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2900 - Site Mitigation Program
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PR0544500
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Last modified
2/10/2020 9:51:05 AM
Creation date
2/10/2020 8:55:53 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0544500
PE
2965
FACILITY_ID
FA0013894
FACILITY_NAME
DDJC TRACY
STREET_NUMBER
25700
Direction
S
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
02
SITE_LOCATION
25700 S CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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WASTE DISCHARGE REQUIREM_ :S ORDER NO.R5-2004-XXXX -4- <br /> DEFENSE DISTRIBUTION DEPOT SAN JOAQUIN <br /> SHARPE WASTEWATER TREATMENT FACILITY <br /> SAN JOAQUIN COUNTY <br /> Response Plan. This Order requires that the Discharger implement this Manual or subsequent <br /> updates approved by Regional Board staff. <br /> Site Specific Conditions <br /> 16. Annual precipitation in the vicinity averages approximately 13.31 inches. The mean pan <br /> evaporation rate is approximately 41.36 inches per year. <br /> 17. The facility lies within the San Joaquin Delta Hydrologic Unit Area No. 544.00, as depicted on <br /> interagency hydrologic maps prepared by the Department of Water Resources in August 1986. <br /> 18. The area surrounding DDJC-Sharpe is a mixture of industrial, agricultural, and residential. <br /> 19. Based on the National Resource Conservation Service soil survey, the soils in the proposed land <br /> application areas are Tinnin loamy coarse sand, Veritas fine sandy loam, Merritt silty clay loam, <br /> and Timor loamy sand. Published infiltration rates for the soils range from 0.3 to 3.0 in/hr. <br /> Based on boring log data from existing monitoring wells, shallow soils in the area are described <br /> as silty sand with clay lenses. <br /> 20. Approximately 208 groundwater monitoring wells, 34 piezometers, 45 extraction wells, and four <br /> drinking water supply wells are present at the Discharger's facility. The monitoring wells, <br /> piezometers, and extraction wells were installed as part of the on-going efforts to remediate <br /> several large groundwater plumes comprised primarily of trichloroethene and tetrachloroethene. <br /> These plumes have migrated beyond the western boundary of the facility,but the extraction well <br /> network is expected to achieve full-containment of the plumes in the next five years. The <br /> designated wastewater discharge areas are within or directly up gradient of the current capture <br /> zone of the extraction well network. The existing well network is considered to be adequate for <br /> monitoring discharge of treated wastewater. <br /> 21. Groundwater from the first aquifer, locally described as the A-aquifer zone, is not considered a <br /> viable source of drinking water without treatment for inorganics. The first aquifer contains <br /> elevated concentrations of arsenic and other inorganics. The Discharger has defined an ambient <br /> arsenic concentration of 273 gg/L for the first aquifer, which exceeds the Federal Maximum <br /> Contaminant Level (MCL) of 10 gg/L. <br /> Groundwater Degradation <br /> 22. State Water Resources Control Board(State Board) Resolution No. 68-16 (hereafter Resolution <br /> 68-16 or the"Antidegradation Policy")requires the Regional Board in regulating the discharge <br /> of waste to maintain high quality waters of the state until it is demonstrated that any change in <br /> quality will be consistent with maximum benefit to the people of the State, will not unreasonably <br /> affect beneficial uses, and will not result in water quality less than that described in the Regional <br /> Board's policies (e.g., quality that exceeds water quality objectives). <br /> 23. Continued operation of Discharger's facility is a benefit to the people of California, and therefore <br /> sufficient reason exists to accommodate limited groundwater degradation beneath the designated <br /> land application areas,provided that: <br />
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