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ARCHIVED REPORTS_XR0008769
Environmental Health - Public
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WASHINGTON
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3500 - Local Oversight Program
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PR0545834
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ARCHIVED REPORTS_XR0008769
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Last modified
7/15/2020 2:59:09 PM
Creation date
7/15/2020 1:54:16 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008769
RECORD_ID
PR0545834
PE
3528
FACILITY_ID
FA0005104
FACILITY_NAME
ECONO GAS
STREET_NUMBER
4325
Direction
E
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15733708
CURRENT_STATUS
02
SITE_LOCATION
4325 E WASHINGTON ST
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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1 <br /> Page 8 <br /> January 30, 1992 <br /> Job No 400511-SA <br /> Figure 5, Groundwater Gradient Map, is a water table contour map for the site based on the <br /> October 15, 1991 measurements The groundwater gradient is very slight towards the southwest at a 1 <br /> magnitude of approximately 0 0004 foot per foot <br /> 53 Occurrence and Extent of Hydrocarbons m the Soil <br /> Soil samples from each borehole were retained and submitted to the State of Callforn>ia-licensed <br /> laboratory, Trace Analysis Laboratory, Inc (Hayward), for analysis Soil samples were collected for <br /> possible laboratory analysis at 5-foot intervals from the boreholes A total. of 160 soil samples were , <br /> collected On-site field screening, utilizing an organic vapor meter (OVM), helped to determine which <br /> samples were sent to the'laboratory for analysis Approximately every other sample was submitted for , <br /> laboratory analysis as per the work plan The samples were analyzed for TPHg by the DHS method <br /> and BTXE by modified EPA Method 8020 A total of 86 soil samples were analyzed The laboratory <br /> reports are summarized in Table C and are presented in Appendix E Methods followed for on-site <br /> screening are contained Appendix A The OVM readings are presented on the well logs in Appendix B <br /> Hydrocarbon concentrations in sods were generally enerally greatest in the permeable sands that occur between <br /> 40 to 65 feet below grade Vapor extraction well VW-35 had the highest hydrocarbon concentration <br /> in sample 35-10 recovered from a depth of 51 to 515 feet This sample had the highest TPHg <br /> concentration at 1,000 mg/kg Soil samples recovered from the exploratory borings contained variable <br /> concentrations of toluene which ranged, for example, from less than 0 005 mg/kg to 170 mg/kg ' <br /> Benzene occurred at 0 058 mg/kg in sample 30-16 recovered from a depth of 80 5 to 81 feet from MW- <br /> 30 The soil analytical results are summarized in Table C <br /> detected at low levels in almost <br /> Toluene was every soil sample, even where TPHg, benzene, <br /> ethylbenzene, and xylenes were all non detect The toluene detected at low levels is likely to be a <br /> laboratory contaminant A letter from the analytical laboratory stating this probability is included in <br /> Appendix E -Hydrocarbon odor was detected in many soil samples recovered during exploratory drilling <br /> though only a few of these samples had detectable concentrations of TPHg reported by the laboratory ' <br /> This generally occurs with degraded gasoline in soil The odors detected may be from compounds such <br /> as methane which is not generally found in gasoline <br /> Concentrations of TPHg expressed as parts per million (ppm) in the soil are contoured on Cross <br /> Sections A-A' and B-B' in Figures 6 and 7, respectively These figures graphically illustrate the <br /> distribution of petroleum hydrocarbons currently within the soil at the site On Figure 6, TPHg <br /> concentrations are highest in the area of VW-35 at a depth of 50 - 60 feet, and extend laterally to <br /> 4005111_Rev 1 Du Pant Environmental Remediation Services_ <br /> Printed on Recycled Paper ' <br />
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