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2900 - Site Mitigation Program
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PR0541913
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Last modified
2/13/2020 7:07:47 PM
Creation date
2/13/2020 11:53:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
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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i <br /> Work Plan <br /> Frontier Transportation <br /> Page 2 <br /> through MW-7) to assess the extent of subsurface contamination beneath the site (See Figure 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 from 5 ' bg to 25 ' <br /> bg. Groundwater samples were subsequently collected. Results are tabulated in Table 1 . <br /> In January 2000, BEII advanced two borings (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 µg/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 /> - On May 17, 2002, BEII supervised the well abandonment of MW-3 in order to perform <br /> excavation in that area. From May 20 through 24, BEII excavated a total of 325 tons of soil near <br /> the former UST area. The excavation pit measured 30 feet by 30 feet by 15 feet deep. The soil <br /> e ,I consisted of heterogeneous clays with some fine-grained silty sand stringers at groundwater <br /> depth. Groundwater was encountered in the silty sand at approximately 13 ' bg. The excavation <br /> pit was terminated at 15 ' bg to avoid collapsing of the pit from the entry of silty sand and <br /> groundwater. Soil sample results identified the highest concentrations below the encountered <br /> - - - groundwater. <br /> 1 On May 30 and 31 , 2002, BEII supervised the installation of one replacement <br /> groundwater monitoring well (MW-3R) and two deeper groundwater monitoring wells (MW- 12 <br /> and MW-13) to help define the extent of dissolved petroleum hydrocarbons beneath the site (See <br /> Figure 2 for well locations). Monitoring well MW-3R was advanced to 20 ' bg while MW- 12 <br /> - and MW43 were advanced to 40 ' bg. See Table l for groundwater results. <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 /> p, 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 /> L October 16, 1996). BEII encountered clay and a heterogeneous mix of clay from 0' to 25' bg in <br /> January of 1998. <br /> F , <br /> W , <br /> First subsurface water was encountered at depths from I P to 12' bg during tank removal <br /> _ ! ) and monitoring well installation at this site in 1995 and 1996. Since then, shallow subsurface <br /> f <br /> i <br /> 2 <br /> �J <br />
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