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KLEINFELDER <br /> M 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 /> cementlbentomte grout to the surface. <br /> o The wells are secured in below-ground locking water tight cement utility boxes <br /> set flush to the ground surface. <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 /> Monitoring 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 five 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 <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 /> A-4 GROUNDWATER MONITORING <br /> A-4 1 Water Level Measurements <br /> Water level measurements are made in the wells prior to purging and sampling the wells <br /> Measurement protocol is as follows <br /> 1 The wells are opened and allowed to equilibrate with the atmosphere <br /> • 2. The water level probe is decontaminated in a tnsodium phosphate wash, followed by a <br /> distilled water rinse, prior to use in each well. <br /> FWP2-92-25 Page A-3 <br /> Copynglit 1992 Klemfelder, Inc <br />