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Mr. Samuel Savig <br /> August 22,2001 JI <br /> Page 2 of 3 <br /> Drilling,Well Construction and Soil Sampling <br /> I Three soil borings will be drilled to a depth of approximately 22 to 25 feet bgs at the site at the <br /> approximate locations shown on Figure 2. The borings will be drilled in order to collect soil samples and <br />�. to install groundwater monitoring wells. A drilling contractor with a California C-57 license will <br /> advance borings using a rig equipped with 8" diameter hollow stem augers. The borings will be <br /> completed as groundwater monitoring wells and will be constructed of 2-inch diameter, Schedule 40 i <br /> PVC blank and slotted casing. The designated screened interval will consist of 0.010" machine-slotted <br /> casing. The wells will be screened from approximately 5 feet above to approximately 15 feet below the i <br /> first encountered groundwater. The filter pack will consist of No. 2/12 Monterey sand from the bottoms J <br /> of the wells to approximately 2 feet above the tops of the screens. The remaining annular space will be <br /> completed with 2 feet of hydrated bentonite overlain by neat cement grout and/or concrete. Each well <br /> will be fitted at the surface with a locking cap and water tight; traffic rated well box anchored with a <br /> Iconcrete apron. <br /> Drilling and well installation will be conducted under the supervision of California Registered Geologist, 3 <br /> E The borings will be sampled at 5-foot intervals for soil classification and possible analytical testing. All <br /> soil samples will be classified in accordance with ASTM Designation D2488-90, which is equivalent to <br /> the Unified Soil Classification System. Soil samples at 5-foot intervals will be subjectively evaluated for <br /> the presence of contamination using a photo-ionization detector (PID) or equivalent. Up to three soil <br /> samples per boring, dependent upon field evidence of contamination and/or changes in lithology, will be <br /> k submitted for laboratory analysis. Soil samples selected for analysis will be immediately capped, labeled y <br /> and placed in an ice chest for transport to the laboratory. <br /> Sail samples selected for analysis will be submitted to a State-cdrtified laboratory under chain of custody <br /> protocol. The samples will be analyzed for TPHg, total petroleum hydrocarbons as diesel (TPHd), and <br /> total petroleum hydrocarbons as kerosene (TPHk) using EPA Method 8015; benzene, toluene, <br /> ethylbenzene, and xylenes (BTEX) using EPA method 8020; and total lead using EPA method <br /> 3050/7420. In addition, one soil sample pre boring (the one with the greatest field evidence of <br /> contamination)will be analyzed oxygenated gasoline additives using EPA Method 8260. <br /> Drill cuttings will be placed on and covered with plastic sheeting or placed in DOT approved 55-gallon <br /> drums. Water generated from equipment decontamination will be contained in labeled DOT approved i <br /> drums. The soil and/or drums will be stored on site pending laboratory results and the development of <br /> disposal options. <br /> Well Development, Surveying and Groundwater Sampling I <br /> The elevation of the top of the casing in each well will be surveyed to an accuracy of 0.01 feet. After <br /> well completion, an experienced field technician will measure static depth to water and then develop the <br /> wells by pumping and surging until turbidity is minimized. A 'minimum of five casing volumes will be <br /> purged from each well during development. <br /> Groundwater samples will be collected after pH, temperature, and electrical conductivity have stabilized <br /> and the wells have recharged to minimum of 80% -of staticR levels. Groundwater samples will be <br /> G:1Dam1G ROUNDZEI'I'HORPEISo=u\WPMWS.doc <br /> y <br /> �� J <br />