Mo. Code Regs. Ann. tit. 10, § 20-8.200
PURPOSE: This rule specifies the minimum standards for the design of lagoons and wastewater irrigation alternatives that are part of wastewater collection and treatment systems. This rule is to be used with rules 10 CSR 20-8.110 through 10 CSR 20-8.210. It does not address all aspects of design, and the design engineer may refer to other appropriate reference materials so long as these minimum standards set forth in this rule are met.
PUBLISHER’S NOTE: The secretary of state has determined that the publication of the entire text of the material which is incorporated by reference as a portion of this rule would be unduly cumbersome or expensive. This material as incorporated by reference in this rule shall be maintained by the agency at its headquarters and shall be made available to the public for inspection and copying at no more than the actual cost of reproduction. This note applies only to the reference material. The entire text of the rule is printed here.
(1) Applicability. Wastewater systems that utilize lagoons and wastewater irrigation alternatives shall be designed based on criteria contained in this rule, published standards, applicable federal and state requirements, standard textbooks, current technical literature, and applicable safety standards. In the event of any conflict between the above criteria, the requirement in this rule shall prevail.
(2) Supplementary Field Data for the Facility Plan. The facility plan shall contain pertinent information on location, geology, soil conditions, area for expansion, and any other factors that will affect the feasibility and acceptability of the proposed project, including the information required per 10 CSR 20-8.110. The following information must be submitted:
(B) Geohydrological Evaluation. A geohydrological evaluation shall be requested on all new earthen basins, earthen basin major modifications, new wastewater irrigation sites, and subsurface absorption fields.
basins shall not be located in areas with a severe collapse potential rating.
(D) Where geosynthetic liners are used in storage or treatment basins for wastewaters of an industrial nature, the application shall:
structure material is capable of containing the wastewater for at least twenty (20) years;
dures in the event of leakage or damage to the seal; and
containment or leakage detection and collection devices for corrosive or reactive wastewaters and for toxic materials.
(3) Basis of Design.
(A) Area and Loadings for Discharging Lagoons.
shall not exceed thirty-four pounds per day per acre (34 lbs/day/acre) at the three-foot (3') operating depth in the primary cells.
shall be capable of:
dissolved oxygen within a particular cell with one (1) unit in the cell out of service;
oxygen level of two milligrams per liter (2 mg/L) in the lagoon at all times;
pounds of oxygen per pound of biochemical oxygen demand removed (1.4 lbs O2/1 lb BOD); and
sixth tenths pounds of oxygen per pound of ammonia nitrogen removal (4.6 lbs O2/1 lb NH3).
(4) Lagoon Construction Details.
(A) Embankments and Berms.
tively impervious material and compacted to at least ninety-five percent (95%) maximum dry density test method to form a stable structure.
eight feet (8') to permit access of maintenance vehicles.
(2').
vided that—
ting of berms;
erwise constructed to prevent erosion; and
sample to be collected, if discharging.
(C) Lagoon Seal. 10 CSR 20-8
that seepage loss is as low as possible and has a design permeability not exceeding 1.0 x 10- 7 cm/sec.
the compacted clay liner must be twelve inches (12"). For permeability coefficients greater than 1.0 × 10-7 cm/sec or for heads over five feet (5') such as an aerated lagoon system, the following formula shall be used to determine minimum seal thickness, Equation 200-1: Equation 200-1
H × K
t = ______________________ 5.4 × 10-7 cm/sec
where: K = the permeability coefficient of the soil in question; H = the head of water in the lagoon; and t = the thickness of the soil seal.
thickness may vary due to liner material, but the liner thickness shall be no less than twohundredths inch (.02") or twenty (20) mil and be the appropriate material to perform under existing conditions.
drainpipes where they pass through the lagoon seal.
(D) Influent Lines.
not be used due to corrosion problems.
invert at least six inches (6") above the maximum operating level of the lagoon, prior to the entrance into the primary cell, and provide sufficient hydraulic head without surcharging the manhole. For manhole installation, follow the provisions listed in 10 CSR 8.120(4).
along the bottom of the lagoon so that the top of the pipe is just below the average elevation of the lagoon seal; however, there shall be an adequate seal below the pipe.
