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• <br /> • <br /> pump. In most monitoring wells, the amount of water purged before sampling will be <br /> • greater than or equal to three casing volumes. Samples will be collected as soon as the <br /> • monitoring wells have recharged to a level sufficient for sample collection. If a <br /> • monitoring well is evacuated to dryness after removing fewer than three casing volumes, <br /> the monitoring well will be allowed to recharge for up to 24 hours. The actual purge <br /> • volume will be recorded on the field data sheet. If insufficient water has recharged after <br /> 24 hours, the monitoring well will be recorded as dry for the sampling event. <br /> Groundwater purged from the monitoring wells will be discharged onto the ground unless <br /> water quality results warrant discharge to onsite treatment facilities. Field measurements <br /> of pH, specific conductance, and temperature will be recorded on the field data sheet. <br /> • The meter(s) used for measuring pH, specific conductance, and temperature will be <br /> • calibrated each day before field activities are begun. Field meter calibrations will be <br /> recorded on the field data sheet. <br /> • <br /> 4. Well Sampling <br /> All groundwater samples will be collected with either low-flow pump sampling <br /> • techniques or an approved bailer. When samples for Total Trihalomethanes (TTHMs) <br /> are collected, the flow of groundwater will be regulated to minimize turbulence and <br /> • aeration. Glass Volatile Organic Analysis (VOA) bottles of at least 40 milliliters volume <br /> will be used in sampling for TTHMs. The VOAs will be filled completely to prevent air <br /> • from remaining in the bottle. A positive meniscus will form when the bottle is <br /> completely full. A convex septum will be placed over the positive meniscus to eliminate <br /> • air. After the bottle is capped, it will be inverted and tapped to verify that it does not <br /> • contain air bubbles. <br /> The sample containers for other parameters will be filled, filtered as required, and <br /> • capped. Required analytes, appropriate bottle types, and sample volumes are presented in <br /> • Table 1. When required, dissolved metals samples will be collected using appropriate <br /> field filtration techniques (i.e., samples will be field-filtered for dissolved metals).. <br /> • <br /> B. GROUNDWATER SAMPLE PRESERVATION AND HANDLING <br /> The following section specifies sample containers, preservation methods, and sample <br /> • handling procedures. <br /> • <br /> • 1. Sample Containers and Preservation <br /> • Sample containers vary with each type of analytical parameter. Container types and <br /> materials were selected to be nonreactive with the particular analytical parameter tested. <br /> • Required analytes, appropriate bottle types, and sample volumes are provided in Table 1. <br /> • <br /> • <br /> • <br /> • <br /> • Riverbank WWTP Workplan Nolte Associates,Inc. <br /> • March 2005 A-2 \\SasO\project\SA1542\mon_well\new\gwmwiwp\wp.doc <br /> • <br />