank. The generated gases
-escape from the digestion chamber to the surface through the third
-compartment called the _transition_ or _scum_ chamber. Sections of
-Imhoff tanks are shown in Fig. 161. It is essential to the construction
-of an Imhoff tank that the slot in the bottom of the sedimentation
-chamber does not permit the return of gases through the sedimentation
-chamber, and that there be no flow in the digestion chamber.
-
-[Illustration:
-
- FIG. 161.—Typical Sections through Imhoff Tanks.
-
- Eng. News, Vol. 75, p. 15.
-]
-
-The Imhoff tank was invented by Dr. Karl Imhoff, director of the Emscher
-Sewerage District in Germany. Its design is patented in the United
-States, the control of the patent being in the hands of the Pacific
-Flush Tank Co. of Chicago, which collects the royalties which are
-payable when construction work begins. The fee for a tank serving 100
-persons is $10, for 1,000 persons is $80 and for 100,000 persons is
-$2550. The rate of the royalty reduces in proportion as the number of
-persons served increases.[154] As designed by Imhoff and used in Germany
-the tanks were of the radial flow type and quite deep. The depth, as
-explained by Imhoff, is one of the chief requirements for the successful
-operation of the tank. As adapted to American practice the tanks are
-generally of the longitudinal flow type and are not made so deep. An
-isometric view of a radial flow Imhoff tank is shown in Fig. 162. The
-sewage enters at the center of the tank near the surface and flows
-radially outward under the scum ring and over a weir placed near the
-circumference of the tank. One type of longitudinal flow tank is shown
-in isometric view in Fig. 163.
-
-[Illustration:
-
- FIG. 162.—Sketch of Radial Flow Imhoff Tank at Baltimore, Maryland.
-
- Eng. Record, Vol. 70, p. 5.
-]
-
-[Illustration:
-
- FIG. 163.—Isometric View of Longitudinal Flow Imhoff Tank at Cleburne,
- Texas.
-
- Eng. News, Vol. 76, p. 1029.
-]
-
-
-=250. Design of Imhoff Tanks.=—The velocity of flow, period of
-retention, and the quantity of sewage to be treated determine the
-dimensions of the _sedimentation chamber_ as in other forms of tanks.
-The velocity of flow should not exceed one foot per minute, with a
-period of retention of 2 to 3 hours. A greater velocity than one foot
-per minute results in less efficient sedimentation. A longer period of
-retention than the approximate limit set may result in a septic or stale
-effluent, and a shorter period may result in loss of efficiency of
-sedimentation. The bottom of the sedimentation chamber should slope not
-less than 1½ vertical to 1 horizontal, in order that deposited material
-will descend into the sludge digestion chamber. Provision should be made
-for cleaning these sloping surfaces by placing a walk on the top of the
-tank from which a squeegee can be handled to push down accumulated
-deposits. It is desirable to make the material of the sides and bottom
-of the sedimentation chamber as smooth as possible to assist in
-preventing the retention of sludge in the sedimentation chamber. Wood,
-glass, and concrete have been used. The latter is the more common and
-has been found to be satisfactory. The length of the sedimentation
-chamber is fixed by the velocity of flow and the period of retention.
-Tanks are seldom built over 100 feet in length, however, because of the
-resulting unevenness in the accumulation of sludge. Where longer flows
-are desired two or more tanks may be operated in series. The width of
-the chamber is fixed by considerations of economy and convenience. It
-should not be made so great as to permit cross currents. In general a
-narrow chamber is desirable. Satisfactory chambers have been constructed
-at depths between 5 and 15 feet. The depth of the sedimentation chamber
-and the depth of the digestion chamber each equal about one-half of the
-total depth of the tank. This should be made as deep as possible up to a
-limit of 30 to 35 feet, with due consideration of the difficulties of
-excavation. C. F. Mebus states:[155]
-
- In 9 of the largest representative United States installations,
- the depth from the flow line to the slot varies from 10 feet 10
- inches to 13 feet 6 inches.
-
-Imhoff states, concerning the depth of tanks:
-
- Deep tanks are to be preferred to shallow tanks because in them
- the decomposition of the sludge is improved. This is so because in
- the deeper tanks the temperature is maintained more uniformly and
- because the stirring action of the rising gas bubbles is more
- intense.
-
-The stirring action of the gas bubbles is desirable as it brings the
-fresh sludge more quickly under the influence of the active bacterial
-agents. The greater pressure on the sludge in deep tanks also reduces
-its moisture content.
-
-Two or more sedimentation chambers are sometimes used over one sludge
-digestion chamber in order to avoid the depths called for by the sloping
-sides of a single sedimentation chamber. An objection to multiple-flow
-chambers is the possibility of interchange of liquid from one chamber to
-another through the common digestion chamber.
-
-The inlet and outlet devices should be so constructed that the direction
-of flow in the tank can be reversed in order that the accumulated sludge
-may be more evenly distributed in the hoppers of the digestion chamber.
-The sewage should leave the sedimentation chamber over a broad crested
-weir in order to minimize fluctuations in the level of sewage in the
-tank. The gases in the digesting sludge are sensitive to slight changes
-in pressure. A lowering of the level of sewage will release compressed
-gas and will too violently disturb the sludge in the digestion chamber.
-Hanging baffles, submerged 12 to 16 inches and projecting 12 inches
-above the surface of the sewage, should be placed in front of the inlet
-and outlet, and in long tanks intermediate baffles should be placed to
-prevent the movement of scum or its escape into the effluent. An Imhoff
-tank which is operating properly should not have any scum on the surface
-of the sewage in the sedimentation chamber.
-
-The _slot_ or opening at the bottom of the sedimentation chamber should
-not be less than 6 inches wide between the lips. Wider slots are
-preferable, but too wide a slot will involve too much loss of volume in
-the digestion chamber. One lip of the slot should project at least 3
-inches horizontally under the other so as to prevent the return of gases
-through the sedimentation chamber. A triangular beam may be used as
-shown in Fig. 161 A. This method of construction is advantageous in
-increasing the available capacity for sludge storage.
-
-The _digestion chamber_ should be designed to store sludge from 6 to 12
-months, the longer storage periods being used for smaller installations.
-In warm climates a shorter period may be used with success. The amount
-of sludge that will be accumulated is as uncertain as in other forms of
-sewage treatment. A widely quoted empirical formula, presented in
-“Sewage Sludge” by Allen, states:
-
- _C_ = 10.5 _PD_ for combined sewage;
- _C_ = 5.25 _PD_ for separate sewage,
-
- in which _C_ = the effective capacity of the digestion chamber in
- cubic feet;
-
- _P_ = the population served, expressed in thousands;
-
- _D_ = the number of days of storage of sludge.
-
-The effective capacity of the chamber is measured as the entire volume
-of the chamber approximately 18 inches below the lower lip of the slot.
-The capacity as computed from the above formula is assumed as
-satisfactory for a deep tank. Frank and Fries[156] recommend the
-increase of the capacity for shallow tanks to compensate for the
-decreased hydrostatic pressure. In any event the formula can be no more
-than a guide to design. No formula can be of equal value to data
-accumulated from tests on the sewage to be treated. The Illinois State
-Board of Health requires 3 cubic yards of sludge digestion space per
-million gallons of sewage treated. Frank and Fries recommend an
-allowance of 0.007 cubic foot of storage per inhabitant per day for
-combined sewage and one-half that amount for separate sewage. If this is
-based on 80 per cent moisture content, the volume for other percentages
-of moisture can be easily computed. An average figure used in the
-Emscher District is one cubic foot capacity for each inhabitant for the
-combined system, and three-fourths of this for the separate system.
-Metcalf and Eddy[157] recommend the following method for the
-determination of the sludge storage capacity: (1) From analyses of the
-sewage or study of the sources ascertain the amount of suspended matter.
-(2) Assume, or determine by test, the amount which will settle in the
-period of detention selected, say 60 per cent in 3 hours. (3) Estimate
-the amount which will be digested in the sludge chamber at about 25 per
-cent, leaving 75 per cent to be stored. (4) Estimate the percentage
-moisture in the sludge conservatively, say 85 per cent. The total volume
-of sludge can then be computed. This method is more rational than the
-use of empirical formulas, but because of the estimates which must be
-made its results will probably be of no greater accuracy than those
-obtained empirically.
-
-The digestion chamber is made in the form of an inverted cone or pyramid
-with side slopes at most about 2 horizontal to 1 vertical and preferably
-much steeper without necessitating too great a depth of tank. The
-purpose of the steep slope is to concentrate the sludge at the bottom of
-the hopper thus formed. Concrete is ordinarily used as the material of
-construction as a smooth surface can be obtained by proper workmanship.
-Where flat slopes have been used, a water pipe perforated at intervals
-of 6 to 12 inches may be placed at the top of the slopes, and water
-admitted for a short time to move the sludge when the tank is being
-cleaned.
-
-A cast-iron pipe, 6 to 8 inches in diameter, is supported in an
-approximately vertical position with its open lower end supported about
-12 inches above the lowest point in the digestion chamber. This is used
-for the removal of sludge. A straight pipe from the bottom of the tank
-to a free opening in the atmosphere is desirable in order to allow the
-cleaning of the pipe or the loosening of sludge at the start, and to
-prevent the accumulation of gas pockets. The sludge is led off through
-an approximately horizontal branch so located that from 4 to 6 feet of
-head are available for the discharge of the sludge. A valve is placed on
-the horizontal section of the pipe. A sludge pipe is shown in Fig. 162
-and 163. Under such conditions, when the sludge valve is opened the
-sludge should flow freely. The hydraulic slope to insure proper sludge
-flow should not be less than 12 to 16 per cent. Where it is not possible
-to remove the sludge by gravity an air lift is the best method of
-raising it.
-
-The volume of the _transition_ or _scum_ chamber should equal about
-one-half that of the digestion chamber. The surface area of the scum
-chamber exposed to the atmosphere should be 25 to 30 per cent of the
-horizontal projection of the top of the digestion chamber. Some tanks
-have operated successfully with only 10 per cent, but troubles from
-foaming can usually be anticipated unless ample area for the escape of
-gases has been provided.
-
-All portions of the surface of the tank should be made accessible in
-order that scum and floating objects can be broken up or removed. The
-gas vents should be made large enough so that access can be gained to
-the sludge chamber through them when the tank is empty.
-
-Precautions should be taken against the wrecking of the tank by high
-ground water when the tank is emptied. With an empty tank and high
-ground water there is a tendency for the tank to float. The flotation of
-the tank may be prevented by building the tank of massive concrete with
-a heavy concrete roof, by underdraining the foundation, or by the
-installation of valves which will open inwards when the ground water is
-higher than the sewage in the tank. Dependence should not be placed on
-the attendant to keep the tank full during periods of high ground water.
-
-Roofs are not essential to the successful operation of Imhoff tanks.
-They are sometimes used, however, as for septic tanks, to assist in
-controlling the dissemination of odors, to minimize the tendency of the
-sewage to freeze, and to aid in bacterial activity. In the construction
-of a roof, ventilation must be provided as well as ready access to the
-tank for inspection, cleaning, and repairs.
-
-
-=251. Imhoff Tank Results.=—The Imhoff tank has the advantage over the
-septic tank that it will not deliver sludge in the effluent, except
-under unusual conditions. The Imhoff tank serves to digest sludge better
-than a septic tank and it will deliver a fresher effluent than a plain
-sedimentation tank. Imhoff sludge is more easily dried and disposed of
-than the sludge from either a septic or a sedimentation tank. This is
-because it has been more thoroughly humified and contains only about 80
-per cent of moisture. As it comes from the tank it is almost black,
-flows freely and is filled with small bubbles of gas which expand on the
-release of pressure from the bottom of the tank, thus giving the sludge
-a porous, sponge-like consistency which aids in drying. When dry it has
-an inoffensive odor like garden soil, and it can be used for filling
-waste land, without further putrefaction. It has not been used
-successfully as a fertilizer.
-
-Offensive odors are occasionally given off by Imhoff tanks, even when
-properly operated. They also have a tendency to “boil” or foam. The
-boiling may be quite violent, forcing scum over the top of the
-transition chamber and sludge through the slot in the sedimentation
-chamber, thus injuring the quality of the effluent. The scum on the
-surface of the transition chamber may become so thick or so solidly
-frozen as to prevent the escape of gas with the result that sludge may
-be driven into the sedimentation chamber.
-
-Some chemical analyses of Imhoff tank influents and effluents are given
-in Table 86 and the analyses of some sludges from Imhoff tanks are given
-in Table 83. It is to be noted that the nitrites and nitrates are still
-present in the effluent, whereas they are seldom present in the effluent
-from septic tanks. The per cent of moisture in the Imhoff sludge is less
-than that in the septic tank sludge, and its specific gravity is higher.
-It is heavier and more compact because of the longer time and the
-greater pressure it has been subjected to in the digestion chamber of
-the Imhoff tank.
-
-
-=252. Status of Imhoff Tanks.=—The introduction of the Imhoff tank into
-the United States, like the introduction of the Burkli-Ziegler Run-Off
-Formula, and Kutter’s Formula, is to be credited to Dr. Rudolph Hering.
-He advised Dr. Imhoff to come to the United States to introduce his tank
-and gave him material aid through recommendations and introductions to
-engineers. Shortly after its introduction, in 1907, the tank became very
-popular and installations were made in many cities. This popularity was
-caused by a growing dissatisfaction with the septic tank, the litigation
-then progressing over septic patents, the production of inoffensive
-sludge, and the promising results which had been obtained in Germany. As
-a result of the extended experience obtained in the use of Imhoff tanks
-American engineers have learned that, like all other sewage treatment
-devices introduced up to the present time, the Imhoff tank requires
-experienced attention for its successful operation. These tanks are now
-being installed in the place of septic tanks, and they are frequently
-used in conjunction with sprinkling filters.
-
-
-=253. Operation of Imhoff Tanks.=—The important feature in the
-successful operation of an Imhoff tank is the proper control of the
-sludge and transition chambers. During the ripening process, which may
-occupy 2 weeks to 3 months after the start of the tank, offensive odors
-may be given off, the tank may foam violently, and scum may boil over
-into the sedimentation chamber. This is usually due to an acid condition
-in the digestion chamber which may possibly be overcome by the addition
-of lime. A very fresh influent will have a similar effect. Too violent
-boiling is not likely to occur where the area for the escape of gas has
-been made large and the gas is not confined. Any accumulation of scum
-should be broken up and pushed down into the digestion chamber, or
-removed from the tank. The stream from a fire hose is useful in breaking
-up scum. The side walls of the sedimentation chamber should be squeegeed
-as frequently as is necessary to keep them free from sludge, which may
-be as often as once or twice a week. Material floating on the surface of
-the sedimentation chamber should be removed from the tank or sunk into
-the digestion chamber through the gas vents in the transition chamber.
-
-No sludge should be removed, except for the taking of samples, until the
-tank is well ripened. The ripening of the sludge can be determined by
-examining a sample and observing its color and odor. An odorless, black,
-granular, well humified sludge is indicative of a ripened tank. After
-the tank has ripened, sludge should be removed in small quantities at 2
-to 3–week intervals, except in cold or rainy weather. The sludge should
-be drawn off slowly to insure the removal of the oldest sludge at the
-bottom of the digestion chamber. After the drawing off of the sludge has
-ceased the pipe should be flushed with fresh water to prevent its
-clogging with dried sludge in the interim until the next removal. Under
-no circumstances should all the sludge in the tank be removed at any
-time. The removal of some sludge during foaming after ripening may
-reduce or stop the foaming. The ripening of a tank can be hastened by
-adding some sludge from a tank already ripened.
-
-Sludge should not be allowed to accumulate within 18 inches of the slot
-at the bottom of the digestion chamber. The elevation of the surface of
-the sludge can be located by lowering into the tank, a stoppered,
-wide-mouthed bottle on the end of a stick. The stopper is pulled out by
-a string when the bottle is at some known elevation. The bottle is then
-carefully raised and observed for the presence of sludge. The process is
-repeated with the bottle at different elevations until the surface of
-the sludge has been discovered. Another method is to place the suction
-pipe of a small hand pump at known points, successively increasing in
-depth, and to pump in each position until one position is found at which
-sludge appears in the pump. When the sludge in one portion of the
-digestion chamber has risen higher than in another portion, the
-direction of flow in the sedimentation chamber should be reversed if
-possible. In the ordinary routine of operation it is never necessary to
-shut down an Imhoff tank. Sludge is removed while the tank is operating.
-The shut down of a tank will be caused by accidents and breaks to the
-structure or control devices.
-
-
-=254. Other Tanks.=—The Travis Hydrolytic Tank represents a step in the
-development from the septic tank to the Imhoff tank. The Doten tank and
-the Alvord tank are recent developments, and are somewhat similar in
-operation to the Imhoff tank.
-
-The Travis Hydrolytic Tank when first designed differed from the later
-design of the Imhoff tank in the slot between the sedimentation chamber
-and the digestion chamber which was not trapped against the escape of
-gas from the latter to the former, and in operation a small quantity of
-fresh sewage was allowed to flow through the digestion chamber. The tank
-is called a hydrolytic tank because some solids are liquefied in it. The
-tank is mainly of historic interest as designs similar to it are rarely
-made to-day. Better results are obtained from the use of the Imhoff
-tank. Recent developments have altered the original design of the Travis
-tank so that it is hardly recognizable. The Travis tank at Luton, Eng.,
-is shown in Fig. 164. The detailed description given in the _Engineering
-News_ in connection with this illustration shows that the governing
-object of the design is to separate as quickly as possible the sludge
-deposited by the sewage without septic action being set up. To aid in
-the collection and settlement of flocculent matter vertical wooden grids
-or colloiders are used. The suspended matter strikes these and forms a
-slimy deposit on them that in a short time slips off in pieces large
-enough to settle readily.
-
-[Illustration:
-
- FIG. 164.—Plan and Section of Hydrolytic Tank at Luton, England.
-
- Eng. News, Vol. 76, 1916, p. 194.
-]
-
-[Illustration:
-
- FIG. 165.—Doten Tank for Army Cantonment Sewage Disposal.
-
- Eng. News-Record, Vol. 79, 1917, p. 931.
-]
-
-The Doten tank[158] is a single-storied, hopper-bottomed septic tank,
-views of which are shown in Fig. 165. It was devised by L. S. Doten for
-army cantonments during the War. Its chief purpose was to avoid the
-foaming and frothing so common to Imhoff tanks when overdosed with fresh
-sewage. The first Alvord tank was constructed in Madison, Wis., in
-1913.[159] As now constructed the tank consists of three deep,
-single-story compartments with hopper bottoms. These compartments are
-arranged side by side in any one unit. Sewage enters at the surface of
-one of the compartments and is retained here during one-half of the
-total period of retention. It leaves the first compartment over a weir
-and passes in a channel over the top of the intermediate compartment to
-the third or effluent compartment, where it is held for the remainder of
-the period of detention. Accumulated scum and sludge are drawn off into
-the intermediate compartment at the will of the operator, this
-compartment being used for sludge digestion only. Such tanks as the
-Doten and the Alvord have been used for plants receiving very fresh
-sewages such as is discharged from military cantonments, in order to
-assist in the prevention of the foaming to be expected from an Imhoff
-tank receiving such a fresh influent. The tanks are suitable for small
-installations, or where excavation to the depth required for an Imhoff
-tank is not practicable.
-
-
-
-
- CHAPTER XVII
- FILTRATION AND IRRIGATION
-
-
-=255. Theory.=—The cycle through which the elements forming organic
-matter pass from life to death and back to life again has been described
-in Chapter XIII. It has been shown in Chapter XVI that septic action
-occupies that portion of the cycle in which the combinations of these
-elements are broken down or reduced to simpler forms and the lower
-stages of the cycle are reached. The action in the filtration of sewage
-builds up the compounds again in a more stable form and almost complete
-oxidation is attained, dependent on the thoroughness of the filtration.
-In the filtration of sewage only the coarsest particles of suspended
-matter are removed by mechanical straining. The success of the
-filtration is dependent on biologic action. The desirable form of life
-in a filter is the so-called nitrifying bacteria which live in the
-interstices of the filter bed and feed upon the organic matter in the
-sewage. Anything which injures the growth of these bacteria injures the
-action of the filter. In a properly constructed and operated filter, all
-matter which enters in the influent, leaves with the effluent, but in a
-different molecular form. A slight amount may be lost by evaporation and
-gasification but this is more than made up by the nitrogen and oxygen
-absorbed from the atmosphere. The nitrifying action in sewage filtration
-is shown by the analysis of sewage passing through a trickling filter,
-as given in Tables 86 and 87. It is shown by the reduction of the
-content of organic nitrogen, free ammonia, oxygen consumed, and the
-increase in nitrites, nitrates, and dissolved oxygen. The reduction of
-suspended matter is interrupted periodically when the filter “unloads.”
-The suspended matter in the effluent is then greater than in the
-influent.
-
-The nitrifying organisms have been isolated and divided into two
-groups—_nitrosomonas_, the nitrite formers, and _nitrobacter_, the
-nitrate formers. Experiments indicate that the growth of the nitrobacter
-organisms is dependent on the presence of the nitrosomonas organisms,
-which are in turn dependent on the presence of the putrefactive
-compounds resulting from the action of putrefying bacteria. The
-existence of these organisms is an example of symbiotic action in
-bacterial growth. The organisms have been found to grow best on rough
-porous material on which their zoögleal jelly can be easily deposited
-and affixed. Sewage filters were constructed to provide these ideal
-conditions before the action of a filter was thoroughly understood.
-
-The action in irrigation is similar to that in filtration. Although more
-strictly a method of final disposal rather than preliminary treatment,
-the similarity of the actions which take place, and the grading of sand
-filtration into broad irrigation with no distinct line of difference has
-resulted in the inclusion of the discussion of irrigation in the same
-chapter with filtration.
-
-
-=256. The Contact Bed.=—A contact bed is a water-tight basin filled with
-coarse material, such as broken stone, with which sewage and air are
-alternately placed in contact in such a manner that oxidation of the
-sewage is effected. A contact bed has some of the features of a
-sedimentation tank and an oxidizing filter. As such it marks a
-transitory step from anaërobic to aërobic treatment of sewage. A plan
-and a section of a contact bed are shown in Fig. 166.
-
-Because of its dependence on biologic action a contact bed must be
-ripened before a good effluent can be obtained. The ripening or maturing
-occurs progressively during the first few weeks of operation, the
-earlier stages being more rapidly developed. The time required to reach
-such a stage of maturity that a good effluent will be developed will
-vary between one and six or eight weeks, dependent on the weather and
-the character of the influent. During the period of maturing the load on
-the bed should be made light.
-
-The use of contact beds has been extensive where a more stable effluent
-than could be obtained from tank treatment has been desired, yet the
-best quality of effluent was not required. The sewage to undergo
-treatment in a contact bed should be given a preliminary treatment to
-remove coarse suspended matter. The efficiency of the contact treatment
-can be increased by passing the sewage through two or three contact beds
-in series. In double contact treatment the primary beds are filled with
-coarser material and operate at a more rapid rate than the secondary
-beds. Double contact gives better results than single contact, but
-triple contact treatment, though showing excellent results, is hardly
-worth the extra cost. An advantage which contact treatment has over all
-other methods of sewage filtration is that the bed can be so operated
-that the sewage is never exposed to view. As a result the odors from
-well-operated contact beds are slight or are entirely absent and there
-should be no trouble from flying insects. Such a method of treatment is
-favorable to plants located in populous districts and to the fancies of
-a landscape architect. Another advantage of the contact bed is the small
-amount of head required for its operation, which may be as low as 4 to 5
-feet. This low head consumption by a sewage filter is equaled only by
-the intermittent sand filter.
-
-[Illustration:
-
- FIG. 166.—Plan and Section of Treatment Plant at Marion, Ohio, Showing
- Septic Tank, Contact Bed, and Sand Filter.
-
- 1908 Report Ohio State Board of Health.
-]
-
-The quality of the effluent from some contact beds is shown in Table 85.
-It is to be noted that nitrification has been carried to a fair degree
-of completion, and that the reduction of oxygen consumed has been
-marked. In comparison with the effluent from filters, contact effluent
-contains a smaller amount of nitrogen as nitrites and nitrates, and
-suspended solids. Contact effluent is usually clear and odorless, but it
-is not stable without dilution. The absence of nitrites and nitrates is
-sometimes advantageous as the effluent will not support vegetable
-growths dependent on this form of nitrogen. The absence of suspended
-solids obviates the use of secondary sedimentation basins which are
-needed with trickling filters. The head of 5 to 8 feet required for
-contact treatment is low in comparison to the 10 to 15 feet required for
-trickling filters, but is slightly higher than the head required for
-intermittent sand filtration. The cost of contact treatment is higher
-than the cost of trickling filters but is lower than the cost of
-intermittent sand filtration, as shown in Table 90.
-
- TABLE 85
-
- QUALITY OF EFFLUENTS FROM CONTACT BEDS
-
- Report on Sewage Purification at Columbus, Ohio, by G. A. Johnson, 1905.
-
- ──────┬──────┬─────────┬───────┬────────┬─────────────────────────────────
- Filter│Depth,│ Size of │ Rate, │ Oxygen │ Nitrogen as
- │ Feet │Material │Million│Consumed│
- │ │in Inches│Gallons│ │
- │ │ │ per │ │
- │ │ │ Acre │ │
- │ │ │per Day│ │
- ──────┼──────┼─────────┼───────┼────────┼───────┬───────┬────────┬────────
- │ │ │ │ │Organic│ Free │Nitrites│Nitrates
- │ │ │ │ │ │Ammonia│ │
- ──────┼──────┼─────────┼───────┼────────┼───────┴───────┴────────┴────────
- │ │ │ │ │ Parts per Million
- │ │ │ │ │ │ │ │
- A │ 5│0.25–1.00│ 0.953│ 23│ 3.5│ 8.7│ 0.20│ 1.6
- B │ 5│0.25–2.00│ 1.514│ 21│ 4.0│ 8.4│ 0.15│ 1.4
- C │ 5│0.25–1.50│ 1.222│ 24│ 3.5│ 10.8│ 0.11│ 0.6
- D │ 5│0.50–1.50│ 1.405│ 22│ 3.3│ 9.5│ 0.13│ 0.9
- │ │ │ │ │ │ │ │
- │ │ │Per Cent Removal of Constituents of Applied Sewage
- │ │ │ │ │ │ │ │
- A │ 5│0.25–1.00│ 0.953│ 48│ 49│ 10│ │
- B │ 5│0.25–2.00│ 1.514│ 52│ 40│ 11│ │
- C │ 5│0.25–1.50│ 1.222│ 47│ 31│ 12│ │
- D │ 5│0.50–1.50│ 1.405│ 46│ 37│ 19│ │
- ──────┴──────┴─────────┴───────┴────────┴───────┴───────┴────────┴────────
-
- ──────┬──────┬────────────────────┬─────────
- Filter│Depth,│ Suspended Matter │Dissolved
- │ Feet │ │ Oxygen
- │ │ │
- │ │ │
- │ │ │
- │ │ │
- ──────┼──────┼─────┬────────┬─────┼─────────
- │ │Total│Volatile│Fixed│
- │ │ │ │ │
- ──────┼──────┴─────┴────────┴─────┴─────────
- │ Parts per Million
- │ │ │ │ │
- A │ 5│ 832│ 94│ 737│ 0.3
- B │ 5│ 831│ 85│ 746│ 0.1
- C │ 5│ 826│ 92│ 734│ 0.8
- D │ 5│ 810│ 91│ 717│ 0.9
- │ │ │ │ │
- │ Per Cent Removal of Constituents of Applied Sewage
- │ │ │ │ │
- A │ 5│ 73│ 70│ 76│
- B │ 5│ 80│ 77│ 83│
- C │ 5│ 70│ 70│ 70│
- D │ 5│ 67│ 61│ 72│
- ──────┴──────┴─────┴────────┴─────┴─────────
-
-The depth of the contact bed is generally made from 4 to 6 feet. The
-deeper beds are less expensive per unit of volume, to construct, as the
-cost of the underdrains and the distribution system is reduced in
-relation to the capacity of the filter. The increased depth reduces the
-aëration, and the periods of filling and emptying are so increased as to
-limit the depths to the figures stated. The other dimensions of the bed
-are controlled by economy and local conditions, as the success of the
-contact treatment is not affected by the shape of the bed. Contact units
-are seldom constructed larger than one-half an acre in area, as larger
-beds require too much time for filling and emptying. A large number of
-small units is also undesirable because of the increased difficulty of
-control. In general it is well to build as large units as are compatible
-with efficient operation, elasticity of plant, and which can be filled
-within the time allowed at the average rate of sewage flow, or from
-dosing tanks in which the storage period is not so long as to produce
-septic conditions.
-
-The interstices in a contact bed will gradually fill up, due to the
-deposition of solid matter on the contact material, the disintegration
-of the material, and the presence of organic growths. The period of rest
-allowed every five or six weeks tends to restore partially some of this
-lost capacity through the drying of the organic growths. It is
-occasionally necessary to remove the material from the bed and wash it
-in order to restore the original capacity. It may be necessary to do
-this three or four times a year, in an overloaded plant, or as
-infrequently as once in five or six years in a more lightly loaded bed.
-The period is also dependent on the character of the contact material
-and the quality of the influent. This loss of capacity may reduce the
-voids from an original amount of 40 to 50 per cent of voids to 10 to 15
-per cent. If the bed is not overloaded the loss of capacity will not
-increase beyond these figures.
-
-The rate of filtration depends on the strength of the sewage, the
-character of the contact material, and the required effluent. It should
-be determined for any particular plant as the result of a series of
-tests. For the purposes of estimation and comparison the approximate
-rate of filtration should be taken at about 94 gallons per cubic yard of
-filtering material per day on the basis of three complete fillings and
-emptyings of the tank. This is equivalent to 150,000 gallons per acre
-foot of depth per day, or for a bed 5 feet deep to a rate of 750,000
-gallons per acre per day. The net rate for double or triple filtration
-is less than these figures, but on each filter the rates are higher.
-
-The material of the contact bed should be hard, rough, and angular. It
-should be as fine as possible without causing clogging of the bed.
-Materials in successful use are: crushed trap rock or other hard stone,
-broken bricks, slag, coal, etc. Soft crumbling materials such as coke
-are not suitable as the weight of the superimposed material and the
-movement of the sewage crushes and breaks it into fine particles which
-accumulate in the lower portion of the filter and clog it. Roughness,
-porosity, and small size are desirable, as the greater the surface area
-the more rapid the deposition of material. After a short time, however,
-the advantages of roughness and porosity are lost, as the sediment soon
-covers all unevenness alike. The minimum size of the material is limited
-by the tendency towards clogging. The sizes in successful use vary
-between ¼ and ¾ of an inch, ½ inch being a common size. The same size of
-material is used throughout the depth of the bed except that the upper 6
-inches may be composed of small white pebbles or other clean material,
-which does not come in contact with the sewage and which will give an
-attractive appearance to the plant. In double or triple contact beds 3
-or 4–inch material is sometimes used for the primary beds, and ¼-inch
-material in the final bed.
-
-Sewage may be applied at any point on or below the surface. The sewage
-is withdrawn from the bottom of the bed. It is undesirable to have too
-few inlet or outlet openings as the velocity of flow about the openings
-will be so great as to disturb the deposit on the contact material. The
-distribution system and the underdrains for the bed at Marion, Ohio, are
-shown in Fig. 166.
-
-The cycle of operation of a contact bed is divided into four periods. A
-representative cycle might be: time of filling, one hour; standing full,
-2 hours; emptying, one hour; standing empty, 4 hours. The length of
-these periods is the result of long experience based on many tests and
-are an average of the conclusions reached. Wide variations from them may
-be found in different plants, and tests may show successful results with
-different periods. The combination of these four periods is known as the
-contact cycle.
-
-The period of filling should be made as short as possible without
-disturbing the material of the bed nor washing off the accumulated
-deposits. The sewage should not rise more rapidly than one vertical foot
-per minute. During the contact or standing full period sedimentation and
-adsorption of the colloids are occurring on the area of surface exposed
-to the sewage. This period should be of such length that septic action
-does not become pronounced, and long enough to permit of thorough
-sedimentation. The period of emptying should be made as short as
-possible without disturbing the bed, on the same basis that the period
-of filling is determined. During the period of standing empty, air is in
-contact with the sediment deposited in thin layers on the contact
-material, and the oxidizing activities of the filter are taking place.
-The filter is given a rest period of one or two days every five or six
-weeks, in order that it may increase its capacity and its biologic
-activity.
-
-The control of a contact bed may be either by hand or automatic, the
-latter being the more common. Hand control requires the constant
-attention of an operator and results in irregularity of operation,
-whereas automatic control will require inspection not more than once a
-day and insures regularity of operation. A number of automatic devices
-have been invented which give more or less satisfaction. The air-locked
-automatic siphons, without moving parts, have proven satisfactory and
-are practically “fool-proof.” The operation of these devices is
-explained in Chapter XXI.
-
-
-=257. The Trickling Filter.=—A trickling or sprinkling filter is a bed
-of coarse, rough, hard material over which sewage is sprayed or
-otherwise distributed and allowed to trickle slowly through the filter
-in contact with the atmosphere. A general view of a trickling filter in
-operation at Baltimore is shown in Fig. 167. The action of the trickling
-filter is due to oxidation by organisms attached to the material of the
-filter. The solid organic matter of the sewage deposited on the surface
-of the material, is worked over and oxidized by the aërobic bacteria,
-and is discharged in the effluent in a more highly nitrified condition.
