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COMPLIANCE INFO
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0544500
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COMPLIANCE INFO
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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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INFORMATION SHEET 5 <br /> WASTE DISCHARGE REQUIREMENTS ORDER NO.R5-2004-XXXX <br /> DEFENSE DISTRIBUTION DEPOT SAN JOAQUIN <br /> SHARPE WASTEWATER TREATMENT FACILITY <br /> SAN JOAQUIN COUNTY <br /> 4 Ayers,R. S. and D.W.Westcot,Water Quality for Agriculture,Food and Agriculture <br /> Organization of the United Nations—Irrigation and Drainage Paper No. 29,Rev. 1,Rome <br /> (1985) <br /> 5 Title 22, California Code of Regulations(CCR), section 64449,Table 64449-B <br /> 6 Title 22, CCR, section 64449,Table 64449-A <br /> 7 Title 22, CCR, section 64431,Table 64431-A <br /> 8 Title 22,CCR, section 64439 <br /> 9 Title 22, CCR, section 64439 <br /> 10 Title 40, Code of Federal Regulations, Section 143.3 <br /> 11 California Department of Health Services,Division of Drinking Water and Environmental <br /> Management,Drinking Water Action Levels,http://www.dhs.cahwnet.gov/ps/ddwem. <br /> Domestic wastewater contains numerous dissolved inorganic waste constituents (i.e., <br /> salts,minerals)that together comprise total dissolved solids (TDS). Each component <br /> constituent is not individually critical to beneficial use protection unless they are <br /> individually listed. The cumulative impact from these other constituents, along with the <br /> cumulative affect of the constituents that are individually listed can be effectively <br /> controlled using TDS as a generic indicator parameter. <br /> Not all TDS constituents pass through the treatment process and soil profile in the same <br /> manner or rate. Chloride tends to pass through both rapidly to groundwater. As chloride <br /> concentrations in most groundwaters in the region are much lower than in treated <br /> municipal wastewater, chloride is a useful indicator parameter for evaluating the extent to <br /> which effluent reaches groundwater. Boron is another TDS constituent that may occur in <br /> wastewater in concentrations greater than groundwater depending on the source water, to <br /> the extent residents use cleaning products containing boron, and whether any industrial <br /> dischargers utilize boron(e.g., glass production, cosmetics). Other indicator constituents <br /> for monitoring for groundwater degradation due to recharged effluent include total <br /> coliform bacteria, ammonia, total nitrogen, and Total Trihalomethanes (TTHMs), a by- <br /> product of chlorination. Dissolved iron and manganese are useful indicators to determine <br /> whether components of the WWTF with high-strength waste constituents, such as sludge <br /> handling facilities, are ineffective in containing waste. Exceptionally high TDS and <br /> nitrogen also typifies this type of release. <br /> Treatment Technology and Control <br /> Given the character of wastewater from the types of sources present at DDJC-Sharpe, <br /> secondary treatment,technology is generally sufficient to control degradation of <br /> groundwater from decomposable organic constituents. Adding disinfection significantly <br /> reduces populations of pathogenic organisms, and reasonable soil infiltration rates and <br /> unsaturated soils can reduce them further. Neither organics nor total coliform organisms, <br /> the indicator parameter for pathogenic organisms, should be found in groundwater in a <br /> well-designed,well-operated facility. <br />
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