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ARCHIVED REPORTS_XR0004474
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2900 - Site Mitigation Program
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PR0541913
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ARCHIVED REPORTS_XR0004474
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Last modified
2/13/2020 5:57:50 PM
Creation date
2/13/2020 1:47:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004474
RECORD_ID
PR0541913
PE
2960
FACILITY_ID
FA0024043
FACILITY_NAME
FRONTIER TRANSPORTATION FACILITY
STREET_NUMBER
425
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21220009
CURRENT_STATUS
01
SITE_LOCATION
425 LARCH RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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' 2003 1st Quarter Groundwater Report <br /> SFrontier Transportation <br />' June 4, 2003 <br /> Page 2 <br />' Site Layout Map) Soil samples were collected every five feet Laboratory analysis of soil <br /> samples identified no detectable concentrations of TPH-g, BTEX, or MTBE Groundwater <br /> samples were subsequently collected and results are tabulated in Table 1 <br />' In January 2000, BEH advanced two bonngs (B-5 and B-6), installed four additional <br /> groundwater monitoring wells (MW-8 through MW-11), and collected nine soil vapor samples <br />' for a soil vapor survey as part of an additional site assessment (See Figure 2, Site Layout Map for <br /> well locations) Soil sample analysis identified no detectable concentrations of petroleum <br /> hydrocarbons with the exception of boring B-6 Maximum contaminant levels in B-6 were <br />' identified 100 mg/kg as TPH-g, 2,343 gg/kg as BTEX, and 10,600 µg/kg as MTBE at 10' bg <br /> Maximum soil vapor concentrations were identified at sample point V5 at 4' bg Groundwater <br /> samples were subsequently collected from all monitoring wells Results are tabulated in Table 1 <br /> IIn May 2002, BEH installed two additional groundwater monitoring wells (MW-12 and <br /> MW-13) screened from 30' bg to 40' bg Soil sample results identified maximum TPH-g, <br />' BTEX, and MTBE concentrations of 700 mg/kg, 115,000 gg/kg, and 25,000 gg/kg in soil <br /> collected from MW-13 at 10' bg Soil concentrations attenuate by 99% at 15' bg No detectable <br />'• TPH-g, BTEX, and MTBE were identified in MW-12 Also, monitoring well MW-3 was <br /> abandoned prior to excavation and removal of 325 tons of impacted soil and replaced by MW- <br /> 3R <br />' 3.0) SITE GEOLOGYIHYDROGEOLOGY <br /> The site is located on the boundary of the Sacramento Valley and the San Joaquin Valley <br />' within the west-central portion of the Great Valley Geomorphic province of California The <br /> Great Valley has been filled with a sequence of older to younger alluvium of Pliocene to <br />' Holocene age which overlay sedimentary rocks of Cretaceous to Tertiary age These sedimentary <br /> units, in turn, overlay a crystalline basement of Paleozoic and Mesozoic metamorphic and <br /> igneous rocks The shallow subsurface geology in the site vicinity is a heterogeneous mix of <br />' gravel, sand, silt, and clay(Reference, Site Characterization Report, Twining Laboratories, <br /> October 16, 1996) BEH encountered predominantly clays with traces of interbedded sands from - <br /> 0' to 25'bg during well advancement in January of 1998 — T <br /> First subsurface water was encountered at depths from 11' to 12'bg during tank removal <br /> and monitoring well installation at this site in 1995 and 1996 Since then, shallow subsurface <br />' water has been encountered beneath the site between C and 10'bg Data collected in Apnl of <br /> 2003 identified the flow of groundwater in a generally western direction beneath the site (See <br /> Figure 3, Groundwater Gradient Map) Monitoring well WM 31 w sa installed within the -- <br />' excavation backfill material, which was coarser than the native soil The permeability difference <br /> 1 <br /> 1 <br />
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