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ARCHIVED REPORTS XR0002739
Environmental Health - Public
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3500 - Local Oversight Program
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PR0508502
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ARCHIVED REPORTS XR0002739
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Last modified
11/7/2018 9:04:44 AM
Creation date
11/6/2018 3:30:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002739
RECORD_ID
PR0508502
PE
3526
FACILITY_ID
FA0008117
FACILITY_NAME
ARCO STATION #4932
STREET_NUMBER
16
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
13902001
CURRENT_STATUS
01
SITE_LOCATION
16 E HARDING WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Atlantic Richfield Company Page 5 <br /> isARCO Station No 4932 Stockton Califomia Aagust 29,2002 <br /> were measured at 29 and 28 feet bgs,respectively TPHg was detected in four of the ten <br /> samples at a maximum concentration of 780 mgfkg (EW-1, 27 5') Benzene was detected in <br /> six of the ten samples at a maximum concentration of 5 1 mg/kg (EW-1, 27 5') MtBE was <br /> detected in eight of the ten samples at a maximum concentration of 290 mg/kg (EW-1, <br /> 27 5') <br /> On April 2 through 4, 2002, a step drawdown pumping test, constant rate drawdown <br /> pumping test, and aquifer test were completed Results were as follows <br /> • Capture zones of approximately 31 feet and 48 feet were calculated in the <br /> downgradient and cross-gradient directions, respectively The capture zone was <br /> calculated using the Javandel and Tsang method <br /> • A pumping rate 4 and 6 gallons per minute was used for the constant rate drawdown <br /> pumping test <br /> The well installation and aquifer pumping test is documented in SECOR's report titled, Site <br /> Assessment and Aquifer Testing Results, dated June 7, 2002 <br /> 2.3 Geology and Hydrogeology <br /> • Geologic cross-sections presented in SECOR's November 9, 2001 report titled Additional <br /> Site Assessment Report depict the following conditions <br /> • Interbedded layers of sandy silt and silty clay encountered from ground surface to <br /> approximately 20 feet bgs <br /> • Fine grain sands and silt mixtures from 20 feet bgs to the total depth explored(80 <br /> feet bgs) <br /> • Groundwater was encountered at approximately 27 feet bgs <br /> These conditions are generally consistent with the soils encountered on March 14 and 15, <br /> 2002, when West Hazmat installed one deep groundwater monitoring well (DMW-1) and one <br /> GYVE well (EW-1) at the site (Figures 2) In each of the borings for wells DMW-1 and EW- <br /> 1, soil consisted predominantly of sandy silt from ground surface to approximately 25 feet to <br /> 30 feet bgs, with occasional interbedded layers of silty sand Below approximately 25 feet to <br /> 30 feet bgs, soils within borings for DMW-1 and EW-1 were comprised of interbedded layers <br /> of sandy silt, clayey silt, sand, and silty sand to the total depths explored (81 feet and 50 feet <br /> bgs, respectively) Boring logs showing soil stratigraphy are included in Attachment B <br /> Updated geologic cross-sections including 6 recently installed extraction and monitoring <br /> wells illustrating soil conditions beneath the site are included as Figure 3 Historical cross- <br /> sections prepared by SECOR are included in Appendix G <br /> Groundwater levels have vaned from approximately 14 feet to 18 feet below mean sea level <br /> The general hydraulic gradient at the site has been reported to the east-northeast with a <br /> I 1ARCO\49321PAR\PAR doc <br />
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