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Project No 034-98081 <br /> Appendix B <br /> METHODOLOGY <br /> i <br /> The methods used to accomplish the purpose and scope of the September 1998 monitoring well <br /> installation are listed below The assessment activities were accomplished in accordance with the <br /> Regional Water Quality Control Board (RWQCB) Tri-Regional Board guidelines and the requirements <br /> listed in the "Recommendations for Preliminary Investigation and Evaluation of Underground Storage <br /> Tank Sites " A copy of the workplan was submitted to the SJCEHD for review and written approval <br /> before commencing the field investigation <br /> September 1998 Phase Il Assessment <br /> • Three groundwater monitoring wells were installed during this assessment The <br />' locations of the wells are shown on Figure 2 The total depths of the wells were based <br /> on the existing depth to groundwater, which is approximately 35 feet bgs, and on the <br /> anticipated vertical seasonal fluctuations of the water table The wells are approximately <br /> 50 feet in depth The wells are constructed of 2-inch diameter Schedule 40 PVC water <br /> well casing and screen The screen interval has 0 020-inch diameter slot size The <br /> screen interval was designed to extend from 15 feet below, and from 5 to 10 feet above, <br /> the water table The screened interval extends from between 25-30 to 50-52 feet bgs <br /> (well dependent) A filter pack, consisting of rounded 20 x 16 mesh washed, bagged <br /> sand was placed into the annular space to a depth of approximately two feet above the <br />' screen interval A two foot thick seal, consisting of hydrated bentonite pellets, was <br /> placed above the filter pack The remaining annular space was filled with 21-sack neat <br /> grout The grout was introduced into the annular space by a tremae pipe or equivalent <br /> i system depending on the depth of the open annular space of the boreholes A flush- <br /> mounted, traffic-rated well vault was emplaced to provide access to the wellhead The <br /> well vault was set above existing site grade to promote positive drainage away from the <br /> wellhead Well construction specifications are diagramatically presented on soil boring <br /> logs in Appendix E <br /> • During the drilling of monitoring wells, the drill cuttings (soil) were subjectively <br /> analyzed for odor and discoloration Additionally, the soil were field scicened with a <br /> portable pliotoionization detector(PID) The PID readings were recorded on field notes <br /> The PID is a direct reading real-time analyzer that can detect most of the volatile <br /> hydrocarbon constituents present in the vapor phase of petroleum-affected soils <br /> • Soil samples from the soil borings were obtained for logging purposes at five foot <br /> intervals, beginning at grade Soils were logged in accordance with the Unified Soil <br /> Classification System <br /> • Soil samples from the proposed soil borings were collected from the capillary fringe (� <br /> 32 feet bgs) and submitted for analysis of BTEX and TPH-G at a laboratory certified by <br /> the State of California for analysis of hazardous waste <br /> KRAZAN & ASSOCIATES, INC <br /> Ten Offices Serving the Western United States <br /> 3498081 SG2 <br />