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ARCHIVED REPORTS XR0004315
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ARCHIVED REPORTS XR0004315
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Last modified
7/23/2019 11:44:28 AM
Creation date
7/23/2019 11:31:21 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004315
RECORD_ID
PR0544686
PE
3528
FACILITY_ID
FA0000916
FACILITY_NAME
7-ELEVEN INC #19976
STREET_NUMBER
1399
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21633034
CURRENT_STATUS
02
SITE_LOCATION
1399 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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9 <br /> Second Quarter 2000 Monitoring and Sampling Report June 29 2000 <br /> 7-Eleven Inc Store#19976 1399 North Main Street Manteca CA <br /> Groundwater Monitoring Data <br /> Before monitoring, each well cap was opened to allow the water level in each well to stabilize to <br /> ' atmospheric pressure The DTW was measured to the nearest 0 01 foot from the top of the well casing <br /> using an Interface probe <br /> Two potentiometric surface maps were prepared using the quarterly groundwater elevation data Based <br /> on the groundwater elevation data, groundwater flow In the shallower water-bearing zone Is toward the <br /> northwest at a gradient of approximately 0 003 ft/ft (Figure 2) Groundwater flow In the deeper part of the <br /> ' water-bearing zone is toward the north-northwest at a gradient of about 0 003 ft/ft (Figure 3) Groundwater <br /> monitoring results are presented in Table 1 Field data sheets are Included in Attachment 3 <br /> Monitoring Well Sampling And Analytical Results <br /> tBefore sampling, at least four well-casing volumes of groundwater was removed from each monitoring <br /> well unless the well was purged dry The groundwater samples were collected using disposable bailers <br /> ' Groundwater samples were placed in analysis-specific containers with analysis-specific preservative The <br /> samples were then sealed using Teflon septum caps, labeled with the fob identification number, the <br /> sample number, date, time, and type of laboratory analysis required The samples were stored on ice and <br /> transported with a chain-of-custody record to a state-certified laboratory for analysis for BTEX and TPH-G <br /> using Environmental Protection Agency(EPA) method 8020/modified 8015 and for oxygenates TBA, <br /> ' MTBE, DIPE, ETBE and TAME using EPA method 8260 <br /> Laboratory analytical results for quarterly groundwater samples and historical results are summarized in <br /> Table 2 Analytical results for the shallower part of the water-bearing zone indicated dissolved <br /> concentrations of up to 5,600 pg/L benzene, 58,000 pg/L TPH-G, and 1,400 pg/L MTBE Highest levels <br /> were found in well MW-2, located near to/directly downgradient from the hydrocarbon source area (the <br /> ' underground storage tanks/pump island area) Downgradient attenuation In the shallower water-bearing <br /> zone is evidenced by lower concentrations (86 lag/L benzene, 1,200 pg/L TPH-G, and 130 lag/L MTBE) in <br /> well MW-5 In the deeper water-bearing zone, hydrocarbon levels ranged up to 2 9 tag/L benzene in <br /> ' upgradient well MW-4A Down/crossgradient concentrations attenuate as observed by non-detectable <br /> benzene, TPH-G, and MTBE in well MW-5A <br /> Well Search <br /> tSensitive receptor surveys completed in 1999 (IT Corporation, April 1999) and March 2000 (Attachment 5) <br /> indicate that there are no active public water supply wells within 2,000 feet downgradient from the site, <br /> although there are two wells of unknown status within 2,000 feet upgradient/crossgradient of the site <br /> 19976020 RPT <br />
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