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' KLEINFELDER <br /> well volumes are generally removed from each monitoring well. Discharge water is stored in 55- <br /> gallon drums and left on site for later discharge or disposal by the client, depending on laboratory <br /> results. The drums are labeled with the date, well number, and a contact person and phone <br /> number. <br /> A-3.3 Equipment Decontamination <br /> To reduce the potential for cross-contamination between wells, developing equipment is washed <br /> ' in a trisodiuln phosphate or non-phosphate detergent solution and rinsed in distilled water or <br /> steam cleaned prior to 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 are 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 groundwater is measured from a set location at the top of the PVC casing (usually <br /> the north rim). The depth of water is then subtracted from the elevation of the top of the well <br /> ' casing to provide a groundwater 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 /> ' l. Prior to obtaining water level measurements, the monitoring wells would be opened and <br /> allowed to equilibrate for a period of approximately %2 hour. <br /> ' 2. The water level probe is decontaminated in a trisodium phosphate or non-phosphate <br /> detergent wash, followed by a distilled water rinse,prior to use in each well. <br /> 20-4587-01.WP1/201IP128 Page A-G <br /> ' Copyright 2001, Klcinfclder, Inc. May 8,2001 <br />