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2.2 Well Construction and Development <br /> Ground water was first encountered during drilling of AW-9 at approximately 12.5 fbg, and <br /> stabilized at 10.10 fbg, as measured on April 24, 1992. AW-9 was installed to a depth of 28.5 <br /> fbg using 6-inch-diameter, flush-threaded, Schedule 40, PVC blank casing, and 0.010-inch, <br /> slotted PVC casing. Based on initial water depth encountered and results of previous <br /> investigations, the slotted casing was installed from 8.5 fbg to the total depth of the boring <br /> and completed with blank casing from 0.5 to 8.5 fbg to provide adequate annular space for <br /> grout materials. Monitoring well installation procedures and construction details are included <br /> in the boring logs (Appendix E). <br /> During installation, AW-9 was surged prior to sealing the well to: (1) reduce possible <br /> smeared sediment on the sidewall of the boring; (2) compact annular filter-pack sand to <br /> enhance filter-pack utility; (3)restore the natural hydraulic conductivity of the formation; and <br /> (4) remove foreign sediment to ensure turbid-free ground water samples. The monitoring <br /> well was developed on April 7, 1992, by removing 10 casing volumes of ground water. <br /> General field procedures for monitoring well development and field survey forms are <br /> presented in Appendix F. <br /> 2.3 Well Survevins, Fluid-Level Monitoring, and Ground Water Sampling <br /> The top of casing elevations for Monitoring Wells AW-1 through AW-4 were originally <br /> surveyed on October 22, 1990, by Associated Professions. After installation of ground water <br /> Monitoring Wells AW-5 through AW-8, all wells were surveyed on May 7, 1991, by Land <br /> Improvement Services. AW-9 was tied into the May 7, 1991 survey on April 9, 1992; <br /> subsequently an elevation error in the May 7, 1991 survey was noted and all wells were <br /> resurveyed on May 7, 1992. Surveying activities were performed by California-registered <br /> surveyors. Elevations used in the surveys were in reference to a local benchmark with an <br /> elevation of 31.50 feet msl (NGVD-1929); a railroad spike set in an island on the <br /> approximate centerline of East Grantline Road, 19.5 feet west of the centerline of the <br /> railroad spur tracks. <br /> Prior to ground water sampling on April 7 and 24, 1992, the depth to fluid in each well was <br /> measured to one-hundredth of a foot from a surveyed, permanent mark on the top of casing <br /> of each well casing. Survey data and fluid-level measurements are presented in Table 1. <br /> Ground water elevations and elevation contours estimated from the April 24 monitoring data <br /> are shown in Figure 3. General field procedures for monitoring and sampling are included <br /> with the field survey forms in Appendix F. <br /> As part of this supplemental site investigation, ground water samples were collected from all <br /> monitoring wells on April 7, 1992. Confirmation sampling was conducted on April 24, 1992. <br /> Due to the cold storage breakage of a Miter amber sample container collected from AW-9, <br /> two additional liters were collected on April 27, 1992, to ensure sufficient sample volume. <br /> 3 <br />