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' . k'g KLEINFELDER <br /> ' 2. Approximately one week to one month prior to conducting the sampling, the residual <br /> pressures at the air-line of each lysimeter are measured ad the vacuums reset to <br /> ' manufactured recommended value (usually 50 centibars). The measurements and applied <br /> vacuums are noted on a sampling log form. Kleinfelder has found that resetting the <br /> lysimeters vacuums before the sampling yields good sample recovery. <br /> 3. The residual pressures are measured just prior to collecting the sample. The water line is <br /> then opened and nitrogen gas applied to the air line until either fluid or air is discharged <br /> ' (for dry lysimeters). The sample is contained in a 1 liter unpreserved bottle and the <br /> volume recovered is estimated. The fluid is then poured into appropriate preserved or <br /> unpreserved bottles of the requested analysis. <br /> 4. After the sample is collected, the lysimeter vacuum is reset to the manufacturer's <br /> recommended value. The lysimeter is also tested to evaluate potential leaks that may <br /> ' cause vacuum pressure loss. <br /> ' B-6 Leachate Monitoring <br /> ' 1. The leachate riser or wells are first opened and allowed to equilibrate with the <br /> atmosphere. <br /> ' 2. The leachate elevation is then measured from a set location using a conductivity-based <br /> water-level meter. The level is generally measured from a surveyed mark on the north <br /> rim of the casing. <br /> ' 3. A leachate sample is then collected using a clean, disposable bailer. <br /> ' 4. The sample is labeled and immediately stored in an iced cooler pending transport to the <br /> analytical laboratory. The sample is logged on a chain-of-custody. <br /> ' B-7 Surface Water Monitoring <br /> ' 1. Prior to collecting surface water samples, the depth of water is estimated at a designated <br /> location in the surface water body. <br /> t 2. Surface water samples are collected directly from the stream or surface water using a <br /> clean unpreserved plastic bottle, disposable bailer, bailer, coliwasa, DipstikTM, dipper, <br /> peristaltic pump, etc., or by directly filling the sample containers. Sampling equipment <br /> ' will either be disposable, dedicated or decontaminated in accordance with the above- <br /> defined decontamination protocols. Care is taken not to disturb the stream bottom and <br /> introduce sediment in the sample. The fluid is then poured into appropriate preserved or <br /> unpreserved bottles for the requested analysis. <br /> 204341-II.EOI/201IR959 Page B-7 <br /> Copyright 2001,Kleinfelder,Inc. August 21,2001 <br />