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AUG 24 '94 ©E AM. .FUGR' WEST ROSE'i I LLE PG,' P. 1/1 <br /> 514CI-1- L CO, <br /> G <br /> STANDARD OPERATING PROCEDURES <br /> RE: EXCAVATION SAMPLING (SOIL,AND WATER) <br /> SOP-2b <br /> Soil <br /> Excavation and subsequent soil sampling is performed under the direction of a registered <br /> geologist or civil engineer. To reduce the potential for cross-contamination, all excavation <br /> equipment is either steam-cleaned or washed prior to use and between excavations. Soil <br /> samples are typically collected directly from the excavation surface or from material <br /> removed from the excavation in a backhoe or excavator bucket. A portion of the sampled <br /> area or material may be sealed in a plastic bag, jar, or other suitable container for <br /> volatile organic screening with either a portable photoionization detector, flame ionization <br /> detector, or an explosimeter. Another portion of the sample may be used to describe the <br /> excavated material. <br /> Soil samples for chemical analysis are collected in Leaned, thin-walled brass tubes of <br /> varying diameters and lengths (typically 6 inches long by 2 inches outside-diameter) or <br /> other appropriate cleaned sample container. A hand-driven sampler holding an inset <br /> sample container may be used. To reduce the potential for cross-contamination between <br /> samples, the sampler is cleaned between each sampling event. Upon recovery, the <br /> sample container is sealed to minimize the potential of volatilization and cross- <br /> contamination prior to chemical analysis. Brass soil sampling tubes are typically closed <br /> at each end with plastic caps over Teflon or aluminum foil sheeting. The caps may be <br /> sealed with duct tape or similar material lacking inappropriate chemical compounds, The <br /> sealed sample is labeled and refrigerated for delivery, under strict chain-of-custody, to the <br /> analytical laboratory. <br /> Water <br /> Excavation water samples are not advised, because soil particles typically present may <br /> affect the sample. However, if required, water samples are collected either directly from <br /> the water surface, if accessible, by dipping the sampling container, or from a clean bailer <br /> or similar sampling device lowered into the excavation. Water samples may be collected <br /> from the excavating equipment bucket, if necessary. Depending on the intended <br /> analyses, 0.5 to 1-liter plastic or glass containers, or 40-milliliter glass, volatile organic <br /> analysis (VOA) vials, with "Teflon" septa, are typically used as sample containers. <br /> For volatile organic analyses, the water sample is decanted into each VOA vial in such <br /> a manner that there is no meniscus at the top of the vial. A cap is quickly secured to the <br /> top of the vial. The vial is inverted and gently tapped to see if air bubbles are present, <br /> If none are present, the vial is labeled and refrigerated for delivery, under strict chain-of- <br /> custody, to the analytical laboratory. Label information typically includes a unique sample <br /> identification number, job identification number, sampler identification, date, and time. <br /> ArrACHMENTMP•2WAY 1=4 <br />