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T1, uf <br /> 1 <br /> a <br /> Standard Operating Procedures <br /> GROUNDWATER LEVEL MEASURING, PURGING AND SAMPLING <br /> Prior to groundwater sampling,static water level measurements are recorded for <br /> each well using a battery-powered sounder with a precision of plus or minus 0.01 <br /> feet. All measurements are recorded as depth-to-water from the surveyed <br /> measuring point at the top-of-casing. Depth-to-water readings are converted to <br /> water level elevations referenced to the USGS mean sea level datum. <br /> Thzn each well is purged by evacuating a minimum of three to five well casing <br /> volumes of groundwater using either adedicated polyvinyl chloride(PVC)bailer, <br /> sterile disposable bailer or a stainless steel pump. During the purging of each well <br /> and prior to sampling,discharge water temperature,specific conductivity,and pH <br /> measurements are recorded and are allowed to stabilize. Stabilized measurements <br /> indicate that formation water has entered the well. The groundwater sample is <br /> _ taken when the water level in the well recovers to 80%of its static level. <br /> Following purging,a groundwater sample is collected in accordance with <br /> California Regional Water Quality Control Board(RWQCB)procedures described <br /> in the Leaking Underground Fuel Tank(LUPI}Field Marural,the Tri-Regional <br /> Board Staff Recommendarimu for Preliminary Evaluation and Investigation of <br /> Underground Tank Sites,and local regulatory guidelines. <br /> A groundwater sample is first collected and checked for;he presence of free <br /> p,-oduct in the sampling bailer. Thickness of possible free product is measured <br /> using an electronic interface probe with a plus or minus 0.01 foot detection limit. <br /> Groundwater samples are collected using a pre-cleaned teflon or stainless steel <br /> bailer equipped with a ball-check valve,and sample containers are filled directly <br /> from the bailer as soon after purging as possible. <br /> Agitation is minimized during sample retrieval and sample transfer to laboratory <br /> prepared sample containers in order to minimize sample aeration. Groundwater <br /> samples to be analyzed are carefully decanted into laboratory-prepared,40- <br /> milliliter volatile organic analysis(VOA)vials. The VOA vials are fulled <br /> completely,leaving no headspace,and are capped and.sealed with Teflon-lined <br /> lids. Additional groundwater samples may be collected in 1 liter bottles. A11 <br /> s-mples are labeled and stored in an ice chest with crushed ice to maintain a <br /> constant temperature of 4 degrees Celsius. A thermometer is kept in the ice chest <br /> to ensure that the proper temperature is maintained- The samples are then <br /> delivered under chain-of-custody to a state-cerdfied hazardous materials testing <br /> laboratory. <br /> Monitor well purge water is properly stored on-site pending off-site disposal. <br /> Parker Environmental Services, 4185 Rialto Court, Pittsburg, CA 94555-6116 <br /> Phone (415) 439-1024 Fax (415) 439-2566 <br /> � mi�e�we� �o1,7f�A <br />