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FIELD PROCEDURES <br /> The following section describes field procedures that were completed by Delta personnel in the performance of the <br /> tasks involved with this project. <br /> 1.0 HEALTH AND SAFETY PLAN <br /> Fieldwork performed by Delta and subcontractors at the site was conducted according to guidelines established in <br /> a Site Health and Safety Plan (SHSP). The SHSP is a document describes the hazards that may be encountered <br /> in the field and specifies protective equipment, work procedures, and emergency information. A copy of the SHSP <br /> was at the site and available for reference by appropriate parties during work at the site. <br /> 2.0 SOIL BORING AND SOIL SAMPLING PROTOCOL <br /> Soil borings and soil sampling was performed under the supervision of a Delta geologist. The soil borings were <br /> advanced using a truck-mounted hollow-stem auger drilling rig. <br /> To reduce the chances of cross-contamination between boreholes, all downhole drilling equipment was steam- <br /> cleaned between each boring. To reduce cross-contamination between samples, the split-barrel sampler was washed <br /> in a soap solution and double-rinsed between each sampling event. <br /> ,. Soil sampling was conducted in accordance with ASTM I586-84. Using this procedure, a 2-inch diameter, slit- <br /> barrel sampler (California-type sampler) lined with three 2-inch by 6-inch long brass sample tubes is driven into <br /> the soil at approximately 5-foot intervals by a 140-pound weight falling 30 inches. The number of blow counts <br /> required to advance the sample 18 inches was recorded at each sample interval. <br /> Upon recovery, a portion of the soil sample was placed in a plastic bag and sealed for later screening with an hNu <br /> type photoionization detector (PID). Another portion of the soil sample was used for classification and description. <br /> One of the brass tubes was sealed and stored at approximately 4°C for transport to the laboratory. After the soil <br /> samples, placed in a plastic bags, were allowed to warm, inducing volatilization of petroleum hydrocarbon vapors, <br /> the headspace vapors were screened with the organic vapor meter. The highest observed readings were then <br /> recorded on the boring logs. <br /> 3.0 GROUND WATER DEPTH DETERMINATION <br /> Depth to ground water was measured to the nearest 0.01 foot using an electronic hand held water level indicator. <br /> The tip of the probe was examined to determine whether a product sheen was present. <br /> LRP083.TA <br />