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ARCHIVED REPORTS_XR0007096
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544811
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ARCHIVED REPORTS_XR0007096
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Last modified
11/20/2024 9:21:18 AM
Creation date
9/5/2019 1:31:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007096
RECORD_ID
PR0544811
PE
3528
FACILITY_ID
FA0000091
FACILITY_NAME
Colonial Energy CE 40138 (DBA Power Mart)
STREET_NUMBER
14000
Direction
E
STREET_NAME
STATE ROUTE 88
City
LOCKEFORD
Zip
95237
CURRENT_STATUS
02
SITE_LOCATION
14000 E HWY 88
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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February 28, 1997 <br /> Ms. Anastasia Duarte-Wilkinson SEC%f1_'11X <br /> Time Oil Company International incorporated <br /> 2737 West Commodore Way <br /> Seattle, WA 98199 <br /> SUBJECT: Quarterly Monitoring Report, October-December 1996 <br /> Jackpot Food Mart <br /> 14000 East Highway 88 <br /> Lockeford, California <br /> Ms. Duarte-Wilkinson: <br /> This report presents the results of quarterly groundwater monitoring and sampling conducted at the <br /> Jackpot Food Mart at 14000 East Highway, Lockeford, California(the site, see Figure 1). <br /> GROUNDWATER MONITORING AND SAMPLING <br /> Ten groundwater monitor wells were sampled on December 19, 1996 at the site. Monitor wells MW-i <br /> through MW-4 were installed as part of an environmental investigation conducted in December 1994. <br /> In July 1996,monitor wells MW-5 through MW-10 were installed as part of an additional environmental <br /> site assessment. Prior to purging each groundwater monitor well,a water sample was taken and subjective <br /> analyses performed. The subjective analyses consisted of checking for floating product or a hydrocarbon <br /> sheen by lowering a clean teflon bailer down the well and collecting a sample at the groundwater-air <br /> interface. Wells not containing floating product were purged of approximately 2 to 4 casing volumes of <br /> water or until groundwater parameters of pH, temperature, and conductivity stabilized as measured by <br /> portable meters calibrated to a standard buffer and conductivity standard. If the well was slow to recover <br /> or purged dry, the water level in the monitor well was allowed to recover to at least 80 percent of its static <br /> level before sampling. The groundwater samples were then collected by lowering a clean disposable <br /> bailer into the well and collecting a representative sample. The groundwater samples were slowly <br /> transferred to laboratory-cleaned sample containers, sealed with teflon caps, labelled with the sample <br /> number, sample time and date,and immediately placed on ice in an insulated container. Each sample was <br /> logged onto a chain-of-custody record for subsequent delivery to Excelchem Environmental Labs located <br /> in Roseville, California. Groundwater samples were analyzed for TPHg and BTEX,using modified EPA <br /> Method 8015, and EPA Method 602 respectively. <br /> Groundwater Elevation Data <br /> Depth to groundwater was obtained from the existing groundwater monitor wells at the site using a water <br /> level indicator graduated to 0.01 foot. The depth to groundwater measurement was converted to a <br /> groundwater elevation for each well and used to construct a potentiometric surface map (Figure 2), and <br /> calculate the local groundwater flow direction and hydraulic gradient. The groundwater potentiometric <br /> surface elevation averaged approximately 73.87 feet below ground surface (bgs) during this monitoring <br /> event. The groundwater flow direction at the site is directed toward the southwest with a hydraulic <br /> gradient of approximately 0.02 feet per feet (ft./ft). A summary of data regarding groundwater'levels <br /> LCKFRDgm.996 SECOR <br /> J0710-001-01 February 28,1997 <br /> !/87 Trihule Road. Siiitc C. Sacramento, CA 95575-4404 (916)648-9160 19161648-8051 FAX <br />
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