South Carolina Code of Regulations
Chapter 61 - DEPARTMENT OF HEALTH AND ENVIRONMENTAL CONTROL
Subchapter 61-9 - Water Pollution Control Permits
Subchapter 61-9.505 - LAND APPLICATION PERMITS AND STATE PERMITS
Part C - LAND APPLICATION PERMIT AND STATE PERMIT CONDITIONS
Section 61-9.505.C.42 - Additional conditions applicable to specified categories of Land Application permits and State permits

Universal Citation: SC Code Regs 61-9.505.C.42

Current through Register Vol. 48, No. 9, September 27, 2024

The following conditions, in addition to those set forth in section505.41, apply to all Land Application permit or State permits within the categories specified below:

(a)R.61-9.122.42(a) and (b)(a) and (b) shall apply.

(b) Irrigation of treated wastewater. This includes all methods of surface application, including but not limited to, fixed gun application, travelling or mobile gun application, or center pivot application.

(1) Spray field slopes shall not exceed 10 percent unless approved by the Department. The Department may require that slopes be less than 10% based on site conditions.

(2) Effluent distribution systems shall be designed so that the distribution pattern maximizes uniform application. The Department may require the permittee to modify existing land application site(s) distribution systems based on site conditions (e.g., potential for ponding, runoff, or discharges to open ditches).

(3) Soil borings may be required by the Department to depict the lithologic and hydrogeologic characteristics of the subsurface. The requirements of R.61-67 would apply.

(4)
(i) At proposed spray sites with satisfactory soil conditions, design application rates for hydraulic loading shall not exceed (with the exception of seasonal application) the rates shown in Table I (unless one of the conditions in (4)(ii)-(vi) apply) :

Table I

Depth to Seasonal High Water (or measured high water depth, e.g. piezometer readings)

Design Application Rate (gallons per day per acre) (gpd/acre)

5 feet or more

2 inches/week (in/wk), 7,758 gpd/acre

4 feet

1 in/wk, 3,879 gpd/acre

3 feet

0.5 in/wk, 1,940 gpd/acre

less than 3 feet

no application (unless otherwise

(ii) The applicant may request intermediate loading rates, if the seasonal high water table is between the depths shown in the table.

(iii) If the seasonal high water table (or measured high water depth e.g. piezometer readings), is less than three (3) feet, the Department may consider permitting the land application site if the domestic wastewater facilities are designed to meet monthly average effluent limits for 5-day Biochemical Oxygen Demand (BOD5) of 10 mg/l, Ammonia nitrogen (NH3-N) of 2 mg/l and Nitrate (N) of 10 mg/l, or industrial facilities with non-process wastewater or other suitable wastes. The Department may eliminate some or all of the groundwater monitoring requirements for these facilities.

(iv) The application rate may be limited based on pollutant loading including any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471). The applicant for domestic wastewater or other systems with a nitrate/nitrogen loading may be required to provide the Department, a nitrate to nitrogen loading balance to determine if the application rates shown in Table I shall be adjusted.

(v) The Department may consider application rates in excess of two (2) inches per week for sites that meet the depth to groundwater shown in Table I, provided the application period is only for a portion of the year, or the application is for reclaimed water. The applicant must provide sufficient information to the Department to justify a higher application rate (information required may include, but is not limited to a water balance for the summer season).

(vi) For Domestic wastewater facilities designed to meet monthly average effluent limits of a 5-day Biochemical Oxygen Demand (B0D5) of 10 mg/l, NH3-N of 2 mg/l and Nitrate of 10 mg/l, or industrial facilities with non-process wastewater, or other suitable wastes. If the seasonal high water table (or measured high water depth e.g. piezometer readings), for the land application site is three (3) feet or more, the Department may eliminate some or all of the groundwater monitoring requirements for these facilities.

(5) The design application frequency for effluent irrigation shall not exceed a spray to rest ratio suitable for the soil conditions. A spray to rest ratio of 1:20 shall be used unless an alternative rate is approved by the Department. The application frequency for other activities (such as sludge or septage application) would be determined on a site specific basis.

