On-Site Wastewater Treatment and Disposal Systems - Forced ...

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7.3.3.7 Seasonal, Multifamily, and Commercial Applications Use of evaporation and evaporation/infiltration lagoons for summer homes would result in somewhat reduced area requirements per gallon of wastewater handled, since storage would not need to be provided during the winter months. Otherwise, application of these systems to seasonal dwellings is comparable to year-round residences. Evaporation and evaporation/infiltration lagoons are also applicable to multifamily and commercial applications, although additional ,pretreatment may be required depending on the wastewater characteristics. 7.4 Outfall to Surface Waters Direct discharge of onsite treatment system effluent is a disposal op- tion if an appropriate receiving water is available and if the regula- tory agencies permit such a discharge. The level of treatment required varies, depending on local regulations, stream water quality requirements, and other site-specific conditions. In general, onsite treatment system effluent disposed by surface discharge must at least meet secon- dary treatment standards for publicly owned treatment works. Depending on site-specific conditions, more stringent BOD and SS discharge requirements and/or limitations on N and P discharges may be applicable. The performance, operation, and maintenance requirements, and the environmental acceptability of the surface discharge depend predominantly on the preceding treatment system. Operation and maintenance associated specifically with the surface discharge pipe are minimal in a gravity situation. If the effluent must be pumped, then routine pump maintenance will be required. Discharge pipes should be made of corrosion- and crush-resistant materi- als such as cast iron or rigid plastic pipe. For single-family systems, the pipe should range from 2 to 4 in. (5 to 10 cm) in diameter, should be buried, and should be moderately sloped (between 0.5 and 3%). Steep slopes may cause washout at the discharge point. 7.5 References 1. Bendixen, T. W,, M. Berk, J. P. Sheehy, and S. R. Weibel. Studies on Household Sewage Disposal Systems, Part II. NTIS Report No. PB 216 128, Environmental Health Center, Cincinnati, Ohio, 1950. 96 PP* 316
2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. Bouma, J. Unsaturated Flow During Soil Treatment of Septic Tank Effluent. J. Environ. Eng. Div., Am. Sot. Civil Eng., 101:996-983, 1975. Manual of Septic Tank Practice. Publication No. 526, Public Health Service, Washington, D.C., 1967. 92 pp. Small Scale Waste Management Project, University of Wisconsin, Madison. Management of Small Waste Flows. EPA 600/Z-78-173, NTIS Report No. PB 286 560, September 1978. 804 pp. Laak, R. Pollutant Loads From Plumbing Fixtures and Pretreatment to Control Soil Clogging. J. Environ. Health, 39:48-50, 1976. Winneberger, J. H., L. Francis, S. A. Klein, and P. H. McGauhey. Biological Aspects of Failure of Septic Tank Percolation Systems; Final Report. Sanitary Engineering Research Laboratory, University of California, Berkeley, 1960. Winneberger, J. T., and J. W. Klock. Current and Recommended Prac- tices for Subsurface Waste Water Disposal Systems in Arizona. En- gineering Research Center Report No. ERC-R-73014, College of Engi- neering Service, Arizona State University, Tempe, 1973. Subsurface Wastewater Disposal Regulations. Plumbing Code, Part II. Department of Human Services, Division of Health Engineering, Augusta, Maine, 1978. Weibel, S. R., T. W. Bendixen, and J. B. Coulter. Studies on Household Sewage Disposal Systems, Part III. NTIS Report No. PB 217 415, Environmental Health Center, Cincinnati, Ohio, 1954. 150 PP* Corey, R. B., E. J. Tyler, and M. V. Olotu. Effects of Water Soft- ener Use on the Permeability of Septic Tank Seepage Fields. In: Proceedings of the Second National Home Sewage Treatment Symposium, Chicago, Illinois, December 1977. American Society of Agricultural Engineers, St. Joseph, Michigan, 1978. pp. 226-235. Machmeier, R. E. Town and Country Sewage Treatment. Bulletin 304, University of Minnesota, St. Paul, Agricultural Extension Service, 1979. Otis, R. J., G. D. Plews, and D. H. Patterson. Design of Conven- tional Soil Absorption Trenches and Beds. In: Proceedings of the Second National Home Sewage Treatment Symposium, Chicago, Illinois, December 1977. American Society of Agricultural Engineers, St. Joseph, Michigan, 1978. pp. 86-99. 317
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DE SIGN MANUAL WASTEWATER TREATMENT
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FOREWORD Rural and suburban communi
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Chapter CONTENTS Page FOREWORD ACKN
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Number FIGURES Wastewater Managemen
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FIGURES Number Page ne Saturator Sa
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FIGURES Number Page Use of Metal Ho
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Number TABLES Selection of Disposal
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Number TABLES (continued) Operati o
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TABLES (continued) Number Page of D
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In many areas, onsite systems have
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2.1 Introduction CHAPTER 2 STRATEGY
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subsurface soil absorption is the p
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features of the site (See 3.3.1 and
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2.2.2 System Selection With the pot
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2.2.4 Onsite System Management Past
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determined largely by the physical
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16 - I ,
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Step Client Contact Preliminary Eva
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FIGURE 3-2 EXAMPLE OF A PORTION OF
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Property USDA Texture Flooding Dept
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TABLE 3-3 SOIL SURVEY REPORT INFORM
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found for a subsurface soil absorpt
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Instrument Supported - Abney Level:
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FIGURE 3-8 PREPARATION OF SOIL SAMP
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Sandy Loam + _. ,i . L Silt Loam Cl
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Depth (Ft.) 0 2 4 6 8 10 12 14 Text
