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i <br /> ENVIRONMENTAL SCIENCE & ENGINEERING, INC. <br /> CONCORD, CALIFORNIA OFFICE <br /> STANDARD OPERATING PROCEDURE NO. 1 <br /> FOR SOIL BORINGS AND SOIL SAMPLING WITH HOLLOW-STEM AUGERS <br /> IN UNCONSOLIDATED FORMATIONS <br /> Environmental Science&Engineering,Inc.(ESE)typically drills soil borings using a truck-mounted,continuous- <br /> flight, hollow-stem auger drill rig. The 'dell rig is owned and operated by a drilling company possessing a valid <br /> State of California C-57 license. The soil borings are conducted under the direct supervision and guidance of <br /> an experienced ESE geologist. The ESE geologist logs each borehole during drilling in accordance with the <br /> Unified Soil Classification System (USCS). Additionally, the ESE geologist observes and notes the soil color, <br /> relative density or stiffness, moisture content, odor (if obvious) and organic content (if present). The ESE <br /> geologist will record all observations on geologic boring logs. <br /> Soil samples are collected during drilling at a minimum of five-foot intervals by driving an 18-inch long Modified <br /> California Split-spoon sampler(sampler),'lined with new,thin-wall brass sleeves,through the center of and ahead <br /> of the hollow stem augers, thus collecting a relatively undisturbed soil sample core. The brass sleeves are <br /> typically 2-inches in diameter and 6-inches in length. The sampler is driven by dropping a 140-pound hammer <br /> 30-inches onto rods attached to the top of the sampler, Soil sample depth intervals and the number of hammer. <br /> blows required to advance the sampler each six-inch interval are recorded by the ESE geologist on geologic <br /> boring logs. The ends of one brass sleeve are covered with Teflon sheeting,then covered with plastic end caps. <br /> The end caps are sealed to the brass sleeve using duct tape. Each sample is then labeled and placed on ice in <br /> a cooler for transport under chain of custody documentation to the designated analytical laboratory. A portion <br /> of the remaining soil in the sampler is placed in either a new Ziploe* bag or a clean Mason Jar* and set in <br /> direct sunlight to enhance the volatilization of any Volatile Organic Compounds (VOCs) present in the soil. <br /> After approximately 15-minutes that sample is screened for VOCs using a photoionization detector(PID). The <br /> PID measurements will be noted on they geologic boring logs. The PID provides qualitative data for use in <br /> selecting samples for laboratory analysis. Soil samples from the saturated zone(beneath the ground-water table) <br /> are collected as described above, are riot screened with the PID, and are not submitted to the analytical <br /> laboratory. The samples from,the saturated zone'are used for descriptive purposes. Soil samples from the <br /> saturated zone may be retained as described above.for physical analyses (grain size, permeability and porosity <br /> testing). <br /> p , <br /> If the soil boring is not going to be completed as.a well,then the boring is typically terminated upon penetrating <br /> the saturated soil horizon or until a predetermined interval of soil containing no evidence of contamination is. <br /> penetrated. This predetermined interval is typically:based upon site specific regulatory or client guidelines. The <br /> boring is then backfilled using either neat cement, neat cement and bentonite powder mixture (not exceeding . <br /> 5% bentonite), bentonite pellets, or a sand and cement mixture (not exceeding a 2:1 ratio of sand to cement). <br /> However, if the boring is to be completed as a monitoring well, then the boring is continued until either a <br /> competent, low estimated-permeability, lower confining soil layer is found or 10 to 15-feet of the saturated soil <br /> horizon is penetrated,whichever occurs first. If a low estimated-permeability soil layer is found,the soil boring <br /> will be advanced approximately five-feet into that layer to evaluate its competence as a lower confining layer, <br /> prior to the termination of that boring. <br /> All soil sampling equipment is cleaned between each sample collection event using an Alconoxo detergent and <br /> tap water solution followed by a tap water rinse. Additionally, all drilling equipment and soil sampling f <br /> equipment is cleaned between borings,using a high pressure steam cleaner,to prevent cross-contamination. All <br /> wash and rinse water is collected and contained onsite in Department of Transportation approved containers <br /> (typically 55-gallon drums) pending laboratory analysis and proper disposal/recycling. <br /> a <br /> ' F <br />