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ARCHIVED REPORTS XR0000690
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2900 - Site Mitigation Program
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PR0522496
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ARCHIVED REPORTS XR0000690
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Last modified
2/15/2019 10:42:20 PM
Creation date
2/15/2019 4:10:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000690
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
Scanner
WNg
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EHD - Public
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19 June 2000 <br /> AGE-NC Project No 96-0232 <br /> Page 13 of 35 <br /> During the first stage of the pump test (pump rate at 4 3 GPM), ground water was drawn below the <br /> pressure transducer in MW-1 after 19 minutes ofpumping operation,no measurable draw-down was <br /> observed from wells MW-2 (located 120 feet towards the east),MW-4(located 95 feet towards the <br /> north) or MW-6A (located 75 feet towards the south) during the first stage of the pump test A <br /> transmissiv>ty value from well MW-1 was calculated at 135 gal/day-ft <br /> During the second stage of the pump test (pump rate at 3 5 GPM), the greatest ground water draw- <br /> down was observed at 6 91 feet after 11 minutes of pumping operation, due to an equipment <br /> malfunction,the test was terminated after 11 minutes of operation No measurable draw-down was <br /> observed from wells MW-2, MW-4 or MW-6A during the second stage of the pump test A <br /> transmissivrty value from well MW-1 was calculated at 349 gal/day-ft <br /> During the third stage of the pump test(pump rate at 3 GPM),the greatest ground water draw-down <br /> was observed at 4 42 feet after 125 minutes of pumping operation,due to an equipment malfunction, <br /> the test was terminated after 125 minutes of operation No measurable draw-down was observed <br /> from wells MW-2,MW-4 or MW-6A during the third stage of the pump test A transmissivlty value <br /> from well MW-1 was calculated at 932 gal/day-ft <br /> Pump test results are summarized in Table 10 <br /> 6.0. ASSESSMENT OF HYDROCARBON-IMPACTED SOIL <br /> Between July 1996 and May 2000, soil sampling was performed at thirty-five soil borings (PI <br /> through P35) and twelve ground water monitoring wells (MW-1, MW-2, MW-4 through MW-12) <br /> as part of a subsurface petroleum hydrocarbon investigation <br /> The greatest MTBE-impacted soil was encountered at soil borings P1-35 feet bsg (0 14 mg/kg), <br /> P20-20 feet bsg (0 35 mg/kg), P22-15 feet bsg (0 63 mg/kg), P31-10 feet bsg (0 54 mg/kg) and <br /> P34-10 feet bsg (0 72 mg/kg) Soil boring P1 Is located at the southwest corner of the site, P20 is <br /> located near the southwest storm dram, P22 Is located near the storm drain discharge pipe system, <br /> P31 Is located near the southeast fuel dispenser and P34 is located near the northeast fuel dispenser <br /> (Figure 2) <br /> TPH-g and TPH-d were detected from P31-10 feet at concentrations of 3 2 and 2 2 mg/kg, <br /> respectively,BTEX compounds were detected from P31-10 at concentrations as high as 0 26 mg/kg <br /> TBA was detected in soil samples collected at P31-10 feet and P34-10 feet at concentrations of 0 071 <br /> and 0 120 mg/kg, respectively <br /> Adsanced GcoEnNironmental,Inc <br />
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