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Grade Structureless Weak Moderate S
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Excavated Soil Material (Tamped in
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If test results agree with this tab
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Percolation test FIGURE 3-15 PERCOL
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mm..--- - --- FIGURE 3-16 COMPILATI
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FIGURE 3-16 (continued) 0 Texture S
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13. Winneberger, J. T. Correlation
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is the overall socioeconomic status
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FIGURE 4-l FREQUENCY DISTRIBUTION F
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extreme, however, minimum and maxim
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4i2.2.2 Individual Activity Contrib
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and the resultant wastewater charac
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TABLE 4-7 TYPICAL WASTEWATER FLOWS
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TABLE 4-9 FIXTURE-UNITS PER FIXTURE
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4.3.2 Wastewater Quality The qualit
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* FIGURE 4-3 STRATEGY FOR PREDICTIN
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12. Witt, M. Water Use in Rural Hom
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5.2 Water Conservation and Wastewat
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5.2.2 Water-Saving Devices, Fixture
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TABLE 5-2 (continued) Total Flo Red
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Generic Typea Description Pit Privy
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TABLE 5-4 WASTEWATER FLOW REDUCTION
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5.2.2.3 Clotheswashing Devices and
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Generic Typea Description Mixing Va
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TABLE 5-6 WASTEWATER FLOW REDUCTION
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TABLE 5-7 EXAMPLE POLLUTANT MASS RE
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FIGURE 5-l EXAMPLE STRATEGIES FOR M
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In most situations, projections of
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FIGURE 5-3 FLOW REDUCTION EFFECTS O
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5.7 References 1. 2. 3. 4. 5. 6. 7.
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6.1 Introduction CHAPTER 6 ONSITE T
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l SauJUOdtUo3 lesodsip pue JuJmeJJa
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318QaQEi33aNON 01-9 3msu simaotld N
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SNOIlQ~tl9I~N03 1NQld 39QI3Qd NOIlQ
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El-9 31av1 S3ItX-US 01313 1INt-l 31
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d. Method of Aeration Oxygen is tra
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contain electrical components, they
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control that results in power savin
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TABLE 6-16 OPERATIONAL PROBLEMS--EX
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I TRICKLING FILTFR FIGURE 6-12 EXAM
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presents suggested design ranges fo
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Item Media Tank Aeration System RBC
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Observation Filter Ponding Filter F
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TABLE.6-21 HALOGEN PROPERTIES (27)
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The use of chlorine as a disinfecta
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HOC1 , would predominate. It is cle
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6.5.2.5 Construction Features a. Fe
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e Wastewater FIGURE 6-14 IODINE SAT
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(experience with some units indicat
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directing flow through and around t
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FIGURE 6-17 TYPICAL UV STERILIZING
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Shigella TABLE 6-25 UV DOSAGE FOR S
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Cleaning of quartz glass enclosures
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the bubble diffuser units to lo-30
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TABLE 6-26 POTENTIAL ONSITE NITROGE
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Nitrification of septic tank efflue
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Influe? Effluent 0 Tank Denitrifica
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solution. It can be used to remove
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TABLE 6-27 POTENTIAL ONSITE PHOSPHO
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Anionic polyelectrolytes can be use
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component of the onsite treatment s
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7. 8. 9. 10. 11. 12. 13. 14. 15. 16
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30. 31. 32. 33. 34. 35. 36. 37. 38.
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58. 59. 60. 61. 62. 63. 64. 65. 66.
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7.1 Introduction CHAPTER 7 DISPOSAL
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7.2.1.2 System Selection The type o
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Distribution FIGURE 7-2 TYPICAL BED
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TABLE 7-l SITE CRITERIA FOR TRENCH
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TABLE 7-2 RECOMMENDED RATES OF WAST
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can slough off the sidewall. These
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FIGURE 7-3 ALTERNATING TRENCH SYSTE
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FIGURE 7-4 PROVISION OF A RESERVE A
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FIGURE 7-5 TRENCH SYSTEM INSTALLED
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TABLE 7-4 DOSING FREQUENCIES FOR VA
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The depth of the porous media may v
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Distr Pipe, FIGURE 7-6 TYPICAL INSP
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against freezing and to stabilize .
