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T_ 3,:r <br /> _ sr� <br /> r•m <br /> SG <br /> D <br /> Color Spot, Inc. Cl <br /> February 14, 1990 (881680 <br /> rr- <br /> APPENDIX C <br /> i,, <br /> SAMPLING AND ANALYTICAL PROTOCOLS <br /> i <br /> k <br /> r. <br /> GROUND WATER SAMPLING <br /> Four existing domestic ground water wells were sampled by purging the <br /> E ! sample cock for two to three minutes and completely filling the sample container <br /> with water, to ensure no headspace in the container to prevent volatilization of <br /> s the sample. The. samples from each well were collected in two 40-m1 VOA vials and <br /> a l: liter amber glass bottle. The VOA vials were preserved with sodium azide or <br /> sodium hydrogen sulfate and were used for analyses of organic contaminants. The <br /> I liter amber glass bottles were preserved with nitric acid and were used for <br /> b �-j analyses for total lead. <br /> Immediately after the samples were collected, the containers were <br /> sealed,. without headspace, labeled, taped shut, secured in guard bottles (VOA <br /> vials), and vlaced in an ice chest containing artificial ice for preservation. <br /> :.� Chain-of-custody documentation accompanied the ground water samples. from <br /> A i"'� collection until delivery to Coast to Coast Analytical Services (CCAS) in Goleta, <br /> California. <br /> SOIL SAMPLING <br /> t <br /> Six confirmatory soil samples were collected from the calls and base <br /> of the resulting excavations following the completion of the soils removal <br /> # program. Each samples was collected in 3-inch long, 2.5-inch diameter, stainless <br /> steel sampling sleeves. Following the collection of each sample, both ends of <br /> the sleeve were sealed with Teflon sheets and airtight plastic caps, taped, <br /> labeled, and placed in a cE-oler artificially cooled for preservation. All <br /> �M ; ! samples were delivered to CCAS accompanied by chain-of-custody documentation. <br /> After the samples was obtained, additional soil was collected from i <br /> the sampler and monitored for organic vapors using a photoionization detector <br /> (PID). A stainless steel sample sleeve with plastic end caps was filled <br /> ` - - ---- <br /> approximately-one-third--full-with-soil--from-the-sampler-and-shaken with-the-end----- --r: -- <br /> cap covered to liberate soil vapors into the void space. The soil vapor was then <br /> iyI measured for volatile hydrocarbon compounds by inserting the PID probe into a <br /> hole in the end cap. The sample sleeve and two end caps were cleaned between <br /> ' each use with a nonphosphate detergent solution and rinsed with potable water, ! <br /> and air dried to prevent cross-contamination. <br /> kk1 <br /> l <br /> r�y <br /> 4 }- ., <br /> j <br />