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k" KLEIN FELDER <br /> used Installation of the 0130 sand may require that the sand be tremmied, <br /> using clean water. In this event, a sample of the tremae water is collected, <br /> unless the source is thought to be clean <br /> o A 3- to 5-foot bentonite plug is placed above the sand pack to provide a seal <br /> against surface water infiltration and to reduce the potential for cement grout to <br /> infiltrate into the water <br /> o The remaining annular space is filled to the surface with tremmied <br /> cement/bentonite grout to the surface. <br /> o The wells are secured in an above- or below-ground locking stovepipe. The <br /> well heads may be enclosed in a water tight cement utility box set flush to the <br /> ground surface when located in a traffic area <br /> A-3 2 Monitoring Well Development <br /> The wells are developed to reduce the effects of drilling on the formation and to increase the <br /> effective hydraulic radius of the well. <br /> Monitonng wells are generally developed 24 to 48 hours after installation to allow the grout to <br /> set. Each well is first sampled with a clear acrylic bailer to visually inspect for hydrocarbon <br /> layer or sheen If no product layer or sheen is observed on the water, the well is developed by <br /> surging, pumping or bailing Surging along the screened interval of the well is performed to <br /> draw the sediment from the formation into the filter pack and the well, and to set the sand <br /> pack. The sediment laden water is purged from the well at a rate of between 0 75 to 10 <br /> gallons per minute (gpm) depending on recharge rate and casing size. Development continues <br /> until the discharge runs relatively clear of fines. Approximately 5 to 10 well volumes <br /> generally are removed from each monitoring well. Discharge water is stored in 55-gallon <br /> drums and left on site for later discharge or disposal by the client, depending on laboratory <br /> results. <br /> A-3 3 Equipment Decontamination <br /> To reduce the potential for cross-contamination between wells, developing equipment is <br /> washed in a trisodium phosphate solution and rinsed in distilled water or steam cleaned prior to <br /> use in the next monitoring well <br /> A-3.4 Well Survey (3 wells only) <br /> The locations of soil borings and monitoring wells, and the elevation of the top of the PVC <br /> casings is usually surveyed and tied into permanent markers, if readily available Survey <br /> accuracy is 0.1 foot for the "x" and "y" coordinates and 01 foot for the "z" coordinate. The <br /> depth to static ground water is measured from a set location at the top of the PVC casing The <br /> depth of water is then subtracted from the elevation of the top of the well casing to provide a <br /> ground water elevation for each monitoring well location. <br /> • <br />