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ARCHIVED REPORTS_XR0012700
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2900 - Site Mitigation Program
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PR0542014
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ARCHIVED REPORTS_XR0012700
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Last modified
1/16/2020 6:26:24 PM
Creation date
1/16/2020 4:16:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012700
RECORD_ID
PR0542014
PE
2960
FACILITY_ID
FA0023306
FACILITY_NAME
LARRYS AUTO REPAIR
STREET_NUMBER
308
Direction
N
STREET_NAME
GRANT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
01
SITE_LOCATION
308 N GRANT ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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t <br /> 15.5 foot sample (See Drill Log) . Field inspection and PID <br /> testing did not record the presence of organic vapors or <br /> visual staining of soils typically associated with waste oil <br /> F contamination in Boring SB2 to a depth of 17.5 feet, Slight <br /> to strong gasoline hydrocarbon odors were noted in boring <br /> Sa3 to a depth of 31.5 feet, the maximum depth explored. <br /> PID readings in the 20.5, 25.5 and 30.5 samples were 4751, <br /> 4122, and 1400 ppm, respectively. The depth to first <br /> 3 => groundwater beneath the site was recorded approximately 32 <br /> feet below grade in boring SB1. <br /> 4.2 Laboratory Analysis - Soil <br /> The laboratory analysis of samples collected at 20.5, 25.5 <br /> and 30.5 feet in boring SB1 did not record the presence of <br /> BTEX above the 0.02 ppm method detection limit. The TPH-G <br /> concentrations in these samples and the TPH-PT concentration <br /> in the 30.5 foot sample were not detected above the 5.0 ppm <br /> ' z detection limit (Table 1). Elevated concentrations of BTEX <br /> and TPH-G were recorded in the 20.5, 25.5 and 30.5 samples <br /> from boring SB3. The 30.5 foot sample exhibited the highest <br /> t: . levels with BTEX and TPH-G concentrations of 215, 967, 279, <br /> 1358 and 11089 ppm, respectively. The laboratory test <br /> results for these samples, including BTEX concentrations, <br /> are summarized in Table 2. The 11.5 and 16.5 foot samples <br /> from boring SB2 did not record EPA 8010 constituents, <br /> including Chloroform and Trichloroethane, above method <br /> detection limits (Table 3). Laboratory data sheets, chain <br /> of custody forms and laboratory quality control data are <br /> presented in Appendix IV. <br /> t <br /> 5.0 CONCLUSIONS <br /> The result of field inspection and laboratory analysis of <br /> soils collected during tank removal and subsequent borings <br /> r drilled within the former tank pits, indicate hydrocarbon <br /> contamination has occurred a a result of leakage of <br /> gasoline product to the subsurface from Tanks A and C. The <br /> := absence of significant contamination in the pit sample from <br /> Tank B and the non-detectable concentrations of EPA 8010 <br /> constituents (including Chloroform and Trichloroethane) in <br /> samples collected from soil boring SB2 indicate no <br /> significant leakage of waste oil occurred at this location. <br /> Primary source coâ–ºztrol has been achieved at the site with <br /> .. . ... . the...removal-.of...--the....three u/g......tanks. .and associated ;}, oduct.. __. ...._. .. <br /> lines. The only other source for continuing contar;'nation <br /> are the soils contaminated by the leakage of gasoline <br /> b product from Tanks A and C. <br /> The elevated concentrations of total petroleum hydrocarbons <br /> recorded in soils to a depth of 30.5 feet beneath Tank A <br /> indicates a significant volume .of gasoline has leaked. The <br /> highest TPH concentration detected .in the 30.5 foot sample, <br /> 4 <br />
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