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ARCHIVED REPORTS_XR0004042
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3500 - Local Oversight Program
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PR0545387
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ARCHIVED REPORTS_XR0004042
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Last modified
3/5/2020 9:09:33 AM
Creation date
3/5/2020 8:22:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004042
RECORD_ID
PR0545387
PE
3528
FACILITY_ID
FA0005718
FACILITY_NAME
SINCLAIR TRUCKING
STREET_NUMBER
3780
Direction
W
STREET_NAME
LINNE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
3780 W LINNE RD
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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Clutogkof Teekn"t". Page 10 <br /> Sinclair Trucking <br /> Project No.: 1030.2 <br /> August 11,2005 <br /> 2.8.3 Soil Sample Results <br /> Below is a summary of the findings for MW-1R installed and sampled on March 11, 2005: <br /> • 7 ft: Non-detect above laboratory reporting limits for all analyzed constituents. <br /> ' • 10 ft: Trace levels of benzene were detected. The sample from this depth was non- <br /> detect above laboratory reporting limits for all other analyzed constituents. <br /> ' • 12 ft: Low levels of ethylbenzene, total xylenes and TPH-G were detected. The <br /> sample from this depth was non-detect above laboratory reporting limits for all other <br /> analyzed constituents. <br /> ' 2.8.4 Monitoring Well Survey <br /> On June 23, 2005, GTI and Thompson-Hysell Engineering (Licensed Land Surveyor #6953) <br /> ' personnel arrived on-site to survey the new monitoring well (MW-1R) as required under and <br /> in accordance with the guidelines outlined in AB-2886. The surveyors report is attached as <br /> Appendix E. <br /> ' The location (xy) data and elevation (z) data were submitted to GeoTracker on August 4, <br /> 2005. Confirmation numbers are 5363050699 and 2905349552, respectively. <br /> ' 3.0 CONTAMINANT MASS ESTIMATE CALCULATIONS <br /> Original mass balance calculations, discussed in GTI's: Initial Site Conceptual Model dated <br /> June 18, 2003, indicated as much as 3,400 pounds of TPH-G is bound to the soil at the <br /> ' Sinclair site. Mass estimate calculations generated after the soil excavation activities suggest <br /> there is approximately 748 pounds of TPH-G remaining in the soil. The calculations suggest <br /> that the excavation activities removed approximately 80% of the soil contamination. The <br /> ' mass balance calculations are summarized in Table 4 of Appendix A. <br /> The following summarizes the data and assumptions used in the mass balance estimates: <br /> ' • Figure 5 shows contours of TPH-G concentrations generated using soil data gathered <br /> from sidewall soil samples and new well installation soil samples. The contours were <br /> generated by importing analytical results from the sidewall and well installation soil <br /> ' samples into Surfer 7.00 contour generating software. Bold lines indicate the separation <br /> of the two selected zones; the core and the ring. <br /> • The heaviest contamination is found in an area of approximately 300-ft2 near the former <br /> ' UST. This 300-ft2 area is called the core and an average concentration of 1,250 mg/Kg <br /> was used to calculate the mass in the core. <br /> • The area between the non-detect and the 800 mg/Kg contours is approximately 3,000-ft2 <br /> and is called the ring. The largest portion of the ring lies between the.non-detect and the <br /> Z g000— 200 mg/Kg contour lines. To be conservative'250�g/Kg was used to calculate the mass <br /> in the ring. <br /> • The thickness of the TPH-G contamination is assumed to be 7-feet, primarily occupying <br /> the depths between 7 and 14 feet bgs. Groundwater depth at the time of this work was <br /> 1 <br />
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