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ARCHIVED REPORTS_XR0010337
Environmental Health - Public
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PR0545688
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ARCHIVED REPORTS_XR0010337
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Last modified
5/21/2020 3:39:54 PM
Creation date
5/21/2020 2:59:51 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010337
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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II. SITE ASSESSMENT SUMMARY <br /> A. ASSESSMENT HISTORY <br /> The following document describes the history, extent of impact, and prescribed remedial actions for <br /> hydrocarbon concentrations at the Former Canteen Facility located just east of Highway 99,between <br /> Waterloo Road (Highway 88) and Fremont Street (Highway 26) The one-acre property is zoned <br /> for manufacturing and light industrial use,there are no residences in the immediate area The project <br /> site and associated operations are expected to remain commercial The site is located in Section 31, <br /> T 2N , R 7E , M B B &M , on a portion of Section 54 Weber Grant, San Joaquin County, California <br /> (Figures 1 and 2) <br /> Site assessment activities include UST excavation activities conducted in March and November <br /> 1992 From February 1993 through May 1999 a total of eight (8) soil borings and 13 monitoring <br /> wells were drilled and installed at the site and surrounding vicinity <br /> The level and extent of hydrocarbon concentrations at the project site are described in the following <br /> sections The sections have been organized by which media is impacted <br /> B. SITE GEOLOGY & HYDROCARBON CONCENTRATIONS — SOIL <br /> The soil stratigraphy across the site is depicted utilizing geologic cross-sections locations as <br /> indicated on Figure 3 Cross-Section A-A' (Figure 4) extends from monitoring wells MW-6 to <br /> MW-9 (north to south) and Cross-Section B-B' (Figure 5) extends from monitoring wells MW-7 to <br /> MW-1 (southwest to northeast) Both cross-sections include wells screened in the shallow and deep <br /> aquifers In general, shallow subsurface soil at the site consists of interbedded units of fine-grained <br /> (silt) deposits and coarse-grained (sand) deposits Based on the soil boring logs, relatively fine- <br /> grained soil consisting of silt and clay was encountered from the ground surface to approximately <br /> 60 feet below ground surface (bgs) These fine-grained soils appeared to be underlain primarily by <br /> deposits consisting of clayey to silty sand and sand to a depth of approximately 116 feet bgs A stiff <br /> silt layer was encountered from about 116 to 118 feet bgs The silt layer was underlain by silty sand <br /> and sand Soil boring and monitoring well construction details are presented in Appendix A <br /> Concentrations of sorbed-phase hydrocarbons detected in the soil were compared to the EPA <br /> Region 9 PRGs The soil samples collected from the south and southeast walls of the UST <br /> excavation (14 to 19 feet bgs) exceeded the Industrial PRGs for benzene, toluene, and xylenes The <br /> benzene PRG was also exceeded in borings SB-2 and SB-13D (46 5 feet bgs) The TPH-G <br /> concentrations detected in these soil samples vaned from 10 3 to 17,600 mg/kg The location of soil <br /> borings installed at the site and analytical results are presented on Figure 6 <br /> II-1 <br />
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