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• aN��en srir� <br /> * � * <br /> GROUNDWATER WELL SOP# 2007 <br /> DATE 01/26/95 <br /> 7FAM SAMPLING REV # 0 0 <br /> 1.0 SCOPE AND APPLICATION and need not be the same as the device used for <br /> purging Care should be taken when choosing the <br /> The objective of this standard operating procedure sampling device as some will affect the integrity of <br /> (SOP) is to provide general reference information on the sample Sampling should occur in a progression <br /> sampling of ground water wells This guideline is from the least to most contaminated well, if this <br /> primarily concerned with the collection of water information is known <br /> samples from the saturated zone of the subsurface <br /> Every effort must be made to ensure that the sample The growing concern over the past several years over <br /> is representative of the particular zone of water being low levels of volatile organic compounds in water <br /> sampled These procedures are designed to be used in supplies has led to the development of highly <br />' conjunction with analyses for the most common types sophisticated analytical methods that can provide <br /> of ground water contaminants (e g , volatile and semi- detection limits at part per trillion levels While the <br /> volatile organic compounds, pesticides, metals, laboratory methods are extremely sensitive, well <br /> biological parameters) controlled and quality assured, they cannot <br /> compensate for a poorly collected sample The <br /> These are standard (i e , typically applicable) collection of a sample should be as sensitive, highly <br /> operating procedures which may be varied or changed developed and quality assured as the analytical <br />�. as required, dependent upon site conditions, procedures <br /> equipment limitations or limitations imposed by the <br /> procedure In all instances, the ultimate procedures 3.0 SAMPLE PRESERVATION, <br />' employed should be documented and associated with CONTAINERS, HANDLING, <br /> the final report AND STORAGE <br /> Mention of trade names or commercial products does The type of analysis for which a sample is being <br />' not constitute U S Environmental Protection Agency collected determines the type of bottle,preservative, <br /> (EPA)endorsement or recommendation for use holding time, and filtering requirements Samples <br /> should be collected directly from the sampling device <br /> 2.0 METHOD SUMMARY into appropriate laboratory cleaned containers Check <br />' that a Teflon liner is present in the cap, if required <br /> In order to obtain a representative groundwater sample Attach a sample identification label Complete a field <br /> for chemical analysis it is important to remove data sheet, a chain of custody form, and record all <br />' stagnant water in the well casing and the water pertinent data in the site logbook <br /> immediately adjacent to the well before collection of <br /> the sample This may be achieved with one of a Samples shall be appropriately preserved, labelled, <br /> number of instruments The most common of these logged, and placed in a cooler to be maintained at <br />' are the bailer, submersible pump, non-contact gas 4EC Samples must be shipped well before the <br /> bladder pump, inertia pump and suction pump At a holding time is up and ideally should be shipped <br /> minimum, three well volumes should be purged, if within 24 hours of sample collection It is imperative <br />' possible Equipment must be decontaminated prior to that samples be shipped or delivered daily to the <br /> use and between wells Once purging is completed analytical laboratory in order to maximize the time <br /> and the correct laboratory-cleaned sample containers available for the laboratory to perform the analyses <br /> have been prepared,sampling may proceed Sampling The bottles should be shipped with adequate packing <br />' may be conducted with any of the above instruments, and cooling to ensure that they arrive intact <br /> 1 <br /> I <br />