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WORK PLANS FILE 1
Environmental Health - Public
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0544513
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WORK PLANS FILE 1
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Last modified
5/31/2019 4:42:10 PM
Creation date
5/31/2019 4:38:19 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 1
RECORD_ID
PR0544513
PE
3528
FACILITY_ID
FA0024115
FACILITY_NAME
WEST CLAY PROPERTY
STREET_NUMBER
639
Direction
W
STREET_NAME
CLAY
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14707110
CURRENT_STATUS
02
SITE_LOCATION
639 W CLAY ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Site Background Information: West Clay Properties <br /> Page 9 of 10 <br /> MW-2, MW-3 and MW-5. The ground water plume appears to be somewhat symetrical, <br /> extending approximately 80 feet east to west and 80 feet north to south, surrounding UST <br /> No. 3 area. <br /> • Maximum concentrations detected were in the UST No. 3 area are: TPH-g at 47,000 µg/1; <br /> TPH-d at 30,000 µg/1; and benzene at 5,100 gg/1 (MW-2). Significant concentrations of <br /> TPH-g, TPH-d and BTEX have been consistently reported in samples collected from well <br /> MW-1,located east of the former UST No. 3 area. The new wells installed(MW-16 through <br /> MW-24)to define the vertical extent of dissolved hydrocarbon contamination demonstrated <br /> limited impact at the southern edge of the UST No. 3 area at a depth of 75 feet bsg, and not <br /> greater than 100 feet across the entire UST No. 3 area. Off-site grab ground water samples <br /> were"non-detect'for hydrocarbon contamination at all depths sampled.A minor release of <br /> 1,2-DCA mostly likely occurred with the TPH; the 1,2-DCA plume appears to be stable in <br /> samples collected from the monitoring well network. The maximum concentration of <br /> 1,2-DCA at the site is currently 41 µg/1 (MW-1). <br /> • The lateral and vertical extent of TPH and BTEX has been defined by the sample set. <br /> Northern UST Cluster Area <br /> • A release of TPH-g,BTEX and MTBE occurred from dispenser lines at the northern portion <br /> of the tank area. Samples collected from beneath the southern ends of each tank (upon <br /> removal) were "non-detect" for chemicals of concern. TPH-g was reported in a samples <br /> collected from the north end of the tank excavation at 988 mg/kg of TPH-g; TPH-g was <br /> reported in the 15-foot soil sample collected from boring B9 at 7,000 mg/kg TPH-g <br /> • Chemicals of concern were not detected in shallow soil samples collected near wells MW-2 <br /> and MW-7. The highest TPH-g and BTEX impact to soil in the upper vadose zone was <br /> removed through excavation in December 2003. Currently, no residual vadose zone <br /> hydrocarbon contamination is present at the site. The aerial extent of the soil contamination <br /> in soil appears defined to the near the former northern cluster area. Available data is <br /> suggestive of a release was most severe at the northern edge of the former northern cluster <br /> UST area.After the release,TPH/BTEX and MTBE migrated only slightly north in the area <br /> of well EW-1 and vertically to a depth of approximately 35 feet bsg near boring B9. The <br /> "deep"migration of hydrocarbons indicates a historically depressed water table depth of near <br /> 30 feet bsg. <br /> • Based on six-years of ground water monitoring, the impacted ground water appears stable <br /> between wells MW-10, MW-12, MW-13, MW-14 and MW-15. The plume appears to be <br /> laterally less than than 40 feet east to west and approximately 40 feet north to south, <br /> surrounding the former UST area at well EW-1. The maximum concentrations detected <br /> were: TPH-g at 11,000 µg/l; TPH-d at 110,000 µg/l; and benzene at 640 µg/l (MW-10). <br /> • Significant concentrations of TPH-g,TPH-d and BTEX compounds were detected in ground <br /> Advanced CeoEnvironmental,Inc. <br />
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