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ARCHIVED REPORTS_XR0011916
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0540573
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ARCHIVED REPORTS_XR0011916
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Last modified
4/9/2020 2:38:04 PM
Creation date
4/9/2020 2:21:50 PM
Metadata
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011916
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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EHD - Public
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The depth to groundwater in the Riverbank Formation had been monitored in GT-1, GT-2, and GT-3 <br />. on seven occasions prior to the current drilling phase (Table 1) These data were used to map the <br /> piezometric surface and determine the groundwater gradient and flow direction In all but one instance, <br /> flow appeared to be southward <br /> As described in section 3 3 1, a southward gradient was confirmed when GT-5 and GT-6 were drilled <br /> in August, 1996 However, the gradient of 0 011 ft/ft was more than twice as steep as previously <br /> calculated when only three wells were available for measurement, implying that groundwater flow is <br /> more rapid than was assumed <br /> Groundwater monitoring after GT-9 was drilled in October further complicates the interpretation of the <br /> groundwater flow direction (Figure 9) Although the southward gradient from GT-5 toward GT-3 is <br /> confirmed, the gradient does not continue in this direction from GT-3 to GT-9 The elevation of the <br /> piezometric surface in GT-9 is 0 04 R higher than would be expected if the southward gradient <br /> continued This is a small amount, but it forces the conclusion that the flow direction turns sharply from <br /> south to southwestward near the Gillies-Barbot property line, creating a narrow trough in the surface <br /> of the water table This probably indicates that water flow is deflected along a high-permeability axis <br /> within the Riverbank aquifer between GT-3 and GT-9 <br /> 4.4 Soil Chemistry and Bacterial Activity <br /> In response to a request from PHS/E D, several soil samples were submitted for analysis of their <br /> ability to support natural biodegradation of the contaminants Samples were analyzed for bulk density, <br /> moisture content, Total Organic Carbon (TOC), nitrate, phosphate, potassium, Ph, and bacterial <br /> abundance Laboratory reports for these analyses are included in Appendix E The results are discussed <br /> briefly below <br /> As shown in Table 2, the samples that were analyzed for hydraulic conductivity were also analyzed for <br /> bulk density and moisture content, parameters that may be used in the future if a nsk assessment is <br /> performed Density ranges from 86 to 108 pounds per cubic foot Density is not related to gram size or <br /> moisture content Except for GT-4-45', (which was collected at the top of the saturated zone), all have <br /> sufficient moisture to sustain bacterial growth <br /> Two samples from the Modesto aquifer in GT4 were analyzed for TOC Both samples came from the <br /> lower part of the aquifer, where high diesel concentrations are present, and both samples yielded <br /> significant TOC values (Table 3) Samples from uncontaminated zones have TOC concentrations that <br /> range from less than 50 mg/kg to at least 170 mg/kg <br /> Two samples were submitted for analysis of the bacterial nutrients (nitrate, phosphate, and potassium) <br /> and Ph One sample was from the silt bed in the middle of the Modesto Formation (GT-8-30'), and <br /> one was from the upper part of the Riverbank Formation (GT-5-65') Nutrient concentrations in both <br /> samples are quite low, below what would be considered sufficient for healthy plant growth (Table 3) <br /> Both samples are slightly alkaline, with Ph values above 7 0 <br /> 9 <br />
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