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Ms. Dot Lofstrom <br /> Page 3 of 5 <br /> samples are summarized in Table 3 and Table 4, respectively. The locations of the borings are <br /> shown in Figure 2. <br /> 2.3 Recent Groundwater Sampling <br /> Monitoring well MW 1 was most recently sampled on May 31, 2000. At the request of PHS/EHD <br /> the analytical suit included TPHg, BTEX and a full VOC scan by EPA method 8260. The <br /> wellhead elevation of MW 1 was also tied to the elevations of the monitoring wells installed as part <br /> of the investigation of the adjacent 601 E. Miner site. <br /> No analytes except for MTBE were detected in the groundwater sample (Table 2). Groundwater <br /> flowed in an easterly direction. Groundwater elevation data are presented in Table 5. <br /> 3.0 WORKPLAN <br /> To further evaluate the nature and extent of groundwater impact on the property the following <br /> workscope is proposed. <br /> 3.1 Monitoring Well Drilling and Construction <br /> One additional groundwater monitoring well will be constructed at the site. The well will be located <br /> downgradient of existing well MW 1 and north of previous hydropunch boring HP4. The proposed <br /> location of the well is shown on Figure 2. The following drilling procedures and construction <br /> specifications will be used: <br /> All work will be performed by a C-57 licensed drilling contractor under the supervision of an <br /> experienced geologist. The contractor will advance one soil boring using a rig equipped with 8" <br /> diameter hollow stem augers and complete the boring as a groundwater monitoring well. The well <br /> will be completed at a depth of approximately 50 feet below ground surface (bgs), and will be <br /> constructed with 2-inch diameter, Schedule 40 PVC casing and 0.020" slotted screen. The screened <br /> interval will be from approximately 25 feet to 50 feet bgs to accommodate water level fluctuations. <br /> Filter pack will consist of No. 3 Monterey sand from the bottom of the well to approximately 2 feet <br /> above the top of the screen. The remaining annulus will be completed with 2 feet of hydrated <br /> bentonite overlain by neat cement grout tremied to the surface. At the surface the well will be fitted <br /> with a locking cap and water tight,traffic rated well box. <br /> Soil samples will be collected at 5-foot intervals during drilling for stratigraphic and field screening <br /> concerns. All soil samples will be classified in accordance with ASTM Designation D2488-90, <br /> which is equivalent to the Unified Soil Classification System. Selected soil samples will be <br /> submitted for laboratory analysis. At a minimum these will include the sample collected from the <br /> capillary fringe and the deepest sample collected. Samples selected for analysis will be immediately <br /> capped, labeled and placed in an ice chest at a temperature of 4 degrees Centigrade for shipment to <br /> the laboratory under chain of custody protocol. The samples will be analyzed for TPHg using EPA <br /> Method 8015, and BTEX using EPA method 8020. Gasoline oxygenate additives, 1,2 <br /> • dichloroethane(DCA)and ethylenedibromide(EDB)will be analyzed using EPA Method 8260. <br /> vaIIc"VvpotU\wkpinmw2.doc <br />