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(BTEX) and Total Lead These compounds should cover the contaminants of interest to <br /> the PHS-EHD Microbiotic activity in the soil will also be documented <br /> Scone of Work <br /> Exploratory Soil Borings and Monitoring Well Installation Procedures <br /> One exploratory boring will be drilled with truck mounted hollow-stem auger, which <br /> has been cleaned prior to use The well will be installed by Spectrum Exploration of <br /> Stockton, CA under approved PHS-EHD permits The boring will be advanced to the <br /> uppermost water bearing stratum, and advanced ten to fifteen feet into the aquifer <br /> and terminated in the aquitard underlying that stratum or 125 feet, which ever is <br /> less Construction of wells is expected to require boring greater than 100 feet deep to <br /> encounter water A geologist will log the boreholes by collecting samples at 5-foot <br /> intervals, lithologic contacts of interest and areas of obvious contamination, using <br /> the Unified Soil Classification System For the purposes of this investigation soil <br /> samples will be collected for analysis at 15, 20, 25, 30, 40, 55, 60, 80, and 90 feet, and at <br /> the capillary fringe in precleaned brass liners contained in a split spoon sampler <br /> driven ahead of the drill bit (During the investigation, soil samples may be field <br /> screened with the use of a Hanby test kit and a combustible gas analyzer) Soil <br /> samples for chemical analysis will be removed, sealed with Teflon and endcaps, <br /> labeled, logged onto chain-of custody forms and packed on ice for transport to <br /> Priority Environmental Laboratory of Milpitis, CA (PEL), a state certified laboratory <br /> for analysis The sampler will be decontaminated prior to the next drive Drill <br /> cuttings will be stored on site, between plastic for characterization a later date <br /> Wright will dispose of the drill cuttings subsequent to laboratory results <br /> The monitoring well will be constructed using precleaned, threaded 4-inch diameter <br /> Sch 40 PVC well casing, screening the entire thickness of the aquifer, and a portion <br /> above the capillary fringe to allow observation for possible floating product Glues <br /> will not be used to construct well casing Final well design will depend upon <br /> subsurface conditions encountered The annulus between the casing and the <br /> borehole will be backfilled with 2/12 sand to about two feet above the screens A <br /> bentonite clay spacer about two feet thick will be placed above the sand pack, and <br /> cement grout will be pumped from above the bentonite to the surface using a tremie <br /> pipe A traffic rated access vault box with locking device will cap the well <br /> Monitoring Well Development and Sampling Procedures <br /> The well will be developed prior to sampling by surge and bailing to remove the <br /> drilling muck and borehole "smear" to improve hydraulic contact Completeness of <br /> development will be made on the clarity of water, amount of sand and silt entry based <br /> upon well performance and field judgement Sampling procedures will follow after <br /> development The well will be sampled by first sounding the well with an electronic <br /> probe to measure depth to water and check for presence of floating product if <br /> product is encountered, a bailer will be used to check and measure the apparent <br /> thickness All samples will be labeled, logged onto chain-of-custody and packed on <br /> ice for transport to PEL Well development and sampling water will be stored on-site <br /> in sealed drums Disposal of the water will be provided upon receipt of chemical data <br /> Proper disposal of the development water will be coordinated by Wright <br /> Environmental <br />