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ARCHIVED REPORTS_XR0002998
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545246
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ARCHIVED REPORTS_XR0002998
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Last modified
1/30/2020 4:30:33 PM
Creation date
1/30/2020 3:21:41 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002998
RECORD_ID
PR0545246
PE
3528
FACILITY_ID
FA0003611
FACILITY_NAME
PARKWOODS GAS & FOOD
STREET_NUMBER
1612
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
07728002
CURRENT_STATUS
02
SITE_LOCATION
1612 W HAMMER LN
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Ms. Lori Duncan Page 2 of 5 <br /> San Joaquin County Environmental Health Department <br /> November 23, 2005 <br /> from northeast to southeast, with hydraulic gradients ranging from 0.002 feet/foot (ft/ft) to 0.03 ft/ft(see <br /> Table 1 and Figure 9). <br /> Site History <br /> ' Consult the SCM for site history prior to December 2004. <br /> In December 2004, two groundwater monitoring wells (MW-7 and MW-8) were installed to monitor the <br /> lateral and vertical extent of groundwater impacts at the site.MW-7 is located off site and down gradient of <br /> the former USTs and MW-8 was installed in the vicinity of the former USTs to monitor deep groundwater. <br /> ' Well locations are shown in Figure 2. <br /> f <br /> Selected soil samples were collected and analyzed from each monitoring well boring and submitted for <br /> analysis by gasoline-range organics(GRO)by EPA Method 8015B(preparation by EPA Method 5030),and <br /> r; for benzene,ethylbenzene,toluene,and xylenes,(BTEX),methyl-tert butyl ether(MtBE),tert butyl alcohol <br /> (TBA), di-isopropyl ether (DIPE), ethyl tert-butyl ether (ELBE), tert-amyl methyl ether (TAME), 1,2- <br /> dichloroethane(1,2-DCA),and 1,2-dibromomethane(EDB),by EPA Method 8260B (preparation by EPA <br /> Method 5030). <br /> GRO, benzene, toluene, ethylbenzene, and xylenes were reported in soil samples from MW-8. All fuel <br /> oxygenates analyzed were reported as below laboratory detection limits. The soil sample collected from <br /> MW-7 was reported below laboratory detection limits for all analytes.Soil analytical data for the December <br /> 2004 sampling event are summarized in Appendix C. <br /> HYDROCARBON DISTRIBUTION <br /> Hydrocarbons in the Unsaturated Zone <br /> Soil samples collected during drilling activities conducted between 1990 and 1993 indicated that <br /> hydrocarbon-impacted soils were confined primarily to the vicinity of the UST complex. Soil samples <br /> collected at 15.5 feet bgs during UST removal activities in February 1998 contained up to 8,200 milligrams <br /> �+ per kilogram (mg/kg) TPHg and up to 4.6 mg/kg benzene. Soil samples collected beneath the piping in <br /> February 1998 contained maximum concentrations of 12 mg/kg of TPHg and 0.03 mg/kg of benzene. Soil <br /> samples collected from MW-8 identified GRO and BTEX from 45 to 98 feet bgs.Because the water table has <br /> risen to approximately 25 feet bgs, the historical soil impacts are now below the water table. <br /> Hydrocarbons in Groundwater <br /> 1, Groundwater at the site has been monitored regularly since site investigations began.Results of monitoring <br /> since 1995 are summarized in Appendix D. Table 2 summarizes construction details for all site wells. <br /> Groundwater analytical data from the September 2005 monitoring event are presented in Figures 3 through 8 <br /> and 10 through 15. <br /> Groundwater impacted by GRO is generally confined to the southeastern portion of the site,extending from <br /> the area of the UST complex downgradient to MW-5(Figures 3 and 4).The maximum concentration of GRO <br /> KAWprocessU5 BP ARCd10054812005 SCM Update\SCM Update Text.doc <br />
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