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Kennedy/Jenks Consultants <br /> washed packaged sand sized accordingly for the well screen slot size selected (Lonestar#2/12 <br /> or equivalent for 0.010-inch slots). The filter pack will extend upwards from the bottom of the <br /> boring to one to two feet above the screened section. All wells will be pre-developed after the <br /> filter pack is installed, and prior to the bentonite seal being installed. A two- to three-foot layer of <br /> protective bentonite clay pellets will be placed to minimize downward migration of the grout seal <br /> into the filter pack. A cement/bentonite grout will be placed so as to extend continuously from <br /> the top of the bentonite pellet layer to ground surface. If the well is constructed in a trafficked <br /> area, the well will be completed with a flush, traffic-rated well enclosure will be installed to <br /> control access to the well opening. If the well is located in the LAA, the well casing will be <br /> extended above ground and a protective steel standpipe will be erected the well casing. A <br /> schematic diagram of well construction details is shown on Figure 6. <br /> After waiting a minimum of 48 hours to allow curing of the grout and concrete, the monitoring <br /> wells will be developed by surging and pumping until the water removed from the wells is <br /> sediment-free or until no further improvement in water quality is observed. The wells will be <br /> allowed to recover for a minimum of 72 hours following well development, prior to monitoring <br /> and sampling. <br /> 2.1.1 Surveying <br /> The locations and well casing elevations of the new monitoring wells will be horizontally and <br /> vertically surveyed by a licensed land surveyor. The ground surface and top of well casing <br /> elevation will be surveyed to the nearest 0.01 foot relative to mean sea level. The ground <br /> surface and casing will be surveyed to the National Geodetic Vertical Datum (NGVD 1983), <br /> relative to nearest benchmark at the Facility. Horizontal locations of the new wells will also be <br /> surveyed relative to the California Coordinate system to 0.1 foot. <br /> 2.1.2 Residuals Management <br /> Residuals generated as a result of these activities are anticipated to include soil cuttings from <br /> the drilling activities, decontamination water resulting from the drilling activities and development <br /> of the monitoring wells, and purge water from sampling of the monitoring wells. The soil cuttings <br /> will be distributed on the ground near each work site. Water residuals will be distributed on the <br /> ground or in the LAA at the Facility, in a manner that does not affect work site safety. <br /> 2.1.3 Groundwater Sampling <br /> An initial sampling of groundwater will be conducted from the two monitoring wells no sooner <br /> than 72 hours after the newly installed wells have been developed. Groundwater sampling will <br /> be performed in accordance with the SOG for Groundwater Sampling (Appendix 13). <br /> Groundwater will be purged from the monitoring wells prior to sampling to acquire samples <br /> representative of aquifer conditions. Field parameters pH, temperature, and specific <br /> conductance will be monitored during purging to document stabilization. The parameters will be <br /> measured in accordance with Kennedy/Jenks' SOG for Field Measurement of pH, Temperature, <br /> and Specific Conductance (Appendix C). Purge water will be distributed on the ground or in the <br /> LAA at the Facility. <br /> Groundwater Investigation Work Plan Page 16 <br /> Barrel Ten Quarter Circle Winery, Escalon, California <br /> 9:6s-groupladminl ob1031030l l8.08 barrelten109-reportslgw invest wrk pinllext doc <br />