-At times the discharge of suspended matter becomes so great that the
-filter is said to be unloading. The action differs from that in a
-contact bed in that there is no period of septic or anaërobic action and
-the filter never stands full of sewage.
-
-The effluent from a trickling filter is dark, odorless, and is
-ordinarily non-putrescible. Analyses of typical effluents are given in
-Tables 86 and 87. The unloading of the filter may occur at any time, but
-is most likely to occur in the spring or in a warm period following a
-period of low temperatures. It causes higher suspended matter in the
-effluent than in the influent and may render the effluent putrescible.
-The action is marked by the discharge of solid matter which has sloughed
-off of the filter material and which increases the turbidity of the
-effluent. Where the diluting water is insufficient to care for the
-solids so carried in the effluent, they can be removed by a 2–hour
-period of sedimentation. The effluent may become septic during this
-time, however. The nitrogen in the effluent is almost entirely in the
-form of nitrates, and the percentage of saturation with dissolved oxygen
-is high. The effluent is more highly nitrified than that from a contact
-bed, and its relative stability is also higher, thus demanding a smaller
-volume of diluting water.
-
-[Illustration:
-
- FIG. 167.—Sprinkling Filter in Operation in Winter at Baltimore.
-]
-
-The principal advantage of a trickling filter over other methods of
-treatment is its high rate which is from two to four times faster than a
-contact bed, and about seventy times faster than an intermittent sand
-filter. The greatest disadvantage is the head of 12 to 15 feet or more
-necessary for its operation. Sedimentation of the effluent is usually
-necessary to remove the settleable solids. During the period of
-secondary sedimentation the quality of the filter effluent may
-deteriorate in relative stability. In winter the formation of ice on the
-filter results in an effluent of inferior quality, but as the diluting
-water can care for such an effluent at this time the condition is not
-detrimental to the use of the trickling filter. In summer the filters
-sometimes give off offensive odors that can be noticed at a distance of
-half a mile, and flying insects may breed in the filter in sufficient
-quantities to become a nuisance if preventive steps are not taken. The
-dissemination of odors is especially marked when treating a stale or
-septic sewage. The treatment of a fresh sewage seldom results in the
-creation of offensive odors.
-
- TABLE 86
-
- ANALYSIS OF CRUDE SEWAGE, IMHOFF TANK, AND SPRINKLING FILTER EFFLUENTS
- AT ATLANTA, GEORGIA
-
- (Engineering Record, Vol. 72, p. 4)
-
- ─────────┬───────────┬──────────────────────────────────────────
- │Temperature│ Parts per Million
- │Fahrenheit │
- │ │
- │ │
- ─────────┼───────────┼─────────────────────────────────┬────────
- │ │ Nitrogen as │ Oxygen
- │ │ │Consumed
- ─────────┼───────────┼───────┬───────┬────────┬────────┼────────
- │ │Organic│ Free │Nitrites│Nitrates│
- │ │ │Ammonia│ │ │
- ─────────┴───────────┴───────┴───────┴────────┴────────┴────────
-
- _Crude Sewage_
-
- ─────────┬───────────┬───────┬───────┬────────┬────────┬────────
- 1913 │ │ │ │ │ │
- Maximum │ 77│ 15.6│ 21.8│ 0.1│ 3.0│ 100.0
- Minimum │ 61│ 10.4│ 16.5│ 0.1│ 1.4│ 78.3
- Average │ 70│ 12.8│ 18.8│ 0.1│ 2.2│ 90.6
- 1914 (7 │ │ │ │ │ │
- months)│ │ │ │ │ │
- Maximum │ 74│ 16.0│ 33.4│ │ 2.3│
- Minimum │ 60│ 9.5│ 18.1│ │ 1.6│
- Average │ 66│ 13.4│ 27.1│ │ 2.0│
- ─────────┴───────────┴───────┴───────┴────────┴────────┴────────
-
- _Imhoff Effluent_
-
- ─────────┬───────────┬───────┬───────┬────────┬────────┬────────
- 1913 │ │ │ │ │ │
- Maximum │ 78│ 13.2│ 21.9│ 0.2│ 3.1│ 68.0
- Minimum │ 58│ 6.5│ 16.8│ 0.1│ 1.1│ 53.1
- Average │ 68│ 9.0│ 20.0│ 0.2│ 2.1│ 60.1
- 1914 (7 │ │ │ │ │ │
- months)│ │ │ │ │ │
- Maximum │ 77│ 10.3│ 30.3│ │ 2.0│
- Minimum │ 59│ 4.1│ 18.0│ │ 1.5│
- Average │ 65│ 7.7│ 25.9│ │ 1.8│
- ─────────┴───────────┴───────┴───────┴────────┴────────┴────────
-
- _Sprinkling Filter Effluent_
-
- ─────────┬───────────┬───────┬───────┬────────┬────────┬────────
- 1913 │ │ │ │ │ │
- Maximum │ 79│ 5.6│ 14.2│ 0.8│ 11.3│ 32.1
- Minimum │ 55│ 2.6│ 6.2│ 0.5│ 5.8│ 23.6
- Average │ 66│ 3.8│ 9.9│ 0.7│ 8.2│ 28.2
- 1914 (7 │ │ │ │ │ │
- months)│ │ │ │ │ │
- Maximum │ 77│ 8.5│ 20.7│ │ 11.2│
- Minimum │ 55│ 4.4│ 8.8│ │ 3.6│
- Average │ 63│ 5.7│ 15.2│ │ 7.2│
- ─────────┴───────────┴───────┴───────┴────────┴────────┴────────
-
- ─────────┬────────────────────┬──────────┬─────────
- │ Parts per Million │ Per Cent │Relative
- │ │Saturation│Stability
- │ │Dissolved │
- │ │ Oxygen │
- ─────────┼────────────────────┼──────────┼─────────
- │ Suspended Matter │ │
- │ │ │
- ─────────┼─────┬────────┬─────┼──────────┼─────────
- │Total│Volatile│Fixed│ │
- │ │ │ │ │
- ─────────┴─────┴────────┴─────┴──────────┴─────────
-
- _Crude Sewage_
-
- ─────────┬─────┬────────┬─────┬──────────┬─────────
- 1913 │ │ │ │ │
- Maximum │ 371│ 154│ 163│ 47│
- Minimum │ 222│ 98│ 112│ 11│
- Average │ 285│ 126│ 138│ 28│
- 1914 (7 │ │ │ │ │
- months)│ │ │ │ │
- Maximum │ 431│ │ │ 48│
- Minimum │ 279│ │ │ 12│
- Average │ 351│ │ │ 30│
- ─────────┴─────┴────────┴─────┴──────────┴─────────
-
- _Imhoff Effluent_
-
- ─────────┬─────┬────────┬─────┬──────────┬─────────
- 1913 │ │ │ │ │
- Maximum │ 90│ 50│ 41│ │
- Minimum │ 35│ 42│ 21│ │
- Average │ 68│ 46│ 33│ │
- 1914 (7 │ │ │ │ │
- months)│ │ │ │ │
- Maximum │ 73│ │ │ 48│
- Minimum │ 49│ │ │ 34│
- Average │ 65│ │ │ 43│
- ─────────┴─────┴────────┴─────┴──────────┴─────────
-
- _Sprinkling Filter Effluent_
-
- ─────────┬─────┬────────┬─────┬──────────┬─────────
- 1913 │ │ │ │ │
- Maximum │ 60│ 31│ 28│ 76│ 99
- Minimum │ 33│ 26│ 28│ 52│ 88
- Average │ 49│ 28│ 28│ 64│ 89
- 1914 (7 │ │ │ │ │
- months)│ │ │ │ │
- Maximum │ 106│ │ │ 79│ 99
- Minimum │ 40│ │ │ 55│ 89
- Average │ 62│ │ │ 65│ 95
- ─────────┴─────┴────────┴─────┴──────────┴─────────
-
- TABLE 87
-
- EFFICIENCY OF SPRINKLING FILTER CHICAGO, ILLINOIS
-
- Depth of Filter 9 feet. Size of stone 2 in. to 3 in.
-
- ────────┬───────────────────────────┬───────────────────────────
- Month │ Organic Nitrogen │ Free Ammonia
- │ │
- ────────┼───────────────────────────┼───────────────────────────
- │ │
- ────────┼─────────┬─────────┬───────┼─────────┬─────────┬───────
- │Influent,│Effluent,│ Per │Influent,│Effluent,│ Per
- │Parts per│Parts per│ Cent │Parts per│Parts per│ Cent
- │ Million │ Million │Removed│ Million │ Million │Removed
- ────────┼─────────┼─────────┼───────┼─────────┼─────────┼───────
- 1910 │ │ │ │ │ │
- October │ 5.1│ 2.8│ 45│ 12.0│ 4.6│ 62
- November│ 5.9│ 2.5│ 58│ 12.0│ 5.9│ 51
- December│ 4.6│ 3.0│ 35│ 12.0│ 6.9│ 42
- │ │ │ │ │ │
- 1911 │ │ │ │ │ │
- January │ 6.3│ 4.8│ 24│ 11.0│ 7.0│ 36
- February│ 9.0│ 4.8│ 47│ 10.0│ 7.2│ 28
- March │ 8.3│ 3.5│ 58│ 9.9│ 6.4│ 35
- April │ 6.4│ 4.0│ 37│ 8.3│ 3.6│ 69
- May │ 7.6│ 5.4│ 29│ 9.2│ 2.4│ 74
- June │ 5.9│ 3.2│ 46│ 11.0│ 0.6│ 95
- July │ 6.2│ 4.2│ 32│ 11.0│ 1.3│ 88
- ────────┴─────────┴─────────┴───────┴─────────┴─────────┴───────
-
- ────────┬───────────────────────────┬───────────────────────────
- Month │ Oxygen Consumed │ Nitrites
- │ │
- ────────┼───────────────────────────┼───────────────────────────
- │ │
- ────────┼─────────┬─────────┬───────┼─────────┬─────────┬───────
- │Influent,│Effluent,│ Per │Influent,│Effluent,│ Per
- │Parts per│Parts per│ Cent │Parts per│Parts per│ Cent
- │ Million │ Million │Removed│ Million │ Million │Removed
- ────────┼─────────┼─────────┼───────┼─────────┼─────────┼───────
- 1910 │ │ │ │ │ │
- October │ 30│ 15│ 50│ │ .90│
- November│ 35│ 15│ 57│ │ .76│
- December│ 39│ 20│ 49│ .07│ .45│ 6.4
- │ │ │ │ │ │
- 1911 │ │ │ │ │ │
- January │ 42│ 20│ 52│ .08│ .15│ 1.9
- February│ 46│ 20│ 56│ .09│ .15│ 1.7
- March │ 47│ 21│ 56│ .09│ .15│ 1.7
- April │ 38│ 21│ 45│ .16│ .21│ 1.3
- May │ 33│ 31│ 6│ .08│ .38│ 4.8
- June │ 28│ 16│ 43│ .00│ .30│ ∞
- July │ 34│ 26│ 24│ .00│ .36│ ∞
- ────────┴─────────┴─────────┴───────┴─────────┴─────────┴───────
-
- ────────┬───────────────────────────┬───────────────────────────
- Month │ Nitrates │ Dissolved Oxygen
- │ │
- ────────┼───────────────────────────┼───────────────────────────
- │ │
- ────────┼─────────┬─────────┬───────┼─────────┬─────────┬───────
- │Influent,│Effluent,│ Per │Influent,│Effluent,│ Per
- │Parts per│Parts per│ Cent │Parts per│Parts per│ Cent
- │ Million │ Million │Removed│ Million │ Million │Removed
- ────────┼─────────┼─────────┼───────┼─────────┼─────────┼───────
- 1910 │ │ │ │ │ │
- October │ │ 7.8│ │ 0.0│ 8.5│ ∞
- November│ │ 5.9│ │ 0.0│ 8.1│ ∞
- December│ .15│ 2.6│ 17│ 2.0│ 8.4│ 4.2
- │ │ │ │ │ │
- 1911 │ │ │ │ │ │
- January │ .27│ 2.2│ 8.2│ 3.0│ 7.8│ 2.9
- February│ .50│ 2.6│ 5.2│ 2.6│ 8.0│ 3.1
- March │ .34│ 3.2│ 9.4│ 2.2│ 6.6│ 3.0
- April │ .53│ 4.5│ 8.5│ 2.1│ 7.1│ 3.4
- May │ .15│ 7.5│ 4.3│ 0.1│ 7.7│ 77
- June │ .16│ 8.3│ 5.2│ 0.0│ 7.6│ ∞
- July │ .09│ 7.7│ 8.0│ 0.0│ 6.5│ ∞
- ────────┴─────────┴─────────┴───────┴─────────┴─────────┴───────
-
- ────────┬───────────┬───────────────────────────────────────────────────────
- Month │ Per Cent │ Suspended Matter
- │Putrescible│
- ────────┼───────────┼───────────────────────────┬───────────────────────────
- │ │ Total │ Volatile
- ────────┼───────────┼─────────┬─────────┬───────┼─────────┬─────────┬───────
- │ │Influent,│Effluent,│ Per │Influent,│Effluent,│ Per
- │ │Parts per│Parts per│ Cent │Parts per│Parts per│ Cent
- │ │ Million │ Million │Removed│ Million │ Million │Removed
- ────────┼───────────┼─────────┼─────────┼───────┼─────────┼─────────┼───────
- 1910 │ │ │ │ │ │ │
- October │ 0│ 75│ 40│ 47│ 54│ 25│ 54
- November│ 5│ 61│ 16│ 74│ 52│ 15│ 71
- December│ 35│ 85│ 40│ 53│ 60│ 26│ 57
- │ │ │ │ │ │ │
- 1911 │ │ │ │ │ │ │
- January │ 38│ 112│ 43│ 63│ 68│ 29│ 57
- February│ 29│ 100│ 49│ 51│ 64│ 32│ 50
- March │ 28│ 106│ 37│ 65│ 63│ 22│ 65
- April │ 9│ 113│ 68│ 40│ 59│ 35│ 41
- May │ 6│ 88│ 150│ _1.7_│ 54│ 70│ _1.3_
- June │ 1│ 92│ 77│ 18│ 56│ 36│ 36
- July │ 4│ 155│ 130│ 16│ 74│ 61│ 18
- ────────┴───────────┴─────────┴─────────┴───────┴─────────┴─────────┴───────
-
- ────────┬───────────────────────────
- Month │ Suspended Matter
- │
- ────────┼───────────────────────────
- │ Fixed
- ────────┼─────────┬─────────┬───────
- │Influent,│Effluent,│ Per
- │Parts per│Parts per│ Cent
- │ Million │ Million │Removed
- ────────┼─────────┼─────────┼───────
- 1910 │ │ │
- October │ 21│ 15│ 29
- November│ 9│ 1│ 89
- December│ 25│ 14│ 44
- │ │ │
- 1911 │ │ │
- January │ 44│ 13│ 70
- February│ 37│ 17│ 53
- March │ 43│ 15│ 65
- April │ 54│ 33│ 39
- May │ 34│ 80│ _2.4_
- June │ 36│ 41│ _1.1_
- July │ 81│ 69│ 15
- ────────┴─────────┴─────────┴───────
-
- NOTE.—Italic figures represent increases.
-
-Raw sewage cannot be treated successfully on a trickling filter. Coarse
-solid particles should be screened and settled out, in order that the
-distributing devices or the filter may not become clogged. The effluent
-from an Imhoff tank has proven to be a satisfactory influent for a
-trickling filter. A septic tank effluent may be so stale as to be
-detrimental to the biologic action in the filter.
-
-In the operation of a trickling filter the sewage is sprayed or
-otherwise distributed as evenly as possible in a fine spray or stream,
-over the top of the filtering material. The sewage then trickles slowly
-through the filter to the underdrains through which it passes to the
-final outlet. The distribution of the sewage on the bed is intermittent
-in order to allow air to enter the filter with the sewage. The cycle of
-operation should be completed in 5 to 15 minutes, with approximately
-equal periods of rest and distribution. Cycles of too great length will
-expose the filter to drying or freezing and will give poorer
-distribution throughout the filter. Cycles which are too short will
-operate successfully only with but slight variation in the rate of
-sewage flow. In some plants it has been found advantageous to allow the
-filters to rest for one day in 3 to 6 weeks or longer, dependent on the
-quality of the effluent.
-
-The rate of filtration may be as high as 2,000,000 gallons per acre per
-day, which is equivalent to 200 gallons per cubic yard of material per
-day in a bed 6 feet deep. This is more than double the rate permissible
-in a contact bed. The exact rate to be used for any particular plant
-should be determined by tests. It is dependent on the quality of the
-sewage to be treated, on the depth of the bed, the size of the filling
-material, the weather, and other minor factors.
-
-The filtering material is similar to that used in a contact bed. It
-should consist of hard, rough, angular material, about 1 to 2 inches in
-size. Larger sizes will permit more rapid rates of filtration, but will
-not produce so good an effluent. Smaller sizes will clog too rapidly.
-
-The depth of the filter is limited by the possibility of ventilation and
-the strength of the filtering material to withstand crushing. The deeper
-the bed the less the expense of the distribution and collecting system
-for the same volume of material, and the more rapid the permissible rate
-of filtration. The depths in use vary between 6 and 10 feet, with 6 to 8
-feet as a satisfactory mean. From a biologic standpoint the action of
-the filter seems to be proportional to the volume of the filtering
-material and therefore proportional to the depth of the bed, being
-limited to a minimum depth of about 5 feet, below which sewage may pass
-through the filter without treatment. The shape and other dimensions of
-the filter depend on the local conditions and the economy of
-construction. The filters need not be broken up into units by
-water-tight dividing walls. One filter can be constructed sufficient for
-all needs and various portions of it can be isolated as units by the
-manipulation of valves in the distribution system. Ventilation is
-provided by the air entrained with the sewage as it falls upon the
-surface. If the sides of the filter are built of open stone crib work
-the ventilation will be greatly improved, but it will not be possible to
-flood the filters to keep down flies, and in cold climates these
-openings must be covered in winter to prevent freezing. Filters have
-been constructed without side walls, the filtering material being
-allowed to assume its natural angle of repose. This has usually been
-found to be more expensive than the construction of side retaining
-walls, due to the unused filling material and the extra underdrains
-required.
-
-The distribution of sewage is ordinarily effected by a system of pipes
-and spray nozzles as shown in Fig. 168 and 169. Other methods of
-distribution have been used. At Springfield, Mo.,[160] a moving trough
-from which the sewage flows continuously is drawn back and forth across
-the bed by means of a cable. In England circular beds have been
-constructed and the sewage distributed on them through revolving
-perforated pipes. At the Great Lakes Naval Training Station[161] the
-distributing pipes in the plant, now abandoned, were supported above the
-surface of the filter. The sewage fell from holes in the lower side of
-these pipes on to brass splash plates 14 inches above the filter. It was
-deflected horizontally from these plates over the filter surface. Pipes
-and spray nozzles have been adopted almost universally in the United
-States. Splash plates, traveling distributors, and other forms of
-distribution have been used only in exceptional cases. In a distributing
-system consisting of pipes and nozzles, a network of pipes is laid out
-somewhat as shown in Fig. 168, in such a manner that the head loss to
-all points is approximately equal. The number of valves required should
-be reduced to a minimum. The pipes may be laid out with the main feeders
-leading from a central point and branches at right angles to them,
-somewhat on the order of a spider’s web, or they may be laid out on a
-rectangular or gridiron system. The radial system is advantageous
-because of the central location of the control house, but it does not
-always lend itself favorably to the local conditions, and the piping and
-nozzle location are not so simple. The gridiron system lends itself
-favorably to the equalization of head losses. The pipes used should be
-larger than would be demanded by considerations of economy alone, both
-for the purpose of reduction of head loss and ease in cleaning. No pipe
-less than 6 inches in diameter should be used, and the average velocity
-of flow should not exceed one foot per second. Cast-iron, concrete, or
-vitrified clay pipe may be used, but cast iron is the material commonly
-used. The system should be arranged for easy flushing and cleaning and
-the pipes so sloped that the entire system can be drained in case of a
-shut down in cold weather.
-
-[Illustration:
-
- FIG. 168.—Section through Sprinkling Filter at Fitchburg, Mass.,
- Showing Distribution System.
-
- Eng. Record, Vol. 67, p. 634.
-]
-
-The pipes are placed far enough below the surface of the filling
-material so that the top of the spraying nozzle is 6 to 12 inches above
-the surface of the filter. If the pipes are placed near the surface they
-are accessible for repairs, but are exposed to temperature changes. If
-the pipes are large their presence near the surface of the filter may
-seriously affect the distribution of the sewage through the filter. If
-the distributing pipes are placed near the bottom of the filter they are
-inaccessible for repairs and the nozzles must be connected to them by
-means of long riser pipes. The distributing pipes should be supported by
-columns extending to the foundation of the filter bed, there being a
-column at every pipe joint with such intermediate supports as may be
-required. In some plants the pipes have been supported by the filtering
-material. Although slightly less expensive in first cost the practice of
-so supporting the pipes is poor, as settling of the material may break
-the pipe or cause leaks, and if the bed becomes clogged, removal of the
-material is made more difficult. Valves should be placed in the
-distributing system in such a manner that different sets of nozzles can
-be cut out at will, thus resting those portions of the filter and
-permitting repairs without shutting down the entire filter.
-
-The spacing of the nozzles is fixed by the type and size of the nozzle,
-the available head, and the rate of filtration. Various types of
-sprinkler nozzles are shown in Fig. 169 and the discharge rates, head
-losses, and distances to which sewage is thrown for the Taylor nozzles,
-are shown in Fig. 170. Nozzles are available which will throw circular,
-square, or semicircular sprays. In the use of circular sprays there is
-necessarily some portion of the filter which is underdosed if the
-nozzles are placed at the corners of squares with the sprays tangent,
-and there is an overdosing of other portions if the sprays are allowed
-to overlap so that no portion of the filter is left without a dose.
-Rectangular sprays will apparently overcome these difficulties, but
-studies have shown that circular sprays with some overlapping, and the
-nozzles placed at the apexes of equilateral triangles as shown in Fig.
-172 will give as satisfactory distribution as other forms.
-
-[Illustration:
-
- FIG. 169.—Sprinkling Filter Nozzles.
-
- Bulletin No. 3, Engineering Experiment Station, Purdue University.
-]
-
-[Illustration:
-
- FIG. 170.—Diagram Showing the Discharge and Spacing of Taylor Nozzles.
-]
-
-The nozzles should be selected to give the best distribution, to consume
-all of the head available, and to give the proper cycle of operation.
-The entire head available should be consumed in order that the fewest
-number of nozzles may be used. An excellent study of the characteristics
-of various types of nozzles has been published in Bulletin No. 3 of the
-Engineering Experiment Station at Purdue University, 1920. As a result
-of the tests on the nozzles shown in Fig. 169, it was determined for all
-nozzles, except No. 8, that
-
- _Q_ = _Ca_√(2_gh_);
-
- in which _Q_ = the rate of discharge in cubic feet per second;
-
- _C_ = a coefficient shown in Table 88;
-
- _a_ = the net cross-sectional opening of the nozzle in square
- feet;
-
- _h_ = the pressure on the nozzle in feet of water.
-
- TABLE 88
-
- COEFFICIENTS OF DISCHARGE FOR SPRINKLER NOZZLES SHOWN IN FIG. 169
-
- ──────────────────────┬──────┬──────┬──────┬──────┬──────┬──────┬──────
- Nozzle Number │ 1 │ 2 │ 3 │ 4 │ 5 │ 6 │ 7
- ──────────────────────┼──────┼──────┼──────┼──────┼──────┼──────┼──────
- Coefficient │ .648 │ .756 │ .696 │ .666 │ .675 │ .598 │ .569
- ──────────────────────┴──────┴──────┴──────┴──────┴──────┴──────┴──────
-
-It is evident that if the head on the nozzles is constant and the nozzle
-throws a circular spray, the intensity of dosing at the circumference
-will be greater than nearer the center. This difficulty is overcome by
-so designing the dosing tank from which the sewage is fed that the head
-on the nozzle and the quantity thrown will vary in such a manner that
-the distribution over the bed is equalized. Intermittent action is
-obtained by an automatic siphon which commences to discharge when the
-tank is full and empties the tank in the period allowed for dosing.
-Under such conditions the tank should discharge for a longer time at the
-higher heads than at the lower heads as there is more territory to be
-covered at the higher heads. The design of the tank to do this with
-exactness is difficult, and the construction of the necessary curved
-surfaces is expensive. Where a dosing tank is used for such conditions
-it has been found satisfactory to construct the tank with plane sides
-sloping at approximately 45 degrees from the vertical (or horizontal). A
-tank with curved surfaces is shown in Fig. 171. The dosing siphon is
-usually placed in the tank as shown in the figure. The head and quantity
-of discharge through the nozzles can be varied also by maintaining a
-constant depth in a dosing tank by means of a float feed valve, and
-varying the head and quantity discharged to the nozzles by a butterfly
-valve in the main feed line, or by the use of a Taylor undulating valve
-designed for this purpose. The butterfly valve is opened and closed by a
-cam so designed and driven at such a rate that the required distribution
-is obtained. The Taylor undulating valve is opened and closed at a
-constant rate, the shape of the valve giving the required variations in
-head and discharge. Other methods of control have been attempted but
-have not been used extensively.
-
-[Illustration:
-
- FIG. 171.—Section of 12–inch Siphon and Dosing Tank, for King’s Park,
- Long Island.
-]
-
-An example of the design of the nozzle layout and dosing tank for a
-sprinkling filter follows:
-
- Let it be required to determine the nozzle layout for one acre of
- sprinkling filters with 5 feet available head on the nozzles.
-
- The selection of the type of nozzle and the size of opening is a
- matter of judgment and experience. Nozzles with large openings are
- less liable to clog and fewer nozzles are needed than where small
- nozzles are used, but the distribution of sewage is not so even as
- with the use of small nozzles. In this example Taylor circular
- spray nozzles will be selected. Fig. 170 shows that a Taylor
- circular spray nozzle will discharge 22.3 g.p.m. under a head of 5
- feet, and that the economical nozzle spacing will be 15.3 feet.
- The least number of nozzles at this spacing required for a bed of
- one acre in area is found as follows: In Fig. 172, let _n_ equal
- the number of nozzles in a horizontal row, counting half-spray
- nozzles as ½, and let _m_ equal the number of rows counting rows
- of half-spray nozzles as half rows.[162] Then the number of
- nozzles, _N_, equals _mn_, and 15.3_m_ × 13.2_n_ equals 43,560 or
- _mn_ equals 215.
-
-[Illustration:
-
- FIG. 172.—Typical Sprinkler Nozzle Layout.
-]
-
-The next step should be the design of the dosing tank and siphon. It is
-possible to design a tank which will give equal distribution over equal
-areas of filter surface. It has been found, however, that the expense of
-this refinement is unwarranted as there are a number of outside factors
-which tend to overcome the theoretical design. The effect of wind,
-unequal spacing, and irregularities in the elevation of the nozzles have
-a tendency to offset refinements in the design of a dosing tank. It is
-therefore the general practice to slope the sides of the tank at an
-angle of about 45 degrees as previously stated. The dosing tank is
-generally designed to have a capacity which will give a complete cycle
-of operation once in 15 minutes. In the ordinary design the factors
-given are the rate of inflow and the given time of filling. In the
-following example the time of filling will be taken as 10 minutes, the
-time of emptying as 5 minutes, and the rate of flow as 1,000,000 gallons
-per day. The capacity of the tank will therefore be (1,000,000)⁄24 x 6 =
-7,000 gallons. The diameter of the siphon to be selected can be computed
-as follows:
-
- Let _Q_ = the capacity of the tank in cubic feet;
- _q__{1} = the rate of discharge of the siphon in cubic feet per
- second;
- _q__{2} = the rate of inflow to the tank in cubic feet per second;
- _q_ = the rate of emptying the tank in cubic feet per second =
- (_q__{1} − _q__{2});
- _A_ = the cross-sectional area of the free surface of the water
- in the tank at any instant, in square feet;
- _a_ = the cross-sectional area of the siphon in square feet;
- _b_ = the small dimension of the base of the tank in feet;
- _h_ = the head of water, in feet, on the discharge siphon;
- _h__{1} = the initial head of water, in feet, on the siphon;
- _h__{2} = the final head of water in feet, on the siphon;
- _t_ = the time, in seconds, required to empty the tank,
-
- then _dQ_ = -_Adh_ = _q__{1}_dt_ − _q__{2}_dt_,
-
- and _dt_ = (_dQ_)⁄_q_ = − _Adh_⁄(_q__{1} − _q__{2}),
-
- but _q__{1} = 0.4 _A_ √((2_gh_)),[163]
-
- therefore _t_ = ∫_{_h__{2}}^{_h__{1}} -_Adh_⁄(0.4_a_√(2_gh_) −
- _q__{2}),
-
- but _A_ = 4_h_^2 + 4_bh_ + _b_^2,
-
- therefore _t_ = ∫_{_h__{1}}^{_h__{2}} ((_b_^2 + 4_bh_ +
- 4_h_^2)_dh_)⁄0.4_a_√(2_gh_) − _q__{2}.
-
-The integration of this expression is tedious. Its solution for siphons
-between 6 inches and 12 inches operating under heads commencing from 3
-feet to 6 feet, with a time of emptying of 5 minutes and time of filling
-of 10 minutes is given in Fig. 173. In the example given the rate of
-inflow is 1.55 sec. feet and the head is 5 feet. Then from Fig. 173 the
-size of the siphon to be used is 12 inches. Where a siphon of the size
-required to empty the tank in the time fixed is not available,
-combinations of available sizes can sometimes be used.
-
-[Illustration:
-
- FIG. 173.—Diagram for the Determination of the Capacities of Dosing
- Tanks for Trickling Filters.
-
- Time of emptying, 5 minutes. Time of filling, 10 minutes. Shape of
- tank is a right pyramid or a truncated right pyramid with all four
- sides making an angle of 45 degrees with the vertical. All
- horizontal cross-sections are squares.
-]
-
- For example, if the given head is 6 feet, and the rate of inflow
- is 1.4 sec. feet, it is evident from Fig. 173 that a 6,300–gallon
- dosing tank and two 8–inch siphons will give the required cycle.
-
-The method used for the design of the setting of Taylor nozzles by the
-Pacific Flush Tank Co., is less rational but more simple and probably as
-satisfactory. In this method the steps are as follows:
-
- (1) Divide the maximum daily rate of sewage flow by 1,000 to get
- the maximum minute inflow.
-
- (2) The number of nozzles required is determined by dividing the
- preceding figure by 6. Generally a Taylor nozzle with an orifice
- of ⅞ of an inch will discharge about 20 g.p.m. at the high head
- and about 8 g.p.m. at the low head, and as the nozzles must have a
- capacity which will take care of the inflow at the low head, the
- divisor 6 is used as a factor of safety instead of using 8 as the
- divisor.
-
- (3) The type of nozzle to be used is selected from experience or
- as a matter of judgment. Circular-spray nozzles are more generally
- used.
-
- (4) The spacings are determined from Fig. 170.
-
- (5) The dosing tank of the shape described is then designed. The
- capacity is such as to give a complete cycle once every 15
- minutes. The method of this design is similar to that followed
- previously.
-
- (6) The dosing siphons are designed so that they will have a
- capacity at the minimum head of from 40 to 50 per cent in excess
- of the maximum minute inflow, and the draining depth of the siphon
- will be limited to a maximum of 5 to 5½ feet. The siphons are all
- made adjustable with a variation of 6 inches or more on either
- side of the normal discharge line so that the spraying area and
- cycle can be varied to secure the best results.
-
-The underdrainage of a trickling filter should consist of some form of
-false bottom such as the types shown in Fig. 174. Where possible the
-underdrains should be open at both ends for the purpose of ventilation
-and flushing. It is desirable that the drains be so arranged that a
-light can be seen through them in order that clogging can be easily
-located. The drains should be placed on a slope of approximately 2 in
-100 towards a main collector. The length of the drains is limited by
-their capacity to carry the average dose from the area drained by them.
-The main collecting conduits must be designed in accordance with the
-hydraulic principles given in Chapter IV. No valves, or other
-controlling apparatus, are placed on the underdrains or outlets from the
-filter.
-
-Covers have been provided in winter for some trickling filters in cold
-climates. The Taylor sprinkling nozzle has been found to work
-successfully in extremely cold weather, and it is generally accepted
-that the covering of filters is unnecessary, if the filter is not to be
-shut down for any length of time in cold weather.
-
-The operation of devices for automatically controlling the operation of
-a trickling filter is explained in Chapter XXI.
-
-[Illustration:
-
- FIG. 174.—Types of False Bottoms for Trickling Filters.
-
- Eng. News, Vol. 74, p. 5.
