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2900 - Site Mitigation Program
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PR0508462
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
1/30/2020 12:22:14 PM
Creation date
1/30/2020 11:02:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508462
PE
2960
FACILITY_ID
FA0008093
FACILITY_NAME
CONTINENTAL GRAIN CO
STREET_NUMBER
9504
Direction
S
STREET_NAME
HARLAN
STREET_TYPE
RD
City
FRENCH CAMP
Zip
95231
CURRENT_STATUS
01
SITE_LOCATION
9504 S HARLAN RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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INFORMATION SHEET <br /> WASTE DISCHARGE REQUIREMENTS ORDER NO.R5-2004-0160 <br /> CONTIGROUP COMPANIES,INC. <br /> FRENCH CAMP GRAIN ELEVATOR <br /> ENHANCED REMEDIATION PILOT STUDY <br /> SAN JOAQUIN COUNTY <br /> ContiGroup Companies,Inc. (Discharger) formerly owned the active grain storage and transfer <br /> facility at 9504 South Harlan Road in French Camp (Site). Historically,liquid fumigants <br /> containing carbon tetrachloride were stored on site in five-gallon buckets. Carbon tetrachloride <br /> was found in groundwater in 1999. Several investigations have been conducted to delineate the <br /> extent of carbon tetrachloride and its breakdown product, chloroform. Three water bearing <br /> zones are identified at the Site with most of the mass of pollution in the B water bearing zone. <br /> The B water bearing zone is about 60 to 80 feet below ground surface(bgs) axed varies from <br /> about 5 to 15 feet thick across the Site. <br /> The Discharger proposes a nine-month granular zero valent iron(GZVI)injection pilot study to <br /> reduce carbon tetrachloride and chloroform concentrations. GZVI is a strong reducing agent. <br /> Electrons released during GZVI oxidation reduce the chlorinated compound whereby the <br /> chlorine atoms are replaced by hydrogen atoms. During the reductive dechlorination process, the <br /> R carbon tetrachloride and chloroform act as electron acceptors. The purpose of the pilot study is <br /> to reduce pollutant concentrations and evaluate GZVI as a remedial alternative. Under reductive <br /> dechlorination,carbon tetrachloride and its breakdown product chloroform are reduced to <br /> methylene chloride. As the groundwater moves out of the area of the GZVI into aerobic <br /> conditions,the methylene chloride breaks down with the ultimate end products of carbon dioxide <br /> and chloride. <br /> The Discharger will drill three borings to about 85 feet bgs. Points of injection will be <br /> spaced at about 77.5 feet bgs, 72.5 feet bgs, 67.5 feet bgs, and 62.5 feet bgs to create four <br /> iron layers per boring. About 4 cubic meters of GZVI slung will be injected into each layer <br /> for a total of about 16 cubic meters per boring. The GZVI slung consists of guar gum,which <br /> makes the slurry viscous and allows the GZVI to be suspended and pumped in to the boring, <br /> cross-linker to make the slurry more viscous, and an enzyme breaker to reduce viscosity once <br /> the layer is emplaced in the subsurface. The mixture of slurry is 400 kilograms of iron, eight <br /> kilograms of guar gum,three quarters to two liters of cross-linker, and 0.02 liters of enzyme <br /> breaker per cubic meter of slurry. The amount injected may be less,but not more than 4 <br /> cubic meters per layer because the mass of GZVI injected is controlled by the amount that <br /> can be hydraulically fractured into the subsurface. The WDRs require extensive monitoring <br /> to evaluate the effects of the proposed injections. When the pilot study is completed,the <br /> amendments and byproducts shall not exceed baseline levels. <br /> DLL 9/14/04 <br />
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