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driven sampling device To reduce the potential for cross-contamination between samples, the <br /> sampler will be cleaned between each sampling event Upon recovery, the sample container will be <br /> sealed at each end with TeflonT"" sheeting and plastic caps to minimize the potential of volatilization <br /> and cross-contamination prior to chemical analysis The soil sample will be labeled, placed in an ice <br /> chest cooled to 4° Celsius, and delivered to a state-certified analytical laboratory, along with the <br /> appropriate chain-of custody documentation <br /> Sample Identification and Chain-of Custody <br /> Sample identification and chain-of-custody procedures document sample possession from the time of <br /> collection to ultimate disposal Each sample container submitted for analysis has a label affixed to it <br /> to identify the lob number, sampler, date and time of the sample collection, and the sample number <br /> unique to that sample This information, in addition to a description of the sample, field <br /> measurements made, sampling methodology, names of onsite personnel, and any other pertinent <br /> field observations, are recorded on the borehole log or in the field records A chain-of-custody form <br /> is used to record possession of the sample from the time of collection to its arrival at the laboratory <br /> When samples are shipped, the person in custody of them relinquishes the samples by signing the <br /> chain-of custody form and noting the time <br /> Monitoring Well Installation <br /> Monitoring wells will be completed by installing one two-inch-diameter Schedule 40 polyvinyl chloride <br /> (PVC) casing The two-inch diameter monitoring wells will be installed using 8-inch diameter hollow <br /> stem augers <br /> Monitoring wells will be constructed using threaded, factory-perforated and blank Schedule 40 PVC <br /> The perforated interval consists of slotted casing, 0 02 inches wide by 1 5-inch long slots, with 42 <br /> slots per foot The screened interval will allow for seasonal fluctuation in water level and for <br /> monitoring floating product A threaded PVC cap is secured to the bottom of the casing The well <br /> casing is thoroughly washed and/or steam cleaned, or may be purchased as pre-cleaned, prior to <br /> completion <br /> A filter pack of graded sand will be placed in the annular space between the PVC casing and the <br /> borehole wall Sand will be added to the borehole through the hollow stem of the augers provide a <br /> uniform filter pack around the casing and to stabilize the borehole The sand pack will be placed to a <br /> maximum of 2 feet above the screens, followed by a minimum 1-foot seal consisting of bentonite <br /> pellets or chips <br /> Cement grout containing 5 percent bentonite will be placed above the bentonite seal to the grout <br /> surface A concrete traffic-rated vault box will be installed over the monitoring wells A water tight <br /> locking cap will be installed over the top of the well casing Monitoring well elevations will be <br /> surveyed by a state-certified land surveyor to the nearest 0 01 vertical feet relative to mean sea level <br /> (MSL) Horizontal coordinates of the wells will also be obtained at the same time <br /> Equipment Cleaning <br /> Sample bottles, caps, and septa used in sampling for volatile and semivolatde organics will be triple <br /> rinsed with high-purity deiornzed water After being rinsed, sample bottles will be dried overnight at a <br /> temperature of 200°C Sample caps and septa will be dried overnight at a temperature of 60°C <br /> Sample bottles, caps, and septa will be protected from solvent contact between drying and actual use <br /> at the sampling site Sampling containers will be used only once and discarded after analysis is <br /> complete <br />