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ARCHIVED REPORTS XR0009996
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544800
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ARCHIVED REPORTS XR0009996
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Entry Properties
Last modified
11/19/2024 10:19:02 AM
Creation date
9/4/2019 10:24:38 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009996
RECORD_ID
PR0544800
PE
3528
FACILITY_ID
FA0010235
FACILITY_NAME
AMERICAN TRUCK & TRAILER BODY CO
STREET_NUMBER
7474
Direction
W
STREET_NAME
ELEVENTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
25020001
CURRENT_STATUS
02
SITE_LOCATION
7474 W ELEVENTH ST
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\wng
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EHD - Public
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Ceo(agicaCTec(inics Znc. <br /> C&B Equipment Page 3 <br /> Site Closure Check List <br /> Project No.336.2 <br /> August 31, 1998 <br /> A <br /> The calculations were prepared as follows: <br /> • The contamination was assumed to extend from four feet below ground surface (bgs) <br /> down to 12 feet bgs in center core, field notes indicate a significant decrease in soil <br /> contamination between 10 and 15 feet bgs in MW-101. <br /> • The contaminant load in the center core was assumes to equal the TPH-G concentration <br /> s from the 5 foot sample in MW-101 (2880 mg/Kg). This most likely results in an over <br /> estimation of contaminant mass in the soil. <br /> -� • Because TPH-G was non-detect in the deeper soil samples, the TPH-G contaminant <br /> >I loading for the ring was assumed to equal the detection limit of TPH-G(1.0 mg/L). <br /> • The volume of the core is subtracted from the volume of the ring. <br /> • The volume of soil is multiplied by the density of the soil (lbs/ft') then by 0.4536 to <br /> :. convert from pounds of soil to kilograms of soil. The contaminant load is then multiplied <br /> to this number to give the mass of contaminant in milligrams. The contaminant mass in <br /> milligrams is then converted to kilograms which is the contaminant mass value one is <br /> -1 after. <br /> ,__ • The inner groundwater plume was assumed to extend from 6 feet bgs to 15 feet bgs. <br /> There is no data to support this, however the soil in this region is highly contaminated so <br /> it would be expected that the shallow groundwater in this area would also be impacted to <br /> a greater extent. <br /> • The contaminant load for the inner groundwater plume was assumed to equal 100 mg/L, a <br /> value much higher then has ever been observed at this site. <br /> -:-.� • The outer groundwater plume was assumed to extend from 6 feet bgs. to 45 feet bgs, 5 <br /> Fj feet deeper then the deepest depth explored. <br /> • The TPH-G contaminant load for the outer groundwater plume was assumed to be the <br /> average of the twogroundwater samples from MW-101 (0.5 mg/L). <br /> + The volume of groundwater in the inner plume was subtracted from the volume of the <br /> outer plume. <br /> 14. Model Parameters <br /> Risk evaluation and fate and transport modeling have not been performed. The data suggests <br /> !==1 that this site is low risk so this level of investigation is not needed. <br /> 15. Rationale <br /> For the following reasons, the conditions at this site should not adversely impact water <br /> quality, health or beneficial use of this property. <br /> + The tank and primary soil contamination source have been removed. Residual <br /> gasoline is present as estimated below. <br /> • Groundwater monitoring results show that the contaminants in the groundwater <br /> plume have reduced significantly over the past three years. <br /> • The estimated mass of contaminants is very small, with only approximately 502 <br /> gallons in the soil, most of this is in the top ten feet, and 6 gallons in the groundwater. <br /> , I <br /> -_JI <br />
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