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3.0 DRILLING PROCEDURES <br /> Drilling was done with a truck-mounted direct-push Geoprobe boring rig on May 11, 1998. Five <br /> borings were drilled, ranging from 26 to 37 feet in depth. As directed by PHS/EHD, two borings <br /> were continuously sampled from 21 to 26 feet; otherwise, samples were usually collected at 5-foot <br /> intervals. Each sample was collected in a 2-foot-long plastic sleeve, screened for organic vapors <br /> with a photo-ionization detector (PID), described on the boring log, cut,into shorter sections, <br /> capped, and placed into a cooled ice chest for preservation. <br /> The first boring (GP-1, Figure 2) was drilled through a conductor casing that had been previously <br /> set into the former UST cavity at a depth of 15 feet. The first sample was collected at 20 feet, and <br /> the boring was continuously sampled to 26 feet (Appendix A). The boring was terminated at a <br /> depth of 36 feet, where no evidence of contamination was detected. All other borings were drilled <br /> into native soil, and sampling began at approximately 15 feet. All borings except GP-1 were <br /> grouted to the surface with a bentonite-cement grout when drilling was completed. <br /> 4.0 GROUNDWATER MONITORING PROCEDURES <br /> Groundwater monitoring took place on May 12. Upon an-ival at the site, Upgradient personnel <br /> opened the wells and allowed them to equalize with air pressure. Well KF-3 was particularly <br /> difficult to open, because the well cover has been bent out-of-round (probably by vehicular traffic) <br /> and can no longer be screwed shut. Approximately 15 minutes after opening, the depth to <br /> groundwater was measured with a Solinst water level meter. The water depths are shown in Table I <br /> and Appendix B. <br /> A two-stage submersible pump was then used to purge the wells of standing water, which was <br /> deposited in a 55-gallon drum. During purging, the temperature, pH, and conductivity of the water <br /> were measured at 4 to 5-gallon intervals with a Corning Checkmate meter until these parameters <br /> stabilized (see Appendix B). To prevent cross-contamination, the pump was washed in a TSP <br /> solution between wells. The water samples were collected with a disposable plastic bailer and <br /> placed in 40-ml vials. The vials were labeled and logged and placed in a cooled ice chest. <br /> 5.0 RESULTS <br /> 5.1 Stratigraphy <br /> Three distinct layers underlie the site in the upper 35 feet. The shallowest layer consists of brown to <br /> gray or blue clayey silt or silty clay. This layer extends to a depth of approximately 21 feet in most <br /> borings and was exposed in the sidewalls of the tank excavation during the UST removal (Figures 3 <br /> and 4). In three of the five Geoprobe borings, samples from this layer emit moderate to strong <br /> gasoline odors. <br /> 4 <br />