-]
-
-
-=258. Intermittent Sand Filter.=—An intermittent sand filter is a
-specially prepared bed of sand, or other fine grained material, on the
-surface of which sewage is applied intermittently, and from which the
-sewage is removed by a system of underdrains. It differs from broad
-irrigation in the character of the material, the care and preparation of
-the bed, and the thoroughness of the underdrainage. A distinctive
-feature of the intermittent sand filter is the quality of the effluent
-delivered by it. In a properly designed and operated plant the effluent
-is clear, colorless, odorless, and sparkling. It is completely
-nitrified, is stable and contains a high percentage of dissolved oxygen.
-It contains no settleable solids except at widely separated periods when
-a small quantity may appear in the effluent. The percentage removal of
-bacteria may be from 98 to 99 per cent. Some analyses of sand filter
-effluents are given in Table 89. The dissolved solids, the remaining
-bacteria, and the antecedents of the effluent are the only differences
-between it and potable water. An effluent from an intermittent sand
-filter is the most highly purified effluent delivered by any form of
-sewage treatment. The effluent can be disposed of without dilution, on
-account of its high stability. The treatment of sewage to so high a
-degree is seldom required, so that the use of intermittent filters is
-not common. Other drawbacks to their use are the relatively large area
-of land necessary and the difficulty of obtaining good filter sand in
-all localities.
-
- TABLE 89
-
- QUALITY OF EFFLUENTS FROM SAND FILTERS
-
- (Report on Sewage Purification at Columbus, Ohio, by G. A. Johnson, 1905)
- ────────────┬───────────────────────────────────────────────────────┬───────
- Source of │ Parts per Million │Rate of
- Sample │ │Filtra-
- │ │ tion
- │ │Gallons
- │ │ per
- │ │ Acre,
- │ │per Day
- ────────────┼────────────────────────────────────┬────────┬─────────┼───────
- │ Nitrogen as │ Oxygen │ Oxygen │
- │ │Consumed│Dissolved│
- ────────────┼───────┬──────────┬────────┬────────┼────────┼─────────┼───────
- │ Free │Albuminoid│Nitrites│Nitrates│ │ │
- │Ammonia│ Ammonia │ │ │ │ │
- ────────────┼───────┼──────────┼────────┼────────┼────────┼─────────┼───────
- Filter │ 11.0 │ 8.6 │ │ │ 59. │ │
- influent │ │ │ │ │ │ │
- from grit │ │ │ │ │ │ │
- chamber │ │ │ │ │ │ │
- Filter │ 1.12 │ 0.88 │ 0.08 │ 11.5 │ 6.9 │ 6.3 │ 0.081
- effluent │ │ │ │ │ │ │
- Filter │ 0.81 │ 0.88 │ 0.10 │ 12.6 │ 6.5 │ 6.2 │ 0.118
- effluent │ │ │ │ │ │ │
- ────────────┼───────┼──────────┼────────┼────────┼────────┼─────────┼───────
- Filter │ 9.7 │ 5.4 │ │ │ 33. │ │
- influent │ │ │ │ │ │ │
- from plain│ │ │ │ │ │ │
- settling │ │ │ │ │ │ │
- tank │ │ │ │ │ │ │
- Filter │ 0.62 │ 0.77 │ 0.11 │ 14.9 │ 6.0 │ 8.2 │ 0.139
- effluent │ │ │ │ │ │ │
- Filter │ 0.99 │ 1.10 │ 0.10 │ 12.6 │ 7.8 │ 6.5 │ 0.274
- effluent │ │ │ │ │ │ │
- Filter │ 2.61 │ 1.39 │ 0.09 │ 9.0 │ 9.7 │ 3.9 │ 0.357
- effluent │ │ │ │ │ │ │
- ────────────┼───────┼──────────┼────────┼────────┼────────┼─────────┼───────
- Filter │ 10.7 │ 5.6 │ │ │ 38. │ │
- influent │ │ │ │ │ │ │
- from │ │ │ │ │ │ │
- septic │ │ │ │ │ │ │
- tank │ │ │ │ │ │ │
- Filter │ 1.63 │ 1.16 │ 0.09 │ 11.2 │ 8.0 │ 5.8 │ 0.357
- effluent │ │ │ │ │ │ │
- ────────────┼───────┼──────────┼────────┼────────┼────────┼─────────┼───────
- Filter │ 13.4 │ 4.7 │ │ │ 40. │ │
- influent │ │ │ │ │ │ │
- from coke │ │ │ │ │ │ │
- strainer │ │ │ │ │ │ │
- Filter │ 2.24 │ 1.35 │ 1.03 │ 14.6 │ 10.1 │ 6.9 │ 0.372
- effluent │ │ │ │ │ │ │
- ────────────┼───────┼──────────┼────────┼────────┼────────┼─────────┼───────
- Filter │ 8.6 │ 3.6 │ 0.19 │ 1.6 │ 24. │ 0.3 │
- influent │ │ │ │ │ │ │
- from │ │ │ │ │ │ │
- contact │ │ │ │ │ │ │
- bed │ │ │ │ │ │ │
- Filter │ 2.62 │ 1.35 │ 0.31 │ 8.1 │ 8.3 │ 5.8 │ 0.516
- effluent │ │ │ │ │ │ │
- Filter │ 2.44 │ 2.41 │ 0.16 │ 9.4 │ 12.5 │ 5.0 │ 0.525
- effluent │ │ │ │ │ │ │
- Filter │ 3.40 │ 1.15 │ 0.20 │ 10.9 │ 9.7 │ 5.2 │ 0.525
- effluent │ │ │ │ │ │ │
- ────────────┼───────┼──────────┼────────┼────────┼────────┼─────────┼───────
- Filter │ 9.0 │ 4.8 │ 0.42 │ 1.3 │ 27. │ 3.4 │
- influent │ │ │ │ │ │ │
- from │ │ │ │ │ │ │
- sprinkling│ │ │ │ │ │ │
- filter │ │ │ │ │ │ │
- after │ │ │ │ │ │ │
- sedimen- │ │ │ │ │ │ │
- tation │ │ │ │ │ │ │
- Filter │ 2.95 │ 1.25 │ 0.19 │ 7.0 │ 8.8 │ 3.8 │ 0.675
- effluent │ │ │ │ │ │ │
- Filter │ 4.77 │ 2.63 │ 0.51 │ 4.6 │ 11.8 │ 2.5 │ 0.749
- effluent │ │ │ │ │ │ │
- Filter │ 3.47 │ 1.61 │ 0.31 │ 7.2 │ 11.9 │ 3.7 │ 1.129
- effluent │ │ │ │ │ │ │
- ────────────┴───────┴──────────┴────────┴────────┴────────┴─────────┴───────
-
-The action in an intermittent sand filter is more complete than in other
-forms of filters because a greater surface is exposed to the passage of
-sewage by the fine sand particles, and the sewage is in contact with the
-filtering material a longer time due to the lower rate of filtration and
-the slow velocity of flow through the filter. It is essential that the
-sewage be applied to the bed intermittently in order that air shall be
-entrained in the filter. The period between doses should not be so long
-that the filter becomes dry.
-
-In the operation of an intermittent sand filter one dose per day is
-considered an ordinary rate of application, although some plants operate
-with as many as four doses per day per filter, and others on one dose at
-long and irregular intervals. It is not always necessary to rest the
-filter for any length of time unless signs of overloading and clogging
-are shown. The intermittent dosing action may be obtained by the action
-of an automatic siphon as is described in Chapter XXI. The sewage is
-distributed on the beds through a number of openings in the sides of
-distributing troughs resting on the surface of the filter. The sewage is
-withdrawn from the bottom of the filter through a system of underdrains,
-into which it enters after its passage through the bed. There are no
-control devices on the outlet, as the rate of filtration is controlled
-by the action of the dosing apparatus and the rate at which sewage is
-delivered to it. The action of the dosing apparatus should respond
-quickly to variations in sewage flow. As the doses are applied to a sand
-filter, a mat of organic matter or bacterial zoöglea is formed on the
-surface of the bed. The mat is held together by hair, paper, and the
-tenacity of the materials. It may attain a thickness of ¼ to ½ an inch
-before it is necessary to remove it. So long as the filter is draining
-with sufficient rapidity this mat need not be removed, but if the bed
-shows signs of clogging, the only cleaning that may be necessary will be
-the rolling up of this dried mat. It is believed that the greater
-portion of the action in the filter occurs in the upper 5 to 8 inches of
-the bed, but occasionally the beds become so clogged that it is
-necessary to remove ¾ of an inch to 2 inches of sand in addition to the
-surface mat, or to loosen up the surface by shallow plowing or
-harrowing. The necessity for such treatment may indicate that the filter
-is being overloaded as a result of which the rate of filtration should
-be decreased or the preliminary treatment should be improved. The
-plowing of clogging material into the bed should be avoided as under
-these conditions the final condition of the bed will be worse than its
-condition when trouble was first observed.
-
-In winter the surface of the bed should be plowed up into ridges and
-valleys. The freezing sewage forms a roof of ice which rests on the
-ridges and the subsequent applications of sewage find their way into the
-filter through the valleys under the ice. In a properly operated bed the
-filtering material will last indefinitely without change. If a filter is
-operated at too high a rate, however, although the quality of the
-effluent may be satisfactory, it will be necessary at some time to
-remove the sand and restore the filter.
-
-The rate of filtration depends on the character of the influent, the
-desired quality of the effluent, and the depth and character of the
-filtering material. Filters can be found operating at rates of 50,000
-gallons per acre per day and others at eight times this rate. For sewage
-which has had some preliminary treatment, the rate should not exceed
-100,000 gallons per acre per day, whereas the rate for raw sewage should
-be less than this. For rough estimates made without tests of the sewage
-in question, the rate should not be taken at more than 1,000 persons per
-acre. If the preliminary treatment of the sewage has been thorough and
-the material of the sand filter is coarser than ordinary the rate of
-filtration can be high. For less careful preliminary treatment and fine
-filtering material the rates must be reduced. The sewage must undergo
-sufficient preliminary treatment to remove large particles of solid
-matter which would otherwise clog the dosing apparatus and the filter.
-This treatment should include grit removal, screening, and some form of
-tank treatment. Some plants have operated successfully with a stale
-sewage and no preliminary treatment, as at Brockton, Mass. Septic tank
-effluent can be treated successfully on an intermittent sand filter, but
-not so satisfactorily as the effluent from a tank delivering a fresh
-sewage.
-
-The material of the filter should consist of clean, sharp, quartz or
-silica sand with an effective size[164] of 0.2 to 0.4 mm., preferably
-about 0.25 to 0.35 mm., and a uniformity coefficient[165] of 2 to 4.
-Within the limits mentioned no careful attention need be given to the
-size of the material. Natural sand found in place has been underdrained
-and used successfully for sewage treatment. The size of the sand is
-fixed by the rate of filtration rather than the bacteriological action
-of the filter. A coarse sand will permit the sewage to pass through the
-bed too rapidly, and a fine sand will hold it too long or will become
-clogged. The same size of material should be used throughout the bed,
-except that a layer of gravel from 6 to 12 inches thick, graded from
-very small sizes to stones just passing a 2–inch ring should be placed
-at the bottom to facilitate the drainage of the bed.
-
-The thickness of the sand layer should not be less than 30 inches to
-insure complete treatment of the sewage. In shallower beds the sewage
-might trickle through without adequate treatment. Beds are ordinarily
-made from 30 to 36 inches deep, but when deeper layers of sand are found
-in place there is no set limit to the depth which may be used. The shape
-and overall dimensions of the bed should conform to the topography of
-the site and the rate of filtration adopted. A plan and cross-section of
-an intermittent sand filter showing the distribution and under drainage
-systems are given in Fig. 166 and 175.
-
-The distribution system consists of a system of troughs on the surface
-of the filter, laid out in a branching form, as shown in the figure. The
-openings in the troughs should be so located that the maximum distance
-from any point on the bed to the nearest opening should not exceed 20 to
-30 feet. If the filters are small enough, troughs need not be used, the
-sewage being distributed from one corner, or from mid-points on the
-sides. Where troughs are used they should be supported from the bottom
-of the filter in order to prevent uneven settling due to the washing of
-the sand. The openings in the troughs are made adjustable by swinging
-gates as shown in Fig. 176, or by other means so that after the filter
-is in operation the intensity of the dose on any portion of the filter
-can be changed. The troughs may be placed with their bottoms level with
-the surface of the sand and with sides of sufficient height to give the
-required gradient to the water surface, or they may be built up above
-the surface of the filter and given the required slope so that the
-surface of the flowing water is parallel to the bottom of the trough. In
-either case a splash plate should be placed at each opening, so that not
-less than 2 feet of the surface of the sand is protected in all
-directions from the opening. A stone or concrete slab 2 to 4 inches
-thick makes a satisfactory splash plate. Either wood or concrete may be
-used for the construction of the troughs. The former is less durable,
-but also less expensive in first cost. The capacity of the troughs may
-be computed by Kutter’s formula with the quantity to be carried equal to
-the maximum rate of discharge of the feeding siphon, with a reduction in
-size below each branch or outlet proportional to the amount which will
-be discharged above this point.
-
-[Illustration:
-
- FIG. 175.—Plan and Section of an Intermittent Sand Filter Showing
- Central Location of Control House.
-]
-
-The operation of automatic devices for dosing the bed is explained in
-Chapter XXI. The dosing tank should have a capacity sufficient to cover
-the bed to a depth of about 1 to 3 inches at one dose, and the siphon
-should discharge at a rate of about one second-foot for each 5,000
-square feet of filter area. A dose should disappear within 20 minutes to
-half an hour after it is applied to the filter. With the rate stated and
-four applications per day to a depth of 1 inch at each dose, the rate
-per acre per day will be 109,000 gallons.
-
-[Illustration:
-
- FIG. 176.—Distributing Trough with Adjustable Openings.
-]
-
-The filtration of sewage through sand in a manner similar to the _rapid
-sand filtration_ of water is being attempted at the Great Lakes Naval
-Training Station. No results of this treatment have been published and
-the practical success of the method has not been assured.
-
-
-=259. Cost of Filtration.=—Only comparative figures can be given in
-stating the costs of filtration, as most data available are based on
-pre-war conditions, and are therefore unreliable for present conditions.
-The variations from the figures given may be very large but in general
-the relative costs have not changed. The figures given in Table 90 are
-suggestive of the relative costs of the different forms of filtration.
-
- TABLE 90
-
- RELATIVE COSTS OF DIFFERENT METHODS OF SEWAGE TREATMENT
-
- Costs in Dollars per Million Gallons per Day
- ─────────────────────────┬───────────────┬──────────────┬──────────────
- Form of Treatment │First Cost[166]│Operation and │ Total
- │ │ Maintenance │
- ─────────────────────────┼───────────────┼──────────────┼──────────────
- Coarse screens │ │ │ 0.20
- Fine screens │ │ │ 3.00
- Plain sedimentation │ 7.00│ 3.00│ 10.00
- Chemical precipitation │ │ │ 22.00[167]
- Septic tank │ 7.00│ 1.00│ 8.00
- Imhoff tank │ 10.00│ 1.00│ 11.00
- Contact bed │ 8.00│ 2.00│ 10.00
- Trickling filter │ 4.00│ 2.00│ 6.00
- Intermittent sand filter │ 15.00│ 10.00│ 25.00
- Activated sludge │ 6.50│ 8.50│ 15.00[168]
- ─────────────────────────┴───────────────┴──────────────┴──────────────
-
-
- IRRIGATION
-
-
-=260. The Process.=—Broad irrigation is the discharge of sewage upon the
-surface of the ground, from which a part of the sewage evaporates and
-through which the remainder percolates, ultimately to escape in surface
-drainage channels. Sewage farming is broad irrigation practiced with the
-object of raising crops. Broad irrigation can be accomplished
-successfully without the growing of crops, but it is seldom attempted as
-some return and sometimes even a profit can be obtained from the crops
-raised. Broad irrigation and sewage farming differ from intermittent
-sand filtration in the intensity of the application of the sewage, the
-method of preparing the area on which the sewage is to be treated, and
-the care in operation. In broad irrigation and intermittent sand
-filtration the paramount consideration is successful disposal of the
-sewage. In sewage farming the paramount consideration is the growing of
-crops. The growing of crops may be combined with irrigation and
-filtration, however, but the crop should be sacrificed to the successful
-disposal of the sewage.
-
-The change which occurs in the characteristics of the sewage due to its
-filtration through the ground is the same as occurs in aërobic
-filtration. The effect on the crops is mainly that of an irrigant, as
-the manurial value of the sewage is small.
-
-
-=261. Status.=—The disposal of sewage by broad irrigation was practiced
-in England previous to the development of any of the more intensive
-biologic methods of treatment. It was considered the only safe and
-sanitary method for the disposal of sewage, and as a result, areas
-irrigated by sewage were common throughout England. Crops were grown on
-these areas as a minor consideration, and sewage farming gained some of
-its popularity from the apparent success of these disposal areas. The
-success of sewage farms is due more to generous irrigation in dry years
-than to fertilization by sewage.
-
-The sewage farms of Paris and Berlin are frequently cited as examples of
-the successful and remunerative disposal of sewage by farming in
-connection with broad irrigation. Kinnicutt, Winslow, and Pratt[169]
-state:
-
- The Berlin Sewage farms offer examples of broad irrigation under
- better conditions ... of 21,008 acres receiving sewage, 16,657
- acres were farmed by the city, 3,956 acres were leased to farmers,
- and only 395 acres were unproductive. The contributing population
- at this time was 2,064,000 and the average amount of sewage
- treated was 77,000,000 gallons, giving a daily rate of treatment
- of about 3,700 gallons per acre of prepared land. The soil is
- sandy and of excellent quality. A quarter of the area operated by
- the authorities is devoted to pasturage, and about a third to the
- cultivation of cereals, of which winter rye and oats are the most
- important. Potatoes and beets are grown in considerable amounts
- and a wide variety of other crops in smaller proportions.... Even
- fish ponds are made to yield a part of the revenue, and the drains
- on some of the farms have been successfully stocked with breed
- trout.
-
- The cost of the Berlin farms to March 31, 1910, was $17,470,000,
- somewhat more than half being the purchase price of the land. The
- expenses for this year amounted to $1,300,385 for maintenance, and
- $741,818 for interest charges. The receipts were $1,240,773 and
- there was an estimated increase of $122,593 in value of live stock
- and other property.
-
-The conditions at Berlin are quoted at length to indicate the success
-which can accompany broad irrigation, and as an example of what is being
-done abroad, where the rainfall is light and the soil is suitable.
-
-In the United States success in sewage farming has not been marked. This
-may be due partially to the relative weakness of American sewages, to
-the cost of labor, to lack of satisfactory irrigation areas, and to
-inattention to details. An attempt was made to grow crops on the sand
-filters at Brockton, Mass., but it was finally abandoned as the
-interests of the crops and the successful treatment of the sewage could
-not both be satisfied. At Pullman, Illinois,[170] in 1880, there was
-commenced probably the most extensive attempt at sewage farming in
-eastern United States. The farm was a failure from the start, because of
-the clay soil, and it was subsequently abandoned. Sewage farming, mainly
-as a subsidiary consideration to the filtration of sewage, is practiced
-in a few cities in the eastern portion of the United States to-day.
-Among the cities mentioned by Metcalf and Eddy[171] are Danbury, Conn.,
-and Fostoria, Ohio. In the western portion of the United States where
-water is scarce and the ground is porous, sewage has been used as an
-irrigant with some success. Such use of sewage cannot be considered as a
-method of treatment since the prime consideration is the growing of
-crops. In this process all sewage not used as an irrigant is discharged
-without treatment into water courses. According to Metcalf and Eddy
-there were 35 cities in California in 1914 that were operating sewage
-farms. Among these are Pasadena, Fresno, and Pomona. Other farms,
-notably the pioneer farm at Cheyenne, Wyo., have been abandoned because
-of the local nuisance created and the lack of financial success.
-
-
-=262. Preparation and Operation.=—A porous sandy soil on a good slope
-and with good underdrainage is most suitable for broad irrigation.
-Impervious clay or gumbo soils are unsuitable and should not be used.
-They become clogged at the surface, forming pools of putrefying sewage,
-or in hot weather form cracks which may permit untreated sewage to
-escape into the underdrains.
-
-The sewage may be distributed to the irrigated area in any one of five
-ways which are known as: flooding, surface irrigation, ridge and furrow
-irrigation, filtration, and subsurface irrigation. In flooding, sewage
-is applied to a level area surrounded by low dikes. The depth of the
-dose may be from 1 inch to 2 feet. In surface irrigation the sewage is
-allowed to overflow from a ditch over the surface of the ground into
-which it sinks or over which it flows into another ditch placed lower
-down. This ditch conducts it to a point of disposal or to another area
-requiring irrigation. Ridge and furrow irrigation consists in plowing a
-field into ridges and furrows and filling the furrows with sewage while
-crops are grown on or between the ridges. In filtration the sewage is
-distributed in any desired fashion on the surface and is collected by a
-system of underdrains after it has filtered through the soil. In
-subsurface irrigation the sewage is applied to the land through a system
-of open-joint pipes laid immediately below the surface, similarly to a
-system of underdrains. Combinations of and modifications to these
-methods are sometimes made. Underdrains may be used in connection with
-any of these forms of distribution.
-
-The preparation of the ground consists in: the construction of ditches
-or dikes to permit of any of the above described methods of application,
-grading of the surface to prevent pooling, the laying of underdrains,
-and the grubbing and clearing of the land. The main carriers may be
-excavated in open earth or earth lined with an impervious material. The
-distribution of the sewage from the main carriers to groups of laterals
-may be controlled by hand-operated stop planks. If the soil has a
-tendency to become waterlogged it may be relieved by installing
-underdrains at depths of 3 to 6 feet, and 40 to 100 feet apart. The tile
-underdrains may discharge into open ditches excavated for the purpose
-which serve also to drain the land. Drains should be used where the
-ground water is within 4 feet of the surface, and the open ditches
-should be cut below the drains to keep the ground water out of them.
-Four or 6–inch open-joint farm tile may be used for underdrains. The
-porosity of the soil will be increased by cultivation. Where particular
-care is taken in the cultivation of the soil so that sewage can be
-applied at a high rate, broad irrigation merges into the more intensive
-intermittent filtration through sand.
-
-Before being turned on to the land, sewage should be screened and
-heavy-settling particles should be removed. The rate of application may
-be increased as the intensity of the preliminary treatment is increased.
-The rate at which sewage may be applied is dependent also on the
-character of the soil, and may vary between 4,000 and 30,000 gallons per
-acre per day, although higher rates have been used with the effluent
-from treatment plants and on favorable soil. The sewage should be
-applied intermittently in doses, the time between doses varying between
-one day and two or three weeks or more, dependent on the weather and the
-condition of the soil. The methods of dosing vary as widely as the
-rates. The dose may be applied continuously for one or two weeks with
-correspondingly long rests, or it may be applied with frequent
-intermittency alternated with short rests, interspersed with long rest
-periods at longer intervals of time. When applying the sewage to the
-land the rate of application of the dose is about 10,000 to 150,000
-gallons per acre per day. The area under irrigation at any one time may
-be as much as 10 to 15 acres. The rate of the application of the sewage
-is also dependent on the weather and may vary widely between seasons. It
-is obvious that a rain-soaked pasture cannot receive a large dose of
-sewage without danger of undue flooding. One of the principal
-difficulties with the treatment or disposal of sewage by broad
-irrigation is that the greatest load of sewage must be cared for in wet
-seasons when the ground is least able to absorb the additional moisture.
-
-
-=263. Sanitary Aspects.=—A well-operated sewage farm should cause no
-offense to the eye or nose, and is not a danger to the public health. In
-Berlin, a portion of the sewage farms are laid out as city parks. The
-liquid in the drainage ditches or underdrains may be clear, odorless,
-and colorless, high in nitrates and non-putrescible. Where the farm has
-been improperly managed or overdosed the condition may be serious from
-both esthetic and health considerations. Sewage may be spread out to
-pollute the atmosphere and to supply breeding places for flying insects
-which will spread the filth for long distances surrounding the farm. The
-character of the crop is also a sanitary consideration.
-
-
-=264. The Crop.=—From a sanitary viewpoint no crops which come in
-contact with the sewage should be cultivated on a sewage farm. Such
-products as lettuce, strawberries, asparagus, potatoes, radishes, etc.,
-should not be grown. Grains, fruits, and nuts are grown successfully and
-as they do not come in contact with the sewage there is no sanitary
-objection to their cultivation in this manner. Italian rye grass and
-other forms of hay are grown with the best success as they will stand a
-large amount of water without injury. The raising of stock is also
-advisable for sewage farms where hay and grain are cultivated. The stock
-should be fed with the fodder raised on the irrigated lands and should
-not be allowed to graze on the crops during the time that they are being
-irrigated. This is due as much to the danger of injury to the
-distributing ditches and the formation of bogs by the trampling of the
-cattle, as to the danger to the health of the cattle.
-
-
-
-
- CHAPTER XVIII
- ACTIVATED SLUDGE
-
-
-=265. The Process.=—In the treatment of sewage by the activated sludge
-process the sewage enters an _aëration tank_ after it has been screened
-and grit has been removed. As it enters the aëration tank it is mixed
-with about 30 per cent of its volume of activated sludge. The sewage
-passes through the aëration tank in about two to four hours during which
-time air is blown through it in finely divided bubbles. The effluent
-from the aëration tank passes to a _sedimentation tank_ where it remains
-for one-half an hour to an hour to allow the sedimentation of the
-activated sludge. The supernatant liquid from the sedimentation tank is
-passed to the point of final disposal. A portion of the sludge removed
-from the tank is returned to the influent of the aëration tank. The
-remainder may be sent to any or all of the following: the _sludge drying
-process_, the reaëration tanks, or to some point for final disposal.
-Sections of the activated sludge plant at Houston, Texas, are shown in
-Fig. 177.
-
-The biological changes in the process occur in the aëration tank. These
-changes are dependent on the aërobic organisms which are intensively
-cultivated in the activated sludge. When placed in intimate contact with
-fresh sewage, brought about by the agitation caused by the rising air,
-and in the presence of an abundance of oxygen, the organic matter is
-partially oxidized. The putrefactive stage of the organic cycle is
-avoided. Colloids and bacteria are partially removed probably by the
-agitation effected in the presence of activated sludge but the exact
-action which takes place is not well understood.
-
-[Illustration:
-
- FIG. 177.—Activated Sludge Plant at Houston, Texas.
-
- Eng. News, Vol. 77, p. 236.
-]
-
-
-=266. Composition.=—Activated sludge is the material obtained by
-agitating ordinary sewage with air until the sludge has assumed a
-flocculent appearance, will settle quickly, and contain aërobic and
-facultative bacteria in such numbers that similar characteristics can be
-readily imparted to ordinary sewage sludge when agitated with air in the
-presence of activated sludge. Copeland described activated sludge as
-follows:[172]
-
- The sludge embodied in sewage and consisting of suspended organic
- solids, including those of a colloidal nature, when agitated with
- air for a sufficient period assumes a flocculent appearance very
- similar to small pieces of sponge. Aërobic and facultative
- bacteria gather in these flocculi in immense numbers—from 12 to 14
- million per c.c.—some having been strained from the sewage and
- others developed by natural growth. Among the latter are species
- that have the power to decompose organic matter, especially of an
- albuminoid or nitrogenous nature, setting the nitrogen free; and
- others absorbing the nitrogen convert it into nitrites and
- nitrates. These biological processes require time, air, and
- favorable environment such as suitable temperature, food supply
- and sufficient agitation to distribute them throughout all parts
- of the sewage.
-
-Ardern states that the sludge differs entirely from the usual tank
-sludge. It is inoffensive and flocculent in character. The percentage of
-moisture is from 95 to 99 per cent. American experience has generally
-been that the sludge does not readily separate from its moisture by
-treatment on fine-grain filters, but the results in England and at
-Milwaukee, Wisconsin, are in conflict with this general experience. Upon
-standing 24 hours or more partially dried activated sludge may start to
-decompose accompanied by the production of offensive odors.
-
-Duckworth states:
-
- The activated sludge at Salford contained three times as much
- nitrogen, twice as much phosphoric acid and one-half as much fatty
- matter as ordinary sludge.
-
- TABLE 91
-
- COMPOSITION OF SEWAGE, IMHOFF SLUDGE, AND ACTIVATED SLUDGE AND EFFLUENT AT
- MILWAUKEE
-
- (W. R. Copeland, Eng. News, Vol. 76, p. 665)
- ──────┬──────────┬────────────────────────────────────────────────────────────
- Period│Source of │ Parts per Million
- of │ Sample │
- Test │ │
- ──────┼──────────┼──────┬──────────────────────────────────────┬──────────────
- │ │ Sus- │ Nitrogen as │Nitrogen
- │ │pended│ │ Reported as
- │ │Matter│ │ Ammonia on a
- │ │ │ │ Basis of
- │ │ │ │ Sludge Dried
- │ │ │ │ to 10 Per
- │ │ │ │ Cent
- │ │ │ │ Moisture.
- │ │ │ │ Three
- │ │ │ │ samples of
- │ │ │ │ Sludge
- ──────┼──────────┼──────┼───────┬───────┬────────┬──────┬──────┼──────────────
- │ │ │ Free │ Albu- │Organic │ Ni- │ Ni- │
- │ │ │Ammonia│minoid │Nitrogen│trites│trates│
- │ │ │ │Ammonia│ │ │ │
- ──────┼──────────┼──────┼───────┼───────┼────────┼──────┼──────┼────┬────┬────
- Aug., │Sewage │ 253│ 14.6│ 7.88│ 29│ 0.15│ 0.13│ │ │
- 1915│ │ │ │ │ │ │ │ │ │
- │Imhoff │ 105│ 16.2│ 6.10│ 27│ 0.19│ 0.13│2.87│3.82│
- │ effluent│ │ │ │ │ │ │ │ │
- │Activated │ 14│ 3.8│ 3.19│ 6│ 0.29│ 6.00│5.71│4.97│7.04
- │ sludge │ │ │ │ │ │ │ │ │
- │ effluent│ │ │ │ │ │ │ │ │
- ──────┼──────────┼──────┼───────┼───────┼────────┼──────┼──────┼────┼────┼────
- Sept.,│Sewage │ 300│ 13.5│ 8.81│ 29│ 0.25│ 0.14│ │ │
- 1915│ │ │ │ │ │ │ │ │ │
- │Imhoff │ 116│ 15.4│ 7.10│ 27│ 0.12│ 0.09│3.88│ │
- │ effluent│ │ │ │ │ │ │ │ │
- │Activated │ 8│ 5.7│ 2.22│ 9│ 0.24│ 5.01│8.69│9.00│
- │ sludge │ │ │ │ │ │ │ │ │
- │ effluent│ │ │ │ │ │ │ │ │
- ──────┴──────────┴──────┴───────┴───────┴────────┴──────┴──────┴────┴────┴────
-
-These results have been roughly checked by American experimenters as
-shown in Table 91.[173] In the recovery of nitrogen from sewage the
-activated sludge process is the most promising for satisfactory results.
-In all other processes of sewage treatment the sludge is digested to
-some extent and nitrogen lost in the gases or in the soluble matter
-which passes off with the effluent. In the activated sludge process a
-negligible amount of gasification and liquefaction take place and only a
-small amount of nitrogen passes off with the effluent as compared with
-the loss from the Imhoff process as shown in Table 91. The percentage of
-nitrogen in dried activated sludge is shown in Table 92.
-
- TABLE 92
-
- NITROGEN CONTENT OF DRY ACTIVATED SLUDGE AND SLUDGE FROM OTHER
- PROCESSES
-
- (G. W. Fuller, Eng. News, Vol. 76, p. 667)
- ────────────────────────────────────────┬──────────────────────────────
- Source │ Per Cent Nitrogen
- ────────────────────────────────────────┼──────────────────────────────
- Milwaukee (Copeland) │ 4.40
- Manchester, England (Ardern) │ 4.60
- Salford, England (Melling) │ 3.75
- Urbana, Illinois (Bartow) │ 3.5 to 6.4
- Armour and Co. (Noble) │ 4.6
- Approximate range of all other processes│ 1.0 to 3.0
- ────────────────────────────────────────┴──────────────────────────────
- These figures are expressed in terms of nitrogen and not of ammonia.
- Nitrogen is only 82 per cent of the ammonia content.
-
-Nitrifying bacteria and other species which have the power of destroying
-organic matter have been isolated from the sludge. An analysis of the
-dried sludge at Urbana[174] showed the following results after the
-weight had been reduced 95.5 per cent by drying: 6.3 per cent nitrogen,
-4.00 per cent fat, 1.44 per cent phosphorus, and 75 per cent volatile
-matter or loss on ignition. Analyses of other domestic sewages have not
-shown such high contents of these desirable constituents.
-
-The dewatering of activated sludge is a problem which offers serious
-obstacles to the successful operation of the process. It is its greatest
-disadvantage. Five to ten times the volume of sludge may be produced by
-the activated sludge process as by an Imhoff tank, and the activated
-sludge contains a greater percentage of water. According to Copeland:
-
- The best information now available points to a combination of
- settling and decantation as a preliminary dewatering process. By
- this means the water will be cut down from about 99 per cent to 96
- per cent. On passing the concentrated residue through a pressure
- filter the moisture can be cut down to 75 per cent. The press cake
- can be dewatered in a heat drier to 10 per cent moisture or
- less.[175]
-
-The quantity of sludge produced at Milwaukee[176] is about 15 cubic
-yards per million gallons of sewage, the sludge having about 98 per cent
-moisture. On the basis of 10 per cent moisture it produces ½ ton of dry
-sludge per million gallons of sewage treated. At Cleveland,[177] 20
-cubic yards per million gallons at 97.5 per cent moisture are produced.
