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EL DORADO
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3500 - Local Oversight Program
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PR0544688
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Last modified
7/24/2019 9:39:48 AM
Creation date
7/24/2019 9:30:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE HISTORY
RECORD_ID
PR0544688
PE
3526
FACILITY_ID
FA0001946
FACILITY_NAME
El Dorado Food Mart
STREET_NUMBER
1901
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
16508019
CURRENT_STATUS
02
SITE_LOCATION
1901 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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20 March 2006 <br /> AGE-NC Project No. 03- 1071 <br /> Page 12 of 13 <br /> 12 milligrams per kilogram (mg/kg) at 30 feet, and 2,600 mg/kg at 40 feet. TPH-g was <br /> detected in VW-4 at a depth of 25 feet and at a concentration of 1 .5 mg/kg. <br /> • BTEX compounds were detected in all three soil samples from EW- 1 ; maximum <br /> concentrations were detected in the sample collected at 40 feet. Benzene was detected at a <br /> maximum concentration of 16 mg/kg; toluene at 66 mg/kg; ethylbenzene at25 mg/kg; xylene <br /> at 128 mg/kg. Benzene was detected in VW-3 at 35 feet at a concentration of 0.03 mg/kg. <br /> Ethylbenzene was detected in VW-3 at 25 feet and VW-4 at 25 feet, at concentrations of <br /> 0 .014 and 0.013 mg/kg, respectively. Xylenes were detected in VW-3 at 25 feet and VW-4 <br /> at 25 at concentrations of 0.028 and 0.024 mg/kg, respectively. <br /> • MTBE was detected in the sample collected from EW- 1 at 30 feet only, at a concentration <br /> of 0 .78 mg/kg. MTBE was detected in seven out of the nine samples from VW- 1 through <br /> VW-4, at a maximum concentration of 0.31 mg/kg in VW- 1 at 35 feet bsg. 1 ,2-DCA was <br /> detected in all three samples from EW- 1 , at a maximum concentration of 1 .2 mg/kg in the <br /> sample from 40 feet. No other constituents of concern were detected from the laboratory <br /> analysis <br /> • On 29 August, a variable rate ground water pumping test was conducted. During the test, <br /> maximum ground water draw-down during the first stage of the pump test (pump rate of 1 <br /> GPM) measured in extraction well EW- 1 was 23 . 12 feet after approximately 60 minutes of <br /> pumping operation; no significant draw-down was recorded in observation well MW4 (53 .5 <br /> ft south of EW- 1); MW- 1 through MW-3 showed very slight draw-downs of between 0.03 <br /> and 0 .08 ft (19.5 , 26, and 25.5 ft west, north, and east of EW- 1 , respectively). Observed draw <br /> downs during the second stage of the pump test (pump rate at 0.75 GPM) were similar: the <br /> maximum ground water draw-down measured in well EW- 1 was 19.53 feet after <br /> approximately 125 minutes of pumping operation (after the restart); no significant <br /> draw-down was recorded in observation well MW-4; MW- 1 through MW-3 showed very <br /> slight draw-downs of between 0.02 and 0.04. <br /> • Due to the results of the 8-hour variable rate pump test, the proposed 24-hour constant rate <br /> i <br /> test was cancelled. <br /> • Utilizing the time limited data a semi-logarithmic plot of ground water draw-down vs. <br /> observation well distance to pumping well (Jacob straight-line method), a best-fit line was <br /> utilized to project a theoretical radius of influence for EW- 1 at approximately 29.8 feet at 1 .0 <br /> GPM (Appendix H) . However, no observable or re-measurable drawdown was shown in the <br /> field at the designated observation wells. <br /> • Utilizing the Distance-Drawdown Method (Jacob straight-line method) for the limited <br /> duration of the first stage of the pump test (1 .0 GPM), a transmissivity was calculated at 10.6 <br /> ftZ/day (equivalent to 79. 1 gallons per day/ft) and a storativity value calculated at 0 .0012 . For <br /> the second stage of the pump test (0 .75 GPM), a transmissivity was calculated at 9.4 ft'/day <br /> Advanced GeoEnvironmental, Inc. / <br />
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