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ARCHIVED REPORTS_XR0004481
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2900 - Site Mitigation Program
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PR0541913
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ARCHIVED REPORTS_XR0004481
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Last modified
2/13/2020 4:21:36 PM
Creation date
2/13/2020 1:52:24 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004481
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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I2004 2nd Quarter Groundwater Report <br /> iFrontier Transportation <br />' August 9, 2004 <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 Groundwater <br />' samples were subsequently collected and 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' bgs <br /> Maximum soil vapor concentrations were identified at sample point V5 at 4' bgs Groundwater <br />' samples were subsequently collected from all monitoring wells Results are tabulated in Table 1 <br /> In May 2002, BEII installed two additional groundwater monitoring wells (MW-12 and <br />' MW-13) screened from 30' bgs to 40' bgs Soil sample results identified maximum TPH-g, <br /> BTEX, and MTBE concentrations of 700 mg/kg, 115,000 µg/kg, and 25,000 µg/kg in soil <br /> collected from MW-13 at 10' bgs Soil concentrations attenuate by 99% at 15' bgs No <br /> 1 detectable TPH-g, BTEX, and MTBE were identified in MW-12 Also, monitoring well MW-3 <br /> was abandoned prior to excavation and removal of 325 tons of impacted soil and replaced by <br />' MW-3R <br /> In June 2003, BEII installed an additional groundwater monitoring well (MW-14) <br />' screened from 30' bgs to 40' bgs Soil sample results identified a maximum MTBE <br /> concentration of 1,020 gg/kg at 10' bgs using EPA Method 8260B No detectable TPH-g and <br /> BTEX were identified in MW-l�4� 1n41 zed�"�"OF ho/40/1" <br /> y i 9�y9,o <br />' In January 2004, BEII installed four additional groundwater monitoring wells Deep <br /> monitoring wells MW-15, MW-16 and MW-18 were advanced to 40' bgs and screened from 30' <br />' bgs to 40' bgs Shallow monitoring well MW-17 was advanced to 20' bgs and screened from 5' <br /> bgs to 20' bgs Soil sample results identified a maximum MTBE concentration of 1,310 gg/kg at <br /> 10' bgs in MW-15 using EPA Method 8260B No other oxygenates or lead scavengers were <br />' detected The maximum TPH-gas detected was 17 mg/kg at 10' bgs in MW-15 using EPA <br /> Method 8015M No detectable BTEX was identified in the soil column for MW-15 through <br /> MW-18 See Figure 2 for well locations <br />' 3.0 SITE GEOLOGY/HYDROGEOLOGY <br />' The site is located on the boundary of the Sacramento Valley and the San Joaquin Valley <br /> 1 <br /> I <br />
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