(5) Covers for Lagoon Retrofits.
(6) Surface Irrigation of Wastewater.
(B) Wetted Application Area. The wetted application area is the land area that is normally wetted by wastewater application. The wetted application area must be:
having a flood frequency greater than once every ten (10) years;
2. Established—
(150') from existing dwellings or public use areas, excluding roads or highways;
property line;
from any sinkhole, losing stream, or other structure or physiographic feature that may provide direct connection between the ground water table and the surface;
from any existing potable water supply well not located on the property. Adequate protection shall be provided for wells located on the application site;
lands, ponds, gaining streams (classified or unclassified; perennial or intermittent); and
or the wastewater is disinfected, the setbacks established in subsections (A)–(E) above may be decreased if the applicant demonstrates the risk is mitigated.
the construction permit application or the facility plan, the—
lized;
limited and not expected to be present.
(C) Preapplication Treatment. At a minimum, treatment prior to irrigation shall provide performance equivalent to that obtained from a primary wastewater lagoon cell designed and constructed in accordance with sections (3) and (4) of this rule, except that the lagoon depth may be increased to include wastewater storage in addition to the primary volume.
based on the design wastewater flows and net rainfall minus evaporation expected for a one (1) in ten (10) year twenty-four (24) hour return frequency for the storage period selected and shall meet the minimum storage days listed below.
located in Scott, Stoddard, Butler, Dunklin, New Madrid, Pemiscot, Mississippi, McDonald, Newton, Jasper, Lawrence, Barry, Stone, Taney, Christian, Green, Webster, Douglas, Ozark, Howell, Texas, Dent, Shannon, Oregon, Ripley, Carter, Reynolds, Iron, Madison, Wayne, Cape Girardeau, Barton, Dade, Perry, and Bollinger counties.
ed in Vernon, Bates, Henry, St. Clair, Cedar, Dallas, Polk, Hickory, Benton, Cooper, Morgan, Moniteau, Miller, Cole, Camden, Laclede, Pulaski, Phelps, Maries, Osage, Gasconade, Franklin, Jefferson, St. Louis, Ste. Genevieve, St. Francois, St. Charles, and Crawford counties.
facilities located in Cass, Johnson, Pettis, Platte, Jackson, Clay, Ray, Lafayette, Carroll, Saline, Chariton, Randolph, Howard, Boone, Callaway, Audrain, Monroe, Ralls, Pike, Lincoln, Warren, and Montgomery counties.
facilities located in Atchison, Holt, Andrew, Nodaway, Worth, Gentry, DeKalb, Harrison, Daviess, Grundy, Mercer, Putnam, Sullivan, Linn, Macon, Adair, Schuyler, Scotland, Clark, Knox, Lewis, Shelby, Buchanan, Clinton, Caldwell, Livingston, and Marion counties.
that operate and generate flows only from April through October season, a minimum storage capacity of forty-five (45) days shall be provided. For facilities that operate or generate flows only from November through March, the minimum storage listed in subsection (A)–(D) above is required.
(D) Application Rates and Soils Information. The application rates for each individual site shall be based on topography, soils, geology, hydrology, weather, agricultural practice, adjacent land use, and application method. Application of wastewater shall not be allowed during periods of ground frost, frozen soil, saturated conditions, or precipitation events. In design of the application rates, the following shall apply:
rate at the design sustained permeability rate except for short periods when initial soil moisture is significantly below field capacity. Do not exceed an hourly rate of one-half (½) the design sustained permeability for slopes exceeding ten percent (10%).
rates on soil moisture holding capacity, antecedent rainfall, and depth to the most restrictive soil permeability.
four inches per year (24"/yr), the application rate cannot exceed one inch (1") per day and three inches (3") per week.
ty-four inches per year (24"/yr), the application rate cannot exceed the values determined in the soils report and loading design. Follow the provisions in 10 CSR 20-8.110(7), Soils Reports for additional information.
tion rate not to exceed ten percent (10%) of the design sustained soil permeability rate for the number of days per year when soils are not frozen.
