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ARCHIVED REPORTS XR0000658
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2900 - Site Mitigation Program
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PR0522496
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ARCHIVED REPORTS XR0000658
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Last modified
2/15/2019 8:06:41 PM
Creation date
2/15/2019 3:10:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000658
RECORD_ID
PR0522496
PE
2957
FACILITY_ID
FA0015317
FACILITY_NAME
FLAG CITY CHEVRON
STREET_NUMBER
6421
STREET_NAME
CAPITOL
STREET_TYPE
AVE
City
LODI
Zip
95245
APN
05532024
CURRENT_STATUS
02
SITE_LOCATION
6421 CAPITOL AVE
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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A l L'i <br /> • 15 October 2000 <br /> AGE-NC Project No 96-0232 <br /> Page 4 of 11 <br /> The process pump, located behind the holding tank, will be controlled by electrode switches placed <br /> at various levels in the holding tank An emergency shut-off switch will be located immediately <br /> below the top of the holding tank An Intermediate pump-on switch will be placed approximately <br /> 8-inches below the emergency shut-off switch to activate the process pump Intermediate pump-off <br /> switches will be utilized near the bottom of the holding tank to turn the process pump off <br /> One 750-gallon poly tank equipped with a suspended-solids pre-filter will be used to temporarily <br /> store extracted water prior to processing The tank will be equipped with various level control <br /> switches to control the rate at which extracted water is introduced into the treatment vessels, to <br /> provide safety shutoff capabilities and to allow coarse sediment to settle out prior to treatment The <br /> process pump is located directly behind the holding tank <br /> The first stage of treatment media will contain two 2,500-pound GAC absorption vessels designed <br /> to adsorb TPH-g, TPH-d and BTEX compounds, the final stage of treatment media will contain two <br /> 2,500-pound SunSolve absorption vessels, a liquid-phase filtration media specifically designed to <br /> adsorb MTBE and TBA Sample ports are located between all vessels to allow detection of media <br /> break through and to obtain final discharge samples The system layout is depicted in Figure 3 <br /> • l 8 Ground Water Analysis <br /> Chlorinated volatile hydrocarbons (EPA Method 8260), aromatic volatile hydrocarbons (EPA <br /> Method 8020) and total petroleum hydrocarbons quantified as gasoline and diesel (EPA Method <br /> 8015M/5030) have been sampled at site in monthly/quarterly ground water monitoring events and <br /> grab ground water samples collected from soil borings and the results submitted to the RWQCB in <br /> quarterly reports, results were tabulated in Problem Assessment Report, dated 19 June 2000 <br /> A grab sample from EW-1, was collected on 06 October 2000 and submitted to a DHS-certified <br /> Iaboratory for analysis of lead, chlorinated pesticides and general minerals Copies of the laboratory <br /> reports are included In Appendix B <br /> 2.0. SITE HYDROGEOLOGY <br /> In accordance with Section B of Attachment A from General Order 5-00-119, AGE has evaluated <br /> the following mentioned site hydrogeology characteristics - <br /> 2 1 Depth To Ground Water <br /> Review of historical depth to ground water maps published by the San Joaquin County Flood Control <br /> • <br /> .Advanced GeoEnvironmental,Inc <br />
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