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ARCHIVED REPORTS XR0008662
Environmental Health - Public
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EHD Program Facility Records by Street Name
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EL DORADO
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1605
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3500 - Local Oversight Program
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PR0544687
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ARCHIVED REPORTS XR0008662
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Last modified
7/24/2019 9:00:33 AM
Creation date
7/24/2019 8:37:51 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008662
RECORD_ID
PR0544687
PE
3528
FACILITY_ID
FA0006185
FACILITY_NAME
El Dorado Gas & Mart
STREET_NUMBER
1605
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
16703101
CURRENT_STATUS
02
SITE_LOCATION
1605 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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' concentrations corresponded to the maximum levels detected over the past two years in offsite <br /> downgradient well MW-7 (see Table 1) Use of maximum levels over the past two years as representative <br /> of current and future concentrations is considered conservative, given the absence of a continuous source <br /> and sporadic detection of hydrocarbons in groundwater (ET1C, 2000) <br /> Table 1 <br /> ' Tier IUser-Defined Data <br /> Parameter,'w Designation _ Comments <br /> ' Chemicals of Potential Concern All chemicals detected in soil <br /> COPCs BTEX,MTBE and/or groundwater samples <br /> Representative COPC Source Benzene <0 002 mg/kg Maximum detected concentration <br /> ' Concentrations in Soil-Onsite Toluene <0 002 mg/kg in unsaturated soil confirmation <br /> Commercial/Industrial Receptor and Ethylbenzene <0 002 mg/kg samples from the former tank <br /> Construction Worker Receptor Xylenes 0 569 mg/kg balm area <br /> MTBE <0 01 in <br /> ' Representative COPC Source Benzene 13 ppb Site maximum concentrations <br /> Concentrations in Groundwater- Toluene 22 ppb during the past two years of <br /> Onsite Commercial/Industrial Ethylbenzene 7 4 ppb sampling in onsite wells(MW-5, <br /> ' Receptor and Residential Receptor at Xylenes 38 ppb VEW-2) <br /> Offsite Agricultural/Irrigation Wells MTBE 190 pLb <br /> Representative COPC Source Benzene 1 7 ppb Site maximum concentrations <br /> Concentrations in Groundwater- Toluene <0 5 ppb during the past two years of <br /> Offsite Residential Receptor at Ethylbenzene<0 5 ppb sampling in offsite well (MW-7) <br /> Apartment Building Xylenes <0 5 ppb <br /> MTBE 13 ppb <br /> ' Distance to Nearest Offsite Water Based on July,2000 Area Well <br /> SyMIX Wells '/4 mile= 1,320 ft Survey(ETIC,2000 <br /> Source Dimensions in Groundwater Width= 100 ft Conservative estimates based on <br /> D th=5 ft groundwater quality data <br /> Target Carcinogenic Risk Level Lowest target risk level defined <br /> 1 x 10-6 by USEPA, DTSC, and ASTM <br /> Target Non-Carcinogenic Hazard. Consistent with USEPA,DTSC, <br /> Quotient 10 and ASTM guidelines <br /> Benzene Carcinogenic Slope Factor Conservative value defined by <br /> inhalation and oral 0 1 (mg/kg/day)-' DTSC(1994 <br /> MTBE Carcinogenic Slope Factor Conservative value defined by <br /> inhalation 1 6x 10-4(mg/kg/day)° California EPA OEHHA, 2000 <br /> MTBE Carcinogenic Slope Factor Conservative value defined by <br /> ' (oral) I 1 8x 10"3(m /k da "i California EPA OIHHA,2000 <br /> For evaluation of risks associated with direct exposure to groundwater at the agriculturaVirrigation wells <br /> located 14-mile south-southeast of the site, site maximum groundwater concentrations over the past two <br /> years were used to estimate potential exposure point concentrations at the wells This calculation assumed <br /> that the wells are perforated in the shallow water-bearing formation and that transport in groundwater is <br /> governed by advective and dispersive transport as depicted by the highly conservative Domenico solute <br /> transport model (ASTM, 1995 and 1998, USEPA, 1996, and Domenico, 1987) Biodegradation and other <br /> mass-loss mechanisms were conservatively ignored along the path of chemical transport form the site to the <br /> wells Hydraulic parameters used in the Domenico model correspond to conservative ASTM (1995 and <br /> 9 <br />
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