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I <br /> Working To Restore Nature <br /> FIELD PROCEDURES <br /> Site Safety Plan <br /> The site safety plan describes the basic safety requirements for the drilling of soil borings <br />' at the work site. The safety plan is applicable to personnel of RESNA and to <br /> subcontractors of RESNA The representative from RESNA acts as the Site Safety Officer <br /> Personnel at the site are informed of the contents of the site safety plan before work began <br /> A copy of the plan is kept at the work site and is available for reference by appropriate <br /> parties during the work <br /> Drilling and Soil Sampling <br /> Before drilling, soil borings were started by hand-augering to a depth of approximately 5 <br /> feet to reduce the risk of damaging underground structures The soil borings were drilled <br /> using a truck-mounted drill rig equipped with 8-inch-diameter,continuous-flight,hollow-stem <br /> augers. The drilling was performed under the guidance of a field geologist Relatively <br /> undisturbed soil samples were collected from each boring at 5-foot intervals or other <br /> appropriate intervals from the ground surface to the total boring depth, identified using <br /> visual and manual methods, and classified according to the Unified Soil Classification <br /> System. <br /> Soil samples were collected using a California-modified, split-spoon sampler equipped with <br /> clean brass sleeves Samples were collected by drilling the boring to a point gust above the <br /> sampling depth and then driving the sampler into the soil through the hollow center of the <br /> auger The split-spoon sampler was driven 18 inches with a standard 140-pound hammer <br /> dropped 30 inches. The number of blows required to drive the sampler each successive 6- <br /> inch interval was counted and recorded on the field boring log to give an indication of soil <br /> consistency. <br /> Soil samples were evaluated for relative levels of hydrocarbons using a photoiomzation <br /> detector (PID) Field instruments such as the PID provide a preliminary assessment of the <br /> total volatile constituents and cannot identify or distinguish between individual compounds <br /> The PID may also be affected by moisture, fluctuations in the air and/or soil temperature, <br /> and the specific soil type Subjective evidence of hydrocarbons such as soil discoloration or <br /> obvious odor were noted <br /> Soil samples collected for possible chemical analysis were promptly sealed with aluminum <br /> foil, plastic caps, and tape They were then labeled and placed in iced storage for transport <br /> to the analytical laboratory A Chain of Custody Record was initiated by the field geologist <br /> and accompanied the samples to the laboratory <br /> 0820ccar <br /> 3804$-7 <br />