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Moderate to severe flowing conditions were encountered in some boreholes which required drilling <br /> methods to be alternated between push and auger drilling depending upon the severity of the flowing <br /> condition. Some soil samples were not recovered in instances of severe flowing since the sampler could <br /> not be advanced to the desired depth. <br /> The boreholes were drilled with a truck mounted hollow stem auger and/or direct push drilling equipment. <br /> All drilling equipment and sampling tools were cleaned prior to arriving, between driving samples and <br /> before leaving the site. The augers were advanced to the desired sampling depth interval,and a drive split <br /> spoon sampler was driven ahead of the drill bit. The sampler was then retrieved and dissembled. The soil <br /> filled brass or acetate liners retained for chemical analysis were sealed with Teflon® paper and plastic <br /> endcaps, labeled, logged onto chain-of-custody forms and place in a chilled ice chest on crushed ice. Drill <br /> cuttings were drummed and left on-site. <br /> The boreholes were logged using the Unified Soil Classification System under the supervision of a <br /> registered geologist. Additional lithologic information was collected to describe the subsurface geology. <br /> Soil samples were field screened for presence of contaminants by checking for presence of odor and <br /> staining, and a photoionization meter was used for soil field vapor measurement use. Soil samples were <br /> collected at minimum five-foot intervals, with additional samples collected at intervals of obvious <br /> contamination and at stratigraphic features of interest using field discretion. <br /> Upon completion of the borehole drilling and collection of information, all boreholes were backfilled with <br /> grout,placed from the bottom to top of the borehole with a tremie line. <br /> Field Modification of Workplan for Borehole Locations <br /> The PHS EHD representative and field geologist discussed the sampling as the borehole drilling and <br /> sampling progressed on March 17, 2000. Field observations indicated that contaminants were not <br /> widespread and a modification to the field work and sampling was approved by PHS EHD in the field. <br /> One boring(originally proposed furthest north under the canopy)was deleted. One boring was moved to <br /> a location lateral from the two former tank pits to search for possible lateral contaminant migration in that <br /> area(see Figure 1). <br /> Reconnaissance Groundwater Sampling <br /> Groundwater from each borehole was sampled using push or drill rods or hollow stem auger as temporary <br /> casing in the uppermost aquifer. Depth to groundwater measurements were made to the nearest one-one <br /> hundredth of one foot from existing grade, and also checked for the presence of separate phase product. <br /> The groundwater sample was carefully collected with a clean disposable bailer and poured into the <br /> appropriate laboratory prepared container with minimum cavitation and headspace. Each water sample <br /> was labeled,logged onto a chain-of-custody form, and placed in a chilled ice chest on crushed ice. <br /> Off-Site Water Well <br /> Domestic water for the lavatories is obtained through an agreement with Calaveras Cement, the property <br /> owner on the west side, who has an industrial well used in concrete batch operations. Wright's scope of <br /> work included collection of water samples from the Calaveras Cement well(Water Weil), located at 8181 <br /> 1 lth Street(just west of the M&M building). <br /> Water Well sampling used the faucet.near.the_well head-and the.existing-pump in the-well. The water <br /> sample was collected after first clearing the faucet for thirty seconds, then filling the laboratory prepared <br /> containers with minimum cavitation and headspace. The water sample was labeled, logged onto a chain- <br /> of-custody form,and placed in a chilled ice chest on crushed ice. <br />