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COMPLIANCE INFO_FILE 3
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2300 - Underground Storage Tank Program
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PR0231945
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COMPLIANCE INFO_FILE 3
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Last modified
12/19/2022 4:38:41 PM
Creation date
6/3/2020 9:55:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
COMPLIANCE INFO
FileName_PostFix
FILE 3
RECORD_ID
PR0231945
PE
2361
FACILITY_ID
FA0003934
FACILITY_NAME
Lawrence Livermore National Lab - Site 300
STREET_NUMBER
15999
Direction
W
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
15999 W CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\UST\UST_2361_PR0231945_15999 W CORRAL HOLLOW_FILE 3.tif
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EHD - Public
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June 27—Soil samples 2, 5, and 6 consisted of a sample from each end of <br /> the tank excavation at a depth of 2 ft beneath the tank excavation floor and <br /> a sample from the north wall of the tank excavation at 2 ft beneath the <br /> piping. Of the two soil samples that were collected from beneath the tank <br /> excavation floor, the east end sample (5) was below the TEPH-Diesel <br /> detection limit and the west end (6) sample yielded a concentration of 65 <br /> ppm TEPH-Diesel. <br /> • July 10 — Soil sample 7 was collected from the floor of the piping <br /> excavation at approximately 3 ft below the depth of the piping. Neither of <br /> the soil samples (2 or 7) collected from beneath the piping exceeded the <br /> detection limit for TEPH-Diesel. <br /> As shown on Figure 4, none of the six soil samples yielded detectable concentrations of <br /> benzene, toluene, xylenes, or ethylbenzene (BTE or X). The proposed soil sample specified in <br /> the Closure Pan as 1 was not collected because the SJCPHS-EHD representative said it was <br /> unnecessary. Sample 1 would have been collected 1 ft above sample 2. <br /> Leaching Potential Analysis <br /> All diesel-stained soil was removed from the piping excavation. The non-detectable (ND) <br /> concentrations of TEPH-Diesel and BTE and X in sample 7 support this fact. The diesel-stained <br /> soil from above the tank was excavated before the tank was removed from the excavation. As <br /> mentioned earlier, this soil was sampled twice and yielded TEPH-Diesel concentrations of 2,300 <br /> and 4,400 ppm. These concentrations are probably the result of diesel fuel spillage from fueling <br /> operations while the tank was in service. No diesel-stained soil was evident in the floor or walls <br /> of the tank excavation. However, due to the depth of the tank excavation and the proximity of <br /> numerous utilities the removal of all soil with detectable concentrations of diesel from the floor <br /> of the tank excavation was not possible. Since soil sample 6 from the west end of the tank <br /> excavation yielded a TEPH-Diesel concentration of 65 ppm, this soil had to be evaluated to <br /> determine if it could be left in place. To do that, a Leaching Potential Analysis was performed. <br /> The analysis is excerpted from the Leaking Underground Fuel Tank (LUFT) Manual as <br /> Appendix G of this report. It estimates the concentrations of petroleum hydrocarbons that can be <br /> left in place without threatening ground water. See Table 1 for the site characteristics and scores <br /> based on their potential influence for increasing the vertical migration of fluids in the vicinity of <br /> the tank excavation (McIlvride et al., 1990). <br /> 6 <br />
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