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ARCHIVED REPORTS_XR0002658
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545259
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ARCHIVED REPORTS_XR0002658
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Last modified
1/31/2020 5:06:46 PM
Creation date
1/31/2020 3:15:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002658
RECORD_ID
PR0545259
PE
3528
FACILITY_ID
FA0004966
FACILITY_NAME
CHEVRON USA (INACT)
STREET_NUMBER
45
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12707037
CURRENT_STATUS
02
SITE_LOCATION
45 E HARDING WAY
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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r <br /> November 12, 1996 <br /> Page 7 <br /> 0calculate the volume and estimate average conceirtration of the remaining soil contaml- <br /> nation is also presented in Attachment A <br /> RESIDUAL PETROLEUM HYDROCARBONS IN SOIL <br /> Currently, residual petroleum hydrocarbons in soil occur below and northeast of the <br /> former UST cluster (installed in 1980 and adjacent product island The vertical and <br /> lateral extent of petroleum hydrocarbons in soil are shown on Figures 6 through 8 <br /> These hydrocarbon-affected soils occur in what can be described as two localized verti- <br /> cal soli columns Hydrocarbon-impacted soils in these two vertical soil columns occur <br /> from a depth of approximately 15 to 50 feet bgs The horizontal extent of hydrocarbon- <br /> affected soils within these soil columns occur primarily within a range of 5 to 10 feet, <br /> with occasional thin zones that extend horizontally an additional 10 feet from the soil <br /> column These soil columns occur within vadose zone soils, soils within the capillary <br /> fringe and zone of groundwater fluctuation, and currently saturated soils Figures 6 <br /> through 8 depict these conditions and show soilanalytical data from soil borings and <br /> wells drilled after the operation of the SVE system <br /> The location of the residual hydrocarbons in soils are characterized by soil borings <br /> located in two areas These include Soil Borings SB-2 and SB-12 located in the north- <br /> ern portion of the UST complex and Borings SB-3 and SB-13 located adjacent to the <br /> western product island Hydrocarbons in these two areas are well defined and appear to <br /> be isolated based on data collected from several borings as shown on the geologic cross- <br /> sections (Figures 7 and 8) <br /> The concentration of the residual hydrocarbons in soils are characterized by the presence <br /> of the relatively high molecular weight compounds TPPH-g concentrations range in <br /> concentration from less than 10 to 10,000 ppm Benzene with few exceptions has not <br /> been detected The remaining elevated concentrations of TPPH-g tend to reside in rela- <br /> tively tight soils consisting of sandy to clayey silt, or silty sandy clay <br /> RESIDUAL PETROLEUM HYDROCARBONS IN GROUNDWATER <br /> Quarterly groundwater monitoring was initiated in November 1988 Dissolved hydro- <br /> carbon concentrations in groundwater samples collected from Well MW-9, located in the TYewt f k7 <br /> source area, have generally decreased with the overall increase in groundwater elevation M V <br /> This trend indicates that SVE was effective in remediating hydrocarbon-affected soils in iidkLAA r <br /> the source area Furthermore, during 1996, groundwater elevations in site monitoring of b�T <br /> wells have risen allowing collection of groundwater samples from wells which were <br /> previously dry (Wells MW-1, and MW-3 through MW-8) Third quarter groundwater <br /> monitoring (July 30, 1996, Attachment D) indicates the maximum residual concentration <br /> of TPPH-g in groundwater to be'310 ppb (Well MW-4) The maximum residual <br /> 3201337B1CL0S1 RE2 <br /> t <br /> r <br />
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