(6) The application site shall be divided into designed spray areas to meet this spray to rest ratio and a continuous application period per defined spray area shall be designed not to exceed 1.2 hours per day, or up to 8 consecutive hours per week (only under those limited conditions when excessive rainfall on the application sites requires application in one day). If the design application rate on a daily basis is exceeded, the Department may require the permittee to provide additional spray application area or alternative disposal methods may be required (e.g. expanding storage capacity for effluent at the facility). Alternative application periods (such as golf course irrigation) may be approved by the Department.

(7) For permitted spray disposal areas which already receive irrigation (e.g. stormwater, potable water or well water), the effluent application rates may be modified by the Department to correspond to the depth to the measured high water table or to the seasonal high water table, whichever is more shallow.

(8) The new or expanding spray field shall be at least 200 feet from surface waters of the State, occupied buildings and potable water wells unless otherwise approved by the Department. The new or expanding spray field shall be at least 100 feet from the property boundary except for golf courses where it shall be at least 75 feet. The Department may require modification to existing permitted spray fields to control the application areas by the addition or expansion of a buffer zone. The applicant may request the buffer zone for specific spray areas be eliminated for sites where the adjacent property owner agree to the elimination of the buffer in writing. The Department may approve an elimination of the buffer zone based on the information provided by the applicant.

(9) A dike or berm around the perimeter of the spray field may be required in specific areas determined by the Department as necessary to prevent potential surface runoff from entering or leaving the spray site. The Department may consider alternate methods of runoff controls that may be proposed by the applicant.

(10) A system for monitoring the quality of groundwater shall also be established for the proposed spray site (for those systems requiring groundwater monitoring). The location of all the monitor wells shall be approved by the Department. The applicant shall provide at least one monitoring well up-gradient of the spray area and at least two groundwater monitoring wells down-gradient. For larger spray fields, more than three groundwater monitoring wells may be required. For land application on golf courses with secondary effluent limits, nine monitor wells shall be provided for 18 fairways (or one groundwater well per two fairways for differing course sizes). The Department may reduce the number of groundwater monitoring wells required based on site conditions (e.g. a significant number of existing groundwater monitoring wells in a small area with multiple golf courses, or existing groundwater monitoring data).

(11) Groundwater samples for new application sites (for those systems requiring groundwater monitoring) shall be analyzed for the following parameters. Background groundwater sampling data may be required for new sites prior to the use of the site using similar parameters. For existing or expanding sites the Department may eliminate any parameter based on actual site information, wastewater characteristics or the groundwater data from consistent wastewater plant operations. Groundwater sampling may be required for existing sites (with no current groundwater monitoring wells), or expanding sites prior to the permitting of the expansion, to determine actual groundwater conditions.
(i) Water table elevation and water table depth

(ii) [Reserved]

(iii) Chloride

(iv) Ammonia (NH3)

(v) Nitrate (N)

(vi) [Reserved]

(vii) pH (field)

(viii) Sodium

(ix) Total dissolved solids (TDS) This parameter may be added to the continuing groundwater monitoring based on the result of field specific conductance.

(x) Field specific conductance

(12) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required (in a permit) to be monitored in groundwater.

(13) The Department may require the applicant provide a nutrient balance which may include, but not be limited to, nutrient uptake of the proposed groundcover, crop or silviculture, design application rates, size and soil conditions present, and the total nutrient loading to the application site. The Department may adjust the application rates to each site based on the nutrient balance.

(c) Rapid Infiltration.

(1) New or expansions.
(i) New or expanding rapid infiltration basins must be limited to sites where the minimum separation of seasonal high groundwater table will remain 15 feet or more below the basin bottom throughout the year. Consideration may be given to separation of the seasonal high water table by less than 15 feet based on an evaluation of the quality of the effluent being applied. Consideration may also be given to a site when the seasonal high water table is less than 15 feet at some times but the actual separation of the water table is at least 15 feet at any time application occurs.

(ii) The annual hydraulic loading rates shall be no greater than fifteen percent (15%) of the lowest measured basin infiltration rate, unless approved by the Department. Loading rates may also be adjusted by the Department based on the pollutant loading parameters, including any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471). The applicant for domestic wastewater or other systems with a nitrate or nitrogen loading may be required to provide the Department, a nitrate to nitrogen loading balance to determine if the application rates shall be adjusted.

(iii)
(A) cation to rest cycle shall consist of no less than a 1:4 ratio in the summer period (March-October) and a 1:6 ratio in the winter period (November-February). The Department may consider other information (e.g., temperature data) to modify the design summer and winter periods for specific sites.