(E) The applicant shall defer the grazing of animals or harvesting of forage crops, as listed below, following wastewater irrigation, depending upon ambient air temperature and sunlight conditions.
forage harvesting during the period from May 1 to October 31 of each year; and
age harvesting during the period from November 1 to April 30 of each year.
(F) Public Access Areas. Wastewater shall be disinfected prior to irrigation (not storage) in accordance with 10 CSR 20-8.190.
of the indicator organisms as possible and in no case contain more than one hundred twenty-six (126) Escherichia coliform colony forming units per one hundred milliliters (126 cfu/ 100 ml);
an area when irrigation is being conducted; and
all piping and sprinklers associated with the distribution or transmission of wastewater shall be color-coded and labeled or tagged to warn against the consumptive use of contents.
(7) Subsurface Absorption Systems.
(A) Site Restrictions.
1. Subsurface systems shall—
that have been highly compacted and/or disturbed, such as old road beds, foundations, or similar things;
where slopes are less than two percent (2%);
water diversion where necessary, such as a curtain or perimeter drain; and
the property line.
bottom of the drip lines and/or the trench and a limiting layer, including but not limited to, bedrock; restrictive horizon; or seasonal high water table, shall be no less than:
dispersing secondary or higher quality effluent; or
karst features are present unless the site can be reclassified.
(8) Low Pressure Pipe (LPP) Subsurface Systems.
(A) Design.
accordance with the following equations, Equation 200-2 and Equation 200-3: Equation 200-2 Q A = ______ LTAR
and Equation 200-3 A L = ______ 5 ft where: A = Minimum LPP soil treatment area (square feet (sq.ft)) L = Minimum total length of LPP trench (ft) Q = Maximum daily wastewater flow (gallons per day (gpd)) LTAR = Long term acceptance rate (gpd/sq.ft). This is the lowest reported LPP soil loading rate between the soil surface and at least twelve inches (12") below the specified LPP trench bottom, or as approved by the Missouri Department of Natural Resources (department).
distribution piping and fittings with polyvinyl chloride (PVC) shall meet ASTM Standard D 1785 Standard Specification for Poly(Vinyl Chloride) (PVC) Plastic Pipe, Schedules 40, 80, or 120 as approved and published August 1, 2015, or equivalent rated to meet or exceed ASTM D2466 Standard Specification for Poly(Vinyl Chloride) (PVC) Plastic Drain, Waste, and Vent Pipe and Fittings as approved and published August 1, 2017. These standards shall hereby be incorporated by reference into this rule, as published by ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. This rule does not incorporate any subsequent amendments or additions.
protection while assuring uniform distribution and to minimize drain down of laterals into other laterals at a lower elevation between dosing events.
(C) Orifices and Orifice Shielding.
be designed to provide a distribution of no more than six square feet per orifice with an orifice size of not less than one-eighth inch.
and maintained at the end of each lateral to be no less than two feet (2 ft) (0.87 psi) when using three-sixteenth inch (3/16") or larger diameter orifices, and no less than five feet (5 ft) (2.18 psi) when using orifices smaller than three-sixteenth inch (3/16").
(9) Drip Dispersal Subsurface Systems.
(A) Design.
and buffers must be factored into the total area required for the drip dispersal system.
sized with the minimum soil treatment area and total length, in accordance with the following equations, Equation 200-4 and Equation 200-5: Equation 200-4 Q A = ______ HLR Equation 200-5 A L = ______ 2 feet Where: A = Minimum soil treatment area (square feet (sq. ft)) Q = Maximum daily wastewater flow (gallons per day (gpd)) HLR= Maximum hydraulic loading rate determined in the soils report (gpd/sq.ft) L = Minimum total length (ft)
(B) Lines.
placed at a minimum depth of six inches (6") below the surface.
be placed at a minimum on a two foot (2') spacing to achieve even distribution of the wastewater and maximum utilization of the soil.
AUTHORITY: section 644.026, RSMo 2016.* Original rule filed Aug. 10, 1978, effective 10 CSR 20-8 March 11, 1979. Amended: Filed June 15, 2018, effective Feb. 28, 2019. *Original authority: 644.026, RSMo 1972, amended 1973, 1987, 1993.