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CAMBRIA <br /> STANDARD FIELD PROCEDURES FOR MONITORING WELLS <br /> This document presents standard field methods for drilling and sampling soil borings and installing,developing <br /> and sampling ground water monitoring wells. These procedures are designed to comply with Federal, State and <br /> local regulatory guidelines, Specific field procedures are summarized below. <br /> SOIL BORINGS <br /> Objectives <br /> Soil samples are collected to characterize subsurface lithology, assess whether the soils exhibit obvious <br /> hydrocarbon or other compound vapor or staining, and to collect samples for analysis at a State-certified <br /> laboratory. All borings are logged using the Unified Soil Classification System by a trained geologist working <br /> under the supervision of a California Registered Geologist(RG)or a Certified Engineering Geologist(CEG). <br /> Soil Boring and Sampling <br /> Soil borings are typically drilled using hollow-stem augers or push technologies such as the Geoprobe. Soil <br /> samples are collected at least every five ft to characterize the subsurface sediments and for possible chemical <br /> analysis. Additional soil samples are collected near the water table and at lithologic changes. Samples are <br /> collected using lined split-barrel or equivalent samplers driven into undisturbed sediments at the bottom of the <br /> borehole. <br /> Drilling and sampling equipment is steam-cleaned prior to drilling and between borings to prevent cross- <br /> contamination, Sampling equipment is washed between samples with trisodium phosphate or an equivalent EPA- <br /> approved detergent. <br /> Sample Analysis <br /> Sampling tubes chosen for analysis are trimmed of excess soil and capped with Teflon tape and plastic end caps. <br /> Soil samples are labeled and stored at or below 4°C on either crushed or dry ice,depending upon local regulations. <br /> Samples are transported under chain-of-custody to a State-certified analytic laboratory. <br /> Field Screening <br /> One of the remaining tubes is partially emptied leaving about one-third of the soil in the tube. The tube is capped <br /> with plastic end caps and set aside to allow hydrocarbons to volatilize from the soil. After ten to fifteen minutes, <br /> a portable photoionization detector (PID) measures volatile hydrocarbon vapor concentrations in the tube <br /> headspace, extracting the vapor through a slit in the cap. PID measurements are used along with the field <br /> observations,odors,stratigraphy and ground water depth to select soil samples for analysis. <br /> Water Sampling <br /> Water samples,if they are collected from the boring,are either collected using a driven Hydropunch type sampler <br /> or are collected from the open borehole using bailers. The ground water samples are decanted into the appropriate <br /> containers supplied by the analytic laboratory. Samples are labeled,placed in protective foam sleeves,stored on <br /> Page 1 of 3 <br />