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ARCHIVED REPORTS_XR0006675
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0543479
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ARCHIVED REPORTS_XR0006675
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Last modified
5/5/2020 10:25:36 AM
Creation date
5/5/2020 9:26:46 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006675
RECORD_ID
PR0543479
PE
2960
FACILITY_ID
FA0024679
FACILITY_NAME
CANEPA'S CAR WASH
STREET_NUMBER
6230
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95204
APN
081360030
CURRENT_STATUS
01
SITE_LOCATION
6230 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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' Quarterly Monitoring Report January 2001 <br /> Canepa s Car Wash(Pacific Avenue) <br /> Page-0 <br />' bmsl Since November 1993, the depth to groundwater at the site has ranged from approximately 54 5 <br /> feet to 31 8 feet bgs The groundwater elevation contour map (Figure 2, Appendix A) Indicates <br /> groundwater mounding in the center of the site in the vicinity of MW-1 and MW-2 with a primary <br />' groundwater gradient to the west, but with a northeast groundwater gradient reversal on the cast side of <br /> the mound The groundwater mounding effect identified during the Januaty 2001 quarterly groundwater- <br /> monitoring event is generally consistent with previous monitoring iesults <br />' 5 2 DISCUSSION OF ANALYTICAL RESULTS <br /> The first quarter laboratory analytical results (see Figures 3-4 and 6-10, Appendix A) are generally <br />' consistent with recent historical laboratory analytical results The laboratory analytical results indicate <br /> that none of the analytes of interest were detected at or above the labotatory reporting limits in the <br /> groundwater samples collected frorn MW-5, MW-6, and MW-8 BTEX, TPH-G, and MTBE were <br />' detected iii the gror.Indwatcr samples collected from MW-1 and MW-2 MTBE was detected in the <br /> groundwater sample from MW-3 Benzene and TPH-G were detected in MW-4 BTEX constituents were <br /> detected in MW-7 <br />' 5 2.1 DISCUSSION OF BENZENE CONCENTRATIONS <br /> Concentrations of benzene have decreased over time in MW-1, but appear to be increasing in MW-2, <br /> except for a decrease in January 2001 (Figures 6 and 7, Appendix A) It appears that with an increase in <br /> groundwater elevation there is an increase in the concentration of benzene in MW-2, except with this <br /> monitoring event The highest peaks in benzene concentration in Figure 6 generally occur at the <br />�. sampling event following the peak in groundwater elevation Relatively recent groundwater samples <br /> collected from selected soil vapor extraction wells have contained significantly lower concentiatrons of <br /> benzene relative to groundwater samples collected fiom selected soil vapor extraction wells during <br /> previous monitoring events, particularly since startup of the soil vapor system <br /> 5 2.2 DISCUSSION OF MTBE CONCENTRATIONS <br /> MTBE concentrations have increased in both MW-1 and MW-2 over time, with the greatest increase <br /> obscived in MW-i (Figures 9 and 10, Appendix A) There is a recent sharp increase in Concentration of <br /> MTBE in MW-1 The highest concentrations of MTBE have been present in grouridwatet samples <br /> collected from the soil vapor extraction wells, the only wells to have screens not submerged in <br /> groundwater (see Table 3, next page) <br /> • <br /> �� CONDOR <br />
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