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2900 - Site Mitigation Program
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PR0506509
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Last modified
6/1/2020 12:17:28 PM
Creation date
6/1/2020 12:15:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0506509
PE
2960
FACILITY_ID
FA0007466
FACILITY_NAME
GEORGIA PACIFIC CORP (FORMER)
STREET_NUMBER
75
Direction
W
STREET_NAME
VALPICO
STREET_TYPE
RD
City
TRACY
Zip
95336
APN
24613007
CURRENT_STATUS
01
SITE_LOCATION
75 W VALPICO RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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BOREHOLE DRILLING, WELL CONSTRUCTION, DEVELOPMENT <br /> AND SAMPLING PROCEDURES <br /> Borehole Drilling and Sampling <br /> Boreholes will be drilled by a California licensed water well driller, using a truck-mounted <br /> drilling rig equipped with nominal 8- or 10-inch outside-diameter hollow-stem augers. Prior to <br /> drilling, each borehole location will be hand augered to a depth of approximately 5 feet below <br /> ground surface to check for underground utilities. Soil samples will be collected for lithologic <br /> determination by continuous coring the boring or sampling at 5-foot intervals during the drilling <br /> process. Samples will be collected to the total depth of the boring. Borehole depths will be based <br /> on site conditions, including but not limited to depth to water, topography, and depth to bedrock. <br /> Soil cuttings generated during the drilling procedures will be placed on visqueen and covered with <br /> visqueen at the end of the day, or placed in steel 55-gallon drums. At the end of the drilling and <br /> sampling operations, each borehole will be completed as a groundwater monitoring well. <br /> Soil samples will be collected throughout the investigation for Gthologic classification and <br /> chemical analysis. One boring will be continuously cored to total depth and the remaining borings <br /> will be sampled at five foot intervals using a California modified split-spoon sampling device. The <br /> soil core and discrete samples will be examined in the field and classified according the Unified Soil <br /> Classification System. In addition, the soil core and samples will also be screened in the field with a <br /> photoionization detector (PID), or similar instrument, for the presence of volatile organic <br /> compounds (VOCs). The relative permeability of the soil will be qualitatively estimated, and the <br /> Ethology, PID reading, and estimated permeability of each sample interval will be recorded on the <br /> borehole log next to the depth interval from which the sample was obtained. <br /> Soil samples for potential laboratory chemical analysis will be collected from the capillary <br /> fringe zone near the bottom of each boring. The samples will be obtained using a 2-inch-diameter <br /> by 18-inch-long split-spoon sampler lined with three 6-inch-long thin-walled brass tubes. The <br /> sampler will be driven its entire length into undisturbed soil, using a 140-pound drop hammer. <br /> When the sampler is extracted from the borehole, the brass tubes will be removed and the ends of <br /> the tubes will immediately be screened for the presence of VOCs with a PID or equivalent <br /> instrument. The brass tube having the highest PID reading will be selected for possible chemical <br /> analysis. The ends of the selected brass tube will be: (1) covered with aluminum foil and plastic <br /> caps, which will then be taped with plastic tape to provide an air-tight seal; (2) labeled and placed <br /> into re-sealable plastic bags; and (3) stored in a ice chest containing crushed ice for delivery to the <br /> analytical laboratory. These procedures minimize the potential for cross contamination and <br /> volatilization of volatile organic compounds prior to chemical analysis. The remaining soil will be <br /> extracted from the tubes and logged as previously described. <br /> It <br /> is <br /> EA2092\pha ffiwoftl .dm <br />
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