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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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EHD - Public
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Frontier Transportation B2350101A <br /> January 2, 1996 Page 7 <br /> (C57 Contractors License No. 506159) under the supervision of a Twining geologist. Soil <br /> samples will be collected in the boreholes drilled for the monitoring wells at 5-foot intervals <br /> commencing at a depth of 10 feet BSG. Soil samples will be observed in the field for the <br /> purpose of developing lithological logs and screened for evidence of PPCs with a <br /> photoionization detector (PID) consistent with our SOPS. Soil samples will be retained for <br /> chemical analysis only if field screening indicates the possible presence of PPCs in soils <br /> originating from the monitoring well boreholes. <br /> General practice requires that boreholes for groundwater monitoring well installation shall <br /> not pass through impacted soil into the groundwater surface. Therefore, during the drilling <br /> of the boreholes, should evidence of PPCs be encountered, drilling will be terminated and <br /> the borehole backfilled. A new location for the monitoring well will then be chosen further <br /> from the presumed source of the PPCs. <br /> The final depth of the soil borings will be determined by the depth at which groundwater <br /> is encountered. The boreholes will be advanced until they are approximately 15 feet below <br /> the groundwater surface. For the purposes of this work plan, the final depth of the <br /> boreholes for the groundwater monitoring wells is presumed to be approximately 35 feet <br /> BSG. <br /> The monitoring wells will be constructed of 24nch diameter schedule 40 PVC casing and <br /> screened over the bottom 20 feet of the well. Consistent with our SOPS, the well filter pack <br /> material consisting of appropriately-sized pre-washed sand will be placed in the annulus <br /> between the boring wall, from the bottom of the boring to approximately 2 feet abovethe <br /> top of the screen. After filter pack emplacement, preliminary development may be <br /> performed to provide a uniform filter pack about the casing. Above the filter pack, a 3- to <br /> 4-foot thick bentonite seal will be installed. The remainder of the well annulus is sealed <br /> with a 6-sack sand-cement, or cement grout slurry in one continuous operation from the <br /> bottom of the interval to be filled to the top. The grout will be emplaced through the <br /> hollow augers, which will extend to within 10 feet of the bentonite seal. The augers will be <br /> withdrawn from the boring in 10400t increments as the boring fills with grout. A <br /> monitoring well construction (proposed) schematic for the monitoring wells is presented as <br /> Drawing 5. <br /> A minimum of 48 hours after installation, the monitoring wells will be developed consistent <br /> with our SOPS to remove excess sediment and to settle the filter pack. Development will <br /> continue until the purged water is relatively sediment free, and measured field parameters <br /> (pH, electrical conductivity, and temperature) have stabilized. <br /> 4. 1.3 Level Survey: Following installation, the monitoring wells will be surveyed consistent <br /> with our SOPs to determine ground surface/wellhead elevations and locations. The survey <br /> data collected during this phase will be referenced to a United States Geological Survey <br />
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