(B) The Department may require the permittee whenever the scheduled resting cycle fails to restore infiltration rates to acceptable levels, to recondition the basin surface (e.g. by scraping and/or loosening of the soil surface by discing or harrowing).

(iv) The design hydraulic loading rate to the rapid infiltration basin shall be calculated to include monthly average precipitation rates for the site area. The most restrictive soil horizon shall have a 2 inches/hour infiltration rate or greater.

(v) The water table mound shall be maintained 6 feet or more below the bottom of the infiltration basin during effluent application. The Department may require the permittee to modify the application rate to achieve this separation.

(vi) Drinking water supply wells shall be protected from potential groundwater contamination by a minimum buffer zone of at least 1,000 feet beyond the rapid infiltration basin. A greater distance may be required by the Department in some cases depending on local hydrogeologic conditions.

(vii) The minimum number of groundwater monitoring wells shall be one up-gradient and one down-gradient for each infiltration basin. Additional wells may be required depending on the hydrogeologic conditions and/or basin size and number of basins. There shall be a minimum of two down-gradient wells or one per infiltration basin, whichever is greater.

(viii) Groundwater samples for new rapid infiltration basins shall be analyzed for the following parameters. For expanding rapid infiltration basins, the Department may eliminate any parameter based on actual site information, wastewater characteristics or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) [Reserved]

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS)

(J) [Reserved]

(ix) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required (in a permit) to be monitored in groundwater.

(2) All other rapid infiltration facilities.
(i) The minimum number of groundwater monitoring wells shall be one up-gradient and one down-gradient per each infiltration basin. Additional wells may be required depending on the hydrogeologic conditions and/or basin size and number of basins. There shall be a minimum of two down-gradient wells or one per infiltration basin, whichever is greater.

(ii) Groundwater samples for other rapid infiltration basins shall be analyzed for the following parameters. The Department may eliminate any parameter based on actual site information or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) [Reserved]

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS)

(J) (Reserved]

(iii) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required (in a permit) to be monitored in groundwater.

(d) Overland Flow.

(1) New or expansions.
(i) Any discharge to Surface Waters of the State shall require an NPDES permit issued in accordance with R.61-9.122.

(ii) Overland flow systems shall be designed so that the surface water and groundwater standards (R.61-68) shall be maintained.

(iii)
(A) The applicant must include as part of the design for a new or expanding overland flow project, at least three ring and infiltrometer tests which shall be performed on the most permeable soil type(s) encountered during the soil borings.

(B) If, during the infiltration tests, the soils at the site are found to be more permeable than 0.2 in/hr, groundwater monitoring wells around the system as specified in paragraph (vi)(A) below shall be provided.

(iv) The permittee shall be required to maintain a water-tolerant turf grass that will facilitate the treatment of wastewater. Alternative proposed groundcover, crops or silviculture may be requested by the applicant. The Department may approve alternative covers.

(v) The overland flow design application period shall not exceed 12 hours per day for each terrace or slope or portion thereof. The NPDES or land application permit issued for the overland flow facility shall provide specific discharge flow limits or application rates.

(vi)
(A) For those overland flow systems requiring groundwater monitoring, the minimum number of groundwater monitoring wells is one up-gradient of the entire overland flow system and two down-gradient of each area to be monitored.

(B) Groundwater monitoring wells may not be required at overland flow systems containing surficial permeable soils if they are engineered such that partially treated wastewater will not contact groundwater.

(vii) Groundwater monitoring (if required by the Department) for overland flow systems shall be analyzed for the following parameters. The Department may eliminate any parameter based on actual site information, wastewater characteristics or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) (Reserved)

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS)

(J) [Reserved]

(viii) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required (in a permit) to be monitored in groundwater.

(2) All other facilities.
(i)
(A) The minimum number of monitoring wells is one up-gradient of the entire overland flow system and two down-gradient of each area to be monitored.

(B) Groundwater monitoring wells may not be required at overland flow systems containing surficial permeable soils if they are engineered such that partially treated wastewater will not contact groundwater.

(ii) Groundwater monitoring (if required by the Department) for overland flow systems shall be analyzed for the following parameters. The Department may eliminate any parameter based on actual site information or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) [Reserved]

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS)

(J) [Reserved]

(iii) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required to be monitored (in a permit) in groundwater.

(e) Tile Field.

