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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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To prevent cross contamination during drilling and sampling operations, all equipment will be <br /> steam-cleaned or washed with laboratory-grade detergent, rinsed with tap water, and rinsed with <br /> deionized water before each use <br /> Groundwater Monitoring Well Construction <br /> Groundwater monitoring wells will be constructed using schedule 40, flush-threaded, blank <br /> and machine-slotted, polyvinyl chloride (PVC) casing. On-site monitoring wells will be completed <br /> with 4-inch-diameter PVC casing, while off-site wells will be completed with 2-inch-diameter PVC <br /> casing. The well perforations will be 0.020-inch machine-slots factory cut into the PVC casing. <br /> The slotted interval will extending from a depth of approximately 15 feet below the existing shallow <br /> groundwater table to approximately 10 feet above the existing water table. Blank PVC casing will <br /> extend from the top of the perforated section to the ground surface (or three-feet above ground <br /> surface, in the case of above-ground completion). The well design is intended to accommodate <br /> seasonal water-level fluctuations within the slotted interval. The well design may be modified in the <br /> field during the drilling operation, depending upon conditions encountered during drilling. In no <br /> case will the monitoring well penetrate clay zones existing beneath the shallow groundwater surface <br /> which have been identified as being greater than 5 feet thick. Penetration of such zones might allow <br /> downward migration of contaminants into lower water-bearing zones. A flush-threaded PVC cap <br /> will be installed at the bottom of each well. <br /> The annular space surrounding the slotted interval and casing will be packed with Lonestar <br /> No. 3 (or equivalent) silica sand (unless otherwise noted in the work plan), from the bottom of the <br /> slotted interval to approximately 2 feet above the top of the slots. The well will then be surged to <br /> settle the filter pack and additional sand will be added as necessary to return the level to a height of <br /> 2 feet above the top of the slots. A 2-foot-thick seal of bentonite pellets or chips will be placed <br /> above the sand pack and hydrated using tap water. The annulus will then be backfilled with a <br /> bentonite-cement slurry containing approximately 5-percent powdered bentonite, or neat cement, <br /> from the top of the bentonite seal to just below the ground surface. The top of the well casing will <br /> be sealed using a locking, water-tight, cap. Groundwater monitoring wells will be completed at <br /> grade using a flush-mounted, traffic-rated, water-tight containment box set in concrete, or above <br /> grade using steel well monuments set in concrete. <br /> The horizontal location and top of casing (TOC) elevation will be surveyed by a licensed <br /> surveyor, and all depths to water will be measured in relation to the surveyed mark on the TOC. <br /> Groundwater Monitoring Well Development <br /> Prior to development, the well cap will be removed from the top of the casing and the water <br /> within the well will be allowed to come to equilibrium with atmospheric pressure. The depth-to- <br /> E:'2092\ph=ffiworkple do <br />
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