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a, <br /> June 26, 1992 <br /> ARCO Service Station No. 549, Stockton, California <br /> round- ater Monitoring Well <br /> The wells were constructed using clean 4-inch-inner-diameter, thread jointed, Schedule 40 <br /> polyvinyl chloride (PVC) casing. No chemicals, glues, or solvents were used in construction <br /> of the wells. The screened portion of the monitoring well consists of factory-perforated <br /> casing with slots and extends from the total depth of the boring and extends above the depth <br /> where water was first encountered. Unperforated casing is set from the top of the screen <br /> to several inches below surface grade. <br /> The annular space of each well was packed with sorted sand from the total depth of the <br /> boring to approximately 2 feet above the top of the screen. A plug of bentonite pellets <br /> (approximately 2-feet thick)was placed above the sand to prevent cement from entering the <br /> sand pack. This seal reduces the possibility that hydrocarbons migrating downward through <br /> the overlying sand will infiltrate the aquifer. The remaining annulus was backfilled to the <br /> ground surface with a mixture of water, cement, and.bentonite. The construction details of <br /> the individual wells are shown on the Logs of Borings. <br /> The wellheads were secured in cast-aluminum utility boxes with PVC aprons. The boxes <br /> have watertight seals and were set in concrete approximately flush with the surrounding <br /> i ground surface to reduce surface-water infiltration. A special wrench is required to open <br /> the box. This design discourages vandalism and reduces the possibility of accidental <br /> disturbance to the well. Each wellhead was also fitted with a locking well cage to further <br /> protect against unauthorized disturbance of the well. <br /> Vapor-Extraction Well Construction <br /> S <br /> Soil borings chosen for vapor wells were located in soil containing elevated levels of <br /> hydrocarbons based on field observations and field screening using a photoionization <br /> detector. Soil borings were terminated approximately 1 foot above first encountered ground <br /> water, and the vadose wells were constructed in the boring with threadedjointed, 4-inch- <br /> inner-diameter,Schedule 40 PVC casing. No chemical cements, glues, or solvents were used <br /> in well construction. The screened portion of each well consisted of factory-perforated <br /> casing with 0.020-inch-wide slots. The well screen extends from the total depth of the well <br /> to approximately 15 feet below grade for wells VW-1 and VW-2, and 10 feet below grade <br /> for well VW-3. The screen interval was based on field observations and sediments <br /> encountered during_drilling. The annular space in the well was packed with sorted sand to <br /> a point approximately 1 foot above the slotted interval. A bentonite plug was added above <br /> the sand pack to seal out cement. <br /> The remaining annulus was backfilled to grade with a bentonite-cement slurry. The vadose <br />. wells were completed by installing a traffic-rated, cast-aluminum utility box over the well <br /> head. <br /> MW-4 <br />