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ARCHIVED REPORTS_XR0007931
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542364
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ARCHIVED REPORTS_XR0007931
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Last modified
5/4/2020 3:55:32 PM
Creation date
5/4/2020 3:08:56 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007931
RECORD_ID
PR0542364
PE
2960
FACILITY_ID
FA0024340
FACILITY_NAME
PACIFIC CAR WASH
STREET_NUMBER
4405
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11024014
CURRENT_STATUS
01
SITE_LOCATION
4405 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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1 <br />' 15 March 2000 <br /> AGE-NC Protect No 96-0229 <br />' Page 3 of 5 <br />' the ground water flow direction was generally toward the northeast at a gradient of 0 002 ft/ft, or <br /> approximately 11 feet per mile (Figure 3) Ground water was approximately 20 to 22 feet above the <br /> screen intervals at MW-1 and MW i 0-B <br />' 3 2 LABORATORY RESULTS OF GROUND WATER SAMPLES <br /> A total of eleven ground water samples were submitted to a DHS-certified laboratory in January <br />' 2000 TPH-g was detected in water samples collected from wells MW-1, MW-2, MW-3, MW-6, <br /> MW-7, and MW-8 at concentrations ranging as high as 68,000 micrograms per liter (µg/1) <br />' BTEX compounds were detected In ground water samples collected from wells MW-1, MW-2,MW- <br /> 3, MW-6, MW-7, and MW-IOB at concentrations ranging as high as 10,000 µg/l (xylene, MW-2) <br /> The greatest benzene concentration was observed at MWA at a concentration of 7,300 µg/l <br /> MTBE was detected utilizing EPA Method 8020 in ground water samples collected from <br /> wells MW-1, MW-4, MW-7 and MW-8 at concentrations ranging as high as 470 µg/l MTBE was <br /> confirmed utilizing EPA Method 8260 in samples collected from wells MW-1, MW-2, MW-4, <br /> MW-6, MW-7 and MW-8 at concentrations ranging as high as 650 ,ug/l, TBA was detected in <br /> ground water samples collected from wells MW-4 and MW-8 at concentrations of 7 6 µg/1 and 6 4 <br /> µg/l, respectively No other fuel oxygenated additives were detected above laboratory reporting <br /> limits from the analyzed samples <br /> tAnalytical results of the ground water samples are summarized In Table 2 The laboratory reports <br /> (Castle Analytical Laboratory Reference No 2779 and McCampbell A.nalyticaI Inc I D No 29637 <br /> Ithrough 29647) and chain-of-custody forms are presented In Appendix B <br /> 4.0 SUMMARY AND CONCLUSIONS <br /> The implications from the findings of the January 2000 investigation are <br /> • Ground water monitoring data collected in the area of wells MW-1 through MW-10 indicated <br /> a ground water flow direction generally toward the northeast at a gradient of 0 002 ft/ft The <br /> flow direction is close to the norm for,the area Due to the low gradient at the site, slight <br /> variations in ground water measurements or changes of recharge/discharge of the local <br /> ground water could greatly modify ground water flow direction <br /> • The dissolved BTEX and MTBE plume is at least 20 feet thick in the area of MW-1 and <br /> MW-2, with depth, the dissolved BTEX and MTBE plume apparently grades from lower <br /> concentrations to higher concentrations <br /> Advanced 0(oFn%trnnmental,Inc <br />
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