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.s I <br /> SAMPLING AND ANALYSIS PROCEDURES <br /> The sampling and analysis procedures as well as the quality assurance plan are contained <br /> in this appendix The procedures and adherence to the quality assurance plan will <br /> provide for consistent and reproducible sampling methods, proper application of <br /> analytical methods, accurate and precise analytical results, and finally, these procedures <br /> will pro\ide guidelines so that the overall objectives of the monitoring program are <br /> achieved <br /> Gi ound Water and Liquid-Phase Petroleum Hydi ocarbon Depth Assessment <br /> A water/hydrocarbon interface probe is used to assess the liquid-phase petroleum <br /> hydrocarbon {LPH} thickness, if present, and a water level indicator is used to measure <br /> the ground water depth in monitoiing wells that do not contain LPH Depth to -round <br /> water or LPH is measured from a datum point at the top of each monitoring well casing <br /> The datum point is typical a notch cut in the north side of the casing edge If a water <br /> level indicator is used, the tip is subjectively analyzed for hydi ocarbon sheen <br /> Subjective AnaIysis of Ground Water <br /> Prior to purging, a water sample is collected from the monitoring well for subjective <br /> assessment The sample is ietiietied by gently lowering a clean, disposable bailer to <br /> approximately one-half the bailer length past the air/liquid interface The bailer is then <br /> retrieved, and the sample contained Nvithin the bailer is examined foi floating LPH and <br /> the appearance of a LPH sheen <br /> Moliitorina Well Pur61n6 and Sampling <br /> Monitoring wells are purged using a pump or bailer until pH, temperature, and <br /> conductivity of the purge water has stabilized and a iminimum of three well volumes of <br /> water have been removed If three well volumes cannot be iemoz ed in one half hour's <br /> time the well is allowed to recharge to 80% of original level After rechai Jing, a ground <br /> water sample is then removed from each of the wells using a disposable bailer <br /> A Teflon bailer, electric submersible or bladder pump will be the only equipment used <br /> for well sampling When sarnples for volatile orgame analysis ale being collected, the <br /> pump flow will oe regulated at approximately 100 milliliters per minute to minimize <br /> pump effluent turbulence and aeration GIass bottles of at least 40-milliliters volume and <br /> fitted with Teflon-lined septa will be used in sampling for �olatile organics These <br /> bottles -,.A ill be filled completely to prevent air fiom remaining in the bottle A positive <br /> nneniscus forms when. the bottle is completely full A convex Teflon septum �N ill be <br /> placed over the posits-,e meniscus to eliminate air After the bottle is capped, it is inverted <br /> and tapped to verify that it contains no air bubbles The sample containers for other <br /> parameters 1�ill be filled filtered as required and capped <br /> PaL-e 1 <br />