-Methods of drying sludge are discussed in Chapter XX.
-
-Chemical analyses and biological tests indicate that the fertilizing
-value of the sludge is appreciable. Professor C. B. Lipman states, as
-the result of a series of tests in which a sludge and a soil were
-incubated for one month, as follows:[178]
-
- The amounts of nitrates produced in one month’s incubation from
- the soil’s own nitrogen and from the nitrogen from the sludge
- mixed with the soil in the ratio of one part of sludge to 100 of
- soil is, in milligrams of nitrate, as follows: Anaheim soil
- without sludge 6.0, with sludge 10.0; Davis soil without sludge
- 4.2, with sludge 14.0; Oakley soil without sludge 2.2, with sludge
- 4.0.
-
-The effect of the sludge on plant growth is shown in Table 93.[179] The
-results represent the growth obtained after fifteen weeks from the
-planting of 30 wheat seeds in each pot.
-
-
-=267. Advantages and Disadvantages.=—Some of the advantages of the
-process are: a clear, sparkling, and non-putrescible effluent is
-obtained; the degree of nitrification is controllable within certain
-limits; the character of the effluent can be varied to accord with the
-quantity and character of the diluting water available; more than 90 per
-cent of the bacteria can be removed; the cost of installation is
-relatively low; and the sludge has some commercial value.
-
- TABLE 93
-
- FERTILIZING VALUE OF ACTIVATED SLUDGE
-
- (E. Bartow, Journal Am. Water Works Ass’n, Vol. 3, p. 327)
- ───────────────────────────────────────┬───────────────────────────────
- Cultivating Medium │Grams Contained in Experimental
- │ Pot
- ───────────────────────────────────────┼───────┬───────┬───────┬───────
- │ 1 │ 2 │ 3 │ 4
- ───────────────────────────────────────┼───────┼───────┼───────┼───────
- White sand │ 19,820│ 19,820│ 19,820│ 19,820
- Dolomite │ 60│ 60│ 60│ 60
- Bone meal │ 6│ 6│ 6│ 6
- Potassium sulphate │ 3│ 3│ 3│ 3
- Activated sludge │ 0│ 0│ 20│ 0
- Activated sludge extracted with Ligroin│ 0│ 0│ 0│ 20
- Dried blood │ 0│ 8.61│ 0│ 0
- ───────────────────────────────────────┼───────┼───────┼───────┼───────
- Number of heads of wheat │ 14│ 15│ 22│ 23
- Number of seeds │ 85│ 189│ 491│ 518
- Weight of seeds, grams │ 2.38│ 5.29│ 13.748│ 14.504
- Bushels per acre, calculated │ 6.20│ 13.6│ 35.9│ 38.7
- Average length of stalk, inches │ 19.40│ 23.0│ 35.4│ 37.1
- Weight of straw, grams │ 2.25│ 8.25│ 26.75│ 26.21
- Tons per acre, calculated │ 0.18│ 0.68│ 2.23│ 2.18
- ───────────────────────────────────────┴───────┴───────┴───────┴───────
-
-Among the disadvantages of the process can be included, uncertainty due
-to the lack of information concerning the results to be expected under
-all conditions, high cost of operation under certain conditions, the
-necessity for constant and skilled attendance, and the difficulty of
-dewatering the sludge.
-
-
-=268. Historical.=—The most notable work in the aëration of sewage
-within recent years was that performed by Black and Phelps for the
-Metropolitan Sewerage Commission of New York, in 1910,[180] and by Clark
-and Gage at the Lawrence, Massachusetts, Sewage Experiment Station in
-1912 and 1913.[181] The results of these investigations showed that the
-treatment of sewage by forced aëration might give a satisfactory
-effluent, but that the time and expense in connection thereto rendered
-the method impractical.
-
-It remained for Messrs. Ardern and Lockett of Manchester, England, to
-introduce the process of the aëration of sewage in the presence of
-activated sludge, as a result of their connection with Dr. Fowler, who
-attributes his inspiration to his visit to the Lawrence Experiment
-Station and observing the work of Clark and Gage. Ardern and Lockett
-commenced their experiments in 1913. Their results were published in the
-_Journal of the Society of Chemical Industry_, May 30, 1914, Vol. 33, p.
-523. Shortly thereafter experiments were started at the University of
-Illinois by Dr. Edw. Bartow and Mr. F. W. Mohlmann of the Illinois State
-Water Survey. At about the same time an experimental plant was started
-at Milwaukee, by T. C. Hatton, Chief Engineer of the Milwaukee Sewerage
-Commission. The United States Public Health Service became actively
-interested in December, 1914, and on February 20, 1915, announced its
-intention to co-operate with the Baltimore Sewerage Commission in the
-conduct of experiments. In May, 1915, patent number 1,139,024 was
-granted to Leslie C. Frank, Sanitary Engineer of the U. S. Public Health
-Service, covering certain features of the process. Mr. Frank generously
-donated this patent to the public for the use of municipalities.
-
-The first full sized plant for the treatment of sewage by this method
-was erected in Milwaukee in December, 1915. This plant had a capacity of
-1,600,000 gallons per day. It was used for experimental purposes and is
-not now in use. The Champaign, Illinois, septic tank, among the first of
-its kind in the country, was converted into an activated sludge tank on
-April 13, 1916. The changes, developments, and the results obtained from
-these and other plants have been reported in the technical press from
-time to time.
-
-
-=269. Aëration Tank.=—The sewage on leaving the screen and grit chamber
-enters the aëration tank, which is usually operated on the
-continuous-flow principle, although in the early days of experimentation
-the fill and draw method was practiced. This tank should be rectangular
-with a depth of about 15 feet and a width of channel not to exceed 6 to
-8 feet. Such proportions allow better air and current distribution than
-larger tanks. The bottom should be level to insure an even distribution
-of air. The velocity of flow of sewage through the tank is usually in
-the neighborhood of 5 feet per minute, dependent on the length of the
-tank and the period of retention. The period of retention is in turn
-dependent on the desired quality of the effluent. The process is
-flexible and the quality of the effluent can be changed by changing the
-period of retention or by changing the rate of application of the air,
-or both. The period of retention in the aëration tank is usually about 4
-hours.
-
-The bottom of the aëration tank is usually made of concrete arranged in
-ridges and valleys, or small shallow hoppers, at the bottom of which the
-air-diffusing devices are located, as shown in Fig. 177. The inlet and
-outlet devices are similar to those in a plain sedimentation tank.
-
-
-=270. Sedimentation Tank.=—It is evident that as no sedimentation is
-permitted in the aëration tank, the settleable particles will be
-discharged in the effluent unless some provision is made for their
-detention. The effluent from the aëration tank is therefore run through
-a plain sedimentation tank, usually with a hopper bottom, which has been
-arranged to permit frequent and easy cleaning. An air lift or a
-centrifugal sludge pump is satisfactory for this purpose. Another type
-of sedimentation tank which has been used has a smooth bottom with a
-slight slope towards the center. A revolving scraper collects the sludge
-continuously, scraping it towards the center of the tank. Although this
-arrangement gives better results than the hopper-bottom tank, its
-expense has usually prevented its installation.[182]
-
-The period of sedimentation in different plants varies from 30 minutes
-to one hour, although the longer periods usually give the better
-results. Approximately 65 per cent of the sludge will settle in the
-first 10 minutes, 80 per cent in the first 30 minutes, and about 5 per
-cent more in the next half hour.
-
-The effluent from the sedimentation tank is ready for final disposal or
-if desired, for further treatment by some other method. The sludge, or a
-portion of it, is pumped back into the influent of the aëration tank,
-provided the sludge is in a satisfactory state of nitrification.
-Otherwise it should be pumped to the reaëration tanks. The remainder of
-the sludge which is not to be used in the process is ready for drying
-and final disposal.
-
-
-=271. Reaëration Tank.=—The purpose of the reaëration or sludge aëration
-tank is to reactivate the sludge which has gone through the aëration
-tank. During the process of the aëration of the sewage in the aëration
-tank the activated sludge may lose some of its qualities because of the
-deficiency of oxygen to maintain aërobic conditions. By blowing air
-through the sludge in the reaëration tank these properties are returned
-and the sludge made available to be pumped back into the aëration tank.
-The reactivation of the sludge obviates the necessity for supplying
-sufficient air to the entire mass of the sewage to maintain aërobic
-conditions, and results in an economy in the use of air. The use of
-mechanical agitators has also been attempted both in the reaëration and
-the aëration tanks with the expectation of saving in the use of air, but
-with indifferent success.
-
-It is difficult to say, without experimentation, what the size of the
-reaëration tank should be, as the necessary amount or reactivation is
-uncertain. In the experimental plant at Milwaukee, there were eight
-units of aëration tanks, one sedimentation tank, and two reaëration
-tanks, all of the same capacity and general design. This represents a
-ration of about one reaëration tank to four aëration tanks.
-
-
-=272. Air Distribution.=—Air is applied to the sewage at the bottom of
-the aëration tank at a pressure in the neighborhood of 5.5 to 6.0 pounds
-per square inch, dependent on the depth of the sewage, the loss of head
-through the distributing pipes, and the rate of application. In
-different experimental plants the pressure has varied from 3 to 30
-pounds per square inch. Such pressures are on the line which divides the
-use of direct blowers for low pressures from turbo and reciprocating
-pressure machines for pressures above 10 pounds per square inch.
-Positive-pressure blowers or direct blowers operate on the principle of
-a centrifugal pump and because of the lighter specific gravity of air
-they rotate at a very high speed. The Nash Hytor Turbo Blower consists
-of a rotor with a large number of long teeth slightly bent in the
-direction of rotation. The rotor, which has a circular circumference,
-revolves in an elliptical casing. At the commencement of operation the
-rotor and casing are partially filled with water. The revolution of the
-rotor throws the water to the outside of the elliptical casing thus
-forming a partial vacuum between any two teeth as the water is thrown
-from near the center of the short diameter of the casing to the
-extremity of the long diameter of the casing. Air is allowed to enter
-through the inlet port to relieve the vacuum. As the teeth pass from the
-long diameter to the short diameter of the ellipse, the water again
-approaches the center of the rotor compressing the air trapped between
-the teeth and forcing it out under pressure into the exhaust pipe. Among
-the advantages of this compressor are the washing of the air, cooling,
-and ease in operation. Reciprocating air compressors operate similarly
-to direct-acting steam pumps or crank-and-fly-wheel pumps but at much
-higher speeds, and they require more floor space than either of the
-other types. Fig. 178 shows the field of serviceability of various types
-of air compression machinery.
-
-[Illustration:
-
- FIG. 178.—Economic Range of Air Compressors.
-
- From Eng. News, Vol. 74, p. 906.
-]
-
-For pressures up to about 10 pounds per square inch the positive blower
-seems most desirable. It has a low first cost and a relatively high
-efficiency of about 75 to 80 per cent of the power input. No oil or dirt
-is added to the air to clog the distributing plates, as in the
-reciprocating machine. A disadvantage is the difficulty of varying the
-pressure or quantity of the output of the machine. As the required
-pressure and volume of air increases the turbo blower becomes more and
-more desirable within the limits of pressure which are ordinarily used
-in this process. For small installations the best form of power is
-probably the electric drive, but when the capacity becomes such as to
-make turbo blowers advisable they should be driven by directly connected
-steam turbines.
-
-The quantity of air required varies between 0.5 to 6.0 cubic feet per
-gallon of sewage, with from 3 to 6 hours of aëration. The quantity of
-air depends on the degree of treatment required, the strength of the
-sewage, the depth of the tank, and the period of aëration. The deeper
-the tank the less the amount of air needed because of the greater travel
-of the bubble in passing through the sewage, but the higher the pressure
-at which the air must be delivered. Shallow tanks usually require a
-longer period of retention. The depth of the tank then has very little
-to do with economy in the use of air. Hatton states:[183]
-
- The purification of sewage obtained varies decidedly with the
- volume of air applied. Small volumes applied for 5 or 6 hours do
- as well as larger volumes applied for 3 or 4 hours, but the time
- of aëration required to obtain a like effluent does not vary
- directly with the volume of air applied per unit of time. For
- instance air applied at a rate of 2 cubic feet per minute purifies
- the sewage in less time than one cubic foot of air per minute, but
- will not accomplish an equal degree of purification in half the
- time.
-
-It has been found that although a low temperature has a deleterious
-effect on the process, by the use of an additional quantity of air good
-results can be maintained. The effect of changing the quantity of air
-and the period of aëration are shown in Table 94 taken from Hatton.
-
-The velocity of the air in the pipes should be about 1,000 feet per
-minute. There should be relatively few sharp turns in the line, and the
-distributing mains should be arranged without dead ends. It is desirable
-to use as little piping as possible and at the same time to make the
-travel of the sewage long in order to maintain a non-settling velocity
-and intimate contact with the air. The piping should be accessible and
-well provided with valves. It should be non-corrodible, particularly on
-the inside, as flakes of rust will quickly clog the air diffusers. It
-should drain to one point in order that it can be emptied when flooded,
-as occasionally happens.
-
- TABLE 94
-
- EFFECT OF VARIOUS RATES AND PERIODS OF APPLICATION OF AIR ON THE RESULTS
- OBTAINED FROM THE TREATMENT OF SEWAGE BY THE ACTIVATED SLUDGE PROCESS
-
- (Milwaukee Results)
-
- ─────────┬──────┬──────┬──────────┬────────
- Time of │Cubic │Cubic │Appearance│Per Cent
- Aëration,│ Feet │ Feet │of Settled│Removal
- Hours │ Free │ Air │ Liquid │Bacteria
- │ Air │ per │ │
- │ Per │Gallon│ │
- │Minute│ of │ │
- │ │Sewage│ │
- ─────────┼──────┼──────┼──────────┼────────
- │ │ │ │
- │ │ │ │
- ─────────┼──────┼──────┼──────────┼────────
- │ │ │ │
- │ │ │ │
- ─────────┼──────┼──────┼──────────┼────────
- 0│ 0│ 0.0│ Turbid │ 0
- 1│ 160│ 0.67│ Clear │ 52
- 2│ 160│ 1.32│ Clear │ 81
- 3│ 160│ 1.98│ Clear │ 92
- 4│ 160│ 2.64│ Clear │ 94
- 5│ 160│ 3.31│ Clear │ 98
- 2.5│ 90│ 1.07│ │ 92
- 3│ 90│ 1.28│ │ 96
- 4│ 90│ 1.71│ │ 98
- 4│ 80│ 1.82│ │ 97.7
- 4│ 70│ 1.60│ │ 99.6
- 4│ 46│ 1.67│ │ 88.3
- 4│ 105│ 1.75│ │ 92.7
- 3│ 140│ 1.75│ │ 91.2
- 2.5│ 168│ 1.74│ │ 96.7
- │ │ 1.80│ │ 98.1
- │ │ 1.53│ │ 99
- │ │ 1.12│ │ 91
- ─────────┴──────┴──────┴──────────┴────────
-
- ─────────┬─────────────────────────────────────────────────────┬──────────
- Time of │ Parts per Million │Stability,
- Aëration,│ │ Hours
- Hours │ │
- │ │
- │ │
- │ │
- │ │
- ─────────┼─────────────────────────────────┬─────────┬─────────┼──────────
- │ Nitrogen as │Dissolved│Suspended│
- │ │ Oxygen │ Matter │
- ─────────┼───────┬────────┬────────┬───────┼─────────┼─────────┼──────────
- │ Free │Nitrites│Nitrates│Organic│ │ │
- │Ammonia│ │ │ │ │ │
- ─────────┼───────┼────────┼────────┼───────┼─────────┼─────────┼──────────
- 0│ 22│ 0.08│ 0.08│ │ 0.00│ │ 000
- 1│ 17│ 0.00│ 0.04│ │ 0.30│ │ 2
- 2│ 15│ 0.95│ 0.70│ │ 1.90│ │ 33
- 3│ 11│ 1.75│ 2.80│ │ 4.30│ │ 120
- 4│ 7│ 2.20│ 5.60│ │ 5.90│ │ 120
- 5│ 5│ 2.50│ 8.20│ │ 6.70│ │ 120
- 2.5│ 11│ 0.05│ 2.00│ │ │ │ 69
- 3│ 9.9│ 0.12│ 2.9│ │ │ │ 95
- 4│ 1.8│ 0.14│ 5.2│ │ │ │ 120
- 4│ 1.95│ 0.08│ 8.5│ │ │ │ 120
- 4│ 5.79│ 0.14│ 9.0│ │ │ │ 120
- 4│ 7.90│ 0.02│ 2.0│ │ │ │ 61
- 4│ 4.86│ 0.36│ 4.9│ │ │ │ 120
- 3│ 9.39│ 0.60│ 3.0│ │ │ │ 120
- 2.5│ 11.2│ 0.36│ 1.1│ │ │ │ 84
- │ │ │ 8.5│ 4│ │ 11│ 120
- │ 5.79│ │ 9.0│ 8│ │ 9│ 120
- │ 10.1│ │ 2.3│ 14│ │ 42│ 73
- ─────────┴───────┴────────┴────────┴───────┴─────────┴─────────┴──────────
-
- TABLE 95
-
- COMPARATIVE RESULTS FROM THE AËRATION OF SEWAGE IN THE PRESENCE OF
- ACTIVATED SLUDGE WITH THE USE OF DIFFERENT DISTRIBUTING MEDIA
-
- (T. C. Hatton, Eng. Record, Vol. 73, p. 255)
- ─────────────┬──────────┬────────┬────────┬────────┬─────────┬─────────
- Diffusers │Months in │ Pounds │ Air, │Per Cent│Nitrates,│Stability
- │ 1915 │ per │ Cubic │Bacteria│Parts per│Effluent
- │ │ Square │Feet per│Removed │ Million │in Hours
- │ │ Inch │ Gallon │ │ │
- ─────────────┼──────────┼────────┼────────┼────────┼─────────┼─────────
- Filtros plate│June 1 to│ 4.3│ 2.06│ 91│ 3.4│ 78
- │ Aug. 15 │ │ │ │ │
- Air jet │June 1 to│ 3.5│ 1.94│ 91│ 2.2│ 52
- │ Aug. 15 │ │ │ │ │
- Filtros plate│Nov. 18 to│ 4.6│ 1.71│ 90│ 0.3│ 113
- │ Dec. 7 │ │ │ │ │
- Monel metal │Nov. 18 to│ 3.0│ 1.71│ 80│ 0.2│ 63
- │ Dec. 7 │ │ │ │ │
- ─────────────┴──────────┴────────┴────────┴────────┴─────────┴─────────
-
-It is desirable to diffuse the air in small bubbles as by this means the
-greatest efficiency seems to be obtained from the amount of air added. A
-diameter 1/16 to ⅛ of an inch is approximately the maximum limit for the
-size of an effective bubble. Monel metal cloth, porous wood blocks, open
-jets, paddles, and other forms of diffusers have been tried, but none
-have given the satisfaction of the filtros plate. The relative value of
-different types of diffusers is shown in Table 95 taken from
-Hatton.[184] The Filtros plates are a proprietary article manufactured
-by the General Filtration Company of Rochester, N. Y. They are made of a
-quartz sand firmly cemented together and can be obtained with
-practically any degree of porosity, size of pore opening or dimension of
-plate, but they are made in a standard size 12 inches square by 1½
-inches thick. The frictional loss through the plate is not very great
-for the amount of air ordinarily used. The plates are classified in
-accordance with the volume of air which will pass through them, when
-dry, per minute when under a pressure of 2 inches of water. These
-classes run from ½ to 12 cubic feet of air per minute. The type usually
-specified passes about 2 cubic feet of air per minute. The loss of head
-through these plates as tested at Milwaukee showed an initial loss of ¾
-of a pound and an additional loss of about ¼ of a pound for every cubic
-foot of air per minute per square foot of surface. It is necessary to
-screen and wash the air before blowing it through the filtros plate as
-ordinary air is so filled with dirt as to clog the pores of the diffuser
-quite rapidly.
-
-The area of filtros plates required in the bottom of the tank is usually
-expressed in terms of the free surface of the tank or as a ratio
-thereto. In the Urbana tests the best ratio was found to be less than 1
-: 3 and more than 1 : 9. In Milwaukee[185] the ratio adopted is in the
-neighborhood of 1 : 4 or 1 : 5. At Fort Worth the ratio will be about 1
-: 7 and at Chicago it will be 1 : 8. The exact ratio should be
-determined by experiment and will depend on the construction of the tank
-and the character of the raw sewage and the desired effluent. It is
-essential that the filtros plates be placed level and at the same
-elevation as otherwise the distribution of air will be uneven.
-
-
-=273. Obtaining Activated Sludge.=—After a plant is once started
-activated sludge is generated during the process of treatment and with
-careful management a stock of activated sludge can be kept on hand. When
-a plant is new, or if shut down for such a length of time that the
-sludge loses its activation, it is necessary to activate some new
-sludge. This is done by blowing air continuously through sewage either
-on the fill and draw method with periodic decantations of the
-supernatant liquid, or by the continuous-flow process, but more
-preferably by the latter. Where activated sludge is to be obtained from
-fresh sewage alone the time required is in the neighborhood of 10 to 14
-days, and purification begins at the start. An estimate of the quantity
-which will be obtained can not be made with accuracy. After the initial
-quantity of sludge has been obtained activated sludge can be maintained
-during the process of aëration of the raw sewage, or by means of the
-reaëration tanks previously described.
-
-The volume of activated sludge present in the aëration tank should be
-about 25 per cent of the volume of the tank. The volume of the sludge is
-measured in a somewhat arbitrary manner as the amount by volume which
-will settle in 30 minutes in an ordinary test tube. It is found that
-this is almost 90 per cent of the solids settling in 4 to 6 hours.
-
-
-=274. Cost.=—The available information on the cost of the activated
-sludge process is meager and unreliable. The factors entering into the
-cost are: the price of fuel, the size of the plant, the period of
-sedimentation, the amount of air per gallon of sewage, the air pressure,
-and the percentage of sludge to be aërated in the mixture. In
-Milwaukee[186] the cost of construction is estimated at $44,000 per
-million gallons, and $4.75 per million gallons for operation. At
-Houston, Texas, the cost is estimated at $24,000 per million gallons,
-exclusive of the sludge drying plant, which may cost $40,000 per million
-gallons. At Milwaukee, the cost of pressing the sludge is $4.82 per dry
-ton and of drying is $3.93 per dry ton. The sludge may be sold at the
-normal rate of $2.50 per unit of nitrogen. Based on the normal value the
-evident profit will be $3.75 per ton. The net cost of disposing of
-Milwaukee sewage is estimated at $9.64 per million gallons of which
-$4.89 is chargeable to overhead and $4.75 to repairs, operation and
-renewal. In a comparison of the costs of activated sludge and Imhoff
-tanks with sprinkling filters,[187] the information given by Eddy has
-been summarized in Table 96. In comparing the relative areas required
-for different methods of sewage treatment, activated sludge should be
-allowed about 15 million gallons per acre per day on the basis of
-aëration tanks 15 feet deep. This figure represents approximately the
-gross area of the plants at Milwaukee and at Cleveland.
-
- TABLE 96
-
- COMPARATIVE COSTS OF ACTIVATED SLUDGE, AND OF IMHOFF TANKS FOLLOWED BY
- SPRINKLING FILTERS
-
- (H. P. Eddy, Eng. Record, Vol. 74, p. 557)
- ─────────────┬─────────────┬─────────────┬─────────────────────────────
- Process │ First Cost │Operation per│Total Annual Cost at 4 Per
- │ per Million │ Million │ Cent with Sinking Fund at
- │ Gallons, │ Gallons, │ 2.5 Per Cent per
- │ Dollars │ Dollars │
- ─────────────┼─────────────┼─────────────┼──────────────┬──────────────
- │ │ │ Million │ Capita,
- │ │ │ Gallons, │ Dollars
- │ │ │ Dollars │
- ─────────────┼─────────────┼─────────────┼──────────────┼──────────────
- Activated │ 57,100│ 20.00│ 29.85│ 1.09
- sludge │ │ │ │
- Imhoff tank │ 78,500│ 8.50│ 21.84│ 0.80
- and │ │ │ │
- sprinkling │ │ │ │
- filter │ │ │ │
- ─────────────┴─────────────┴─────────────┴──────────────┴──────────────
-
-
- REFERENCES AND BIBLIOGRAPHY ON ACTIVATED SLUDGE
-
-The following abbreviations will be used: A.S. for Activated Sludge,
-E.C. for Engineering and Contracting, E.N. for Engineering News, E.R.
-for Engineering Record, E.N.R. for Engineering News-Record, p. for page,
-and V. for volume.
-
- No.
-
- 1. Cooperation Sought in Conducting A.S. Experiments at Baltimore, by
- Franks and Hendrick. E.R. V. 71, 1915, pp. 521, 724, and 784. V.
- 72, 1915, pp. 23, and 640.
-
- 2. Sewage Treatment Experiments with Aëration and A.S., by Bartow and
- Mohlman. E.N. V. 73, 1915, p. 647, and E.R. V. 71, 1915, p. 421.
-
- 3. A.S. Experiments at Milwaukee, Wisconsin, by Hatton. E.N. V. 74,
- 1915, p. 134.
-
- 4. A.S. in America, An Editorial Survey, by Baker. E.N. V. 74, 1915,
- p. 164.
-
- 5. Choosing Air Compressors for A.S., by Nordell, E.N. V. 74, 1915, p.
- 904.
-
- 6. A Year of A.S. at Milwaukee, by Fuller. E.N. V. 74, 1915, p. 1146.
-
- 7. A.S. Experiments at Urbana. E.N. V. 74, 1915, p. 1097.
-
- 8. Experiments on the A.S. Process, by Bartow and Mohlman. E.C. V. 44,
- 1915, p. 433.
-
- 9. Milwaukee’s A.S. Plant, the Pioneer Large Scale Installation, by
- Hatton. E.R. V. 72, 1915, p. 481 and E.C. V. 44, 1915, p. 322.
-
- 10. A.S. Experiments at Milwaukee, by Hatton. Journal American
- Waterworks Association and Proceedings Illinois Society of
- Engineers, 1916. Also E.R. V. 73, 1916, p. 255. E.C. V. 45, 1916,
- p. 104, and E.N. V. 75, 1916, pp. 262 and 306.
-
- 11. A.S. Defined. E.N. V. 75, 1916, p. 503, and E.N.R. V. 80, 1918, p.
- 205.
-
- 12. Status of A.S. Sewage Treatment, by Hammond. E.N. V. 75, 1916, p.
- 798.
-
- 13. Trial A.S. Unit at Cleveland, by Pratt. E.N. V. 75, 1916, p. 671.
-
- 14. Air Diffuser Experience with A.S. E.N. V. 76, 1916, p. 106.
-
- 15. Nitrogen from Sewage Sludge, Plain and Activated, by Copeland,
- Journal American Chemical Society, Sept. 28, 1916. E.N. V. 76,
- 1916, p. 665. E.R. V. 74, 1916, p. 444.
-
- 16. Tests Show A.S. Process Adapted to Treatment of Stock Yards Wastes.
- E.R. V. 74, 1916, p. 137.
-
- 17. Aëration Suggestions for Disposal of Sludge, by Hammond. Journal
- American Chemical Society, Sept. 25, 1916. E.R. V. 74, 1916, p.
- 448.
-
- 18. Cost Comparison of Sewage Treatment. Imhoff Tank and Sprinkling
- Filters vs. A.S., by Eddy. E.R. V. 74, 1916, p. 557.
-
- 19. Large A.S. Plant at Milwaukee. E.N. V. 76, 1916, p. 686.
-
- 20. A.S. Novelties at Hermosa Beach, Cal. E.N. V. 76, 1916, p. 890.
-
- 21. A.S. Experiments at University of Illinois, by Bartow, Mohlman, and
- Schnellbach. E.N. V. 76, 1916, p. 972.
-
- 22. A.S. Results at Cleveland Reviewed, by Pratt and Gascoigne. E.N. V.
- 76, 1916, pp. 1061 and 1124.
-
- 23. Sewage Treatment by Aëration and Activation, by Hammond.
- Proceedings American Society Municipal Improvements, 1916.
-
- 24. A.S., by Bartow and Mohlman, Proceedings Illinois Society of
- Engineers, 1916.
-
- 25. The Latest Method of Sewage Treatment, by Bartow. Journal American
- Waterworks Association, V. 3, March, 1916, p. 327.
-
- 26. Winter Experiences with A.S., by Copeland. Journal American Society
- of Chemical Engineers, April 21, 1916. E.C. V. 45, 1916, p. 386.
-
- 27. A.S. Process Firmly Established, by Hatton. E.R. V. 75, 1917, p.
- 16.
-
- 28. Operate Continuous Flow A.S. Plant, by Bartow, Mohlman, and
- Schnellbach. E.R. V. 75, 1917, p. 380.
-
- 29. Chicago Stock Yards Sewage and A.S., by Lederer. Journal American
- Society of Chemical Engineers, April 21, 1916. E.C. V. 45, 1916,
- p. 388.
-
- 30. The Patent Situation Concerning A.S. E.C. V. 45, 1916, p. 208.
-
- 31. “Sewage Disposal” by Kinnicutt, Winslow, and Pratt, published by
- John Wiley & Sons. 2d Edition, Chapter 12.
-
- 32. A.S. Tests Made by California Cities. E.N.R. V. 79, 1917, p. 1009.
-
- 33. Conclusions on the A.S. Process at Milwaukee. Journal American
- Public Health Association, 1917. E.N.R. V. 79, 1917, p. 840.
-
- 34. Dewatering A.S. at Urbana, by Bartow. Journal American Institute of
- Chemical Engineers, 1917. E.N.R. V. 79, 1917, p. 269.
-
- 35. Milwaukee Air Diffusion Studies in A.S. E.N.R. V. 78, 1917, p. 628.
-
- 36. A.S. Bibliography (up to May 1, 1917) by J. E. Porter.
-
- 37. Air Diffusion in A.S. E.N.R. V. 78, 1917, p. 255.
-
- 38. A.S. Plant at Houston, Texas. E.N. V. 77, 1917, p. 236, E.N.R. 83,
- 1919, p. 1003, and V. 84, 1920, p. 75.
-
- 39. A.S. Power Costs, by Requardt. E.N. V. 77, 1917, p. 18.
-
- 40. A.S. at San Marcos, Texas, by Elrod. E.N. V. 77, 1917, p. 249.
-
- 41. Filtros Plates Made the Best Showing in Air Diffuser Tests. E.N.R.
- V. 79, 1917, p. 269.
-
- 42. Results of Experiments on A.S., by Ardern and Lockett. Journal
- Society for Chemical Research, V. 33, May 30, 1914, p. 523.
-
- 43. Final Plans at Milwaukee. E.N.R. V. 84, 1920, p. 990.
-
- 44. A.S. Bibliography, published by General Filtration Co., Rochester,
- N. Y., 1921.
-
- 45. A.S. at Manchester, Eng. by Ardern. Journal Society Chemical
- Industry, 1921. E.C. V. 55, 1921, p. 310.
-
- 46. The Des Plaines River A.S. Plant, by Pearse. E.N.R. V. 88, 1920, p.
- 1134.
-
- 47. Sewage Treatment by the Dorr System, by Eagles. Proceedings, Boston
- Society of Engineers, 1920. Public Works V. 50, 1920, p. 53.
-
-
-
-
- CHAPTER XIX
- ACID PRECIPITATION, LIME AND ELECTRICITY, AND DISINFECTION
-
-
-=275. The Miles Acid Process.=—The Miles Acid Process for the treatment
-of sewage was devised and patented by G. W. Miles. It was tried
-experimentally at the Calf Pasture sewage pumping station, Boston,
-Mass., 1911 to 1914. In 1916 it was tried experimentally at the
-Massachusetts Institute of Technology, and it has been tested
-subsequently at other places, notably at New Haven, Conn., in 1917 and
-1918. It is one of the most recent developments in sewage treatment and
-no extensive experience has been had with it. The process consists in
-the acidification of sewage with sulphuric or sulphurous acid, as the
-result of which the suspended matter and grease are precipitated and
-bacteria are removed. The equipment required for the process consists of
-devices for the production of sulphur dioxide (SO_{2}), and for feeding
-niter cake or other forms of acid; subsiding basins; sludge-handling
-apparatus; sludge driers; grease extractors; grease stills; and tankage
-driers and grinders.
-
-The first step is the acidification of the sewage. The period of contact
-with the acid is about 4 hours. Sulphurous acid seems to give better
-results than sulphuric because of the ease in which it can be
-manufactured on the spot. It seems also to be more virulent in attacking
-bacteria than an equal strength of sulphuric acid. In experimental
-plants the acidulation has been accomplished in different ways such as:
-by the addition of compressed sulphur dioxide from tanks; by the
-addition of sulphur dioxide made from burning sulphur; or by the
-roasting of iron pyrite (FeS_{2}). The acidulation precipitates most of
-the grease as well as the suspended matter and results in a sludge which
-gives some promise of commercial value. In referring to the process R.
-S. Weston states:[188]
-
- (1) It disinfects the sewage by reducing the numbers of bacteria
- from millions to hundreds per c.c.
