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' I <br />. ENCLOSURE A <br /> SOIL AND GROUND WATER SAMPLING TECHNIQUES <br /> Proper sampling techniques were followed to assure that samples represented actual field <br /> conditions and that samples were labeled, preserved, and transported properly to retain sample <br /> integrity This exhibit describes procedures followed by Acton • Mickelson • van Dam, Inc <br /> (AMV), during collection of samples of subsurface soil and ground water Sampling guidance <br /> documents from the American Society of Testing and Materials (ASTM), U S Environmental <br /> Protection Agency (EPA), and California Department of Health Services (DHS) were followed <br /> for all sampling procedures Actual sampling procedures employed were based on field <br /> conditions and may differ from those described here <br /> 1.0 EXPLORATION BORING/SOIL SAMPLING PROCEDURES <br /> Soil borings and soil sampling were performed under the direction of an AMV geologist The <br /> soil borings were advanced using a truck-mounted, hollow-stem auger drill ng <br />• Soil samples were collected at 5-foot vertical intervals Soil sampling was done in accordance <br /> with ASTM 1586-84 Using this procedure, three 2-inch-diameter, 6-inch-length, brass tubes <br /> were placed in a California-type split-barrel sampler The sampler was driven into the soil by <br /> a 140-pound weight falling 30 inches After an initial set of 6 inches, the number of blows <br /> required to drive the sampler an additional 12 inches is known as penetration resistance, or the <br /> "N" value The "N" value was used as an empirical measure of the relative density of <br /> cohensionless soils and the consistency of cohesive soils <br /> Upon recovery of the split-barrel sampler, the brass tubes containing the soil were removed <br /> The ends of one of the three brass tubes were sealed with Teflon tape and plastic end caps The <br /> sample was labeled with an identification number, time, date, location, and requested laboratory <br /> analysis The sample was placed in a plastic bag and stored at approximately 4° Celsius (C) in <br /> an ice chest for transport to the laboratory Sample custody procedures outlined in Section 5 0 <br /> of this exhibit were followed This was performed for each sample collection <br /> Soil in one of the brass tubes was extracted upon recovery, placed in a plastic bag, and sealed <br /> for later screening for organic vapors using a photoionization detector (PID) or a flame <br /> ionization detector (FID) The remaining portion of the soil sample was examined and a <br /> complete log of soil conditions was recorded on a soil boring log (Enclosure A) using the <br /> Unified Soil Classification System (Enclosure B) The soil was examined for grain size, color, <br /> and moisture content <br /> The split-barrel sampler was cleaned to prevent cross-contamination for each sampling interval <br /> using procedures described in Section 3 0 <br />