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10-03-1988 Planning Packet
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10-03-1988 Planning Packet
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f thref gallons per <br />e pump. The pump <br />lats will maintain a <br />I pump will route <br />r dissolved volatile <br />and two 200 gallon <br />ximately 350 cubic <br />nd and receives an <br />be directed to the <br />obtained prior to <br />ked wood security, <br />We anticipate that a <br />(r the initial month. <br />01 begins operation, <br />ts are returned and <br />r approval has been <br />md effluent will be <br />»d for EPA 601/602 <br />will be less than one <br />mpling of discharge. <br />-l.MW-2,MW-2D. <br />ion. All other wells at <br />rarded to the MWCC <br />PCA for review and <br />i <br />V f\ <br />4PiiiP <br />•0-J <br />■ <br />.4 <br />l4% <br />- k . -tt. i .* . r <br />comiBenL <br />< 6 Sail »«i SannnM <br />We propose to thinspreakl contaminated soil eaavated during the trench installation. An ideal ar«i for <br />thinspreading b along the southern edge of the proposed trench (Figure 4). There are no residential <br />buildings or industrial buUdings within 200 feet of thb area. In addition, the prevailing winds are <br />westerly across thb area and there are no downwind dwellings or structures for approximately 2,500 <br />feet. <br />We anticipate that approximately 500 to 700 yards of contaminated soil will be excavated during the <br />installation process. The soil will be stockpUed on-site and covered with plastic immediately after <br />excavation. Samples will be collected and forwarded to PACE Laboratories for analysb (EPA 601 /602). <br />The sod will be spread along the southern edge of the trench approximately six inches thick. The soil <br />will be aerated with a field dbc or comparable equipment one time each month until it becomes froien. <br />Aeration tillage would resume again the following spring. <br />Soil samples will be collected 30 days after thinspreading has beer completed. After the initial month, <br />we propose sampling quarterly. Samples will be analyzed for EPA 601/602 parameters. After the first <br />year the sampling schedule wiU be reevaluated. All analytical and operational reports will be forwarded <br />to the MPCA for review. <br />6.0 METHODS ANT) PROCEDURES <br />^■1 Sail Samcllna <br />SoU sampling was done in accordance with ASTM:D 1586-84. Using this procedure, a 2 inch O.D. split <br />barrel sampler b driven into the soil by a 140 pound weight falling 30 inches. After an initial set of 6 <br />inches, the number of blows required to drive the sampler an additional 12 inches b known as the <br />penetration resbtance, or the "N- value. The -N" value b an index of the relaUve density of <br />cohesionless soib and the consbtcncy of cohesive soib. <br />6.1 Soil aassincaUttii <br />As the samples were obtained in the field, they were vbually and manually classified by the crew chief <br />in accordance with ASTM:D 2488-84. Represenative portions of the samples were then returned to the <br />laboratory for further examination and for verification of the field classification. Logs of the borings <br />indicating the depth and identification of the various strata, the N value, water level information and <br />pertinent information regarding the method of maintaining and advancing the drill hole were made. <br />i ■■ <br />Charts iUustrati <br />boring logs wei <br />6.3 Water Lei! <br />All ground wa <br />indicates when <br />lowering the d< <br />measuring the <br />recorded to the <br />0.04 foot. <br />^,4 Wmter Sai <br />All monitorini <br />following pron <br />Step 1: <br />Step 2. <br />Step 3: <br />Step 4: <br />Step 5: <br />Upon complet: <br />records includ' <br />hazard, sampli <br />containers, an: <br />The chain of <br />laboratory, the <br />identification <br />turned over tc
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