-
- (2) If the drying of the sludge and the extraction of the grease
- can be accomplished economically, it is possible that a large
- part, if not all, of the cost of the acid treatment may be met by
- the sale of the grease and fertilizer recovered from the sewage.
-
- (3) The use of so strong a deodorizer and disinfectant as sulphur
- dioxide would prevent the usual nuisances of treatment works.
-
- (4) The addition of sulphur dioxide to the sewage also avoids any
- fly nuisance, which is a handicap to the operation of Imhoff tanks
- and trickling filters.
-
-The amount of acid used varies with the quality of the sewage and the
-desired character of the effluent. At Bradford, England,[189] 5,500
-pounds of sulphuric acid are used per million gallons, producing about
-2,340 pounds of grease or 0.43 pound of grease per pound of sulphuric
-acid. At Boston only 0.215 pound of grease were produced per pound of
-sulphuric acid. The difference is probably due to the great difference
-in the amount of grease in the raw sewage. In the East Street sewer at
-New Haven, Conn.,[190] only 700 pounds of acid are used per million
-gallons of sewage as the alkalinity is only 50 p.p.m. This amount of
-acid secures an acidity of 50 p.p.m. whereas in the Boulevard sewer
-1,130 pounds of acid had to be added to produce the same result. The
-results obtained by the experiments conducted by the Massachusetts
-State Board of Health in 1917 are shown in Table 97. The character of
-the sludge from the same tests is shown in Table 98. After
-acidification[191] the sewage contains bisulphites and some free
-sulphurous acid, with some lime and magnesium soaps which are attacked
-by the acid liberating the free fatty acids. Part of the bisulphites
-and sulphurous acid are oxidized to bisulphates and sulphuric acid. It
-was found as a result of the New Haven[191] experiments that the
-presence of sulphur dioxide in the effluent caused an abnormal oxygen
-demand from the diluting water and that this difficulty could be
-partly overcome by the aëration of the effluent after acidulation and
-sedimentation, without prohibitory expense. The effluent and sludge
-are both stable for appreciable periods of time and are suitable for
-disposal by dilution. The character of the sludge as determined by the
-New Haven tests[192] is shown in Table 99.
-
- TABLE 97
-
- AVERAGE ANALYSIS OF SEWAGE ENTERING BOSTON HARBOR, BEFORE AND AFTER
- TREATMENT, JULY 17 TO SEPTEMBER 27, 1917
-
- (Eng. News-Record, Vol. 80, p. 319)
- ─────────┬───────────────────────────────────────────────┬───────────────
- Sample │ Parts per Million │ Bacteria,
- │ │ Millions
- ─────────┼─────────────────┬───────────┬────────┬────────┼─────┬─────────
- │ Ammonia │ Kjeldahl │Chlorine│ Oxygen │ │
- │ │ Nitrogen │ │Consumed│ │
- ─────────┼─────┬───────────┼─────┬─────┼────────┼────────┼─────┼─────────
- │Free │Albuminoid │ │ │ │ │ │
- ─────────┼─────┼─────┬─────┼─────┼─────┼────────┼────────┼─────┼─────────
- │Total│Total│Diss.│Total│Diss.│ │ │ 20° │ 37°
- ─────────┴─────┴─────┴─────┴─────┴─────┴────────┴────────┴─────┴─────────
-
- _Paddock’s Island_
-
- ─────────┬─────┬─────┬─────┬─────┬─────┬────────┬────────┬─────┬─────────
- Raw │ 14.0│ 3.3│ 1.8│ 6.8│ 3.6│ 134│ 23.1│1.86 │ 4.15
- sewage │ │ │ │ │ │ │ │ │
- Settled │ 12.2│ 1.6│ 1.1│ 3.5│ 2.2│ │ 15.4│ │
- Sewage │ │ │ │ │ │ │ │ │
- Acidified│ 20.9│ 5.2│ 3.9│ 10.0│ 7.5│ │ │units│units 91
- and │ │ │ │ │ │ │ │ 94 │
- settled│ │ │ │ │ │ │ │ │
- sewage │ │ │ │ │ │ │ │ │
- ─────────┴─────┴─────┴─────┴─────┴─────┴────────┴────────┴─────┴─────────
-
- _Deer Island_
-
- ─────────┬─────┬─────┬─────┬─────┬─────┬────────┬────────┬─────┬─────────
- Raw │ 23.3│ 8.2│ 4.8│ 16.8│ 8.9│ 3100│ 87.3│2.63 │ 1.50
- sewage │ │ │ │ │ │ │ │ │
- Settled │ 21.1│ 5.6│ 3.9│ 10.7│ 7.3│ │ 62.2│ │
- sewage │ │ │ │ │ │ │ │ │
- Acidified│ 20.9│ 5.2│ 3.9│ 10.0│ 7.5│ │ │units│units 85
- and │ │ │ │ │ │ │ │ 147 │
- settled│ │ │ │ │ │ │ │ │
- sewage │ │ │ │ │ │ │ │ │
- ─────────┴─────┴─────┴─────┴─────┴─────┴────────┴────────┴─────┴─────────
-
- _Calf Pasture_
-
- ─────────┬─────┬─────┬─────┬─────┬─────┬────────┬────────┬─────┬─────────
- Raw │ 18.0│ 4.5│ 2.0│ 9.7│ 4.1│ 3254│ 41.2│1.89 │ 0.98
- sewage │ │ │ │ │ │ │ │ │
- Settled │ 19.1│ 2.3│ 1.4│ 4.9│ 3.3│ │ 25.8│ │
- sewage │ │ │ │ │ │ │ │ │
- Acidified│ 17.8│ 2.4│ 1.6│ 4.9│ 3.3│ │ │units│units 149
- and │ │ │ │ │ │ │ │ 277 │
- settled│ │ │ │ │ │ │ │ │
- sewage │ │ │ │ │ │ │ │ │
- ─────────┴─────┴─────┴─────┴─────┴─────┴────────┴────────┴─────┴─────────
-
-The success of the Miles Acid Process in comparison with other processes
-is dependent on the commercial value of the sludge produced. The New
-Haven experiments indicate that 16 to 21 per cent of the grease in the
-sludge is unsaponifiable and seriously impairs the value of the process.
-
- TABLE 98
-
- AVERAGE AMOUNT OF SLUDGE AND FATS OBTAINED FROM SEWAGE ENTERING BOSTON
- HARBOR AFTER EIGHTEEN HOURS SEDIMENTATION WITH AND WITHOUT
- ACIDIFICATION
-
- (Eng. News-Record, Vol. 80, p. 319)
- ────────────────────┬────────────────┬────────────────┬────────────────
- │Paddock’s Island│ Deer Island │ Calf Pasture
- ────────────────────┼────────────────┼────────────────┼────────────────
- │ Sedimentation │ Sedimentation │ Sedimentation
- ────────────────────┼─────┬──────────┼─────┬──────────┼─────┬──────────
- │Plain│Acidulated│Plain│Acidulated│Plain│Acidulated
- ────────────────────┼─────┼──────────┼─────┼──────────┼─────┼──────────
- Pounds of SO_{2} │ │ 818│ │ 1513│ │ 1189
- used per million │ │ │ │ │ │
- gallons of sewage │ │ │ │ │ │
- treated │ │ │ │ │ │
- Dry sludge per │ 782│ 959│ 1709│ 1939│ 1208│ 1427
- million gallons │ │ │ │ │ │
- Per cent Nitrogen in│ 3.10│ 3.38│ 3.57│ 3.45│ 3.18│ 2.83
- sludge │ │ │ │ │ │
- Per cent fats in │27.30│ 27.30│24.60│ 19.40│24.30│ 26.30
- sludge │ │ │ │ │ │
- ────────────────────┴─────┴──────────┴─────┴──────────┴─────┴──────────
-
- TABLE 99
-
- CHARACTER OF MILES ACID SLUDGE AT NEW HAVEN
-
- (Eng. News-Record, Vol. 81, p. 1034)
- ─────────────────────────┬───────────────────────────────────┬─────────
- │ East Street Sewer │Boulevard
- │ │ Sewer
- ─────────────────────────┼────────┬────────┬────────┬────────┼─────────
- Length of run in days │ 25│ 24│ 44│ 70│ 29
- Total sewage treated, │ 260│ 239.4│ 407.8│ 602.2│ 145.5
- thousand gallons │ │ │ │ │
- Gallons wet sludge per │ 3750│ 4025│ 3200│ 2600│ 5375
- million gallons sewage │ │ │ │ │
- Specific gravity │ 1.067│ 1.048│ 1.054│ 1.061│
- Per cent moisture │ 86.6│ 88│ 86.3│ 85.7│ 92.5
- Pounds of dry sludge per │ 503│ 483│ 439│ 368│ 403
- million gallons sewage │ │ │ │ │
- Ether extract, per cent │ 23.7│ 24.0│ 29│ 32.6│ 30.9
- dry sludge │ │ │ │ │
- Ether extract, pounds per│ 119│ 116│ 127│ 120│ 124
- million gallons │ │ │ │ │
- Volatile matter, per cent│ 47.2│ 51.2│ 57.3│ 63.8│ 78.5
- dry sludge │ │ │ │ │
- Nitrogen, per cent dry │ 1.6│ 1.6│ 2.4│ 2.0│ 3.0
- sludge │ │ │ │ │
- ─────────────────────────┴────────┴────────┴────────┴────────┴─────────
-
-The conclusions reached as a result of the New Haven experiments
-are:[193]
-
- Our experience with New Haven sewage lends no color to the hope
- that a net financial profit can be obtained by the use of the
- Miles Acid Process, except with sewage of exceptionally high
- grease content and low alkalinity. They do, however, suggest that
- for communities where clarification and disinfection are
- desirable—where screening would be insufficient and nitrification
- unnecessary—the process of acid treatment comes fairly into
- competition with the other processes of tank treatment, and that
- it is particularly suited to dealing with sewages that contain
- industrial wastes, and to use in localities where local nuisances
- must be avoided at all costs and where sludge disposal could be
- provided for only with difficulty.
-
-The conclusions reached as a result of the Chicago experiments are:[194]
-
- The results on hand indicate that treatment of this sewage with
- acid results in a somewhat greater retention of fat. An apparent
- reduction in the oxygen demand over that resulting from plain
- sedimentation, while remarkable, is probably not real, being
- simply due to a retardation of decomposition by the sterilization
- of the bacteria present, the organic matter being left in
- solution.... However, there appears the added cost of acid
- treatment and the cost of recovery of the grease, as well as the
- uncertainty of the price to be received for the grease recovered.
-
-The cost of the treatment is estimated by Dorr to be $18 per million
-gallons, and the value of the sludge obtained from the Boston sewage as
-$24 per million gallons, giving a net margin of profit of $6 per million
-gallons. At New Haven, the total return is estimated at $7.09 per
-million gallons. Based on the production of sulphur dioxide by burning
-sulphur (assumed to cost $36 per long ton) and on drying from 85 per
-cent to 10 per cent moisture with coal assumed to cost $7.50 per ton, it
-appears that the acid treatment of sewage should be materially cheaper
-than either the Imhoff treatment or fine screening under the local
-conditions. A comparison of the cost of the treatment of the East Street
-and the Boulevard sewage at New Haven and the Calf Pasture sewage in
-Boston is given in Table 100. The cost of construction was estimated by
-Dorr and Weston in 1919 as greater than $15,000 per million gallons of
-sewage per day capacity.
-
- TABLE 100
-
- ESTIMATED COST OF SEWAGE TREATMENT AT NEW HAVEN AND BOSTON BY THREE
- DIFFERENT PROCESSES
-
- Cost in Dollars per Million Gallons Treated
-
- (Engineering and Contracting, Vol. 51, p. 510)
- ────────────────┬────────────────────┬────────────────────┬────────────
- │ Miles Acid Process │ Imhoff Tank and │Fine Screens
- │ │ Chlorination │ and
- │ │ │Chlorination
- ────────────────┼──────┬─────┬───────┼──────┬─────┬───────┼──────┬─────
- │ East │Boul-│ Calf │ East │Boul-│ Calf │ East │Boul-
- │Street│evard│Pasture│Street│evard│Pasture│Street│evard
- ────────────────┼──────┼─────┼───────┼──────┼─────┼───────┼──────┼─────
- Tanks and │ 2.47│ 2.47│ 2.47│ 5.28│ 4.44│ │ 4.60│ 4.60
- Buildings Int.│ │ │ │ │ │ │ │
- and Dep. │ │ │ │ │ │ │ │
- Acid treatment │ 6.93│10.74│ 18.65│ │ │ │ │
- Drying sludge │ 2.09│ 2.04│ 10.34│ │ │ │ │
- Degreasing │ 1.78│ 1.91│ 9.12│ │ │ │ │
- sludge │ │ │ │ │ │ │ │
- Superintendence │ 1.06│ 2.65│ 1.06│ 0.46│ 1.15│ │ 0.47│ 1.15
- Labor on tanks │ 1.00│ 1.00│ 1.00│ 1.20│ 1.50│ │ 1.42│ 2.05
- and screens │ │ │ │ │ │ │ │
- Disposal of │ │ │ │ 1.00│ 1.00│ │ 0.50│ 0.50
- sludge or │ │ │ │ │ │ │ │
- screenings │ │ │ │ │ │ │ │
- Chlorination │ │ │ │ 4.05│ 4.05│ │ 4.05│ 4.05
- Gross cost │ 15.50│20.98│ 42.75│ 11.99│12.14│ │ 11.03│12.35
- Revenue │ 6.57│10.66│ 47.59│ │ │ │ │
- Net cost │ 8.93│10.32│ 4.84│ 11.99│12.14│ │ 11.03│12.35
- ────────────────┴──────┴─────┴───────┴──────┴─────┴───────┴──────┴─────
-
-
- ELECTROLYTIC TREATMENT
-
-
-=276. The Process.=—This process has been generally unsuccessful in the
-treatment of sewage and has grown into disrepute. In the words of the
-editor of the _Engineering News-Record_:[195]
-
- Thirty years of experiments and demonstrations with only a few
- small working plants built and most of them abandoned—such in
- epitome is the record of the electrolytic process of sewage
- treatment.
-
-It is probably true that the process has never received a thorough and
-exhaustive test on a large scale, but the small-scale tests have not
-been promising of good results. Among the most extensive tests have been
-those at Elmhurst, Long Island,[196] Decatur, Ill.,[197] and Easton,
-Pa.[198]
-
-Whatever degree of popularity the method has possessed has been due
-possibly to the mystery and romance of “electricity” and to the
-personality of its promoters. The process should, nevertheless, be
-understood by the engineer in order that it may be explained
-satisfactorily to the layman interested in its adoption.
-
-In this process, sometimes called the direct-oxidation process, all grit
-is removed and the sewage is passed through fine screens before entering
-the electrolytic tank. In the electrolytic tank the sewage passes in
-thin sheets between electrodes and an electric current is discharged
-through it. A recent development has been the addition of lime to the
-sewage at some point in its passage through the electrolytic tank. From
-the electrolytic tank the sewage flows to a sedimentation tank, where
-sludge is accumulated, and from which the liquid effluent is finally
-disposed of.
-
-It is claimed that the action of the electricity electrolyzes the
-sewage, releasing chlorine, which acts as a powerful disinfectant. The
-constituents of the sewage are oxidized so that the dissolved oxygen,
-nitrates, and relative stability are increased and the sludge is
-rendered non-putrescible. It is said that the addition of lime increases
-the efficiency of sedimentation and enhances the effect of the electric
-current. The results obtained by tests at Easton, Pa., are shown in
-Table 101. It will be observed from this table that the combination of
-lime and electricity does not have a more beneficial effect than either
-one of them alone. The amount of sludge produced by the combination is
-about the same as by chemical precipitation alone, but the character of
-the sludge produced with electricity is less putrescible. The cost of
-the treatment as estimated at Elmhurst is shown in Table 102.
-
-As a result of the tests at Decatur, comparing lime alone with lime and
-electricity together, Dr. Ed. Bartow stated:
-
- The purification by treatment with lime alone was greater than
- that obtained in several of the individual samples treated with
- lime and electricity.
-
- TABLE 101
-
- COMPARATIVE RESULTS OBTAINED FROM THE TREATMENT OF SEWAGE BY LIME
- ALONE, ELECTRICITY ALONE, AND LIME AND ELECTRICITY COMBINED
-
- (Creighton and Franklin, Journal of the Franklin Institute, August,
- 1919)
- ───────────────────────┬───────────────┬───────────────┬───────────────
- │ Lime and │ Lime Alone │ Electricity
- │ Electricity │ │ Alone
- ───────────────────────┼───────┬───────┼───────┬───────┼───────┬───────
- │Change,│Change,│Change,│Change,│Change,│Change,
- │ Parts │ Per │ Parts │ Per │ Parts │ Per
- │ per │ Cent │ per │ Cent │ per │ Cent
- │Million│ │Million│ │Million│
- ───────────────────────┼───────┼───────┼───────┼───────┼───────┼───────
- Chlorine │ +1.2│ +1.9│ +12.3│ +18.2│ +1.6│ +2.2
- Nitrites │ +0.014│ +58.3│ -.005│ –10.0│ –0.01│ –20.0
- Nitrates │ +0.13│ +23.6│ +.005│ +0.8│ –0.15│ –20.0
- Ammonia │ –3.3│ –18.3│ +0.2│ +1.3│ +0.9│ +6.6
- Albuminoid ammonia │ –3.6│ –12.1│ –0.4│ –1.7│ –0.5│ –2.3
- Oxygen demand │ –13.0│ –20.5│ –7.7│ –8.9│ –6.5│ –10.0
- Dissolved oxygen │ +1.78│ +40.9│ –0.93│ –19.1│ +1.61│ +40.1
- Total bacteria at 37° │ –343│ –92.7│ –373│ –82.4│ –165│ –37.8
- (Thousands) │ │ │ │ │ │
- Total bacteria at 20° │ –688│ –92.7│ –1074│ –90.1│ –635│ –70.0
- (Thousands) │ │ │ │ │ │
- B. Coli (Thousands) │ –77.9│ –99.85│ –96.3│ –92.3│ –45│ –81.8
- Oxygen absorbed in 5 │ –3.40│ –81.6│ –1.03│ –21.│ +1.24│ +31
- days │ │ │ │ │ │
- ───────────────────────┴───────┴───────┴───────┴───────┴───────┴───────
-
-
- DISINFECTION
-
-
-=277. Disinfection of Sewage.=—Sewage is disinfected in order to protect
-public water supplies, shell fish, and bathing beaches; to prevent the
-spread of disease; to keep down odors, and to delay putrefaction.
-Disinfection is the treatment of sewage by which the number of bacteria
-is greatly reduced. Sterilization is the destruction of all bacterial
-life, including spores. Ordinarily even the most destructive agents do
-not accomplish complete sterilization. Chlorine and its compounds are
-practically the only substances used for the disinfection of sewage. The
-lime used in chemical precipitation, the acid used in the Miles Acid
-Process, the aëration in the activated sludge process, all serve to
-disinfect sewage, but are not used primarily for that purpose. Copper
-sulphate has been used as an algaecide but never on a large scale as a
-bactericide.[199] Heat has been suggested, but its high cost has
-prevented its practical application to the disinfection of sewage.
-
- TABLE 102
-
- COST OF ELECTROLYTIC TREATMENT, ELMHURST, LONG ISLAND, AND EASTON,
- PENNSYLVANIA
-
- ────────────────────────────────────────┬───────────────────┬─────────
- │ │ Three
- Item │One Million Gallon │ Million
- │ │ Gallon
- ────────────────────────────────────────┼─────────┬─────────┼─────────
- │ unit at │ unit at │ unit at
- │ Easton, │Elmhurst,│Elmhurst,
- │ Dollars │ Dollars │ Dollars
- ────────────────────────────────────────┼─────────┼─────────┼─────────
- Hydrated lime: │ │ │
- Elmhurst, 1300 pounds at $7.90 ton. │ 12.56│ 5.14│ 15.42
- Easton, 3720 pounds at $6.75 ton. │ │ │
- Electric power electrolysis: │ │ │
- Elmhurst, 85 kw-h. at 4 cents │ 4.19│ 3.40│ 9.60
- Easton, 6.25 kw-h. at 8.05 cents │ │ │
- Electric power, light and agitation: │ │ │
- Elmhurst, 60 kw-h. at 4 cents │ 0.50│ 2.40│ 7.20
- Easton, 6.25 kw-h at 8.05 cents │ │ │
- Heating │ 1.25│ │
- Labor and supervision │ 15.00│ 12.50│ 15.00
- Maintenance, repairs and supplies │ 1.50│ 1.00│ 3.00
- Sludge pressing and removal │ │ 5.11│ 15.33
- ────────────────────────────────────────┼─────────┼─────────┼─────────
- Total │ 35.00│ 29.55│ 65.55
- Cost per million gallons │ 35.00│ 29.55│ 21.85
- ────────────────────────────────────────┴─────────┴─────────┴─────────
-
-The action which takes place on the addition to sewage of chlorine or
-its compounds is not well understood. The idea that the bacteria are
-burned up with “nascent” or freshly born oxygen, has been exploded.[200]
-Likewise the idea that the toxic properties of chlorine have no effect
-has not been borne out by experiments. It has been demonstrated,
-particularly by tests on strong tannery wastes, that the action of
-chlorine gas is more effective than the application of the same amount
-of chlorine in the form of hypochlorite. All that we are certain of at
-present is that the greater the amount of chlorine added under the same
-conditions, the greater the bactericidal effect.
-
-Chlorine is applied either in the form of a bleaching powder or a gas.
-In ordinary commercial bleach (calcium hypochlorite) the available
-chlorine is about 35 to 40 per cent by weight. In order to add one part
-per million of available chlorine to sewage it is necessary to add about
-25 pounds of bleaching powder or 8½ pounds of liquid chlorine per
-million gallons of sewage. This can be computed as follows:
-
- The molecular weight of calcium hypochlorite is 127.0. This reacts
- to produce two atoms of available chlorine with a molecular weight
- of 70.9. If the bleaching powder were pure the available chlorine
- would therefore represent 70.9 ÷ 127, or 56 per cent of its
- weight. Then to obtain one pound of chlorine it would be necessary
- to have 1.79 pounds of pure bleaching powder. Since 1,000,000
- gallons of water weigh approximately 8,300,000 pounds, in order to
- apply one part per million of chlorine to 1,000,000 gallons of
- sewage it is necessary to apply 1.79 × 8.3 or 14.9 pounds of pure
- bleaching powder. Commercial bleaching powder is only about 60 per
- cent calcium hypochlorite. It is therefore necessary to add 14.9 ÷
- 0.60 or about 25 pounds of commercial bleach.
-
- Since liquid chlorine is very nearly pure, approximately 8½ pounds
- of it applied to 1,000,000 gallons of sewage are equivalent to a
- dose of one part per million.
-
-Commercial bleaching powder is a dry white powder which absorbs moisture
-slowly, and which loses its strength rapidly when exposed to the air. It
-is packed in air-tight sheet iron containers, which should be opened
-under water, or emptied into water immediately on being opened. The
-strength of the solution should be from ½ to 1 per cent. The rate of the
-application of the solution to the sewage may be controlled by automatic
-feed devices, or by hand-controlled devices.
-
-Commercial liquid chlorine is sold in heavy cast steel containers, which
-hold 100 to 140 pounds of liquid chlorine under a pressure of 54 pounds
-per square inch at zero degrees C. or 121 pounds per square inch at 20
-degrees.
-
-The amount of chlorine used is dependent on the character of the sewage
-to be treated, the stage of decomposition of the organic matter, the
-desired degree of disinfection, the period of contact, and the
-temperature. The amount of chlorine is expressed in parts per million of
-available chlorine, regardless of the form in which the chlorine is
-applied. In general about 15 to 20 parts per million of available
-chlorine with 30 minutes’ contact at a temperature of about 15° C. will
-effect an apparent removal of 99 per cent of the bacteria from the raw
-sewage. The effect is only apparent because many of the bacteria encased
-in the solid matter of the sewage escape the effect of the chlorine, or
-detection in the bacterial analysis. Stronger and older sewages, higher
-temperatures, and shorter periods of contact will demand more chlorine
-to produce the same results. A septic effluent will require more
-chlorine than a raw sewage because of the greater oxygen demand by the
-septic sewage. The results of experiments on disinfection made at
-different testing stations have shown such wide variations in the amount
-of chlorine necessary, as to demonstrate the necessity for independent
-studies of any particular sewage which is to be chlorinated. For
-instance, at Milwaukee approximately 13 p.p.m. of available chlorine
-applied to an Imhoff tank effluent effected a 99 per cent removal of
-bacteria, whereas the same result was obtained at Lawrence, Mass., on
-crude sewage with only 6.6 p.p.m. and at Marion, Ohio, only 9 per cent
-removal of bacteria was obtained by the addition of 4,815 p.p.m. to
-crude sewage. The Ohio and Massachusetts reports show irrational
-variations among themselves. For instance, 6.2 p.p.m. applied to a
-septic effluent effected 88 per cent removal whereas in another case 7.6
-p.p.m. effected only 36 per cent removal. At Lawrence in one case it
-took 8.6 p.p.m. to remove 99 per cent from a sand filter effluent, but
-only 6.3 p.p.m. to effect the same result in the effluent from a septic
-tank. The most consistent results are those found at Milwaukee which
-show a steadily increasing percentage removal with increasing amounts of
-chlorine.
-
-Some time after sewage has received its dose of chlorine the number of
-bacteria may be greater than in the raw sewage. Such bacteria are called
-aftergrowths. Certain forms of bacteria, particularly the pathogenic or
-body temperature types, are most susceptible to disinfecting agents.
-These are killed off and leave the sewage in a condition more favorable
-to the growth of more resistant forms of bacteria. As the latter are
-non-pathogenic and are generally aërobic their presence is usually more
-beneficial than detrimental, as they hasten the action of
-self-purification.
-
-
- REFERENCES
-
-The following abbreviations will be used: E.C. for Engineering and
-Contracting, E.N. for Engineering News, E.R. for Engineering Record,
-E.N.R. for Engineering News-Record, M.J. for Municipal Journal, p. for
-page, and V. for volume.
-
- No.
-
- 1. Grease and Fertilizer Base for Boston Sewage, by Weston, E.N. V.
- 75, 1916, p. 913 and Journal American Public Health Association,
- April, 1916.
-
- 2. Getting Grease and Fertilizer from City Sewage, by Allen. E.N. V.
- 75, 1916, p. 1005.
-
- 3. New Haven Tests Five Processes of Sewage Treatment. E.N.R. V. 79,
- 1917, p. 829.
-
- 4. Recovery of Grease and Fertilizer from Sewage Comes to the Front.
- E.N.R. V. 80, 1916, p. 319.
-
- 5. Miles Acid Process may Require Aëration of Effluent, by Mohlman.
- E.N.R. V. 81, 1918, p. 235.
-
- 6. Promising Results with Miles Acid Process in New Haven Tests.
- E.N.R. V. 81, 1918, p. 1034.
-
- 7. Baltimore Experiments on Grease from Sewage. E.N. V. 75, 1916, p.
- 1155.
-
- 8. Report on Industrial Wastes from the Stock Yards and Packingtown in
- Chicago to the Trustees of the Sanitary District of Chicago,
- 1914, pp. 187–195.
-
- 9. The Separation of Grease from Sewage, by Daniels and Rosenfeld.
- Cornell Civil Engineer. V. 24, p. 13.
-
- 10. The Separation of Grease from Sewage Sludge with Special Reference
- to Plants and Methods Employed at Bradford and Oldham, England,
- by Allen. E.C. V. 40, 1913, p. 611.
-
- 11. Acid Treatment of Sewage, by Dorr and Weston. Journal Boston
- Society of Civil Engineers, April, 1919. E.C. V. 51, 1919, p.
- 510. M.J. V. 46, 1919, p. 365.
-
- 12. The Miles Acid Process for Sewage Disposal. Metallurgical and
- Chemical Engineering, V. 18, p. 591.
-
- 13. Miles Acid Treatment of Sewage, by Winslow and Mohlman. Journal
- American Society Municipal Improvements, Oct., 1918. M.J. V. 45,
- 1918, pp. 280, 297, and 321.
-
- 14. New Electrolytic Sewage Treatment. M.J. V. 37, 1914, p. 556.
-
- 15. Electrolytic Sewage Treatment. M.J. V. 47, 1919, p. 131.
-
- 16. Electrolytic Treatment of Sewage at Durant, Oklahoma, by Benham.
- E.N. V. 76, 1916, p. 547. Municipal Engineering, V. 49, 1916, p.
- 141.
-
- 17. Electrolytic Treatment of Sewage at Elmhurst, Long Island, by
- Travis. Report to the President of the Borough of Queens, Aug.
- 31, 1914. E.R. V. 70, 1914, pp. 292, 315, and 429. M.J. V. 39, p.
- 551. Municipal Engineering, V. 47, p. 281.
-
- 18. Tests of the Electrolysis of Sewage at Toronto, by Nevitt. E.N. V.
- 71, 1914, p. 1076.
-
- 19. Electrolytic Treatment of Sewage Little Better than Lime Alone, by
- Bartow. E.R. V. 74, 1916, p. 596.
-
- 20. Electrolytic Sewage Treatment Not Yet an Established Process.
- E.N.R. V. 83, 1919, p. 541.
-
- 21. Tests of Electrolytic Sewage Treatment Process at Easton, Pa.
- Journal of the Franklin Institute, Aug., 1919. E.N.R. V. 83,
- 1919, p. 569.
-
- 22. The Disinfection of Sewage. U. S. Geological Survey, Water Supply
- Paper, No. 229.
-
- 23. Sewage Disinfection in Actual Practice, by Orchard. E.R. V. 70,
- 1914, p. 164.
-
- 24. Water and Sewage Purification in Ohio. Report of the Ohio State
- Board of Health, 1908, pp. 738–762.
-
- 25. Water Purification, by Ellms. Published in 1917 by McGraw-Hill Book
- Co.
-
- 26. Electrolytic Sewage Treatment, A Half Century of Invention and
- Promotion. E.N.R. V. 86, 1921, p. 25.
-
-
-
-
- CHAPTER XX
- SLUDGE
-
-
-=278. Methods of Disposal.=—Sludge is the deposited suspended matter
-which accumulates as the result of the sedimentation of sewage. The
-methods for the disposal of sludge as discussed herein will include the
-disposal of scum. Scum is a floating mass of sewage solids buoyed up in
-part by entrained gas or grease, forming a greasy mat which remains on
-the surface of the sewage.[201] The sludges formed by different methods
-of sewage treatment are described in the chapter devoted to the
-particular method. The disposal of sludge is a problem common to all
-methods of sewage treatment involving the use of sedimentation tanks.
-
-Sludge is disposed of by: dilution, burial, lagooning, burning, filling
-land, and as a fertilizer or fertilizer base. Certain methods of
-disposal, such as burning or as a fertilizer, demand that the sludge be
-dried preparatory to disposal. Sludge is dried on drying beds, in a
-centrifuge, in a press, in a hot-air dryer, or by acid precipitation.
-
-
-=279. Lagooning.=—This is a method of sludge disposal in which fresh
-sludge is run on to previously prepared beds to a depth of 12 to 18
-inches or more, and allowed to stand without further attention. The
-preparation of the lagoons requires leveling the ground, building of
-embankments, and, if the ground is not porous, the placing of
-underdrains laid in sand or gravel. At Reading, Pa.,[202] approximately
-one acre was required for 1,700 cubic yards of wet sludge. The results
-of lagooning at Philadelphia are given in Table 103.[202]
-
- TABLE 103
-
- RESULTS OF DRYING SLUDGE IN LAGOONS AT PHILADELPHIA
-
- (“Sewage Sludge” by Allen)
- ─────────────────────┬─────────┬─────────┬─────────┬─────────┬─────────
- Treatment │ Days │ Depth, │Per Cent,│Rainfall,│ Cubic
- │ │ Inches │Moisture │ Inches │Yards per
- │ │ │ │ │ Acre
- ─────────────────────┼─────────┼─────────┼─────────┼─────────┼─────────
- Screened │ 0│ 12.20│ 82.8│ 0│ 1600
- Screened │ 26│ 7.67│ 57.0│ 0│ 1000
- Screened │ 49│ 3.50│ 51.6│ 0.43│ 470
- Screened │ 0│ 13.50│ 90.1│ 0│ 1800
- Screened │ 62│ 7.00│ 61.0│ 3.14│ 950
- Crude │ 0│ 12.00│ 88.7│ 0│ 1600
- Crude │ 59│ 4.70│ 62.8│ 2.59│ 640
- ─────────────────────┴─────────┴─────────┴─────────┴─────────┴─────────
-
-During the period of standing in the lagoon the moisture drains out and
-evaporates and the organic matter putrefies, giving off gases and foul
-odors. In the course of three to six months, biological action ceases
-and the sludge has become humified and reduced to about 75 per cent
-moisture. In the utilization of this method of disposal the lagoons must
-be removed from settled districts and should occupy land of little value
-for other purposes. The odors created at the lagoons may be intense and
-offensive. The land so used is rendered unfit for other purposes for
-many years.
