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ARCHIVED REPORTS_XR0005302
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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MARIPOSA
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2900 - Site Mitigation Program
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PR0541650
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ARCHIVED REPORTS_XR0005302
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Last modified
3/11/2020 6:00:34 PM
Creation date
3/11/2020 3:09:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005302
RECORD_ID
PR0541650
PE
2960
FACILITY_ID
FA0023868
FACILITY_NAME
FORMER USA GASOLINE SERVICE STATION 110
STREET_NUMBER
2132
Direction
E
STREET_NAME
MARIPOSA
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
1730635
CURRENT_STATUS
01
SITE_LOCATION
2132 E MARIPOSA RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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the soil sample collected beneath the diesel fuel dispenser The highest TPHg concentration <br /> detected was 4,800 mg/kg in the soil sample collected beneath the gasoline USTs Benzene was <br /> detected at concentrations up to 4 2 and 6 4 mg/kg in the soil samples collected beneath the USTs <br /> and dispensers, respectively Methyl tertiary butyl ether (MTBE) was detected at concentrations <br /> up to 28 and 18 mg/kg in the soil samples collected beneath the USTs and dispensers, <br /> respectively Approximately 400 cubic yards of soil excavated during UST and associated <br /> pipeline removal were disposed of off-site at a licensed landfill GHH Engineering estimated the <br /> mass of residual gasoline at the site to be approximately 163 gallons based on information in a <br /> Request for No Further Action report dated February 2000 <br /> GHH Engineering performed quarterly groundwater monitoring and sampling from July 1997 to <br /> September 2002 The historical groundwater gradient direction has ranged from northeast to the <br /> southeast <br /> GROUNDWATER MONITORING <br /> Water levels were measured in wells MW-1P through MW-6P, MW-1 and MW-2 on November <br /> 10, 2004 The locations of the monitoring wells are shown on Figure 2 Depth to water levels <br /> ranged from 64 89 to 66 19 feet below the tops of the well casings The groundwater elevation <br /> decreased an average of 0 97 feet since the previous quarter The water level data were used to <br /> develop the groundwater elevation contour map (Figure 3) The average hydraulic gradient on <br /> November 10, 2004 was calculated to be 0 0025 ft/ft or approximately 13 2 ft/mile, and flowed <br /> generally towards the southeast A summary of groundwater monitoring data is presented in <br /> Table 1 <br /> SAMPLING ACTIVITIES <br /> On November 10, 2004, ATC personnel collected groundwater samples from monitoring wells <br /> MW-1P through MW-6P, MW-1, and MW-2 Prior to collection of groundwater samples, the <br /> depth to water was measured in the wells and the pH, electrical conductivity, and temperature <br /> were measured in the groundwater purged from the monitoring wells and recorded Aquifer <br /> parameters were allowed to stabilize and a minimum of three well casing volumes were purged <br /> from each well prior to sampling The wells were allowed to recover and samples were collected <br /> from each well using dedicated disposable bailers Purged well water was contained on site in <br /> DOT approved 55-gallon drums for disposal pending receipt of laboratory results <br /> The groundwater samples collected from each well were submitted to Argon Laboratories, a <br /> state-certified analytical laboratory (Environmental Laboratory Accreditation Program Certificate <br /> No 2359) located in Ceres, California, for analyses Laboratory analyses consisted of TPHg <br /> utilizing EPA Method 8015B, BTEX utilizing EPA Method 8021B, and oxygenate fuel additives <br /> MTBE, ethyl tertiary butyl ether (ETBE), di-isopropyl ether(DIPE), tertiary butyl alcohol (TBA), <br /> tertiary amyl ether (TAME), 1,2-dichloroethane (1,2-DCA), and 1,2-dibromoethane (EDB) <br /> s Ienvironmenta112591210003-StocktonlQuartlyl3QR-2004 doc 2 <br />
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