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ARCHIVED REPORTS_XR0005739
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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N
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99 (STATE ROUTE 99)
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6100
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2900 - Site Mitigation Program
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PR0515353
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ARCHIVED REPORTS_XR0005739
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Last modified
11/19/2024 1:50:32 PM
Creation date
4/1/2020 2:36:24 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005739
RECORD_ID
PR0515353
PE
2950
FACILITY_ID
FA0012099
FACILITY_NAME
ARCO STATION #595
STREET_NUMBER
6100
Direction
N
STREET_NAME
STATE ROUTE 99
City
STOCKTON
Zip
95209
CURRENT_STATUS
01
SITE_LOCATION
6100 N HWY 99
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Atlantic Richfield Company 6 <br /> ARCO 595,6100 North Highway 99,Stockton Cahfomia September 13 2002 <br /> • (Figure 7) Groundwater elevation data are presented in Table 2 Historical shallow <br /> groundwater gradient data are included in Table 5 The groundwater gradient within the <br /> deeper water-bearing zone will be confirmed during subsequent quarterly groundwater <br /> monitoring events <br /> Stockpiled SoiMrge and Rinsate Water <br /> Approximately 17 cubic yards of soil generated during the installation of the wells was <br /> stockpiled on-site One composite sample (4 sleeves to 1 sample) was collected from the <br /> stockpiled soil, and analyzed for TPHg and BTEX by the DHS/LUFT method, and total <br /> lead by EPA Method 6010B <br /> TPHg and BTEX constituents were not detected in the stockpiled soil sample Total lead <br /> was detected at a concentration of 6 8 mg/kg Soil was transported from the site by <br /> Dillard Environmental to Altamont Landfill in Livermore, California on July 10, 2002 <br /> Analytical data for the stockpiled soil are presented in Table 6 <br /> Eight 55-gallon steel drums of nnsatelpurge water were stored on-site The nnsate/purge <br /> water was transported from the site by Dillard Environmental to Altamont Landfill in <br /> Livermore, California for disposal on July 30, 2002 <br /> SUMMARY OF FINDINGS <br /> • TPHg, BTEX,TPHd, MtBE, and fuel oxygenates were not detected in <br /> soil samples collected from the borings for shallow wells MW-8 <br /> through MW-10, and deep wells DMW-1 through DMW-3 <br /> • TPHg and benzene were not detected in groundwater samples from <br /> shallow wells MW-8 through MW-10, and deep wells DMW-1 <br /> through DMW-3 Trace levels of toluene were detected up to 2 6 ppb <br /> 1n wells MW-8, and DMW-1 through DMW-3 A minor concentration <br /> of ethylbenzene was detected in well DMW-1 at 0 51 ppb Minor <br /> concentrations of xylenes were detected in deep wells DMW-1 through <br /> DMW-3 at concentrations up to 2 8 ppb Minor concentrations of <br /> BTEX were also detected in the quality control blank <br /> • Concentrations of MtBE were detected in groundwater samples <br /> collected from shallow wells MW-8, MW-9, and deep wells DMW-1 <br /> through DMW-3 at concentrations up to 53 ppb (EPA Method 8260B) <br /> TBA was detected in deep wells DMW-1 through DMW-3 at <br /> concentrations up to 72 ppb Shallow well MW-8 and deep wells <br /> DMW-1 through DMW-3 contained concentrations of 1,2-DCA up to <br /> 4 6 ppb Other fuel oxygenates were not detected <br /> e Groundwater flow within the shallow water bearing zone on-site was <br /> to the northwest at a gradient of 0 003 ft/ft, groundwater flow within <br /> the shallow water bearing zone off-site was t0 the north-northeast at a <br /> I 1ARC010595\Reportslwe11 msta113 doc <br />
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