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ARCHIVED REPORTS_XR0011910
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0540573
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ARCHIVED REPORTS_XR0011910
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Last modified
4/9/2020 2:35:38 PM
Creation date
4/8/2020 4:21:16 PM
Metadata
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011910
RECORD_ID
PR0540573
PE
2960
FACILITY_ID
FA0023207
FACILITY_NAME
GILLIES TRUCKING INC
STREET_NUMBER
3931
STREET_NAME
NEWTON
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
13207017
CURRENT_STATUS
01
SITE_LOCATION
3931 NEWTON RD
P_LOCATION
01
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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• were re-sampled on October 6 The Gillies domestic*ell was also sampled on October 6 Sample <br /> G-1 A was collected from the sample port on the top of the well pump, and sample G-1 B was <br /> collected from the valve on the storage tank All eight of the samples were analyzed for TPH-diesel <br /> and TPH-gasoline by EPA method 602 and for BTEX and MTBE by method 8020 <br /> 3.0 RESULTS <br /> 3.1 Groundwater Gradient and Flow Direction <br /> Depth-to-groundwater measurements and calculated groundwater elevations are presented in Table <br /> 1 Results from previous momtoring events are included for comparison <br /> The static water level is approximately 8 feet deeper than it was in June of this year, and now <br /> averages approximately 55 feet in depth Hence, it has now dropped below the base of the Modesto <br /> Aquifer and is present within the low-permeability silt bed that constitutes the Modesto Aquitard In <br /> some of the bonngs, this is the interval in which the highest concentrations of contaminants were <br /> detected (e g GT-3, GT-7, GT-10, GT-11) The present elevation (relative to sea level) is almost <br /> minus 28 feet <br /> The calculated water table elevations were used to construct the groundwater gradient map in <br /> Figure 3 The gradient is now much less steep than it was in June, when it appeared to slope rather <br /> • strongly to the northwest or north At this time, the gradient is flat, with no apparent flow direction <br /> Less than 0 5 inches separates the highest elevation from the lowest elevation of the static water <br /> level <br /> 3.2 Laboratory Results <br /> Significant changes in contaminant concentrations also occurred during the third quarter (Table 2) <br /> Diesel concentrations again decreased markedly in GT-10, but increased significantly in GT-1 and <br /> GT-2 In addition, diesel was detected in GT-6 for the first time since December of 1997 Diesel <br /> was not detected in the samples that were collected from the domestic well tank in July or October, <br /> but it was detected in the sample that was collected from the well in October, apparently confirming <br /> the June result from the water faucet outside the men's bathroom <br /> Gasoline was detected in four of the eight samples collected in October Gasoline was detected <br /> right at the reporting limit in GT-6, it had not been previously detected in this well Concentrations <br /> in the other wells were generally within the ranges of concentrations that had previously been <br /> detected in these wells <br /> Benzene and the other aromatic compounds were again detected in GT-10, at concentrations that <br /> are still low but are higher than any previously detected in this well Some of these analytes were <br /> also detected in GT-1, GT-2, GT-3, and GT-6, even though the static water level is still more than <br /> 25 feet above the screened interval in most of these wells Even more surprising, MTBE was <br /> • detected at a concentration of 100 ppb in GT-6 This sample was not re-run using EPA method <br /> z <br />
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