-
-The digestion of sludge in special tanks is a form of lagooning in which
-an attempt is made to maintain septic action as a result of which a
-portion of the sludge is gasified or liquefied, leaving less to be cared
-for by some of the other methods of treatment or disposal. The results
-obtained by digestion tanks have not been entirely satisfactory. A
-partial drying and consolidation of the sludge may be effected, however,
-by the process of decantation, in which the supernatant liquid is run
-off, followed by further sedimentation, rendering the final product more
-compact.
-
-
-=280. Dilution.=—In the disposal of sludge by dilution, as in the
-disposal of sewage by dilution, there must be sufficient oxygen
-available in the diluting water to prevent putrefaction, and a swift
-current to prevent sedimentation. Such conditions exist in localities
-along the sea coast, and in communities situated near rivers, when the
-rivers are in flood. In some seacoast towns, for example at London and
-Glasgow, the sludge is taken out to sea in boats, and dumped. Since it
-is not necessary to discharge sludge continuously, it can be stored to
-advantage in the digestion chamber of a tank, until the conditions in
-the body of diluting water are suitable to receive it.
-
-The amount of diluting water to receive sewage sludge has not been
-sufficiently well determined to draw reliable general conclusions. A
-dilution of 1,500 to 2,000 volumes may be considered sufficiently safe
-to avoid a nuisance provided there is a sufficient velocity to prevent
-sedimentation. Johnson’s Report on Sewage Purification at Columbus, Ohio
-(1905), states that a dilution of 1 to 800 is sufficient to avoid a
-nuisance. The character of the sludge has a marked effect on the proper
-ratio of dilution, the sludge from septic and sedimentation tanks
-requiring a greater dilution than that from Imhoff tanks.
-
-
-=281. Burial.=—Sludge can be disposed of by burial in trenches about 24
-inches deep with at least 12 inches of earth cover, without causing a
-nuisance. The ground used for this purpose should be well drained. This
-method of disposal is generally used as a makeshift and has not been
-practiced extensively because of the large amount of land required.
-Insufficient information is available to generalize on the amount of
-land required or the time before the land can be used for further sludge
-burial, or for other purposes. Indications are that the sludge may
-remain moist and malodorous for years and that the land may be rendered
-permanently unfit for further sludge burial. Under some conditions the
-land may be used again for the same or other purposes. For example,
-Kinnicutt, Winslow and Pratt[203] state that 500 tons of wet sludge can
-be applied per acre and:
-
- The same land, it is claimed, can be used again after a period of
- a year and a half to two years, if in two months or so after
- covering the sludge with earth, the ground is broken up, planted,
- and, when the crop is removed, again plowed and allowed to remain
- fallow for about a year.
-
-
-=282. Drying.=—Before sludge can be disposed of to fill land, by
-burning, or for use as a fertilizer filler it must be dried to a
-suitable degree of moisture. The removal of moisture from the sludge
-decreases its volume and changes its characteristics so that sludge
-containing 75 per cent moisture has lost all the characteristics of a
-liquid. It can be moved with a shovel or fork, and can be transported in
-non-watertight containers. A reduction in moisture from 95 to 90 per
-cent will cut the volume in half.
-
-The change in volume on the removal of moisture can be represented as:
-
- _V__{1} = _V_(100 − _P_)⁄(100 − _P__{1}),
-
- in which _P_ = the original percentage of moisture;
-
- _P__{1} = the final percentage of moisture;
-
- _V_ = the original volume;
-
- _V__{1} = the final volume.
-
-The drying of sludge on coarse sand filter beds is more particularly
-suited to sludge from Imhoff tanks. This sludge does not decompose
-during drying, and is sufficiently light and porous in texture to permit
-of thorough draining. The sludge from plain sedimentation or chemical
-precipitation tanks is high in moisture, putrescible, and when placed on
-a filter bed it settles into a heavy, compact, impervious mass which
-dries slowly. In order to avoid this condition the sludge is run on to
-the beds as quickly as possible, to a depth of not more than 6 to 10
-inches. Lime is sometimes added to the sludge at this time as it aids
-drying by assisting in the maintenance of the porosity of the sludge,
-and it is advantageous in keeping down odors and insects.
-
-Sludge filter beds are made up of 12 to 24 inches of coarse sand,
-well-screened cinders, or other gritty material, underlaid by 6 inches
-of coarse gravel and 6 or 8–inch open-joint tile underdrains, laid 4 to
-10 feet apart on centers, dependent on the porosity of the subsoil. The
-side walls of the filters are made of planks or of low earth
-embankments. The sludge filters at Hamilton, Ontario, are shown in Fig.
-179.
-
-[Illustration:
-
- FIG. 179.—Sludge drying Beds at Hamilton, Ontario.
-
- Eng. News, Vol. 73, p. 426.
-]
-
-The size of the bed is dependent mainly upon the characteristics of the
-sludge. For Imhoff tank sludge which comes from the tank with about 85
-per cent moisture, the practice is to allow about 350[204] square feet
-of filter surface per 1,000 population contributing sludge. For other
-types of sludge the area varies from 900 to 9,000 square foot per 1,000
-population contributing sludge, and only experiments with the sludge in
-hand can determine the proper allowance. Imhoff recommends 1,080 square
-feet per 1,000 population for septic tank sludge, and 6,480 square feet
-for sludge from plain sedimentation tanks.[205] Kinnicutt, Winslow, and
-Pratt in their book on Sewage Disposal state:
-
- With an average depth of 10 inches per dose of sludge of 87 per
- cent water content, one square foot of covered (glass) bed should
- dry to a spadable condition one cubic yard of sludge per year.
-
-The sludge is run on the bed in small quantities at periods from two
-weeks to a month apart. In favorable weather Imhoff sludge will dry in
-two weeks or less to approximately 50 to 60 per cent moisture. It is
-then suitable for use as a filling material on waste land, for burning,
-or for further drying by heat. Glass roofs, similar to those used on
-green-houses, have been used to speed the drying process by preventing
-the moistening of partly dried sludge during rainy weather. In some
-instances sludge has dried to 10 per cent moisture on such beds. Imhoff
-sludge can be removed from the drying beds with a manure or hay fork. It
-has an odor similar to well-fertilized garden soil. It is stable, dark
-brownish-gray in color, is of light coarse material, and is granular in
-texture.
-
-Sludge presses are suitable for removing moisture from the bulky wet
-sludge obtained from plain sedimentation, chemical precipitation, and
-the activated sludge process. The details of a typical sludge press are
-shown in Fig. 180. The press shown is made up of a number of corrugated
-metal plates about 30 inches in diameter with a hole in the center about
-8 inches in diameter. The corrugations run vertically except for a
-distance about 3 inches wide around the outer rim, which is smooth. To
-this smooth portion is fastened, on each side of the plate, an annular
-ring about an inch thick and 2 to 3 inches wide, of the same outside
-diameter as the plate. A circular piece of burlap, canvas, or other
-heavy cloth is fastened to this ring, covering the plate completely. A
-hole is cut in the center of the cloth slightly smaller in diameter than
-the center hole in the plate, and the edges of the cloth on opposite
-sides of the plate are sewed together. The plates are then pressed
-tightly together by means of the screw motion at the left end of the
-machine, thus making a water-tight joint at the outer rim. Sludge is
-then forced under pressure into the space between the plates, passing
-through the machine by means of the central hole. The pressure on the
-sludge may be from 50 to 100 pounds per square inch. This pressure
-forces the water out of the sludge through the porous cloth from which
-it escapes to the bottom of the press along the corrugations of the
-separating plate. After a period of 10 to 30 minutes the pressure is
-released, the cells are opened, and the moist sludge cake is removed.
-The liquid pressed from the sludge is highly putrescible and should be
-returned to the influent of the treatment plant. The pressing of wet
-greasy sludges is facilitated by the addition of from 8 to 10 pounds of
-lime per cubic yard of sludge. The cake thus formed is more cohesive and
-easy to handle. The output of the press depends so much on the character
-of the sludge that a definite guarantee of capacity is seldom given by
-the manufacturer.
-
-[Illustration:
-
- FIG. 180.—Filter Press.
-]
-
-The simplest form of centrifugal sludge dryer is a machine which
-consists of a perforated metal bowl lined with porous cloth in which the
-sludge is placed. Surrounding this bowl is a second water-tight metal
-bowl so arranged as to intercept the water thrown from the sides of the
-inner bowl as it revolves. The peripheral velocity of the inner bowl is
-about 6,000 feet per minute, which makes the effective weight of each
-particle about 250 times its normal weight when at rest. Very few data
-are available on the operation of such machines, and their use has not
-been extensive because of the difficulty of starting and stopping the
-machine at each filling, and the difficulty of removing the partially
-dried sludge from the inner basket. The Besco-ter-Meer centrifuge,
-manufactured by the Barth Engineering and Sanitation Co., can be
-operated continuously and the difficulties of removing the dried sludge
-from the machine have been overcome. According to the manufacturers the
-centrifuge has been operated very successfully in Germany on plain
-septic tank sludge. A removal of 70 per cent of suspended solids in the
-raw sludge and a production of 3,600 pounds of sludge per hour,
-containing 60 to 70 per cent of moisture, can be obtained at less than
-900 r.p.m. with a consumption of 15 horse-power. Extensive tests of the
-machine were made at Milwaukee from October, 1920, to September, 1921,
-on activated sludge, but results of these tests are not as yet
-available. Indications are that the centrifuge has acted as a
-classifier. The coarser particles of sludge have been removed but the
-finer particles have been continuously returned with the liquid to the
-sedimentation tank, ultimately filling this tank with fine particles of
-sludge. An illustration of the unit tested at Milwaukee is shown on this
-page.
-
-[Illustration:
-
- Besco-ter-Meer Sludge Drying Centrifuge at Milwaukee, Wisconsin
- Courtesy, Barth Engineering and Sanitation Co.
-]
-
-Experiments on the drying of sludge by acid flotation have not
-progressed sufficiently to allow the installation of a working unit. The
-method, which has been applied principally to activated sludge, consists
-in adding a small amount of sulphuric acid to the sludge as it leaves
-the storage tank. The sludge is coagulated by this action, the
-coagulated material rising to the surface as a scum containing about 86
-per cent moisture. The consistency is such that it can be removed with a
-shovel. The liquid can be withdrawn continuously from below the scum.
-
-[Illustration:
-
- FIG. 181.—Direct-Indirect Sludge Dryer.
-
- Courtesy, the Buckeye Dryer Co.
-]
-
-The moisture content of sludge to be used in the manufacture of
-fertilizer must be reduced to 10 per cent or less. None of the methods
-of drying described so far can be relied upon for such a product and it
-becomes necessary to use direct or indirect heat dryers. There are
-various types of dryers on the market. The details of a Buckeye dryer
-are shown in Fig. 181. In the operation of this machine moist sludge is
-fed in at the left end at the point marked “feed.” The hot gases pass
-from the fire box up and around the cylinder which revolves at about
-eight r.p.m. The gases are drawn into the inner cylinder through the
-openings marked A which revolve with the two cylinders. The gases escape
-from the inner cylinder through the openings to the right and flow
-towards the left in the outer cylinder. They come in contact with the
-sludge at this point. The gases then pass off through the fan at the
-left. The sludge is lifted by the small longitudinal baffles fastened to
-the outer cylinder, as the drying cylinders revolve. The right end of
-the cylinder is placed lower than the left so that the drying sludge is
-lifted and dropped through the cylinder at the same time that it moves
-slowly toward the right hand end of the cylinder. These dryers require
-about one pound of fuel for 10 pounds of water evaporated. The odors
-from the dryer can be suppressed by passing the gases through a dust
-chamber and washer.
-
-A summary of the results from methods of sludge drying at Milwaukee[206]
-follows:
-
- Excess sludge produced, 12,100 gallons, having 97.5 per cent
- moisture, per million gallons of sewage treated.
-
- Sludge cake produced (by presses), 10,083 pounds having 80.3 per
- cent moisture, per million gallons of sewage treated.
-
- Dried sludge (from heat driers) produced, 2,521 pounds having 10
- per cent moisture, per million gallons of sewage treated.
-
- Press will produce 3 pounds of cake per square foot of filter
- cloth in four and a half hours, or five operations per twenty-four
- hours.
-
- Dryers will reduce 6,700 pounds of sludge cake at 80 per cent
- moisture to 10 per cent moisture, and will evaporate 8 pounds of
- water per pound of combustible.
-
-Thickening devices known as Dorr thickeners, patented and manufactured
-by the Dorr Co. and originally intended for metallurgical purposes, have
-been adapted to the thickening of sewage sludge. These thickeners are
-circular sedimentation tanks, from 8 to 12 feet deep, more or less, and
-are made in any diameter up to 200 feet or more. An arm, pivoted in the
-center and extending to the circumference, is provided at the bottom
-with a number of baffles or squeegees set at an angle with the arm. The
-arm revolves at from one to fifteen revolutions per hour, and the
-squeegees, in contact with the bottom of the tank, scrape the deposited
-sludge towards a central sump, from which it is removed by a pump or by
-gravity, without interrupting the operation of the thickener. The sludge
-so thickened may be reduced to 95 or 96 per cent moisture. These devices
-are ordinarily used only in the activated sludge process in which they
-have been a pronounced success.
-
-
-
-
- CHAPTER XXI
- AUTOMATIC DOSING DEVICES
-
-
-=283. Types.=—Automatic dosing devices are used to apply sewage to
-contact beds, trickling filters, and intermittent sand filters. These
-devices can be separated into two classes; those with moving parts and
-those without moving parts. The latter are better known as air-locked
-dosing devices. Simple devices without moving parts are less liable to
-disorders and are nearer “fool-proof” than any device depending on
-moving parts for its operation.
-
-No one type of moving part device has been used extensively in different
-sewage treatment plants. Designing engineers have exercised their
-ingenuity at different plants, resulting in the production of different
-types.[207] Among the best known forms is the apparatus designed by J.
-W. Alvord for the intermittent sand filters at Lake Forest,
-Illinois.[208] In its operation....
-
- A float in the dosing chamber lifts an iron ball in one of a
- series of wooden columns, and at a certain height the ball rolls
- through a trough from one column to the next, in its passage
- striking a catch, which opens an air valve attached to one of ten
- bell-siphons in the dosing chamber. Each of the siphons discharges
- on one of the ten sand beds, which are thus dosed in rotation.
-
-Since air-locked dosing devices are in more general use their operation
-will be explained in greater detail.
-
-
-=284. Operation.=—The simplest form of these devices is the automatic
-siphon used for flush-tanks, the operation of which is described in Art.
-61.
-
-In the operation of sand filters, sprinkling filters, or other forms of
-treatment where there are two or more units to be dosed it is desirable
-that the dosing of the beds be done alternately. A simple arrangement
-for two siphons operating alternately is shown in Fig. 182. They operate
-as follows: with the dosing tank empty at the start water will stand at
-_bb′_ in siphon No. 2 and at _aa′_ in siphon No. 1. As the water enters
-through the inlet on the left the tank fills. When the water rises
-sufficiently, air is trapped in the bells, and as the water continues to
-rise in the tank, surfaces _a_ and _b_ are depressed an equal amount.
-When _b_ has been depressed to _d_, _a_ has been depressed to _c_. Air
-is released from siphon No. 2 through the short leg, and siphon No. 2
-goes into operation. Surface _c_ rises in siphon No. 1 as the tank
-empties and when the action of Siphon No. 2 is broken by the admission
-of air when the bottom of the bell is uncovered the water in siphon No.
-1 has assumed the position of _bb′_ and that in No. 2 is at _aa′_. The
-conditions of the two siphons are now reversed from that at the
-beginning of the operation and as the tank refills siphon No. 1 will go
-into operation. It is to be noted that these siphons are made to
-alternate by weakening the seal of the next one to discharge and by
-strengthening the seal of the one which has just discharged.
-
-[Illustration:
-
- FIG. 182.—Diagram Showing the Operation of Two Alternating Siphons.
-]
-
-[Illustration:
-
- FIG. 183.—Diagram Showing the Operation of Three Alternating Siphons.
-]
-
-
-=285. Three Alternating Siphons.=—This principle can be extended to the
-operation of three alternating siphons as shown in Fig. No. 183. These
-operate as follows: with the dosing tank empty at the start and water at
-_aa′_ in siphons 1 and 2, and at _bb′_ in siphon No. 3, the dosing tank
-will be allowed to fill. As the water rises in the tank air is trapped
-in all the bells and surfaces _a_ and _b_ are depressed. When surface
-_b_ has been depressed to _d_, _a_ has been depressed to _c_. Air is
-released from siphon No. 3 and this siphon goes into action. Surface _c_
-rises in siphons 1 and 2 to the position _b_, as the dosing tank is
-emptied. At the same time a small amount of water is passed from siphon
-No. 3 to the short leg of siphon No. 1, through the small pipes shown,
-thus filling this leg so that when siphon No. 3 ceases to operate the
-water in siphons 1 and 3 stands at _aa′_ and that in No. 2 stands at
-_bb′_. Siphon No. 2, having the weaker seal, will be the next to
-operate. During its operation it will fill siphon No. 3, leaving No. 1
-weak. When No. 1 operates it will refill No. 2, leaving No. 3 weak, thus
-completing a cycle for the three siphons. This principle has not been
-applied to the operation of more than three alternating siphons and is
-seldom used on recent installations.
-
-[Illustration:
-
- FIG. 184.—Miller Plural Alternating Siphons.
-
- Courtesy, Pacific Flush Tank Co.
-]
-
-
-=286. Four or More Alternating Siphons.=—An arrangement for the
-alternation of four or more siphons is illustrated in Fig. 184. At the
-commencement of the cycle it will be assumed that all starting wells are
-filled with water except well No. 1, and that all main and all blow-off
-traps are filled with water. The following description of the operation
-of the siphons is taken from the catalog of the Pacific Flush Tank
-Company:
-
- The liquid in the tank gradually rises and finally overflows into
- the starting well No. 1 and the starting bell being filled with
- air, pressure is developed which is transmitted, as shown by the
- arrows, to the blow-off trap connected with siphon No. 2. When the
- discharge line is reached, sufficient head is obtained on the
- starting bell to force the seal in blow-off trap No. 2, thus
- releasing the air confined in siphon No. 2 and bringing it into
- full operation.
-
- During the time that siphon No. 2 is operating, siphonic action is
- developed in the draining siphon connected with starting well No.
- 2 and as soon as the level in the tank is below the top of the
- well it is drained down to a point below the bottom of starting
- well No. 2. It can now be seen that after the first discharge
- starting well No. 2 is empty, whereas the other three are full....
- Therefore when the tank is filled the second time, pressure is
- developed in starting bell No. 2, which forces the seal of
- blow-off trap No. 3, thus starting siphon No. 3....
-
-This alternation can be continued for any number of siphons. Other
-arrangements have been devised for the automatic control of alternating
-siphons, but these principles of the air-locked devices are fundamental.
-
-
-=287. Timed Siphons.=—In the operation of a number of contact beds not
-only must the dosing of the tanks be alternated, but some method is
-needed by which the beds shall be automatically emptied after the proper
-period of standing full. To fulfill this need the principle of the timed
-siphon must be employed in conjunction with the alternating siphons.
-Fig. 185 illustrates the operation of the Miller timed siphon. Its
-operation is as follows: water is admitted to the contact bed and
-transmitted to the main siphon chamber through the “opening into bed.”
-Water flows from the main siphon chamber into the timing chamber at a
-rate determined by the timing valve. The contact bed is held full during
-this period. As the timing chamber fills with water air is caught in the
-starting bell and the pressure is increased until the seal in the main
-blow-off trap is blown and the main siphon is put into operation. As the
-water level in the main siphon chamber descends, water flows from the
-timing chamber into the main siphon through the draining siphon and the
-timing chamber is emptied, ready to commence another cycle.
-
-
-=288. Multiple Alternating and Timed Siphons.=[209]—The alternating and
-timing of a number of beds is more complicated. The arrangement
-necessary for this is shown in Fig. 186. It will be assumed at the start
-that all beds are empty and that all feeds are air locked as shown in
-Section _AB_ except that to bed No. 4 into which sewage is running. As
-bed No. 4 fills, sewage is transmitted through the opening in the wall
-into the timed siphon chamber No. 4. When the level of the water in the
-bed and therefore in this chamber has reached the top of the withdraw
-siphon leading to the compression dome chamber No. 4, this latter
-chamber is quickly filled. The air pressure in starting bell No. 4_a_ is
-transmitted to blow-off trap No. 1_a_. The seal of this trap is blown,
-releasing the air lock in feed No. 1 and the flow into bed No. 1 is
-commenced. At the same time the air pressure in compression dome No. 4
-is transmitted to feed No. 4, air locking this feed and stopping the
-flow into bed No. 4. The alternation of the feed into the different beds
-is continued in this manner.
-
-[Illustration:
-
- FIG. 185.—Miller Timed Siphon.
-
- Courtesy, Pacific Flush Tank Co.
-]
-
-Bed No. 4 is now standing full and No. 1 is filling. When compression
-dome chamber No. 4 was filled, water started flowing through timing
-siphon valve No. 4 into timing chamber No. 4 at a rate determined by the
-amount of the opening of the timing valve. As this chamber fills
-compression is transmitted to blow-off trap 4_b_ and when sufficiently
-great this trap is blown and timed siphon No. 4 is put into operation.
-Bed No. 4 is emptied by it, and compression dome chamber No. 4 is
-emptied through the withdraw siphon at the same time. This completes a
-cycle for the filling and emptying of one bed and the method of passing
-the dose on to another bed has been explained. The principle can be
-extended to the operation of any number of beds.
-
-[Illustration:
-
- FIG. 186.—Plural Timed and Alternating Siphons for Contact Bed
- Control.
-
- Courtesy, Pacific Flush Tank Co.
-]
-
-
-
-
- INDEX
-
-
- A. B. C. process of sewage treatment, 4
-
- Abandonment of contract, 225
-
- Access to work, 228, 229
-
- Accident, contractor’s responsibility, 221, 224
-
- Acetylene, explosive, 347
-
- Acid precipitation. _See_ Miles Acid Process.
- of sludge, 503
-
- Acids as disinfectants, 489, 490
-
- Activated sludge. Chapter XVIII, 465–479
- advantages and disadvantages, 469, 470
- aëration tank, 471, 472
- air diffusion, 475, 477
- air distribution, 473–478
- air quantity, 475, 476
- area of filtros plates, 478
- colloid removal, 358
- composition, 465–469
- cost, 478, 479
- definition, 466
- dewatering, 468, 469, 497–505
- fertilizing value, 469, 470
- historical, 470, 471
- how obtained, 478
- nitrogen content, 468
- patent, 471
- process, 465
- quantity, 469
- reaëration tank, 473
- results, 467, 468, 476
- sedimentation tank, 472
-
- Advertisement, 214
-
- Aëration, effect on oxygen dissolved, 373–375
- of sewage, 371, 376, 465–479
-
- Aërobes, 363
-
- Aërobic decomposition, 366, 367
-
- Aftergrowths, 492
-
- Aggregates, specifications, 172–174
-
- Air, see also ventilation, activated sludge, compressed air, etc.
- ejectors, 150
- lock dosing apparatus. Chap. XXI, 506–512
- machinery for activated sludge, 473, 474
-
- Algæ, 363
-
- Alkalinity, 358
-
- Alleys, sewers in, 80
-
- Alum, 407, 408
-
- Alvord tank, 427, 429
-
- Ammonia, 366, 367, 374, 375, 410
- explosives, 297
-
- Analyses, bacteriological, 364
- chemical, 354, 355
- mechanical of sand, 182
- physical, 352–354
- sewage, 352–364
-
- Anaërobes, 363, 365–367
-
- Anaërobic, action, 410
- bacteria, 363
- conditions, 367
- decomposition, 365–367
-
- Ann Arbor, Michigan, Population, 14
-
- Annual expense, method of financing, 157, 158
-
- Ansonia air ejector, 150, 151
-
- Antibiosis, definition, 363
-
- Appurtenances to sewers. Chap. VI, 99–115
-
- Arch, analyses, 204–208
- elastic method, 206–208
- vouissoir analysis, 204–206
- brick construction, 312, 313
- centers for brick sewers, 313
- concrete construction, 318–321
-
- Ardern and Lockett, development of activated sludge, 467, 468, 471
-
- Area of cities, 31
-
- Asphyxiation in sewer gas, 336
-
- Assessments, special, 15, 16
-
- Augers, earth, 21
-
- Automatic, regulators, 117–121
- siphons, flush-tanks, 110
- double alternating, 507
- multiple alternating, 508–512
- timed, 510
- timed and multiple alternating, 510–512
- triple alternating, 508
-
-
- Bacillus, definition and morphology, 362, 363
-
- Backfilling, 328–331
-
- Backfill, puddling, 330
- weight of, 199, 201
-
- Backwater curve, 73
-
- Bacteria, definition and morphology, 362, 363
- good and bad, 363, 364
- nature of, 362, 363
- nitrifying, 431, 432
- sanitary significance of, 364
- in sewage, 362, 363
- total count, 364
-
- Bacterial analyses, results in sewage, 364
-
- Baffles, scum, 404, 413, 414, 421
- in sedimentation tanks, 404
- in septic tanks, 413, 414
- in Imhoff tanks, 421
-
- Balls, for cleaning sewers, 338
-
- Band screen, 384
-
- Barring, definition, 263
-
- Bars for screens, 390
-
- Basins, sedimentation, baffling, 404
- bottoms, 404
- cleaning arrangements, 404
- depth, 401
- economical dimensions, 401–403
- inlets and outlets, 404
- scum boards, 404
- types, 395
-
- Basket handle sewer section, 67, 69
-
- Bathing beaches, pollution, 381
-
- Bazin’s formula, 54
-
- Bearings, for centrifugal pumps, 131, 137, 138
- thrust, 138
-
- Bellmouth, 121, 122
-
- Bends in pipe, loss of head in, 116
-
- Berlin, sewage farm, 460, 461
- sewers, date of, 3
-
- Bids, proposal, 217–219
-
- Bidder’s duties, 215–217
-
- Bio-chemical oxygen demand, 359–361
-
- Biolysis of sewage, 366, 367
-
- Black and Phelps dilution formulas, 377–379
-
- Blasting and explosives, 294–304
- caps, 297, 299, 300
- detonators, 294, 297–300
- firing, 302–304
- fuses and detonators, 297–300
- fuses, delayed action, 291, 300
- fuses, electric, 299, 300
- splicing, 303
- gelatine, 296
- loading holes, 303
- powder, 295
- precautions, 300–302
- priming and loading, 303
- rock, 269
- size of charge, 304, 305
- tunneling, 290, 291
-
- Bleach, characteristics of for disinfection, 491
-
- Block sewer, construction, 311–314
- hollow tile as underdrains, 126
-
- Blocks, vitrified clay, 189, 190
-
- Boilers, steam, 147–150
-
- Boilers, efficiencies, 149
- horse-power, 149
-
- Bond, contractor’s, 213, 214, 232
- issues, 14
-
- Bonds, definition and types, 14–16
-
- Boring underground, 20
-
- Bottom, activated sludge aëration tank, 472
- Imhoff tanks, 423
- sedimentation tanks, 404
- trickling filter, 451, 452
-
- Box sheeting, 272
-
- Branch sewer, defined, 7
-
- Breast boards, 288
-
- Brick, arch construction, 312, 313
- and block sewer construction, 311–315
- invert construction, 311, 312
- sewer construction, 311–315
- arch centers, 313
- invert, 311–312
- organization, 314, 315
- progress, 314
- row lock bond, 312
- specifications, 188, 189
- sewers, life of, 351
-
- Bricks for sewers, 316
-
- British Royal Commission on Sewage Disposal, 4
-
- Broad irrigation. _See_ under Irrigation.
-
- Bucket excavators, 246, 255, 256
-
- Building material, weight of, 201
-
- Burkli-Ziegler formula, 47, 425
-
- Butyrine, 366
-
-
- Cableway excavators, 246, 250–252
-
- Cage screen, 384, 385
-
- Caisson excavation, 285, 286
-
- Calcium carbide, explosive, 347
-
- Calumet pumping station, 128, 142
-
- Cameron septic patent, 411
-
- Capacity of sewers, diagrams, 57–60
-
- Capital, private invested in sewers, 17
-
- Capitalization, method of financing, 157–160
-
- Caps, blasting. _See_ blasting.
-
- Carbohydrate, 366, 367
-
- Carbon, analysis for, 356
- dioxide, 366, 367
-
- Carson Trench machine, 250, 251
-
- Cast-iron pipe, 122, 164, 190, 191
- joints, 164
- quality, 101, 102, 190
-
- Castings, iron, 101, 102
-
- Catch-basins, 99, 107–108, 217
- cleaning, 343, 344
- inspection, 337
-
- Catenary sewer section, 69
-
- Cellars, depth of, 88
-
- Cellulose, 367
-
- Cement. _See also_ Concrete,
- pipe, specifications, manufacture and sizes, 171–179
- vs. concrete, 164
-
- Centrifugal pumps. _See_ pumps, centrifugal.
-
- Centrifuge for sludge drying, 501, 502
-
- Cesspool, 411, 416, 417
-
- Champaign, Illinois, septic tank, 415, 416
-
- Changes in plan, 222, 223
-
- Channeling, definition, 263
-
- Character of surface, 44
-
- Chemical analyses, 354–362
-
- Chemical precipitation, 371, 405–409
- chemicals used, 405–407
- preparation of chemicals, 407, 408
- results, 408, 409
- at Worcester, 408
-
- Chezy formula, 52, 53
-
- Chicago. _See also_ Sanitary District of Chicago.
- drainage canal, 374, 375
- dilution requirement for sewage, 380
- early sewers, 3
- method of sewage disposal, 374
- population and density, 29, 30
- trench excavation in, 248
-
- Chlorine. _See also_ Disinfection.
- disinfectant, 489–493
- in sewage, 358, 374, 375
-
- Chlorine liquid, application, 491, 492
-
- Cholera, transmittable disease, 364
-
- Chromatin, 365
-
- Chutes for concrete, 187
-
- Circular sewer section, hydraulic elements, 65, 66, 69
- types, 70, 71
-
- City, growth of area, 31
- growth of population, 24–28
- legal powers, 219
-
- Clay, life of pipe, 349–351
- manufacture of pipe, 165–167
- specifications for pipe, 168–170
- unglazed for pipe, 165
- vitrified blocks, 167, 189, 190
- vitrified pipe, 165–171
-
- Cleaning, grit chambers, 398, 400
- sedimentation basins, 404
- sewers, cost, 341
- in N. Y. City, 332
- methods, 337–343
- tools, 338–340
- up after completion of work, 228
-
- Coccus, 362
-
- Coefficient of uniformity of sand, 456
-
- Coffin sewer regulator, 117, 118
-
- Colloid, nature of, 358
- treatment for, 358
-
- Color of sewage, 352, 353
-
- Combined sewer system, 78, 79
-
- Commercial districts, characteristics of and sewage from, 32, 34, 35
-
- Compensators for pumps, 142
-
- Compressed air. _See also_ ventilation, tunneling, drilling, etc.
- activated sludge, 473–475
- for drilling, 264–268
- in tunnels, 292–294
- transporting concrete, 320, 321
-
- Concentration, time of flood flow, 41–43, 96, 97
-
- Concrete, aggregates, 172–174
- mixing and placing, 184–188
- pipe, details, 175–179
- manufacture, 171–179
- reinforcement, 177, 178, 209, 210
- pipe, steam process, 176
- sizes, 175
- pressure against forms, 232, 323
-
- Concrete, proportioning, 179–183
- qualities, 179, 180
- reinforcement, placing, 178, 326, 327
- reinforcing steel, quality, 191
- sewer construction, 314–328
- arch, 318–321
- form length, 319
- labor costs, 327, 328
- in open cut, 314–320
- in tunnel, 320, 321
- invert, 315–320
- organization for, 328
- working joints, 319
- sewer costs, 327–329
- strength, 181
- waterproofing, 184
-
- Conduits, special sections, 67, 70, 71
-
- Connections to sewers, ordinances, 344, 345
- record of 92, 238
-
- Construction of sewers, Chap. XI, 233–331
-
- Construction, elements of, 233
- organizations, 315, 328
-
- Contact bed, 432–437, 506
- advantages and disadvantages, 432–434
- automatic control, 437, 506
- cleaning, 435
- clogging, 435
- construction, 434–436
- control, 437, 506
- cycle, 436, 437
- depth, 434
- description, 432, 433
- design, 434–436
- dimensions, 434, 435
- loss of capacity, 435
- material, 435, 436
- multiple, 433, 435
- operating conditions, 432–437
- rate, 435
- results, 433, 434
- ripening, 432
-
- Continuous bucket excavators, 246–250
-
- Contour interval on maps, 79, 80
-
- Contracts, Chap. X, 211–232
- abandonment of, 225
- assignment, 228
- completion of, 222, 228
- bond, 213, 222
- content, 213, 230, 231
- cost-plus, 212, 213
- disputes, 220
- divisions of, 213
- drawings, 213
- engineer as an arbitrator, 220
- the instrument, 230, 231
- interpretation of, 220, 234, 235
- lump sum, 212
- nature of, 211, 212
- sample, 230, 231
- time allowed, 222
- types, 212, 213
- unit-price, 213
-
- Contractor, absence of, 222
- bond, 232
- claims against, 228
- duties, 221
- liability, 224
- relations with other contractors, 228, 229
-
- Contractor’s powder, 294
-
- Control devices, automatic, for sewers, 117–121
- for filters, 500–512
- inspection of, 336, 337
-
- Copper sulphate, disinfectant, 490
-
- Copperas, precipitant, 406–408
-
- Cordeau Bickford, 298, 303
-
- Corrugated iron pipe, 165
-
- Cost. _See_ under item wanted.
