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ARCHIVED REPORTS_XR0005387
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ARCHIVED REPORTS_XR0005387
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Last modified
3/10/2020 6:49:17 PM
Creation date
3/10/2020 4:33:30 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005387
RECORD_ID
PR0545495
PE
3528
FACILITY_ID
FA0006423
FACILITY_NAME
STOCKTON MOBIL 2
STREET_NUMBER
3440
Direction
E
STREET_NAME
MAIN
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
3440 E MAIN ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Beacon Station No, 474 August 26, 1997 <br /> Stockton California Remedial Testing Report <br /> • the discharged groundwater were 100 parts per million (ppm) [or 100,000 parts per billion <br /> (ppb)] of TPHg. <br /> LaboratoEy Water Anal ses <br /> Water samples were collected from pumping well MW-2 on May I3, 16, and 21, and June 4, <br /> 1997. Collected samples were submitted under chain-of-custody (CoC) to Kiff Analytical <br /> (Kiff), a California Department of Health Services-certified analytical laboratory (ELAN <br /> No. 2236) located in Davis, California. Groundwater samples were analyzed for Total <br /> Petroleum Hydrocarbons as gasoline (TPHg) according to EPA Method 8015, benzene, <br /> toluene, ethylbenzene, and xylenes (BTEX) according to EPA Method 602 and Methyl- <br /> tertiary-butyl ether(MTBE) according to Method 8020 /602. <br /> The water samples collected from pumping well MW-2 in May and June 1997 indicated <br /> concentrations of TPHg between 20,000 parts per billion (ppb) and 37,000 ppb; <br /> concentrations of benzene between 4,300 ppb and 12,000 ppb; and nondetectable <br /> concentrations of MTBE (less than 250 ppb). Laboratory analytical results are summarized <br /> in Table 1. Copies of the laboratory reports and CoC are included as Attachment C. <br /> • Results of Aquifer Pumping Tests <br /> Observation water-level data collected between May 14 and 15, 1997 indicated minimal <br /> measurable drawdown in wells MW-1 (0.10-foot), MW-3 (0.11-foot), and MW-4 (0.10- <br /> foot) during the pump test. By May 28, 1997 continued long-term pumping still indicated <br /> minimal measurable drawdown in wells MW-1 (0.15-foot), MW-3 (0.15-foot), and MW-4 <br /> (0.14 foot). Well MW-1 is located approximately 114 feet southwest of pumping well MW- <br /> 2; well MW-3 is located approximately 62 feet west of pumping well MW-2; and well MW- <br /> 4 is located approximately 85 feet northeast of pumping well MW-2. <br /> Graphs of time vs. drawdown, as measured with the data loggers are included in Attachment <br /> B. Using the time-drawdown method for the datalogger data measured in May 1997, and a <br /> pumping rate of 2.0 gpm, the calculated transmissivities (T) were 3,429 gallons per day per <br /> foot (gpd/ft) for the MW-1 data and 3,200 gpd/ft for the MW-3 data. The calculated <br /> storativities (S) were 0.0045 for the MW-1 data and 0.0113 for the MW-3 data. Using an <br /> aquifer thickness of 15 feet from the boring log for well MW-1, results in an estimated value <br /> of hydraulic conductivity (K) of approximately 30 feet per day. Using an aquifer thickness <br /> of 15 feet from the boring log for well MW-3, results in an estimated value of hydraulic <br /> conductivity (K) of approximately 28 feet per day. <br /> Graphs of distance vs. drawdown, as measured with the water level indicators in wells MW- <br /> 1, MW-3, and MW-4 are included in Attachment B. Using the distance-drawdown method <br /> for the long-term water level indicator data collected in June 1997, and an average pumping <br /> rate of 2.0 gpm, the calculated transmissivity (T) was 13,367 gpd/ft, and the calculated <br /> 1474.11-rpt 3 HORIZON ENVIRONMENTAL INC. <br />
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