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2900 - Site Mitigation Program
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PR0522479
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/17/2019 2:14:40 PM
Creation date
5/17/2019 2:01:24 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0522479
PE
2957
FACILITY_ID
FA0015299
FACILITY_NAME
GEWEKE LAND DEVELOPMENT & MARKETING
STREET_NUMBER
16
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04323013
CURRENT_STATUS
01
SITE_LOCATION
16 S CHEROKEE LN
P_DISTRICT
004
QC Status
Approved
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MEMORANDUM <br /> CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD • CENTRAL VALLEY REGION <br /> 3443 Routier Road, Suite A Phone: (916) 155-3000 <br /> Sacramento, CA 95827-3098 CALNET: 8-494-3000 <br /> TO: GORDON L. BOGGS FROM: ELIZABETH A. THAYER <br /> UGT Program Coordinator Associate Engineer <br /> DATE: 15 September 1993 SIGNATURE: ._ <br /> SUBJECT: FINAL REMEDIAL PLAN (FRP), GEWEKE, 16 SOUTH CHEROXF.F LANr,, <br /> LODI, SAN JOAQUIN COUNTY <br /> I have reviewed the Final Remedial Plan (FRP), dated 30 IuIy 1993, prepared by Geweke's <br /> consultants, Geological Audit Services (GeoAudit). For soil remediation options, the PRP includes <br /> excavation, vapor extraction, and in-situ bioremediation. Excavation was considered not viable and <br /> costs were not given. Costs were given for vapor extraction but not for in-situ bio. However, it is <br /> implied that costs for in-situ bio of soil are minimal. For ground water remediation options, the <br /> FRP includes pump and treat and in-situ bio. Costs were provided for pump and treat only. <br /> However, it is implied that costs for in-situ bio of ground water are minimal. No (Aber options <br /> were discussed for either soil or ground water. Based on their discussions of remedial options, <br /> GcoAUdit recommended in-situ hio for both soil and ground water. <br /> The bacteria that GeoAudit will use for in-situ bio are indigenous to soil (although not indigenous to <br /> the site), non-pathogenic, and have been isolated from sites severely contaminated with <br /> hydrocarbons. Without an available hydrocarbon food source, the bacterial population dies hack, <br /> The bacteria will be inoculated into wells that are screened through the contaminant plume. After <br /> inoculation, a low-pressure air source will be manifolded to the wells to provide additional oxygen <br /> and accelerate bioremediation. GeoAudit asserts that essential nutrients are generally available in <br /> the soil, however, if supplements are needed, the amounts will probably be very low. The only <br /> equipment required for this procedure, is a blower unit. <br /> To bioremediate the soil, they propose to introduce the bacteria it, the subsurface through vadose <br /> zone wells, VW1 through VW4, and the dry monitoring wells, MWI, MW3, MW4, and MWS. <br /> Three additional vadose zone wells may be installed at specified locations. To monitor the <br /> effectiveness of the soil bioremediation, GeoAudit proposes to drill one or two borings on a biannual <br /> basis. The borings will be sampled every five feet and monitored in the field with a YID, Selected <br /> soil samples will be analyzed for TPHg and RTRX. The results will be compared to baseline <br /> samples. GeoAudit states that this soil bioremediation procedure will not affect the ground water, <br /> and therefore no Regional Board permit will be required. <br /> To bioremediate the ground water, they propose to introduce the bacteria through existing <br /> unspecified monitoring wells. To monitor the effectiveness of the bioremediation, GeoAudit <br /> recommends monitoring off-site monitoring wells, MW8, MW9, MW 11, MW 12, and MW 13 on a <br /> monthly basis during the first quarter after inoculation. This monitoring is to ensure that the <br /> TO' d 800' ON ££:6 £6' 91 dog ' ON Ili <br />
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