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Pertodic Deternvne Cause u O&loadin
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oils, and greases, can cause failur
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4" Inspection Pip FIGURE 7-9 SEEPAG
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The same guidelines used in locatin
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Straw, Hay or Fabric? FIGURE 7-10 T
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I tern Landscape Position Slope Typ
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The acceptable depth to an impermea
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FIGURE 7-12 PROPER ORIENTATION OF A
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Mound Height TABLE 7-9 DIMENSIONS F
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Example 7.1: Calculation of Mound D
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1.0 + 1.4 = - t 0.75 + 1.5 1 [ = (3
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. Fill Placement Step 1: Place the
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7.2.4.6 Considerations for Multi-Ho
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7.2.5.2 Application a. Site Conside
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7.2.6 Artificially Drained Systems
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---- FIGURE 7-17 UNDERDRAINS USED T
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periods, particularly on level site
Page 284 and 285: TABLE 7-11 DRAINAGE METHODS FOR VAR
Page 286 and 287: high water table elevation. To prev
Page 288 and 289: FIGURE 7-18 TYPICAL ELECTRO-OSMOSIS
Page 290 and 291: 7.2.8.1 Design a. Single Line . Sin
Page 292 and 293: Inlet From Pretreatment or Previous
Page 294 and 295: watertight Pipe & Joints1 FIGURE 7-
Page 296 and 297: ox networks (see Figure 7-23). Howe
Page 298 and 299: 280 s P 4
Page 300 and 301: FIGURE 7-26 LATERAL DETAIL - TEE TO
Page 302 and 303: To simplify the design of small pre
Page 304 and 305: FIGURE 7-29 RECOMMENDED MANIFOLD DI
Page 306 and 307: Step 3: Select lateral diameter. Fo
Page 308 and 309: Step 8: Select proper pump or sipho
Page 310 and 311: Friction loss in 25 ft 2. Velocity
Page 312 and 313: FIGURE 7-32 DISTRIBUTION NETWORK FO
Page 314 and 315: In summary, the final network desig
Page 316 and 317: 7.2.8.3 Construction FIGURE 7-33 SC
Page 318 and 319: Since the network is pressurized, s
Page 320 and 321: FIGURE 7-35 CROSS SECTION OF TYPICA
Page 322 and 323: The capillary rise characteristic o
Page 324 and 325: The hydraulic loading rate is deter
Page 326 and 327: during the critical months of the y
Page 328 and 329: 7.3.3 Evaporation and Evaporation/I
Page 330 and 331: FIGURE 7-37 TYPICAL EVAPORATION/INF
Page 332 and 333: October November December January F
Page 336 and 337: 13. 14. 15. 16. 17. 18. 19. 20. 21.
Page 338 and 339: 38. 39. 40. 41. 42. 43. 44. 45. 46.
Page 340 and 341: The grease traps discussed here are
Page 342 and 343: Type of Fixture Restaurant kitchen
Page 344 and 345: Removable Slab Inlet --CL Tee with
Page 346 and 347: - 8.3.3 Factors Affecting Performan
Page 348 and 349: The pumping head is calculated by a
Page 350 and 351: liquid level drops, the weights los
Page 352 and 353: 8.3.5 Construction The tank must be
Page 354 and 355: Hori FIGURE 8-6 TOP VIEW OF DIVERSI
Page 356 and 357: 9.1 Introduction CHAPTER 9 RESIDUAL
Page 358 and 359: Parameter TABLE 9-2 CHARACTERISTICS
Page 360 and 361: Parameter Total Coliform Fecal Coli
Page 362 and 363: 9.4.1 Land Disposal Four methods ca
Page 364 and 365: TABLE 9-4 (continued) Alternative D
Page 366 and 367: W z Process Lagooning (1)(13)(14) (
Page 368 and 369: Process Description Liouid Stream S
Page 370 and 371: 11. 12. 13. 14. 15. 16. 17. 18. 19.
Page 372 and 373: Some of the techniques discussed ma
Page 374 and 375: 10.3.1 State Agencies Except for th
Page 376 and 377: 10.3.4.1 Private Nonprofit Institut
Page 378 and 379: 10.4.1.1 Standards for Site Suitabi
Page 380 and 381: Scope of Activities Perform inspect
Page 382 and 383: Scope of Activities Perform necessa
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10.4.4.1 Inspections Inspections co
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SYSTEM 1. U.S. Bureau of Reclam$t~o
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FIGURE A-2 TEXTURAL TRIANGLE DEFINI
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Class Platelike. with one dimension
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saturation may be necessary to conf
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the porosity of soils containing mo
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FIGURE A-5 SOIL MOISTURE RETENTION
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A.3.3 Flow of Water Through Layered
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GLOSSARY A horizon: The horizon for
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following chemical flocculation; wi
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floodway: A channel built to carry
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ped: A unit of soil structure such
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solids: Material in the solid state
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TECHNICAL REPORT DATA (Please read
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