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AW <br /> t <br /> Du Pont HLR 599-87 <br /> release of carbon dioxide (this timr. was ehartensd to 30 min* for the first <br /> soil slurry, M-18779). The plastic buckets containing the filter paper were <br /> clipped into 10 mL of scintillation fluid (Aquasol) end were counted in a <br /> TH Analytic Mark III (6882) liquid scintillation system to obtain <br /> disintegrations per minute (DPH) for each bottle. The percent of total <br /> labeled xylene mineralized was determined by dividing the corrected DPH <br /> (minus the formaldehyde control) from each test bottle by the total DPM10 <br /> (379,804) added and eultiplying.by 100. <br /> A small separate experiment was performed to cheek whether another CO <br /> trapping chemical mould provide better results at later time periods for he <br /> groundwater eaample. The above procedure was followed except that 0.2 mi. of a <br /> 5 6N solution of NON was added to the filter in place of PEA. Treatments 5 <br /> and 14 (Table 2) were tested in groundwater (aa received) using this method. <br /> r. Scale-up Study Using Adenoaine Triphosphate and Chemical Analyses <br /> Nutrient combinations and concentrations were chosen from the above <br /> E studies and repeated on a scaled-up basis (100X). Nutrient treatments 5 and <br /> 9 (Table 2) were selected for the scale-up studies. ' Nutrients were added to <br /> two liter media battles. A 25: soil slurry (M-18774) was prepared for a <br /> total volume of 1666 mL. A mixture of benzene, toluene, and xylene (in equal <br /> { volumes) was added (final concentration of 0.21 ppm) and a Teflon® lined cap <br /> with three sample ports was tightly fitted to the bottle. This come mixture <br /> of chemicals was also added to the battles on day 9. Subsemples were <br /> collected on days 0, 2, 5, 7, 9, 12, and 14 of the water phase and the soil <br /> azurry by attaching s syringe to the sample port and removing small aliquots. <br /> Equal amounts of the.soil slurry and an ATP releasing agent were vortexed <br /> together and the particulate metier brought out of solution by <br /> centrifugation. The supernatant was evaluated for ATP. The water samples <br /> mere directly tested without additional manipulation. Fluctuations in total <br /> f biomass were determined by measuring mdenceine triphosphate (ATP) levels. <br /> E All living cella contain ATP while ATP from dead and dying cella in rapidly <br /> hydrolyzed. Therefore, measurement of ATP is a good indicator of the <br /> presence of microorganisms. The ATP eras measured using the LINAC Biocounter® <br /> and a standard curve wga made with a commercial source of ATP. Twenty-five <br /> williliter sampled were collected at the some time periods as above and <br /> placed in mmberglass vials with Teflon$ lined caps and no air apace. These <br /> samples were stored in the refrigerator until time of analysis st the end of <br /> the experiment by Artesian Laboratories, Inc. The analyses were performed by <br /> extracting the soil slurries with methanol. <br /> Ij <br /> 4 <br />