-
- Cost, annual. Method of financing, 157–160
- capitalized. Method of financing, 157–160
- classification of, 235–238
- comparisons of. Methods for
- making, 157–160
- collection of data, 10–14, 235–238
- estimate. Method of making, 10–14
- overhead, 237, 238
-
- Couplings, flexible for shafts, 138
-
- Covers, Imhoff tanks, 424
- septic tanks, 415
- trickling filters, 451
-
- Crops on sewage farms, 463, 464
-
- Cunette, 67, 70
-
- Cut, depth of excavation, 88, 92
-
- Cycle, contact bed, 436
- life and death, 367, 431
- nitrogen, 367, 368
- trickling filter, 441
-
- Cylinders, stresses in, 194, 202–204
-
- Cytoplasm, 365
-
-
- Damages, liquidated, 222
- material, 221, 224
-
- Darcy’s formula, 52
-
- Day labor, 211
-
- Decomposition of sewage, 365–367
-
- Definitions. _See_ word defined.
-
- Deflagration, definition, 294
-
- Delays in contract work, 228
-
- Delayed action fuses, 291, 300
-
- Densities. _See_ population.
-
- Depreciation, of sewers, 348–351
- rate of, financial, 158
-
- Depth of sewers, 88
-
- Design conditions, 88–92
- economical, mathematics of, 401–403
- preparations for, 17–23
-
- Detention period, grit chamber, 397
- Imhoff tank, 419
- plain sedimentation, 392–395, 401
- septic tank, 415
-
- Detonation, definition, 294
-
- Detonator. _See_ blasting cap.
-
- Diameter of sewers, 57–60, 72, 88–92
-
- Diaphragm pump, 257, 258
-
- Diesel engine, 152, 154
-
- Digestion chamber, Imhoff tank, 422, 423
-
- Digestion of sludge in separate tank, 427–430, 497
-
- Dilution, amount needed, 377–380
- conditions for success, 372, 373
-
- Dilution, definition, 372
- formulas for quantity, 378–380
- governmental control, 380, 381
- preliminary studies, 381, 382
- in salt water, 376, 377
- in streams, 372–376
- of sewage, 370 and Chap. XIV, 372–382
-
- Diseases, water-borne, 364
-
- Disinfection, 489–493
- action of, 489–491
- bleaching powder, 491
- chlorine, liquid, 491
- amount of, 492
- disinfectants, 489, 490
- purpose, 489
- selective action of disinfectants, 492, 493
-
- Disk screen, 384
-
- Disposal of sewage, _See_ sewage treatment.
-
- Disputes, engineer to settle, 220
-
- Dissolved oxygen. _See_ Oxygen dissolved.
-
- Distribution of sewage,
- contact beds, 436
- irrigation, 461, 462
- nozzles, 442–449
- sand filter, 450–458
- traveling distributor, 442
- trickling filters, 441–451
-
- Districts, character of, 29, 30, 32–37
- classification of, 34, 35
-
- Domestic sewage, defined, 6, 7, 352
-
- Dorr Thickeners, 472, 504
-
- Dortmund tank, 404
-
- Dosing devices, 506–512
- alternating and timed siphons, 500–512
- Alvord device at Lake Forest, 506
- four or more alternating siphons, 509
- operation of automatic siphon, 110
- three alternating siphons, 508
- timed siphons, 510
- two alternating siphons, 507
- types, 506
-
- Dosing tank design, for trickling
- filter, 446–450
-
- Doten tank, 429, 430
-
- Drag line excavators, 255, 256
-
- Drainage areas, 81, 84, 94
-
- Drills, electric, 267
- jack hammer, 264, 265
- punch, 20
- size of cylinder for, 266
- tripod, 264, 265
-
- Drilling, methods, 20–23, 264–270
- depth, diameter and spacing of
- holes, 268–270
- power for, 267, 268
- rate of, in rock, 267
- steam and air, 267, 268
-
- Drop manhole, 100, 101
-
- Drop-down curve, 73, 77
-
- Drum screen, 384
-
- Dry weather flow, 24, 38
-
- Drying sludge. _See_ sludge drying.
-
- Dualin, 296
-
- Duty of contractor. _See_ Contractor, duties
-
- Duty of engineer. _See_ Engineer, duties.
-
- Duty of inspector. _See_ Inspector, duties.
-
- Duty of a pump, defined, 135
-
- Dynamite, 296–298, 300–302, 304, 305
- cartridge, 268, 296, 302
- thawing, 301, 302
-
- Dysentery, 365
-
-
- Earth pressures, theories, 274, 275
-
- Economical dimensions, mathematics of, 401–403
-
- Effective size of sand, defined, 456
-
- Efficiency of a pump, defined, 135
-
- Effluents, character of
- activated sludge, 467, 468
- chemical precipitation, 408
- contact bed, 434
- Imhoff tank, 414, 424, 425, 432
- lime and electricity, 489
- Miles acid process, 484, 485
- sand filter, 453
-
- Effluents, sedimentation tank, 401
- septic tank, 412–414
-
- Egg-shaped section, 67, 68, 70
-
- Ejectors, air, 150, 151
-
- Elastic arch analysis, 206–208
-
- Electric motors, 150–152
-
- Electrolytic treatment, 487–489
-
- Elevations, method of recording, 92
-
- Emergencies, duties of engineer, 235
-
- Emerson pump, 261
-
- Engines, internal combustion, 152–154
- steam, types, 142–144.
-
- Engineer, absence of, 221
- defined, 220
- disputes settled by, 220, 234
- duties of, 9, 10, 220, 233, 234, 238
- individuality and personality, 9, 234
- qualifications, 9
- sanitary, definition, 2
-
- Engineering News pile formula, 125, 126
-
- Entering sewers, precautions, 335, 336
-
- Enzymes, 365
-
- Equipment for construction, 237
-
- Equivalent sections, defined, 72
- solution of problems in, 67–72
-
- Estimates, cost and work done, 10–14
- when made, 226
- data for, 235
-
- Excavation, depth of open cut, 284
- drainage, 252, 262
- hand, 242–245, 249
- economy, 245
- laborer’s ability, 243
- lay out of tasks, 243
-
- Excavation, hand, opening trench, 243
- vs. machine, 245, 249
- tools, 242
- machine, 244–246
- economy, 245
- limitations, 246
- vs. hand, 245, 249
- specifications, 240, 241
-
- Excavating machines, bucket, 246, 255
- cableway and trestle, 246, 250–252
- Carson machine, 250, 251
- continuous belt, 246
- bucket, 246, 247
- drag line, 255
- Potter machine, 251
- steam shovel, 252–254
- tower cableway, 252
- wheel excavators, 246–250
-
- Excavation, machine, organization, 249
- pumping and drainage, 256, 257
- quicksand, 256
- rock, 263, 264
- payment for, 230
- specifications, 240, 241
- trench bottom, 241, 304, 311
-
- Explosions in sewers, 108, 336, 346–348
- causes of, 346
- historical, 346
- prevention, 108, 348
-
- Explosives. _See also_ Blasting.
-
- Explosives, and blasting, 294–304
- ammonia compounds, 297
- blasting gelatine, 296
- contractor’s powder, 294
- deflagrating, 294
- detonating, 294
- detonators, 294, 297–300
- “Don’ts,” 300, 301
- dynamite, 296–298, 300–302, 304, 305
- fuses and detonators, 297–300
- gelatine dynamite, 296
- gunpowder, 295
- handling, 300–302
- nitro-glycerine, 295
- nitro-substitution compounds, 295
- permissible, 297
- quantity, 304, 305
- requirements, 294
- strength of, 297, 298
- T.N.T., 295
- types, 294–297
-
- Exponential formulas for flow of water, 54, 55
-
- Extra work, compensation, 227
-
-
- Facultative bacteria, 363
-
- Fanning’s run-off formula, 49
-
- Farms, septic tanks for, 416, 417
-
- Farming with sewage. _See_ irrigation.
-
- Fats in sewage, 357–359, 366, 367
- from Miles acid process, 485–487
-
- Feathers, for splitting rock, 264
-
- Ferrous sulphate, precipitant, 406–408
-
- Fertilizer from sludge, 470, 495, 497
-
- Fertilizing value of, activated sludge, 470
- sewage, 459, 460
-
- Filter press for sludge, 500, 501
-
- Filters. _See_ under name of filter.
-
- Filtration, of sewage, 370, 371, 431–459
- action in, theory of, 431
- cost, 458, 459
-
- Filtros plates, 477, 478
-
- Finances, mathematics of, 157–160
-
- Financing, methods of, 14–17
-
- Flamant’s formula, 54, 56
-
- Flies on trickling filters, 438
-
- Flight sewer, 101, 102
-
- Flood, crest velocities, 42, 43
- flow computations, 94–98
- McMath formula, 94, 96, 97
- Rational method, 95–98
-
- Flow, laws of, 52
- velocity of, 52, 90, 91
-
- Fluctuations, in rate of sewage flow, 33–38
- in quality of sewage, 368–370
-
- Flush-tanks, automatic, 109–113
- capacity, 111
- details, 110, 112
- inspection of, 336, 337
- payment for, 217
- siphon sizes, 111
-
- Flushing, 109–113, 341–343
- amount of water needed, 112
- methods, 341–343
- manhole, 109
- sewer, defined, 8
-
- Foaming of Imhoff tanks, 425, 426
-
- Foot valves, 141
-
- Force main, defined, 8
-
- Forms, design of, 322, 323
- length of, 319
- materials, 321, 322
- oiling, 174, 186, 322
- specifications, 322
- steel, 325, 326
- steel-lined, 325
- support for, 316, 318
- time in place, 319
- wooden, 323, 324
-
- Formulas, hydraulic, methods for solution, 55–61
- for flow of water, 52–55
- for rainfall. _See_ Rainfall,
- for run-off. _See_ Run-off.
-
- Foundations, 99, 124–126
-
- Franchises for sewers, 17
-
- Free ammonia, 366, 367, 374, 375, 410
-
- Freezing, catch-basins, 108
- concrete, 186, 187
- dynamite, 301, 302
-
- Fresh sewage, characteristics, 352–354
-
- Friction losses. _See_ Head losses.
- flow in pipe, 51, 52
-
- Fuel, consumption by prime movers, 153
- costs, 153
- heat value, 150
-
- Fungus growth in sewers, 333
-
- Fuses. _See_ blasting fuses.
-
-
- Ganguillet and Kutter’s formula, 52–65
-
- Gas, chamber in Imhoff tank. _See_ Scum chamber.
- engines, 152–154
- illuminating, explosive, 347
- sewer, 335, 336
-
- Gasoline, explosive, 108, 109, 335, 346, 347
- engines, 152–154
- and oil separator, 109
- odors, significance, 335, 353
-
- Gearing, reduction for turbines, 140, 146
-
- Gelatine dynamite, 296
-
- Glycerol, 366
-
- Gothic section, 67
-
- Governmental control, stream pollution, 380, 381
-
- Grade, of sewers. _See also_ Slope.
- how given, 281–284
- selection of, 90
- stakes, 221, 281–283
-
- Gravel, specifications, 172
-
- Grease, in sewers, 99, 108, 333, 345
- cutter, 340
- ordinance concerning, 345
- traps, 99, 108
-
- Gregory’s imperviousness formulas, 44, 46
-
- Grit, clogs sewers, 333
- chambers, 127, 397–401
- description, 395, 398
- design, 397, 398
- dimensions, 397, 398
- existing, 398–400
- outlet arrangements, 400
- results, 397
- retention period, 397
- sludge analyses, 397
- units, number of, 400, 401
- velocity of flow in, 396–398
- quantity and character of, 397
-
- Grooves in concrete, working joints, 319
-
- Ground water in sewers, 38, 39, 85, 87, 256, 352
-
- Gun cotton, 296
-
- Gunpowder, 295
-
-
- Hazen, theory of sedimentation, 392–395
- dilution formula, 380
-
- Hazen and William’s formula, 55, 57
-
- Head loss, in bends, 116
- entrance, 115
- friction in straight pipe, 51, 52, 115
-
- Hercules powder, 296
-
- Hering, Rudolph, dilution recommendations, 380
-
- Hering, Rudolph, introduction of Imhoff tank and hydraulic formulas,
- 425
-
- Historical résumé of sewerage and sewage treatment, 2–5
-
- Hitch, tunnel frame, 286, 287
-
- Holes, drill. _See_ Drill holes.
-
- Holidays, work on, 221
-
- Hook for lifting pipe, 304, 306
-
- Horse-power, boiler, 149, 150
- of pumps, 144–146
-
- Horseshoe sewer section, 71
-
- House, connections, record of, 92, 234
- drains, 7, 88, 90
- sewer, defined, 7
-
- Hydraulic, elements, 65, 69
- formulas, 52–55
- jump, 73–74
- principles, 51, 52, 72, 73
- value of settling particles, 393
-
- Hydraulics of, sewers, Chap. IV, 51–77
- circular pipes partly full, 65, 66
- equivalent sections, 72
- non-uniform flow, 72–77
- sections other than circular, 67–72
- use of diagrams, 61–65
-
- Hydrocarbon, 367
-
- Hydrogen sulphide, 353, 366, 410
-
- Hydrolytic tank, 427, 428
-
- “Hypo” as a disinfectant, 491
-
- Hytor Turbo blower, 473, 474
-
-
- Illinois River, self-purification, 374–376
-
- Imhoff tank, and chlorination, costs, 487
- cover, 424
- description, 417–419
- design, 419–424
- digestion chamber, 422
- inlet and outlet, 421
- operation, 426–427
- patent, 418
- results, 414, 424, 425, 439, 467
- sedimentation chamber, 419–422
- scum chamber, 424
- slot, 422
- sludge, 414, 467
- sludge pipe, 423, 424
- status, 425, 426
- and trickling filter, cost, 479
-
- Impeller, for centrifugal pump, 131, 136
-
- Imperviousness, relative, 40, 42, 44–46, 95–97
-
- Industrial, districts, 32–37
- wastes, defined, 7, 352
- tannery, 491
-
- Information and instructions for bidders, 213, 215–217
-
- Inlets, street, 93, 94, 99, 104–107
-
- Inspection, contract stipulations, 221–224
- during construction, 233, 234
- for maintenance, 104, 333–337, 348, 349
-
- Inspector, absence of, 221, 222
- duties, 233–234
- qualifications, 234
-
- Institutional sewage treatment plants, 416, 417
-
- Intercepting sewer, defined, 7
-
- Intermittentsand filter. _See_ Sand filter.
-
- Internal combustion engines, 152–154
-
- Inverted siphon, 113–116
-
- Iron, ferrous sulphate, precipitant, 406–408
- cast. _See_ cast iron.
-
- Irrigation. _See also_ Farming and Sewage farming.
- area required, 463
- Berlin sewage farm, 460, 461
- crops, 463, 464
- description, 459
- fertilizing value of sewage, 460, 470, 495, 498
- vs. farming, 459
- operation, 461–463
- preliminary treatment, 462, 463
- preparation for, 461–463
- process, 459, 460
- sanitary aspects 463
- status, 460, 461
- theory, 432
- in the United States, 461
-
-
- Jack hammer drill, 264, 265
-
- Jetting method, 21–23
-
- Jet pump, 259, 341, 343
-
- Joints, bituminous, 309–311
- in cast-iron pipe, 164
- cement, 307, 308
- inspection of, 234
- lead, 164
- mortar, 307
- open, 307
- poured, 309–311
- cement, 309, 311
- riveted steel, 195, 196
- sulphur and sand, 309
- types, for pipe, 307
- working, in concrete, 319
-
- Junctions, 99
-
-
- Kuichling, run-off rules, 46, 47, 49
- storm intensity formulas, 50
-
- Kutter’s formula, 52–65
-
-
- Labor, day vs. contract, 211
- costs on concrete sewer, 328, 329
-
- Labyrinth packing rings, 136, 137
-
- Lagging, tunnel frames, 287
- for forms, 322
-
- Lagooning sludge, 495–497
-
- Laitance, 186, 188
-
- Lakes, self-purification of, 376
-
- Lampé’s formula, 54
-
- Lampholes, 99, 104
-
- Lateral sewer, defined, 7
-
- Lawrence Experiment Station, 4
-
- Leaping weir, 118–121, 337
-
- Legal requirements, construction, 224
- dilution, 380, 381
- in design, 9
-
- Liernur system, 5
-
- Life, organic in sewage, 363, 364
- of sewers, 348–351
-
- Lime as a precipitant, 405–408
- with electricity, 488, 489
- with iron, 406, 407
-
- Line and grade, 281–284
- how given, 281–283
-
- Liquefaction of sludge, 411–413, 496, 497
-
- Liquid chlorine. _See also_ Chlorine, 491
-
- Liquidated damages, 222
-
- Loads on, pipe, 198–202
- Marston’s method, 198–202
- trench, 199–202
-
- Lock bar pipe, 197
-
- Lock-joint pipe, 177
-
- Long loads, 201
-
-
- Machine excavation. _See_ Excavation.
-
- Macroscopic organisms, 363, 368
-
- Main sewer, defined, 7
-
- Maintenance of sewers, Chap. XII, 332–351
- catch-basin cleaning, 343, 344
- cleaning sewers, 337–343
- complaints, 333
- cost, 341
- entering sewers, 335, 336
- flushing, 109–113, 341–343
- hand cleaning, 341
- inspection, 333–337
- organization, 332
- protection of sewers, 344, 345
- repairs, 337
- tools, 338–341
- troubles, 333
- work involved, 332
-
- Man, shoveling ability, 243
-
- Manholes, 81, 99–104
- bottom, 100
- cover, 102–103
- drop, 101
- flushing, 109, 342
- location and numbering, 81
- payment methods, 217, 218
- steps, 100, 103, 104
-
- Manning’s formula, 55
-
- Map, preliminary, 17, 79, 80, 82, 83
-
- Marsh gas, 347, 366, 367, 410, 415
-
- Marston’s methods for external loads on buried pipe, 198–202
-
- Materials, for sewers, Chap. VIII, 164–193
- measurement of, 236, 237
- record of, 237
- unit weights, 201, 202
-
- McMath’s formula, 47, 48, 94, 95
-
- Meem’s theory of earth pressure, 274, 275
-
- Mercaptan, 367
-
- Metabolism, 365
-
- Methane, 347, 366, 367, 410, 415
-
- Methylene blue, 360
-
- Microscopic organisms, 363, 364, 368
-
- Miles acid process, costs, 487
- amount of acid, 483
- analyses of sludge, 485
- description, 482
- results, 483–487
- sludge, 485
-
- Mineral matter in sewage, 357
-
- Mirror, inspecting device, 334
-
- Money retained by city, 227
-
- Mosquitoes in catch-basins, 108
-
- Motors, electric, 150–152
-
- Municipal, bond, 14, 15
- corporations, 15
-
-
- _n_, value of in Kutter’s formula, 53
-
- New York City, density of population, 29, 31
- siphons under subway, 114
- grease and gasoline trap, 108, 109
- aëration of sewage, 377, 470
- cleaning sewers, 332
- depreciation of sewers, 348–351
-
- Needle beam, 286, 287
-
- Night, soil, 5
- work, 221
-
- Nitrates, 355, 356
-
- Nitrites, 355, 356
-
- Nitrifying organisms, 431, 432
-
- Nitrobacter, 431, 432
-
- Nitro explosives, 295, 296
-
- Nitrogen, cycle, 367, 368
- organic, 355, 356
-
- Nitro-glycerine, 295
-
- Nitrosomonas, 431, 432
-
- Nomograph, 55, 56
-
- Non-uniform flow, 72–77
-
- Nozzles. _See also_ Trickling filters.
- coefficients of discharge, 446
- types, 445
-
- Numbering, drainage areas, 81, 94
- manholes, 81
-
- Nye steam pump, 260, 263
-
-
- Obstructions to construction, 235
-
- Odor of sewage, 353
-
- Oil in sewage, 108, 344–348
-
- Oiling forms, 174, 186, 322
-
- Olein, 366
-
- Ordinances, for protection of sewers, 344, 345
-
- Organisms in sewage, 363, 364, 368
-
- Organic matter, composition, 366
-
- Organizations for construction, 315, 317, 328
-
- Orders, to whom given, 222
-
- Outfall sewer, defined, 8
-
- Outlets, 99, 122–124, 373
-
- Overflow weir, 118–121
- inspection of, 337
-
- Overhead, costs, division of, 10, 237, 238
- -track excavators, 246, 250, 251
-
- Oxidation in streams, 373–376
-
- Oxygen, absorption of, 374–377
- consumed, 355, 356
- demand, 359–361
- computation of, 360
- bio-chemical, 359–361
-
- Oxygen dissolved
- exhaustion of, 366
- in dilution, 381
- solubility, 362
- supersaturation, 361
- concentration for successful dilution, 377–380
- formulas for concentration, 378–380
- significance of in sewage, 359–362
-
- Oysters, contamination of, 372, 489
-
-
- Packing rings, labyrinth type, 136, 137
-
- Palmatin, 366
-
- Parasites, 365
-
- Paris sewage farm, 460
-
- Patents. Protection of City by contractor, 224, 225
-
- Pathogenic bacteria, 364
-
- Pavement, replacing, 329
-
- Payment, final on contract, 228
-
- Payments, methods of making, 217, 218
-
- Periscope inspecting device, 334, 335
-
- Permissible explosives, 297
-
- Phenolphthalein indicator, 408
-
- Photographic records, 238
-
- Piles for foundations, 123–126
-
- Pills for cleaning sewers, 338
-
- Pipe, bedding, 230, 304, 328
- cast-iron. _See_ under cast-iron pipe.
- design of ring, Chap. IX, 194–210
- external loads on, 198–202
- joints. _See_ Joints.
- sewer construction, 304–311
- laying, line and grade, 282–284
- organization, 311
- method of laying, 304, 306, 307
- steel, design, 195–197
- stresses in, external forces, 194, 202–204
- stresses due to internal pressure, 194
- stresses in buried pipe, 198–204
- stresses in circular ring, 202–204
- wood design, 197, 198
-
- Plankton, defined, 363
- in sewage, 368
-
- Plans, changes in contract, 222, 223
-
- Plug and feathers for splitting rock, 264
-
- Pneumatic, collection system, 5
- concreting, 320, 321
-
- Poling boards, in open cut, 271, 272
- in tunnel, 287
-
- Pollution, legal features, 380, 381
-
- Population, density, 28–31
- predictions, 24–27
- served by sewers in the U. S., 3
- sources of information, 27, 28
- and quantity of sewage, 31, 32
-
- Potter trench machine, 251
-
- Powder. _See_ Blasting.
-
- Power pump, 132, 133
-
- Precautions in entering sewers, 335, 336
-
- Precipitants, chemical, 405–407
-
- Preliminary, map, 17, 79, 80, 82, 83
- work, 9, 17–23
-
- Present worth, 158, 160
-
- Pressing sludge, 500, 501
-
- Priming explosives, 302–304
-
- Private, capital, 17
- sewers, 17
-
- Privy, 5
-
- Profile, for brick sewers, 312
- sewer, 92
- surface, 88
-
- Progress, rate of, 222
- reports, 238
-
- Promotion (inception of sewers), 9
-
- Proportioning concrete. _See_ Concrete proportioning.
-
- Proposal (contract), 213, 217–219
-
- Protection of sewers (ordinances), 344, 345
-
- Protein, 366
-
- Puddling, backfill, 330
-
- Pulsometer pump, 260, 261
-
- Pumping, in excavations, 256–263
- selection of machinery, 154–156
- equipment, cost comparison, 162
- station, 128, 142
- costs, 156–163
- equipment, 127, 128
-
- Pumps, air ejector, 150, 151
- capacity, 129, 160–163
- capacity of units, 160–163
- centrifugal, details, 130, 131, 136–138
- automatic control, 141, 142
- characteristics, 138–140
- efficiency, 140
- for excavation, 262
- motors for driving, 150–152
- performance, 138–140
- protection of, by screens, 386
- selection of, 154–156
- setting, 140–142
- turbine, 130–132, 154
- types, 130, 131
-
- Pumps, centrifugal, volute, 130–132, 154
- character of load, 129
- costs, 156, 157
- description of types, 130–134
- for construction work, 256–263
- diaphragm, 257, 258
- direct-acting, 133
- duty of, 135, 136
- efficiencies, 135, 136
- ejector, 134, 150, 151, 259, 341, 343
- jet, 259
- need for, 127
- number of units, 160–163
- packing of, 133, 134
- piston, 133
- speed, 133, 134
- plunger, 133
- power, 132, 133
- reciprocating, 130, 132–135, 154–156
- for excavation, 262
- reliability, 127
- sizes, 135
- steam, 134, 135, 142–146
- consumption, 144, 145
- vacuum, 259, 262
- improvised for trench work, 257
- turbine, 130–132, 154
- volute, 130–132, 154
-
- Putrescibility, 359, 360
-
-
- Quantity, of sewage, 24–50, 84–87
- variations, 33–38
- storm water, 40–50, 94–98
-
- Quicksand, definition, 256
- excavation in, 256
- safeguards, 235
-
- Quiescent water, self-purification, 374
-
-
- Racks. _See_ Screens.
-
- Rainfall, 17, 40, 41, 50, 96, 97
- data, 17
- rate, 96, 97
-
- Rangers, 270–274, 276–279
-
- Rankine’s theory of earth pressure, 275
-
- Rapid sand filtration of sewage, 458
-
- Rational method of run-off determination, 40, 95–98
-
- Reaëration tank in activated sludge, 473
-
- Receiving well, capacity, 129, 130
-
- Reciprocating pumps. _See_ Pumps, reciprocating.
-
- Records, character of, on construction, 238–240
-
- Rectangular sewer section, 67–69
-
- Regulators, 99, 117–121, 337
- inspection of, 337
-
- Reinforced concrete sewer design, 209, 210
-
- Reinforcing steel, specifications, 191
- placing, 326, 327
-
- Reinsch Wurl screen, 384
-
- Relative stability numbers, 359
-
- Relief sewer, defined, 7
-
- Repairs to sewers, 337
-
- Report, engineer’s preliminary, 10
-
- Reservoir, collecting capacity, 129, 130
-
- Residences, septic tanks for, 416, 417
-
- Residential districts, characteristics, 32–37
-
- Residue on evaporation, 356, 357
-
- Rideal’s dilution formula, 379
-
- Ring, design. Chap. IX, 194–210
- stresses in circular, 202–204
-
- River pollution, legal features, 380, 381
-
- Rivers, self-purification of, 373–376
-
- Riveted joints, properties, 196
-
- Rock, blasting, 268, 290, 291
- definition, 263
- drill, data on, 266, 267
- drilling. _See_ also Drilling.
- by hand, 264
- by power, 264–268
- rates, 267
- excavation. _See also_ Excavation.
- payment for, 230
- measurement of, in place, 235
- tunnels, 290, 291
-
- Rods, sewer, 338
-
- Roman ordinance relative to sewers, 2
-
- Roofs. _See_ Covers.
-
- Root cutters, 340
-
- Roots, 333, 340
-
- Row lock bond for bricks, 312
-
- Running water, self-purification, 373–376
-
- Run-off, computations, 17, 40, 46–50, 94–98
-
-
- Safeguards during construction, 221, 241
-
- Salt water, dilution in, 376, 377
-
- Sand, effective size, 456
- uniformity coefficient, 456
- filters, 452–459
- action in, 431, 432, 452–454
- control, 458, 506–510
- description, 452
- dimensions, 456
- distribution systems, 433, 456–458
- dosing, 454–456
- dosing devices, 506–510
- materials, 456
- operation, 454, 455
- preliminary treatment, 455
- rate, 455
- results, 452, 453
- size of sand for, 456
- thickness, 456
- in winter, 455
-
- Sanitary District of Chicago,
- dilution factor, 380
- specifications, for manhole covers, 101, 102
- tunnel cover, 284
- tunnel ventilation, 291
-
- Sanitary engineering, 1, 2
-
- Sanitary sewage, defined, 7, 352
-
- Saph and Schoder’s formula, 54
-
- Saprophytes, 365
-
- Screed, 316
-
- Screens, 383–391
- chlorination and fine screens, costs, 487
- coarse, 386, 391
- data on fine, 388, 389
- design of, 389–391
- fine, 381, 382, 387–389
- fixed, 385, 390
- medium, 386
- movable, 385, 386, 389–391
- moving, 384–386
- openings, 386–389
- protection to pumps, 127, 141
- purpose, 383
- results, 386–389
- sewage treatment by, 371, 381
- size and performance, 386–389
- sizes, 386–391
- types, 384–386
-
- Screening, vs. sedimentation, 383
- purpose, object, 383
-
- Screenings, character of, 386–389
-
- Scum, boards for, septic tanks, 413, 414
- Imhoff tanks, 421
- chamber in an Imhoff tank, 424
- definition, 495
-
- Sediment, velocity of transportation, 396, 397
-
- Sedimentation, 383–405
- definition, 383
- Hazen’s analysis, 392–395
- hydraulic values, 393
- a method of treatment, 370
- object, 383
- Peoria Lakes, 376
- protection of siphons, 113, 114
- results from plain sedimentation, 401
- theory of, 391–395
- transportation of debris, 396
- velocity of, 392, 393
- vs. screening, 383
- velocities, limiting, 396, 397
-
- Sedimentation, basins, arrangement, 394
- baffling, 404
- cleaning, 404
- dimensions, 401–403
- inlet and outlet, 404
- operation, 411
- types, 395
- chamber, Imhoff tank, 419–422
-
- Self-purification of lakes, 376
-
- Self-purification of streams, 373–376
-
- Separate sewer systems, 78–80
-
- Septic action, 353, 365–368, 371, 410, 411, 496, 497
- results, 412, 413
- vs. sedimentation, 411
-
- Septic tank, 411
- baffling, 413, 414
- capacities of small tanks, 417
- for country homes, 416, 417
- covers for, 415
- definition, 411
- design, 413–417
- explosions in, 415
- results, 412, 413
- seeding, 413
- sludge storage, 414
- small, 416, 417
- units, 415
-
- Septic sludge analysis, 414
-
- Septicization. Chap. XVI, 410–430
- a method of treatment, 371
- the process, 410, 411
- results, 412, 413
-
- Settling solids, 357
-
- Sewage and water supply, 32
- aëration, 371, 376, 465–479
- alkalinity of, 358
- analyses, chemical, 355, 369, 467
- interpretation of, 356–362
- physical, 352–354
- average, 352–355
- bacteria, 362–365
- biolysis of, 366, 367
- changes in, rate of discharge of, 33–38
- characteristics, 368–370
- characteristics of, 352–354
- chemical constituents, 354–356
- classification of, 6, 7, 352
- collection, 5
- color, 352, 353
- components and properties, 352–356
- decomposition of, 365–367
- definition, 6, 7, 352
- disposal. _See also_ Sewage treatment.
- methods, 6, 370, 371
- purposes, 370, 371
- domestic, 7, 352
- farming. _See_ Irrigation.
- fertilizing value, 459, 460
- flow fluctuations, 33–38
- ratio of maximum to average, 36, 37, 85
- fresh, 352–354
- gas, 335, 336, 353
- industrial, defined, 7, 352
- life in, 363–365, 368
- odor, 353
- physical, analyses, 352–354
- characteristics, 352–354
- quality variations, 368–370
- quantity. Chap. III, 24–50, and 84, 87
- and population, 31, 32
- of sanitary, 24–40
- variations, 33–38
- sanitary, defined, 7, 352
- septic, 353, 365–368, 371, 410, 411, 496, 497
- stability, 359, 360
- stale, 353
- storm, defined, 7, 352
- strong, 355
- temperature, 353
- turbidity, 353
- treatment processes, 370, 371
- A. B. C., 4
- activated sludge, Chap. XVIII, 465–479
- biological, 371
- chemical, 371
- contact bed, 432–437, 506
- costs, 459
- dilution. Chap. XIV, 372–382
- disinfection, 489–493
- electrolytic, 487–489
- filtration, 431–459
- increase of, 3
- irrigation, 431, 459–464
- mechanical, 471
- Miles acid process, 482–487
- purpose of, 6, 370
- résumé, 6, 370, 371
- sand filter, 452–458
- screening, 383–391
- sedimentation, 391–409, 411
- septicization. Chap. XVI, 410–430
- trickling filters, 437–452
- weak, 355
- and water supplies, 31, 32
-
- Sewerage, definition, 7
- demand for, 2
- design, 78–98
- growth of, 2–4
- historical, 2–4
-
- Sewers, ancient, 2, 3
- capacity, diagrams, 56–60
- cost, 10–14
- definitions of various types, 7, 8
- depth of, 88
- diameter, 58–60, 88–92
- flat grades, 73, 109
- flight, 101, 102
- inspection of, 333–337
- life of, 348–351
- location of, 80, 81, 94
- materials. Chap. VIII, 164–193
- medieval, 3
- pipe, properties of concrete, 175
- design. Chap. IX, 194–210
- vitrified clay, properties, 169–171
- profile, 89, 92
- section of different types, 67–72
- separate system, 78, 79, 82, 86, 87
- slope, 88–92
- storm-water system, 78, 79, 83, 93, 94
- stresses in, 194, 198–204
-
- Shafts, for tunnels, 284–287
-
- Sheeting, 270–280
- alignment, 240, 241
- backfilling, 330
- box, 272
- design, 275–280
- driving, 273
- length, 273
- lumber, 277
- moving, 248
- poling boards, 271, 272, 287
- pulling, 274
- skeleton, 270, 271
- stay bracing, 270
- steel, 252, 280, 281
- thickness, 276–278
- types, 270
- vertical, 270, 272–274
- Wakefield piling, 273
-
- Shellfish contamination, 372, 489
-
- Shields, tunnel, 288–290
-
- Short loads on trenches, 202
-
- Shovels, for hand excavation, 242
- steam. _See_ Steam shovels.
