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ARCHIVED REPORTS XR0000697
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0522496
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ARCHIVED REPORTS XR0000697
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Last modified
2/15/2019 7:15:49 PM
Creation date
2/15/2019 4:15:02 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000697
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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31 August 2005 <br /> ' AGE-NC Project No 96-0232 <br /> Page 16 of 30 <br /> a subsurface petroleum hydrocarbon investigation Laboratory analysis of eighty-two soil samples <br /> from the subsurface investigation detected MTBE in 19 samples, TPH-g, TPH-d, BTEX and TBA <br /> were only detected in one sample (P31-10) During the March-April 1995 UST removals, an <br /> additional seventeen soil samples were collected from the tank pit sidewalls, beneath the tank pit <br /> floor and beneath product piping, TPH-g, BTEX were detected beneath one product piping sample <br /> (L3B), and xylene was detected beneath a second product piping sample (L2B) <br /> Based on analytical results of soil samples,the greatest MTBE-impacted soil was encountered near <br /> the south-southwest sections of the site (UST pit area) at soil borings P1-35 feet bsg(0 14 mg/kg), <br /> P20-20 feet bsg (0 35 mg/kg) and P22-15 feet bsg (0 63 mg/kg), significant MTBE-impacted soil <br /> was also encountered near the southeast corner of the fuel dispenser area at P31-10 feet bsg (0 54 <br /> mg/kg) and the northeast corner of the fuel dispenser area at P34-10 feet bsg (0 72 mg/kg) Soil <br /> boring locations are depicted in Figure 2 <br /> TPH-g and TPH-d-impacted soil were detected near the southeast corner of the fuel dispenser area <br /> from P31-10 feet at concentrations of 3 2 and 2 2 mg/kg, respectively, TPH-g-impacted soil was <br /> detected from product piping removal soil sample L3B at a concentration of 1 5 mg/kg, TPH-d- <br /> impacted soil was detected near the northern edge of the property boundary from P41-30 at a <br /> concentration of 1 7 mg/kg <br /> BTEX compounds were detected near the southeast cornier of the fuel dispenser area from P31-10 <br /> and from product piping removal soil sample L3B at concentrations as high as 0 26 mg/kg, total <br /> xylenes were detected from product piping removal soil sample L2B at a concentration of 0 028 <br /> mg/kg <br /> TBA was detected in soil samples collected near the southeast and northeast corners of the fuel <br /> dispenser areas from P31-10 feet and P34-10 feet at concentrations of 0 071 and 0 120 mg/kg, <br /> respectively <br /> The vertical extent of MTBE-impacted soil has been modeled to extend to maximum depths of 40 <br /> feet bsg (Figures 10 through 12) The lateral extent of petroleum impacted soil is mapped as an <br /> elongated, elbow-shaped plume that extends towards the north and southwest(Figure 13) <br /> 3 1 VADOSE ZONE MTBE-IMPACT <br /> Based on depth to ground water measured between May 1991 to March 2005,water level during this <br /> period typically ranged between 7 and 15 feet bsg Therefore, soil samples collected from 7 feet bsg <br /> or less could be considered as representative of vadose zone conditions Vadose zone petroleum- <br /> impacted soil was only encountered beneath product piping removal sample L3B (51/z feet bsg) at <br /> Advanced GeoEnvironmental,Inc <br />
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