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ARCHIVED REPORTS XR0004311
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PR0544686
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ARCHIVED REPORTS XR0004311
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Last modified
7/23/2019 11:41:45 AM
Creation date
7/23/2019 11:29:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004311
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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SJGOV\wng
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EHD - Public
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L <br /> • <br /> Remedial Action Plan and Further Site Assessment 2 <br /> 7-Eleven Store No 19976 1399 N Main St Manteca CA May 30 2000 <br /> 20 SUMMARY OF SITE ASSESSMENT DATA AND PROPOSED NEW ASSESSMENT <br /> ' Underground storage tank replacement and associated soil sampling activities were conducted in <br /> September 1996 Five underground storage tank pit samples were collected on September 19, 1999, one <br /> from beneath each end of the three underground storage tanks (USTs) at 15 feet below grade (except for <br /> the north end of the central tank, which was under an excavation stockpile) Sample analysis for benzene, <br /> toluene, ethylbenzene, and total xylenes (BTEX), methyl-tertiary-butyl-ether (MTBE), total petroleum <br /> ' hydrocarbons as gasoline (TPH-G) (EPA Methods 801518020), total lead (EPA Method 6010), and <br /> confirmation sampling for MTBE by EPA Method 8260 indicated the presence of hydrocarbons in levels of <br /> ' up to 0 93 milligrams per kilogram (mg/kg) benzene, 200 mg/kg TPH-G, and 0 35 mg/kg MTBE (EPA <br /> Method 8260) (IT Corporation, 2000) The tank pit was over excavated slightly to accommodate the new <br /> ' underground storage tanks, which were installed in the old tank pit (Figure 3), and post-excavation <br /> samples collected on September 20, 1999, were largely non-detectable <br /> ' Following receipt of tank replacement findings, the San Joaquin County Public Health Services <br /> Department (SJCPHS) requested site assessment to further evaluate soil and groundwater conditions <br /> Three direct-push borings (GP-1 - GP-3)(Figure 3)were installed on April 29, 1998 near the hydrocarbon <br /> source area (the UST pad and pump island) Nineteen soil samples were collected from depths ranging <br /> ' between 5 and 45 feet below grade for analysis for BTEX, MTBE, and TPH-G (EPA Methods 801518020) <br /> One sample from each soil boring was also analyzed for MTBE and other oxygenates by EPA Method <br /> 8260 Concentrations ranged up to 15 mg/kg benzene, 27 mg/kg TPH-G, and no detectable MTBE (EPA <br /> ' Method 8260)(IT Corporation, 2000) Highest concentrations were at a depth of 35 feet below grade <br /> Grab groundwater samples collected from the base of each boring were also analyzed for the same <br /> ' constituents and contained up to 5,800 micrograms per liter (ug/L) benzene and 290,000 ug/L TPH-G <br /> Dissolved MTBE ranged up to 3,700 ug/L (EPA Method 8260) <br /> ' Upon receipt of these data, the SJCPHS requested further assessment Three groundwater monitoring <br /> wells (well MW-1 is dual-nested to depths of 30 as well as 66 feet below grade)were installed in <br /> ' September, 1998 (Figure 3) Twelve soil samples were analyzed for BTEX, MTBE, and TPH-G (EPA <br /> Methods 801518020) Three of the samples were also analyzed for MTBE and the other oxygenates using <br /> ' EPA Method 8260 The highest benzene and MTBE concentrations were detected in capillary fringe soils <br /> (0 0708 mg/kg in MW-2@25'and 0 0829mg/kg in MW-1@20', respectively) The highest TPH-G <br /> concentration was detected in sample MW-1@45' at 17,000 mg/kg (IT Corporation, 2000) <br /> Upon receipt of these data, the SJCPHS requested additional assessment Soil boring SB-1 and cluster <br /> wells MW-4/4A and MW-5/5A were installed in May 1999 (Figure 3) Soil boring SB-1 was installed to <br />
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