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2900 - Site Mitigation Program
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PR0541913
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WORK PLANS
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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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EHD - Public
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Work Plan <br /> Frontier Transportation <br /> July 23, 2001 <br /> 5.0) SOIL EXCAVATION <br /> 1 The extent of area to be excavated will encompass borings 13-2, B-6, and monitoring well <br /> MW-3 (See Figure 4 for Extent of Excavation) . The pit will be excavated to approximately 30- <br /> -� feet by 25-feet by 10 feet deep only, the depth to groundwater. The SJCPHS-EHD <br /> recommended excavation below groundwater; however, this may compromise the integrity of <br /> the nearby shop structure. If concentrations are detected over 50 ppm with a photoionization <br /> (PID), then soil will be considered impacted. Petroleum impacted soil will be stockpiled on-site <br /> on visqueen and covered with visqueen for proper disposal under manifest or on-site treatment, <br /> depending on the soil analysis concentrations . An additional work plan will be provided to the <br /> SJCPHS-EHD describing in detail the method in which the soil will be treated on-site or <br /> disposed under manifest. <br /> Upon completion of excavation, a total of four soil samples will be collected from the <br /> J north, south, east, and west pit bottom at approximately 10 ' bg (See Figure 4). In addition, a <br /> total of ten soil samples will be collected from the stockpiled soil . Soil samples will be collected <br /> i in 2-inch by 6-inch brass tubes, scaled with Teflon tape and capped for transport in an ice chest <br /> with ice under chain of custody to a certified California Department of Health Services <br /> laboratory. Soil samples will be analyzed for TPH-gas, BTEX and MTBE, using EPA methods <br /> 8015 modified and 8020. Should MTBE be identified, then MTBE concentrations will be <br /> quantified using EPA method 8260. <br /> 6.0) 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 104nch outside diameter and 6-inch inside diameter (See Figure 4 <br /> for well location) . <br /> —I Each well will basically consist of a central section composed of riser and screen. The <br /> riser and screen will be constructed of four-inch inside diameter, schedule 40 polyvinyl chloride <br /> I <br /> (PVC) pipe. The proposed well will consist of slotted PVC extend from approximately 30 ' bg to <br /> 40 ' bg and it will contain three rows of 0.010-inch slots. The annular space around the screen <br /> -- will be filled with sand from 25 ' bg to 40 ' bg to from a filter pack. This will be overlain with a <br /> 5' seal of bentonite pellets, then grouted to near ground surface with a 5% bentonite mixture with <br /> cement and water. The replacement well for MW-3 will be slotted from 5 ' bg to 20 'bg and will <br /> also contain three rows of 0.0104nch slots. The filter pack will extend from 5 ' bg to 20 ' bg. <br /> This will be overlain with a 3 ' seal of bentonite pellets, then grouted to near ground surface with <br /> a 5% bentonite mixture with cement and water (See Figure 5, Well Construction Diagram) . <br /> Ends of the screen and riser sections will be constructed with flush joining threaded fittings to <br /> ensure leak-proof unions. <br /> 3 <br /> ILl <br />
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