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ARCHIVED REPORTS_XR0010299
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545688
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ARCHIVED REPORTS_XR0010299
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Last modified
5/21/2020 3:23:03 PM
Creation date
5/21/2020 10:18:40 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010299
RECORD_ID
PR0545688
PE
3528
FACILITY_ID
FA0003634
FACILITY_NAME
CANTEEN CORPORATION
STREET_NUMBER
1500
Direction
N
STREET_NAME
SHAW
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
14326008
CURRENT_STATUS
02
SITE_LOCATION
1500 N SHAW RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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XtD <br /> r <br /> Monitoring wells MW-8 and MW-9 were installed on December 12, 1990 No soil samples were <br /> collected from these borings All soil PID measurements were reported as non-detected <br /> Monitoring wells MW 10, MW-11 and MW-12 were installed on July 11, 1996 and monitoring <br /> I well MW-3A was installed on July 12, 1996 No hydrocarbon constituents were detected in any <br /> of the soil samples taken from MW-10 and MW-11, except for the sample collected from the 65 <br /> to 66 5 foot interval m MW-10 Concentrations of benzene, toluene, total xylenes, and TPH-G <br />' were detected No soil samples were collected from monitoring well MW-12 All soil PID <br /> measurements were reported as non-detected <br /> On May 24 through June 2, 1999 a site investigation was conducted that included the <br /> advancement of seven soil borings (SB-6, SB-7, SB-8, SB-13D, MW-13, MW-13A and MW- <br /> 13B) and the installation of three monitor wells (MW-13, MW-13A and MW-13B) <br /> Concentrations of benzene, toluene, and total xylenes were detected in a soil sample from soil <br /> boring SB-6 at a depth of 41 5 feet below ground level Concentrations of BTEX, TPH-G and <br /> MTBE were detected in a soil sample from soil boring SB-13D In addition, two soil samples <br /> Ifrom borings SB-13D and MW-13A were submitted for physicochenucal and microbiological <br /> analyses The samples submitted for analysis revealed very low viable recoveries for <br /> I • heterotroptuc and selective microorganisms at the dilutions tested The results suggested the <br /> possibility that some level of biotoxicity existed at the site <br /> Soil boring logs and monitor well construction details are provided in Appendix A Two Cross <br /> Sections (Figure 3) were created to show the soil stratigraphy across the site Cross Section A-A' <br /> (Figure 4) extends from monitoring well MW-6 (north) to MW-9 (south) and includes wells <br /> screened in the shallow and deep aquifers Cross Section B-B' (Figure 5) extends from <br /> monitoring well MW-7 (southwest) to MW-1 (northeast) and includes wells screened in the <br /> shallow and deep aquifers In general, shallow subsurface soil at the site consists of interbedded <br /> units of fine-grained(silt) deposits and coarse-grained (sand) deposits Based on the soil boring <br /> logs, relatively fine-grained soil consisting of silt and clay was encountered from surface to <br /> approximately 60 feet bgs These fine-grained soils appeared to be underlain prmiardy by deposits <br />' consisting of clayey to silty sand and sand to a depth of approximately 116 feet bgs A stiff silt <br /> layer was encountered from about 116 to 118 feet bgs The silt layer was underlain by silty sand <br /> and sand <br />' Soil analytical data are summarized in Table 1 A Soil Boring Location Map presented as Figure <br /> 6 shows the location of each boring, and summarizes the analytical results <br />' Results of the soil and groundwater sampling conducted during the assessment portion of the <br /> project indicate that the horizontal extent of the hydrocarbon impact from the UST release has <br /> I <br /> • 3 <br /> I <br />
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