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APPENDIX B <br />' GROUNDWATER SAMPLING AND ANALYSIS PROCEDURES <br /> Subjective Analysis of Monitoring Wells <br /> ' were collected for subjective analysis from just below the air-fluid interface <br /> Groundwater samples J Y <br /> in the monitoring wells by lowering approximately half the length of a clean Teflon bailer through <br /> the interface The bailer was retrieved and the water sample examined for floating product, sheen, <br /> ' or other subjective evidence of hydrocarbons <br /> Measurement of the Depth to Groundwater in Monitoring Wells <br /> The depth of the groundwater surface in the monitoring wells was measured from the top of the well <br /> casing to the nearest 0 01 foot with a Solinse water level indicator <br /> Groundwater Sampling <br /> The static water level in each well was measured to the nearest 0 01 foot with a Solinst electric <br /> water level indicator cleaned with a laboratory-grade, non-phosphatic detergent and deiomzed water <br /> before use in each well A clean bailer was used to obtain a sample from the surface of the water in <br /> the well for a subjective analysis of hydrocarbons The sample was retrieved and visually examined <br /> for floating product, sheen, color, and clarity <br /> Approximately three casing volumes of groundwater were purged from the wells using a <br /> stainless-steel, electrical, submersible pump The pump, cables, and hoses were cleaned with a <br /> laboratory-grade, non-phosphatic detergent and water before use in each well The wells were <br /> purged until withdrawal was of sufficient duration to result in stabilized pH, temperature, and <br /> electrical conductivity of the water, as measured by portable meters calibrated to a standard buffer <br /> and conductivity standard The wells recovered to more than 90 percent of the static water level <br /> within 5 minutes of turning off the pump <br /> 11SACRFPIICOMMON1sacDP120031Prf188018800391A 3aa doe Shaw Environmental,Inc <br /> (01050000) <br /> B-1 <br />