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File No. 20-3978-01.W 15 KLEINFELDER <br /> January 6, 1997 <br /> • The remaining annular space is tilled to the surface with cement/bentonite grout. <br /> • The wells are secured in an aboveground or underground 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 /> B-3.2 Monitoring Well Development <br /> The wells are developed to reduce the effects of drilling on the formation and to increase <br /> the effective hydraulic radius of the wells. <br /> Monitoring wells are generally developed 24 to 48 hours after installation to allow the <br /> grout to set. Each well is first sampled with a clear disposable bailer to visually inspect <br /> for a hydrocarbon layer or sheen. If no product layer or sheen is observed on the water, <br /> the well is developed by surging, pumping or bailing. Surging along the screened <br /> interval of the well is performed to draw the sediment from the formation into the filter <br /> pack and the well, and to set the sand pack. Development continues until the discharge <br /> runs relatively clear of fines. Approximately 5 to 10 well volumes are generally removed <br /> from each monitoring well. Discharge water is stored in 55-gallon drums and left on site <br /> for later discharge or disposal by the client, depending on laboratory results. The drums <br /> are labeled with the date, well number, and a contact person and phone number. <br /> B-3.3 Equipment Decontamination <br /> To reduce the potential for cross-contamination between wells, developing equipment is <br /> washed in a trisodium phosphate or non-phosphate detergent solution and rinsed in <br /> distilled water or steam cleaned prior to use in the next monitoring well. <br /> B-3.4 Well Survey <br /> The locations of soil borings and monitoring wells, and the elevation of the top of the <br /> PVC casings are usually surveyed and tied into permanent markers, if readily available. <br /> Survey accuracy is 0.1 foot for the "x" and "y" coordinates and .01 foot for the "z" <br /> coordinate. The depth to static groundwater is measured from a set location at the top of <br /> the PVC casing (usually the north rim). The depth of water is then subtracted from the <br /> elevation of the top of the well casing to provide a groundwater elevation for each <br /> monitoring well location. <br /> 203978-01.W151207PE009 Page B-5 January 6, 1997 <br /> Copyright 1997, Kleinfelder, Inc. <br />