(1) New or expanding.
(i) The submission and information requirements will be determined by the Department.

(ii) A public entity shall own the system and shall be responsible for the operation, maintenance and replacement of all components unless otherwise approved by the Department. The Department may consider a request for a private entity or person, however the proposal must be evaluated on a case by case basis. The Department can evaluate the capability of reliable system operation in its evaluation.

(iii) If the project is owned by a private entity or person, the Department shall require financial assurances for the operation and maintenance of the system. This financial assurance would typically be required for residential or domestic wastewater sources.

(iv) [Reserved]

(v) A program for monitoring the quality of groundwater may be established for domestic systems (having contributions from industrial facilities), for applicable industrial wastewater systems and other systems, if required by the Department.

(vi) Groundwater monitoring (if required by the Department) for tile field systems shall be analyzed for the following parameters. The Department may eliminate any parameter based on actual site information, wastewater characteristics or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) [Reserved]

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS) This parameter may be added to the continuing groundwater monitoring based on the result of field specific conductance.

(J) Field Specific Conductance

(vii) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required to be monitored (in a permit) in groundwater.

(2) All other tile field facilities.
(i) A program for monitoring the quality of groundwater may be established for domestic systems (having contributions from industrial facilities), for applicable industrial wastewater systems and other systems, if required by the Department.

(ii) Groundwater monitoring (if required by the Department) for other tile field systems shall be analyzed for the following parameters. The Department may eliminate any parameter based on actual site information or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) [Reserved]

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS) or Field specific conductance

(J) [Reserved]

(iii) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter, but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required (in a permit) to be monitored in groundwater.

(f) Percolation or Evaporation Basins.

(1) A groundwater monitoring program may be required by the Department for existing systems to determine if there is a need to evaluate the groundwater conditions at the site to assure compliance with State Water Quality Standards R.61-68. If a deleterious impact to the groundwaters of the State from the permitted use or disposal practices is documented, through groundwater monitoring levels exceeding the standards set forth in R.61-68 or a significant adverse trend occurs, then it will be the obligation of the permittee as directed by the Department to conduct an investigation to determine the vertical and horizontal extent of groundwater impact. The Department may require remediation of the groundwater to within acceptable levels for groundwater as set forth in R.61-68.

(2) A program for monitoring the quality of groundwater may be established for domestic systems (having contributions from industrial facilities), for applicable industrial wastewater systems and other systems, if required by the Department. The Department may consider influent characteristics in this determination.
(i) Groundwater monitoring (if required by the Department). for percolation or evaporation basins shall be analyzed for the following parameters. The Department may eliminate any parameter based on actual site information or the groundwater data from consistent wastewater plant operations:
(A) Water table elevation and water table depth

(B) [Reserved]

(C) Chloride

(D) Ammonia (NH3)

(E) Nitrate (N)

(F) [Reserved]

(G) pH (field)

(H) Sodium

(I) Total dissolved solids (TDS)

(J) [Reserved]

(ii) Additional parameters may be required in the initial background groundwater analysis and subsequent monitoring thereafter but such needs will be assessed on an individual project basis. Any pollutant required for monitoring under effluent guidelines ( 40 CFR Part 136; Subchapter N ( 40 CFR Parts 400 through 402 and 404 through 471)) may be required (in a permit) to be monitored in groundwater.

(g)

(1) Spray irrigation or land application of sewage sludge shall be in accordance with R.61-9.503. Spray irrigation or land application of Industrial sludge shall be in accordance with R.61-9.504.

(2) If total suspended solids concentration of the treated wastewater solids or sludge is less than 2000 mg/l the Department may require the facility to comply with the additional requirements for land application of wastewater (R.61-9.505.42(b)(b)).

(h) Reclaimed wastewater systems.

(1) Provided the level of treatment meets the requirement outlined in section505.45(i)(i), there would not be specific buffer area requirements.

(2) A groundwater monitoring program may be required by the Department for existing or new systems to determine if there is a need to evaluate the background groundwater conditions at the site to assure compliance with State Water Quality Standards R.61-68.

(3) Piping shall be clearly marked to identify reclaimed water lines and the Department may establish specific guidelines for use of reclaimed water systems.

(4) Reclaimed wastewater systems may be required to provide covered storage systems (or other alternative methods) to maintain effluent quality prior to distribution.

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