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WORK PLANS FILE 1
Environmental Health - Public
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0544513
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WORK PLANS FILE 1
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Entry Properties
Last modified
5/31/2019 4:42:10 PM
Creation date
5/31/2019 4:38:19 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 1
RECORD_ID
PR0544513
PE
3528
FACILITY_ID
FA0024115
FACILITY_NAME
WEST CLAY PROPERTY
STREET_NUMBER
639
Direction
W
STREET_NAME
CLAY
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14707110
CURRENT_STATUS
02
SITE_LOCATION
639 W CLAY ST
P_LOCATION
01
QC Status
Approved
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Site Background Information: West Clay Properties <br /> Page 8 of 10 <br /> SITE CONCEPTUAL MODEL <br /> The model presented is interpretational and will be modified as more data is collected. Depths are <br /> approximate can vary by several feet across the site. Hydrogeologic units are depicted in cross <br /> onal views A- '. ased on the data developed to date, including all soil borings, monitoring <br /> soundings, AGE has developed a site subsurface model for the release, <br /> migration and distribution of the varying contaminants in the subsurface as described below: <br /> • The subsurface from site grade to approximately 170 feet bsg is composed primarily of fine- <br /> grained soil with a coarse-grained interval of variable thickness and lateral distribution.The <br /> major coarse-grained sand intervals occurring between 30 and 40 feet below surface grade <br /> (bsg), a laterally continuous coarse-grained sand interval at approximately 75 feet to 80 feet <br /> bsg and again at a depth 100 feet bsg and a deep laterally continuous coarse-grained sand <br /> interval at approximately 180 feet bsg.A laterally discontinuous sand unit extends from 135 <br /> feet to 140 feet bsg in the UST No. 3 area. The remaining stratigraphy of the site is <br /> comprised of silt with clay inter-channel fill areas. A laterally continuous clay is present at <br /> 65 feet to 70 feet bsg across most of the UST No. 3 area. These characteristics allowed <br /> construction of a site hydrogeologic model as described above with the water table near <br /> approximately 20 feet bsg. <br /> Southern UST Area <br /> • A release of petroleum hydrocarbons(TPH-g,TPH-d)and benzene,toluene,ethyl benzene <br /> and xylene (BTEX) compounds with low concentrations of 1,2-DCA occurred from <br /> dispenser line releases near the northern excavation (UST No. 3 area). The southern UST <br /> removal samples were non-detected for chemicals of concern. Additionally, shallow soil <br /> samples collected near well MW-2,MW-7 were non-detect for chemicals of concern.TPH-g <br /> was reported at a concentration as great as 2,100 mg/kg in the soil sample collected from the <br /> northern UST removal samples; TPH-g was also reported at 320 mg/kg in a soil sample <br /> collected at 20 feet bsg in boring B10. The highest TPH-g and BTEX impact to soil in the <br /> upper vadose zone was removed through excavation at the UST No. 3 area; it does not <br /> appear that any residual vadose zone hydrocarbons are present in this area.The aerial extent <br /> of the soil contamination in soil appears defined to the near the former UST No. 3 area. <br /> • Available data is suggestive of a release was most significant at the northern edge of the <br /> former UST No. 3 area. Once the petroleum hydrocarbons were released to the subsurface, <br /> the contaminants migrated north under well MW-7 and vertically to a depth of <br /> approximately 60 feet bsg near well MW-2.The"deep"migration of hydrocarbons indicates <br /> a historically depressed water table depth of near 35 feet bsg. <br /> • Based on ten years of ground water monitoring for TPH-g and BTEX compounds near the <br /> UST No. 3 area,the impacts to ground water appear to be stable in the areas of wells MW-1, <br /> Advanced GeoEnvironmentai,Inc. <br />
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