-
- Shovel vane screen, 384
-
- Shoveling by hand, height raised, 244
- performance by one man, 243
-
- Symbiosis, definition, 363
- example, 432
-
- Sinking fund, 158
-
- Siphons, automatic. Chap. XXI, 506–512. _See also under_ Dosing
- devices.
- in flush-tanks, 109–110
- inspection, 337
- operation, 109–110, 506–512
- for trickling filter, 448–451
- true and inverted, 113–117
-
- Skeleton sheeting, 270, 271
-
- Slope, of sewers, 88–92
- of tank bottoms, Imhoff, 419, 423
- sedimentation tank, 404
-
- Skewback, 204
-
- Sludge. Chap. XX, 495–505
- activated. Chap. XVIII, 465–479. _See also under_ Activated sludge.
- analyses, 414, 467, 468, 485, 496
- characteristics, 495
- definition, 495
- digestion tanks, 427–430, 497
- disposal methods, 495
- drying, 497–505
- acid flotation, 503
- beds, 498, 500
- centrifuge, 501–502
- heat, 502, 503
- press, 500–501
- thickeners, 504, 505
- fertilizing value, 470, 495, 497
-
- Sludge, filters, 498–500
- lagooning, 495, 496
- measurement, 427
- press, 500, 501
- sedimentation, 401
- septic analysis, 434
- treatment methods, 495
-
- Soaps, 357
-
- Soil, bearing value, 125
- stack, definition, 7
-
- Solids in sewage, 356–368
-
- Special assessment, 15, 16
-
- Specifications. Chap. X, 211–232
- general, 219–229
- special, 230
- technical, 229, 230
-
- Spiling. _See_ Piles.
-
- Spirillum, 362
-
- Spores, 363
-
- Springing line, 204
-
- Sprinkling filter. _See_ Trickling filter
-
- Square sewer section, 68, 69
-
- Stability, relative, 359–361
-
- Stagnant water, 374
-
- Stakes, contractor to provide, 221
- where driven, 281, 282
-
- Stationing, 92
-
- Stay bracing, 270
-
- Steam boilers, 147–150
-
- Steam, consumption by, pumps, 144, 145
- turbines, 144, 147
- engines, 144, 145
- pumping engines, 142–146
- pumps. _See_ Pumps, steam.
- shovels, 246, 252–254
- turbines, 146, 147
-
- Stearin, 366
-
- Steel, forms. _See_ Forms, steel.
- pipe, 164, 191, 192
- design, 195–197
- specifications, 191
- reinforcement for concrete, 191, 326–327
- sheet piling, 252, 280, 281
-
- Stench, historic in London, 4
-
- Sterilization. _See_ Disinfection.
-
- Storm, sewage, definition, 7, 352
- Storm, sewer system design, 93–98
- water, quantity, 40–50
-
- Storms, extent and intensity, 50
-
- Stream pollution, regulation, 380, 381
-
- Streams, self-purification, 373–376
-
- Street, inlet. _See_ Inlets.
- wash, definition, 352
-
- Stresses, in buried pipe, 198–204
- in circular ring, 194, 202–204
-
- Sub-main, defined, 7
-
- Subsurface surveys, 18–20
-
- Suction for centrifugal pump, 141
-
- Sulphur and sand joint compound, 309
-
- Sunday work, 221
-
- Surface, elevation, 92
- of ground, character, 44–46
- profile, 88
- water, 7, 352
-
- Surveys, underground, 18–20
-
- Suspended matter, 357
-
-
- Talbot’s run-off formula, 49
-
- Tamping, backfilling, 328–331
-
- Tannery wastes, disinfection, 491
-
- Taxation, general, 16, 17
-
- Taylor nozzles, 444, 445
-
- Temperature of sewage, 353
-
- Templates, brick sewers, 312
-
- Thawing dynamite, 301, 302
-
- Tide gate, 122
-
- Timbering tunnels, 286–288
-
- Timber, strength of, 277
-
- Time of concentration, 41–43, 95–97
-
- Tools, for cleaning sewers, 337–341
- excavating, 242, 246
-
- Tower cableways, 252
-
- Trade wastes. _See_ Industrial wastes.
-
- Traps, in catch-basins, 107
- grease, gasoline, and oil, 108, 109
- in street inlets, 104, 105
-
- Travis tank, 427, 428
-
- Tree roots, 333, 340
-
- Tremie, 187, 188
-
- Trench, backfilling, 328–331
- blasting in, 244, 269
- bottom, shape of, 241, 304, 311
- breaking surface, 243, 244
- drainage, 256–263
- excavating, by hand, 242–245
- machine, 244–256
- guarding and lighting, 221
- layout of tasks, 243
- length of open, 241, 248
- line and grade, 281–284
- location, 243, 281
- opening, 243, 244
- pumps, 256–263
- sheeting, 270–280
- width, 240, 241, 246
-
- Trestle excavators, 250, 251
-
- Trickling filter, 437–452
- advantages, 438, 439
- covers for, 451
- depth, 441, 442
- description, 437, 438
- dimensions, 442
- distribution of sewage, 442–451
- dosing siphon, 446–451
- dosing tank, 446–451
- head lost, 438
- insects, 438
- material, 441
- nozzles, 442–451
- layout, 447–451
- odors, 438, 439
- operation, 441
- rate, 441
- results, 439, 440
- siphon size, 449–451
- underdrainage, 451, 452
- unloading, 431, 437
-
- Tripod drill, 265
-
- Triton, 295
-
- Troubles with sewers, causes, 333
-
- Trumpet arch, 121
-
- Trunk sewer, defined, 7
-
- Tunnels, 283–294
- backfilling, 331
- breast boards, 288
- brick invert, 313
- compressed air in, 292–294
- concrete construction, 320, 321
- depth of cover, 284
- line and grade in, 283
- machines, 290
- rock, 290–292
- shafts, 284–286
- shield, 288–290
- timbering, 284–288
- ventilation, 291, 292
-
- Turbidity of sewage, 353
-
- Turbine, for cleaning sewers, 340
- pumps, 130, 132
- steam, 146, 147
-
- Typhoid fever, 364
-
-
- U-shaped sewer section, 67, 69, 71
-
- Underdrains for, sewers, 126
- trickling filters, 451, 452
-
- Underground surveys, 18–20
-
- Unexpected situations, 235
-
- Uniformity coefficient of sand, 456
-
- Unloading of filters, 431, 437
-
- Urea, 367
-
-
- Valuation of sewers, 332, 348–351
-
- Velocities, depositing, 395–397
- distribution of, 51
- flow in sewers, 90
- over surface of ground, 42
- limiting for sedimentation, 396, 397
- limiting in sewers, 396, 397
- principles of flow in sewers, 51
- transporting, 396
-
- Ventilation, air pressures, 291
- compressed air, 292–294
- pipes, 291
-
- Ventilation, of sewers, 102, 103, 335
- tunnel, 291
-
- Vertical sheeting, 270–274
-
- Vitrified clay. _See_ Clay vitrified.
-
- Volatile matter in sewage, 357
-
- Volute pumps, 130, 132, 154
-
- Vouissoir arch analysis, 204
-
-
- Wakefield piling, 273
-
- Wales, 288
-
- Waste pipe, defined, 7
-
- Wastes. _See_ Industrial wastes.
-
- Water consumption, 31–33
- flow of, 51–77
- rate of steam engines, 144, 145
- supply and sewage flow, 31–33
-
- Watershed. _See_ Drainage area.
-
- Weight, of backfill, 199
- of building material, 201
- of moving loads, 200, 202
-
- Well, hole, 101
- points, 262, 263
-
- Wheel excavator, 246–250
-
- Wing screen, 384
-
- Wood, forms. _See_ Forms.
- pipe, materials, 164, 165, 190, 192, 193
- design, 197, 198
- working strength of, 277
-
- Work, extra, 227
- preliminary to design, 9
- Sunday, night, and holiday, 221
-
- Workmen, competent, 227
- dishonesty, 233, 234
-
------
-
-Footnote 1:
-
- Frontinus and the Water Supply of Rome, p. 81, by Clemens Herschel.
-
-Footnote 2:
-
- Estimated by G. W. Fuller, Trans. Am. Society of Civil Engineers, Vol.
- 44, 1905, p. 148. The total population connected with sewerage systems
- was assumed to be the total population in the United States in cities
- over 4000 in population.
-
-Footnote 3:
-
- Estimated by Metcalf and Eddy, American Sewerage Practice, Vol. III,
- p. 240.
-
-Footnote 4:
-
- Computed from report of the United States Census, 1920, on the same
- basis as Fuller’s estimate for 1905.
-
-Footnote 5:
-
- Cosgrove, History of Sanitation.
-
-Footnote 6:
-
- Sedgwick: Sanitary Science and Public Health.
-
-Footnote 7:
-
- No detrimental effect on the public health was noted as a result of
- this condition however. It has never been conclusively proven that
- such nuisances are detrimental to the public health.
-
-Footnote 8:
-
- Moore and Silcock, Sanitary Engineering, p. 67, 1909.
-
-Footnote 9:
-
- Similar to the definition proposed by the Am. Public Health Assn.
-
-Footnote 10:
-
- Definition recommended by Am. Public Health Assn.
-
-Footnote 11:
-
- Ibid.
-
-Footnote 12:
-
- Ibid.
-
-Footnote 13:
-
- Eng. News, Vol. 76, 1916, p. 781. See also Eng. News-Record, Vol. 85,
- 1920, pp. 22, 1175.
-
-Footnote 14:
-
- For a more extensive treatment of the subject see Principles and
- Methods of Municipal Administration by W. B. Munro, 1916.
-
-Footnote 15:
-
- Eng. Record, Vol. 74, 1916, p. 263.
-
-Footnote 16:
-
- Professional paper No. 46, United States Geological Survey, 1906, p.
- 97.
-
-Footnote 17:
-
- United States Geological Survey, Water Supply paper No. 257, 1911.
-
-Footnote 18:
-
- From Eng. Cont., Vol. 41, 1914, p. 698.
-
-Footnote 19:
-
- Max. represents only the average maximum, not the greatest maximum.
-
-Footnote 20:
-
- Eng. News-Record, Vol. 80, page 1233, 1918.
-
-Footnote 21:
-
- Infiltration of Ground Water into Sewers. Transactions of the American
- Society of Civil Engineers, Vol. 76, 1913, p. 1909.
-
-Footnote 22:
-
- A comprehensive discussion of rainfall formulas will be found in Vol.
- 54 of the Transactions Am. Society of Civil Engineers, 1905.
-
-Footnote 23:
-
- Formula devised by H. E. Babbitt from Allen’s 25–year curve.
-
-Footnote 24:
-
- See Note under Table 14.
-
-Footnote 25:
-
- Sewerage by A. P. Folwell.
-
-Footnote 26:
-
- From an article by E. Kuichling in Transactions American Society of
- Civil Engineers, Vol. 65, 1909, p. 399.
-
-Footnote 27:
-
- Trans. Am. Society Civil Engineers, Vol. 58, 1907, p. 483.
-
-Footnote 28:
-
- Trans. American Society of Civil Engineers, Vol. 58, 1907, p. 498.
-
-Footnote 29:
-
- Ibid.
-
-Footnote 30:
-
- The principles governing the run-off from large areas are explained in
- Elements of Hydrology, by A. F. Meyer, 1917.
-
-Footnote 31:
-
- Transactions of the American Society of Civil Engineers, Vol. 51,
- 1903, p. 11.
-
-Footnote 32:
-
- Municipal and County Engineering, Vol. 58. 1920, p. 164.
-
-Footnote 33:
-
- Industrial waste Treated as ground water.
-
-Footnote 34:
-
- For diagrams for the Solution of the Rational Method, see Eng.
- News-Record, Vol. 83, 1919, p. 868 and Vol. 85, 1920, p. 151.
-
-Footnote 35:
-
- Municipal and County Engineering, October, 1909.
-
-Footnote 36:
-
- “Cleaning and Flushing Sewers.” Journal of the Association of
- Engineering Societies, Vol. 33, 1904, p. 212.
-
-Footnote 37:
-
- Notes on the Design and Principles of Sewage Siphons, Eng.
- News-Record, Vol. 85, 1920, p. 1041.
-
-Footnote 38:
-
- From A. E. Phillips, Trans. Am. Society of Municipal Improvements,
- 1898, p. 70.
-
-Footnote 39:
-
- Trans. Am. Society of Civil Engineers, Vol. 15, 1886.
-
-Footnote 40:
-
- True Siphon at East Providence, Eng. News-Record, Vol. 85, 1920, p.
- 862.
-
-Footnote 41:
-
- “The Effect of Mouthpieces on The Flow of Water Through a Submerged
- Short Pipe,” by F. B. Seely. Bulletin No. 96, 1917, of the Eng’g.
- Experiment Station of the University of Illinois.
-
-Footnote 42:
-
- Trans. Am. Society of Civil Engineers, Vol. 49, 1902.
-
-Footnote 43:
-
- Described by W. L. Stevenson before the Boston Society of Civil
- Engineers in 1916.
-
-Footnote 44:
-
- Multiple Outlet for Calumet Intercepting Sewer, by S. T. Smetters,
- Eng. News-Record, Vol. 83, 1919, p. 728.
-
-Footnote 45:
-
- “Direct Acting Steam Pumps,” by F. R. Nickel, 1915.
-
-Footnote 46:
-
- From Heat Engines, by Allen and Bursley.
-
-Footnote 47:
-
- “The Economy Resulting from the Use of Variable Speed Induction Motors
- for Driving Centrifugal Pumps” by M. L. Enger and W. J. Putnam.
- Journal Am. Water Works Ass’n., 1920, Vol. 7, p. 536.
-
-Footnote 48:
-
- C. A. Hague in Trans. Am. Society of Civil Engineers, Vol. 74, 1911,
- p. 20.
-
-Footnote 49:
-
- Includes screen chamber, collecting reservoir, and building.
-
-Footnote 50:
-
- Computed on the assumption that the pumps may be operated at 50 per
- cent overload for short periods, the rated capacity being equal to the
- loads given in Table 33.
-
-Footnote 51:
-
- For description of type see note under Table 35.
-
-Footnote 52:
-
- Proceedings Illinois Society of Engineers, 1916, page 81.
-
-Footnote 53:
-
- Municipal Engineers’ Journal for April, 1918.
-
-Footnote 54:
-
- Workability involves ease in placing and smoothness of working.
-
-Footnote 55:
-
- Johnson’s Materials of Construction, 5th Edition, 1918, p. 432.
-
-Footnote 56:
-
- Trans. Am. Society of Civil Engineers, Vol. 59, 1907, p. 146.
-
-Footnote 57:
-
- L. N. Edwards, Trans. Am. Society Testing Materials, 1918, and R. B.
- Young, Eng. News-Record, Vol. 82, 1919, p. 33.
-
-Footnote 58:
-
- Bulletin No. 1, Structural Materials Research Laboratory, Lewis
- Institute, Chicago, Illinois.
-
-Footnote 59:
-
- Proportioning Concrete by Voids in the Mortar, A. N. Talbot, read
- before Am. Society Testing Materials, June 22, 1921. Abstract in Eng.
- News-Record, Vol. 87, 1921, p. 147.
-
-Footnote 60:
-
- Trans. Am. Society of Civil Engineers, Vol. 81, 1917, p. 1122.
-
-Footnote 61:
-
- See also Tentative Specifications for Concrete and Reinforced Concrete
- submitted by the Joint Committee to its Constituent Organizations,
- June 4, 1921.
-
-Footnote 62:
-
- Journal Illinois Society of Engineers for 1916, p. 75.
-
-Footnote 63:
-
- See A. S. T. M. Standards for 1918, p. 148.
-
-Footnote 64:
-
- Trans. Am. Society Civil Engrs., Vol. 82, 1918, p. 459.
-
-Footnote 65:
-
- See Trans. Am. Society Civil Eng., Vol. 82, 1918, p. 482.
-
-Footnote 66:
-
- See Trans. Am. Society Civil Engr., Vol. 41, 1899, p. 76, and Vol. 82,
- 1918, p. 433, Eng. News, Vol. 74, 1915, p. 400, and Vol. 75, 1916, p.
- 911.
-
-Footnote 67:
-
- Trans. Am. Soc. Civil Engrs., Vol. 82, 1918, p. 433.
-
-Footnote 68:
-
- Bulletin No. 31 of the Engineering Experiment Station of the Iowa
- State College of Agriculture.
-
-Footnote 69:
-
- From bulletin No. 31, Engineering Experiment Station, Iowa State
- College of Agriculture.
-
-Footnote 70:
-
- From Bulletin No. 31, Engineering Experiment Station, Iowa State
- College of Agriculture.
-
-Footnote 71:
-
- From Bulletin No. 31, Engineering Experiment Station, Iowa State
- College of Agriculture.
-
-Footnote 72:
-
- From Vouissoir Arches by Cain.
-
-Footnote 73:
-
- Baker’s Masonry, 10th Edition, p. 676.
-
-Footnote 74:
-
- Business Law for Engineers, C. Frank Allen, McGraw-Hill, 1917;
- Engineering Contracts and Specifications, J. B. Johnson, McGraw-Hill,
- 1904; Contracts in Engineering, J. I. Tucker, McGraw-Hill, 1910; The
- Law Affecting Engineers, W. V. Ball, Archibald Constable, 1909; Law
- and Business of Engineering and Contracting, C. E. Fowler,
- McGraw-Hill, 1909; The Economics of Contracting, D. J. Hauer, E. H.
- Baumgartner, 1915; The Elements of Specification Writing, R. S. Kirby,
- John Wiley & Son, 1913; Contracts, Specifications and Engineering
- Relations, D. W. Mead, McGraw-Hill, 1916; Engineering and
- Architectural Jurisprudence, J. C. Wait, John Wiley, 1912.
-
-Footnote 75:
-
- See article by E. W. Bush in Eng. News-Record, Vol. 85, 1920, p. 122.
-
-Footnote 76:
-
- An unbalanced proposal is one in which the bids on some of the items
- are obviously low and on other items are obviously or suspiciously
- high. The purpose of submitting unbalanced bids is to keep secret the
- true or supposed cost of the work to the contractor or to obtain more
- money by bidding high on those items which are believed to have been
- underestimated by the Engineer. A low bid is made on other items in
- order to keep down the total amount of the bid.
-
-Footnote 77:
-
- Taken mainly from specifications of the Sanitary District of Chicago
- and the Baltimore Sewerage Commission, with miscellaneous selections
- from other sources.
-
-Footnote 78:
-
- Restrictions are placed on work done outside of ordinary working hours
- in order that the Contractor may not perform work in the absence of an
- engineer or inspector.
-
-Footnote 79:
-
- Cost Keeping and Management, by Gillette and Dana. Practical Cost
- Keeping for Contractors, by F. R. Walker. Cost Keeping in Sewer Work,
- by K. O. Guthrie in Eng. Contracting, Vol. 28, p. 238, 1905. Sewer
- Construction Records at Scarsdale, Eng. News-Record, Vol. 83, p. 111,
- 1919.
-
-Footnote 80:
-
- See Planning and Progress on a Big Construction Job, by Chas. Penrose,
- Eng. News-Record, Vol. 84, 1920, pp. 554 and 627.
-
-Footnote 81:
-
- See also “Ownership and Operation of Trench Excavators by the Water
- Department of Baltimore,” by V. B. Seims, presented before Am. Water
- Works Association, June 9, 1921.
-
-Footnote 82:
-
- Eng. and Contracting, Vol. 48, 1917, p. 492.
-
-Footnote 83:
-
- Earth Excavation by A. B. McDaniel.
-
-Footnote 84:
-
- Courtesy, Sanitary District of Chicago.
-
-Footnote 85:
-
- See article by J. R. Gow, Journal New England Waterworks Ass’n, Sept.,
- 1920, also Public Works, Vol. 50, p. 98.
-
-Footnote 86:
-
- Diameter of diaphragm.
-
-Footnote 87:
-
- Gallons per minute.
-
-Footnote 88:
-
- Eng. News, Vol. 75, 1916 p. 1050.
-
-Footnote 89:
-
- Mun. Engineering, Vol. 53, p. 6.
-
-Footnote 90:
-
- For types of drill bits see article by T. H. Proske, Mining and
- Scientific Press, March 5, 1910.
-
-Footnote 91:
-
- These intermediate holes are seldom more than 3 feet apart.
-
-Footnote 92:
-
- Earth Pressures, Old Theories and New Test Results, Eng. News-Record,
- Vol. 85, 1920, p. 632.
-
-Footnote 93:
-
- Trans. Am. Society Civil Eng’rs, Vol. 60, 1908.
-
-Footnote 94:
-
- Adopted by the Am. Ry. and Maintenance of Way Ass’n in 1907.
-
-Footnote 95:
-
- Tunneling Machines Successful on Detroit Sewers, Eng. News-Record,
- Vol. 84, 1920, p. 329.
-
-Footnote 96:
-
- Rules on Compressed-Air Work of N. Y. State Industrial Commission,
- Eng. News-Record, Vol. 85, 1920, p. 1225.
-
-Footnote 97:
-
- Taken mainly from the Engineer Field Manual of the U. S. Army; Safety
- Factors in the Use of Explosives by W. O. Snelling, Technical Paper
- No. 18, U. S. Bureau of Mines; and an article in Eng’g and
- Contracting, Vol. 52, 1919, p. 585.
-
-Footnote 98:
-
- See paper by C. T. Hall before Am. Inst. Chemical Engineers.
-
-Footnote 99:
-
- Per cubic yard of material displaced.
-
-Footnote 100:
-
- Eng. News, Vol. 75, 1916, p. 592.
-
-Footnote 101:
-
- Pressure of Concrete on Forms Measured in Tests, by E. B. Smith,
- before Am. Concrete Institute, Feb. 15, 1920. Abstracted in Eng.
- News-Record, Vol. 84, 1920, p. 665.
-
-Footnote 102:
-
- See, also, Concrete Form Design, by E. F. Rockwood, Eng. and
- Contracting, Vol. 55, 1921, p. 528.
-
-Footnote 103:
-
- Includes 6 cents per foot for excavation. Labor for this was 58 per
- cent of the total labor cost.
-
-Footnote 104:
-
- Cement at $1.25 per barrel.
-
-Footnote 105:
-
- Mun. Journal, Vol. 36, 1914, p. 736.
-
-Footnote 106:
-
- Mun. Journal, Vol. 39, 1915, p. 911.
-
-Footnote 107:
-
- Formerly the Municipal Journal.
-
-Footnote 108:
-
- See Eng. Record, Vol. 75, 1917, p. 463.
-
-Footnote 109:
-
- Eng. Record, Vol. 73, 1916, p. 141, and Eng. News-Record, Vol. 79,
- 1917, p. 1019.
-
-Footnote 110:
-
- Eng. Record, Vol. 72, 1915, p. 690.
-
-Footnote 111:
-
- Eng. Record, Vol. 71, 1915, p. 256.
-
-Footnote 112:
-
- Eng. and Contr., Vol. 41, 1914, p. 250.
-
-Footnote 113:
-
- H. J. Kellogg in Journal Connecticut Society of Civil Engineers, 1914,
- and Technical Paper 117, U. S. Bureau of Mines.
-
-Footnote 114:
-
- Eng. News, Vol. 70, 1913, p. 1157.
-
-Footnote 115:
-
- Technical Paper No. 117, U. S. Bureau of Mines.
-
-Footnote 116:
-
- Eng. News, Vol. 71, 1914, p. 84.
-
-Footnote 117:
-
- Eng. News, Vol. 71, 1914, p. 82.
-
-Footnote 118:
-
- Similar to definition proposed by the Am. Public Health Ass’n.
-
-Footnote 119:
-
- Economic Values in Sewage and Sewage Sludge, by Raymond Wells,
- Proceedings Am. Society Municipal Improvements, Nov. 12, 1919. Eng.
- News-Record, Vol. 83, 1919, p. 948.
-
-Footnote 120:
-
- Sample boiled for five minutes.
-
-Footnote 121:
-
- Sample immersed in boiling water for 30 minutes.
-
-Footnote 122:
-
- Four months.
-
-Footnote 123:
-
- One week in March, 1914.
-
-Footnote 124:
-
- R represents any chemical element such as K, Na, etc.
-
-Footnote 125:
-
- Standard Methods of Water Analysis, American Public Health
- Association, 1920.
-
-Footnote 126:
-
- Routine tests are ordinarily incubated for this period only, and if
- not decolorized in this time are recorded as stable.
-
-Footnote 127:
-
- Determination of the Biochemical Oxygen Demand of Sewage and
- Industrial Wastes, by E. J. Theriault, Report of the U. S. Public
- Health Service, Vol. 35, May 7, 1920, No. 19, p. 1087.
-
-Footnote 128:
-
- Standard Methods of Water Analysis, American Public Health
- Association, 1920.
-
-Footnote 129:
-
- Jordan, General Bacteriology, 1909, p. 91.
-
-Footnote 130:
-
- Ibid.
-
-Footnote 131:
-
- Reprinted in Vol. III of Contributions from the Sanitary Research
- Laboratory of Massachusetts Institute of Technology.
-
-Footnote 132:
-
- Formerly Chief Engineer of the Sanitary District of Chicago.
-
-Footnote 133:
-
- From “Sewage,” by Samuel Rideal, 1900, p. 16.
-
-Footnote 134:
-
- See Am. Civil Engineers’ Pocket Book, Second Edition, p. 982.
-
-Footnote 135:
-
- Trans. Am. Society Civil Engineers, Vol. 58, 1907, p. 988.
-
-Footnote 136:
-
- Not defined by the American Public Health Association.
-
-Footnote 137:
-
- Trans. Am. Society Civil Engineers, Vol. 78, 1915, p. 892.
-
-Footnote 138:
-
- Removal of Suspended Matter by Sewage Screens, Cornell Civil Engineer,
- 1914. Abstracted in Engineering and Contracting, Vol. 41, 1914, p.
- 451.
-
-Footnote 139:
-
- “The Clarification of Sewage by Fine Screens,” Trans. Am. Society
- Civil Engineers, Vol. 78, 1915, p. 1000.
-
-Footnote 140:
-
- Langdon Pearse, Trans. Am. Society Civil Engineers, Vol. 78, 1915, p.
- 1000.
-
-Footnote 141:
-
- Meshes per inch.
-
-Footnote 142:
-
- See article by Henry Ryon in Cornell Civil Engineer, 1910.
-
-Footnote 143:
-
- The hydraulic coefficient is defined as the rate of settling in mm.
- per second.
-
-Footnote 144:
-
- Definition suggested by the American Public Health Association.
-
-Footnote 145:
-
- Computed from formula by Gilbert in “Transportation of Debris by
- Running Water,” U. S. Geological Survey, Professional Paper No. 86,
- 1914. Diameter in mm. = (1.28 (velocity)^{2.7})⁄(Sp. gv. − 1).
-
-Footnote 146:
-
- Computed from Annual Report of the Superintendent of Sewers, Nov. 30,
- 1919, and 1920.
-
-Footnote 147:
-
- These figures are for 1919.
-
-Footnote 148:
-
- These figures are for 1905.
-
-Footnote 149:
-
- These figures are for 1902.
-
-Footnote 150:
-
- Report of the Ohio State Board of Health, 1908, page 425.
-
-Footnote 151:
-
- Definition proposed by the Am. Public Health Assn.
-
-Footnote 152:
-
- See Eng. News. Vol. 73, 1915, p. 410.
-
-Footnote 153:
-
- Sewage Treatment from Single Houses and Small Communities, by L. C.
- Frank. U. S. Public Health Service, Bulletin 101, 1920.
-
-Footnote 154:
-
- Eng. News-Record, Vol. 78, 1917, p. 566.
-
-Footnote 155:
-
- Municipal Engineering, Vol. 54, p. 149.
-
-Footnote 156:
-
- Eng. Record, Vol. 68, 1913, p. 452.
-
-Footnote 157:
-
- Am. Sewerage Practice, Vol. III, p. 437.
-
-Footnote 158:
-
- Trans. Am. Society Civil Engineers, Vol. 83, 1920, p. 337.
-
-Footnote 159:
-
- Eng. News-Record, Vol. 83, 1919, p. 510.
-
-Footnote 160:
-
- See Eng. News, Vol. 70, 1913, p. 1112; Eng. Record, Vol. 68, 1913, p.
- 440, and Eng. News, Vol. 75, 1916, p. 1028.
-
-Footnote 161:
-
- See Eng. Record, Vol. 67, 1913, p. 232.
-
-Footnote 162:
-
- The use of half-spray nozzles is not always advocated as it is
- considered that their use does not markedly improve the distribution.
- Where half nozzles are used, a margin of 18 inches to 2 feet should be
- allowed between the edge of the filter and the nozzle, to prevent the
- blowing of raw sewage from the filter.
-
-Footnote 163:
-
- From paper by E. G. Bradbury in Proceedings of the Ohio Eng. Society,
- 1910, p. 79.
-
-Footnote 164:
-
- The effective size of sand is the diameter in millimeters of the
- largest grain in that 10 per cent, by weight, of the material which
- contains the smallest grains.
-
-Footnote 165:
-
- The uniformity coefficient is the ratio of the diameter of the largest
- particle of the smallest 60 per cent, by weight, to the effective
- size.
-
-Footnote 166:
-
- Interest at 6 per cent.
-
-Footnote 167:
-
- Worcester figures.
-
-Footnote 168:
-
- This method may show a profit from the sale of sludge.
-
-Footnote 169:
-
- Sewage Disposal, 1919, p. 223.
-
-Footnote 170:
-
- See Eng. News, Vol. 9, 1883, p. 203, and Vol. 29, 1893, p. 27.
-
-Footnote 171:
-
- American Sewerage Practice, Vol. III.
-
-Footnote 172:
-
- Reference 11, at end of this chapter.
-
-Footnote 173:
-
- Reference 15.
-
-Footnote 174:
-
- Reference 2.
-
-Footnote 175:
-
- For mechanical methods of drying sludge, see Reference 22, p. 1127,
- and No. 33, p. 843.
-
-Footnote 176:
-
- Reference 10.
-
-Footnote 177:
-
- Reference 13.
-
-Footnote 178:
-
- University of California, Bulletin 251, 1915.
-
-Footnote 179:
-
- Reference 25.
-
-Footnote 180:
-
- See Report by Black & Phelps of Metropolitan Sewerage Commission,
- 1911, reprinted as Vol. VII of Contributions from the Sanitary
- Research Laboratory of the Massachusetts Institute of Technology.
-
-Footnote 181:
-
- See Reports, Mass. State Board of Health.
-
-Footnote 182:
-
- Reference 47.
-
-Footnote 183:
-
- Reference 10.
-
-Footnote 184:
-
- Reference 10.
-
-Footnote 185:
-
- Reference 10.
-
-Footnote 186:
-
- Hatton, reference 33.
-
-Footnote 187:
-
- Reference 18.
-
-Footnote 188:
-
- Reference 1, at end of this chapter.
-
-Footnote 189:
-
- Reference 2.
-
-Footnote 190:
-
- Reference 6.
-
-Footnote 191:
-
- Reference 5.
-
-Footnote 192:
-
- Reference 6.
-
-Footnote 193:
-
- Reference 6.
-
-Footnote 194:
-
- Reference 8.
-
-Footnote 195:
-
- Reference 20.
-
-Footnote 196:
-
- Reference 17.
-
-Footnote 197:
-
- Reference 19.
-
-Footnote 198:
-
- Reference 21.
-
-Footnote 199:
-
- Reference 24.
-
-Footnote 200:
-
- Inorganic Chemistry, by Alexander Smith.
-
-Footnote 201:
-
- American Public Health Association definition.
-
-Footnote 202:
-
- Sewage Sludge by Allen.
-
-Footnote 203:
-
- Sewage Disposal by Kinnicutt, Winslow and Pratt.
-
-Footnote 204:
-
- Sewage Disposal by Fuller.
-
-Footnote 205:
-
- Sewage Sludge by Allen.
-
-Footnote 206:
-
- From Eng. News-Record, Vol. 84, 1920, p. 995.
-
-Footnote 207:
-
- A Simple Mechanical Control for Dosing Sewage Beds, by P. Thompson,
- Eng. News-Record, Vol. 84, 1920, p. 1018.
-
-Footnote 208:
-
- Sewage Disposal by Kinnicutt, Winslow and Pratt.
-
-Footnote 209:
-
- Design of Siphon by G. H. Bayles, Eng. News-Record, Vol. 84, 1920, p.
- 974.
-
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