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ARCHIVED REPORTS_XR0004381
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PR0539293
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ARCHIVED REPORTS_XR0004381
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Last modified
11/20/2019 3:29:55 PM
Creation date
11/20/2019 3:20:27 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004381
RECORD_ID
PR0539293
PE
2957
FACILITY_ID
FA0022465
FACILITY_NAME
VALLEY MOTORS
STREET_NUMBER
800
Direction
E
STREET_NAME
MAIN
City
STOCKTON
Zip
95202
CURRENT_STATUS
01
SITE_LOCATION
800 E MAIN
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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• from the soil If so, desorption ceased during the `second quarter, because the concentrations of all <br /> analytes remained unchanged in three of the wells and declined by 20-50% in VM-4 (Table 2) It <br /> has been several years since concentrations remained so stable at this site, the last time this <br /> occurred was in late 1996-early 1997 <br /> Total Petroleum Hydrocarbon and total BTEX concentrations are graphed against time for VM-2 <br /> and VM-1 in Figures 4 and 5 Figure 4 illustrates that there has been a trend of increasing <br /> concentrations in VM-2 since monitoring began in 1996, and that concentrations have generally <br /> peaked during the third quarter 6f the year The annual low concentration has usually been <br /> recorded late in the first quarter If this pattern holds true in 2002, concentrations are likely to <br /> peak again within the next three months <br /> In contrast to VM-2, concentrations in VM-1 appear to be on a downward trend Further, neither <br /> the annual peak concentration nor the annual low concentration has been as consistent as in VM- <br /> 2 This is also true of VM-3 and VM-4, neither of which has shown a consistent long-term trend <br /> The samples were also analyzed for gasoline oxygenates, using EPA method 8260, because <br /> MTBE has been reported in four previous samples from VM-4 (Table 3) None of oxygenates <br /> were detected in this or any,of the other wells this quarter, and they have been detected only <br /> rarely Hence, it is clear that they are not a significant component of the contaminant plume <br /> 4.3 Extent of Groundwater Contamination <br /> Although the full lateral extent of groundwater contamination has not been determined and <br /> additional drilling is planned to complete this task, we have constructed a preliminary isocontour <br /> map of dissolved-phase gasoline (TPH-g) using the most recent laboratory data (Figure 6) In <br /> areas where older samples from the hydropunch borings or remediation wells are the only sample <br /> points, we have considered these in constructing the map Our tentative interpretation is that the <br /> plume is elongate in a northwest-southeast direction and extends beneath the sidewalk north of <br /> the site Groundwater beneath most of the site is contaminated, although it may not be <br /> contaminated beneath the garage building or the office building The total area underlain by the <br /> plume appears to be roughly one-quarter acre, and its center lies near the east end of the former <br /> dispenser island, between VM-2 and SW-I In this area, concentrations exceed 50,000 ppb and <br /> may approach 70,000 ppb The benzene concentration is between 5,000 and 10,000 ppb in the <br /> center <br /> 4 <br />
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