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ARCHIVED REPORTS_XR0002670
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ARCHIVED REPORTS_XR0002670
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Last modified
1/31/2020 4:40:10 PM
Creation date
1/31/2020 3:32:12 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002670
RECORD_ID
PR0545259
PE
3528
FACILITY_ID
FA0004966
FACILITY_NAME
CHEVRON USA (INACT)
STREET_NUMBER
45
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12707037
CURRENT_STATUS
02
SITE_LOCATION
45 E HARDING WAY
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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Environmental Assessment Report 2 <br /> Chevron U S A Products Company,45 East Harding Way,Stockton CA July 1b 1995 <br /> 23 Soil Sampling <br /> Soil samples were collected from boreholes SB-10, SB-11, SB-12 AND SB-13 at 5-foot intervals during <br /> drilling, beginning at approximately 5 feet BGS Samples were collected using a 2 5-Inch O D <br /> split-spoon sampler, lined with three 2-inch-diameter by 6-inch-long brass sample tubes The sampler <br /> was driven 18 inches ahead of the augers at each sample point Soil samples were field screened for <br /> hydrocarbon vapors using a photo-ionization detector(PID) Sal was logged using the Unified Soil <br /> Classification System by a Groundwater Technology field geologist working under the supervision of a <br /> California registered geologist(Appendix B) One sample tube from each 5-foot interval was sealed, <br /> labeled and placed on ice in an insulated container for transport under chain-of-custody manifest to <br /> Sequoia Analytical (Sequoia), a California state-certified analytical lab in Sacramento <br /> Soil samples collected at each sampling interval from 15-through 50-feet BGS from each boring were <br /> selected for laboratory analyses (Tables 1 and 2) Samples were analyzed for benzene,toluene, <br /> ethylbenzene and total xylenes (BTEX), and total petroleum hydrocarbons-as-gasoline (TPH-G), using <br /> U S Environmental Protection Agency (EPA) methods 5030/8020/modified 8015 Based on results <br /> from the above analyses,the two samples having the greatest TPH-G concentration from each boring <br /> were selected for Toxicity Characteristic Leaching Procedure (TCLP) analyses of BTEX using EPA <br /> method 8020, one sample with non-detectable levels of BTEX and TPH-G from each boring was <br /> selected for Total Organic Carbon (TOC) analysis using EPA method 9060 modified, and one <br /> • additional sample with non-detectable levels of BTEX and TPH-G from each boring was selected for <br /> dry bulk density analysis using method MSA 13-2 (see Appendix C for details) <br /> Upon completion of drilling and sampling, all four borings were backfilled with a neat cement grout to <br /> surface on June 2, 1995 <br /> 30 RESULTS OF SOIL SAMPLE ANALYSES <br /> Tables 1 and 2 summarize the laboratory analytical results for sod samples collected on June 1 and 2, <br /> 1995 Table 1 presents data on BTEX and TPH-G The highest benzene concentration was reported <br /> in sample SB13-50 0 at a concentration of 0 76 milligrams per kilogram (mg/kg),while the greatest <br /> concentration of TPH-G was reported at 10,000 mg/kg in sample SB13-25 0 The highest levels of <br /> ethylbenzene and total xylenes detected in the TCLP analyses were at respective concentrations of 460 <br /> and 4,000 micrograms per liter(µg/L), concentrations of benzene and toluene were below minimum <br /> detection limits for all samples analyzed for TCLP BTEX <br /> The highest level of TOC was detected in sample SB13-40 Oat a concentration of 370 mg/kg Sample <br /> SBI 3-35 0 yielded the highest dry bulk density value of 2 35 grams per cubic centimeter(g/cm3), <br /> reported for the clay portion of the sample core <br /> 0139EAR rptiChv 35] <br /> ❑®GttOUNDWATm <br /> ❑❑❑TECHNOLOGY. I <br />
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