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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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Frontier Transportation, Inc. <br /> Well Installation Work Plan <br /> r j November 14, 2006 <br /> Page 4 <br /> MW-5, MW- 10 and MW- 11 identified no detectable MTBE along the south of the property. <br /> Monitoring wells MW-6 and MW-7 demonstrate that the MTBE plume has not migrated to the <br /> east. The recent laboratory analytical results presented in Table 1 and in Appendix A. f <br /> ij <br /> However, there are currently no wells along the northern or western edges of the plume to <br /> delineate the extent of the MTBE plume. Currently the westernmost wells (MW-9, MW-20 and <br /> MW-4) demonstrate dissolved MTBE between 377 ug/L and 928 ug/L.- The northernmost wells <br /> (MW-2 and MW-8) identified dissolved MTBE at 1 ,380 ug/L and 2, 150 ug/L, respectively: It is, <br /> therefore, proposed that additional shallow wells be installed; one well (MW-24) should be <br /> placed proximately 50 feet west of MW-9 and another well (MW-25) should be placed 50 feet <br /> north�o <br /> 4W4. The proposed locations of these two wells are based upon elevated <br /> concentrations of MTBE in the westernmost wells at the site. Groundwater samples from these <br /> two locations will provide information regarding MTBE plume migration. See Figure 2 for <br /> proposed well locations. <br /> It may also be beneficial to install a third monitoring well north of MW-2 so that the <br /> northeastern edge of the plume can be monitored. The location of proposed monitoring well <br /> 41 <br /> MW-26 is approximately 70' north of MW-2. Sampling at this location would provide further <br /> MTBE plume delineation. <br /> j Each well will be advanced to a total depth of 20' below grade surface (bgs) with the <br /> screen interval between 5 ' bgs and 20' bgs. (See Figure 2 for proposed well location). The <br /> analytical data from the soil and groundwater samples at the new shallow wells will be <br /> C I significant in determining the boundary of the contaminant plume. <br /> _ 5.0) GROUNDWATER WELL INSTALLATION <br /> A hollow stem auger drill rig will be used to provide the soil borings for well installation. <br /> Drillers will hold a California State C-57 contractor's license. Typical auger size for the well <br /> installation described below is 84nch outside diameter and 6-inch inside diameter. The borings <br /> for shallow well installation will be advanced to 20' bgs. <br /> i` Each well will consist of a central section composed of riser and screen. The <br /> riser and screen will be constructed of two-inch inside diameter, schedule 40 polyvinyl chloride <br /> (PVC) pipe. The proposed shallow wells will consist of slotted PVCextendfrom approximately <br /> 20 ' bgs to 5' bgs and it will contain three rows of 0 . 010-inch slots. The annular space around the <br /> screen will be filled with an appropriate grain size of sand from, 20' bgs to 4.5' bgs to form a <br /> filter pack. This will be overlain with a 1' seal of bentonite pellets, then grouted to near ground <br /> j surface with a 5% bentonite mixture with cement and water. Ends of the screen and riser <br /> I, I <br />
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