Laserfiche WebLink
AEGIS ENVIRONMENTAL, INC. <br /> STANDARD OPERATING PROCEDURE <br /> RE: GROUNDWATER PURGING AND SAMPLING <br /> SOP-7 <br /> Prior to water sampling, each well is purged by evacuating a minimum of three wetted <br /> well-casing volumes of groundwater When required, purging will continue until either <br /> the discharge water temperature, conductivity, or pH stabilize, a maximum of ten well- <br /> bore volumes of groundwater have been recovered, or the well is bailed dry When <br /> practical, the groundwater sample should be collected when the water level in the well <br /> recovers to at least 80 percent of its static level <br /> The sampling equipment consists of either a 'Teflon" bailer, PVC bailer, or stainless <br /> steel bladder pump with a 'Teflon" bladder If the sampling system is dedicated to the <br /> well, then the bailer is usually "Teflon," but the bladder pump is PVC with a <br /> polypropylene bladder. In general and depending on the intended laboratory analysis, <br /> 40-milliliter glass, volatile organic analysis (VOA) vials, with 'Teflon" septa, are used as <br /> sample containers <br /> The groundwater sample is decanted into each VOA vial in such a manner that there <br /> . is no meniscus at the top of the vial A cap is quickly secured to the top of the vial. <br /> The vial is then inverted and gently tapped to see if air bubbles are present If none <br /> are present, the vial is labeled and refrigerated for delivery, under strict chain-of- <br /> custody, to the analytical laboratory Label information should include a unique <br /> sample identification number, lob identification number, date, time, type of analysis <br /> requested, and the sampler's name <br /> For quality control purposes, a duplicate water sample is collected from each well. <br /> This sample is put on hold at the laboratory When required, a trip blank is prepared <br /> at the laboratory and placed in the transport cooler It is labeled similar to the well <br /> samples, remains in the cooler during transport, and is analyzed by the laboratory <br /> along with the groundwater samples In addition, a field blank may be prepared in the <br /> field when sampling equipment is not dedicated The field blank is prepared after a <br /> pump or bailer has been either steam cleaned or properly washed, prior to use in the <br /> next well, and is analyzed along with the other samples The field blank analysis <br /> demonstrates the effectiveness of the in-field cleaning procedures to prevent cross- <br /> contamination <br /> To minimize the potential for cross-contamination between wells, all well development <br /> and water sampling equipment not dedicated to a well is either steam cleaned or <br /> properly washed between use As a second precautionary measure, wells are <br /> sampled in order of least to highest concentrations as established by available <br /> previous analytical data <br /> In the event the water samples cannot be submitted to the analytical laboratory on the <br /> ATTACHMENT/$0P-7/SEFTEMBER 1992 <br />