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Hull & Associates Inc. <br />Page 15 <br />APPENDIX 3: TECHNOLOGY DISCUSSION <br />The options available for a cost-effective and reliable technology to treat chlorinated <br />hydrocarbon contaminants such as tetrachloroethene (PCE), trichloroethene (TCE), cis-1,2- <br />dichlorethene (cis-1,2-DCE), and carbon tetrachloride in groundwater have in recent years <br />moved away from traditional pump -and -treat processes, especially in cases where: <br />• NAPL, micro -emulsions or high concentration adsorbed materials are present leading to <br />high dissolved phase concentrations. <br />• Access to groundwater is restricted by surface structures or uses. <br />• Local restrictions forbid the implementation of other available technologies such as air <br />sparging or natural attenuation. <br />• Pump and Treat technologies have been applied, but have reached asymptotic removal <br />rates. <br />• Contamination is extensive and concentrations are too high for risk based closure but <br />otherwise relatively low (typically 100-7500 ppb). <br />• The migration of dissolved Chlorinated Aliphatic Compounds (CAHs) across property <br />boundaries or into adjacent surface water presents a long-term remediation <br />requirement. <br />• The vertical migration of free phase CAHs (DNAPL) into underlying drinking water <br />aquifers is a concern. <br />The environmental chemistry of a site in part determines the rate of biodegradation of <br />chlorinated solvents at that site. The initial metabolism of chlorinated solvents such as <br />chloroethenes and chloroethanes in ground water usually involves a biochemical process <br />described as sequential reductive dechlorination. The occurrence of different types and <br />concentrations of electron donors such as native organic matter, and electron acceptors such as <br />oxygen and chlorinated solvents, determines to a large degree the extent to which reductive <br />dechlorination occurs during the natural attenuation of a site. To accelerate the natural <br />processes, ZVI and enhanced microbial dechlorination processes are proposed to be utilized at <br />the site. The utilization of coenzymes, oxygen scavengers and nutrients insures that little or no <br />lag phase in the process is experienced and that the most efficient pathways may be utilized. <br />Program Elements <br />Nutrient: Critical to the sustained microbial activity and general microbial health is sufficient bio <br />available nutrient. IET has incorporated nitrogen and o-POa into the remedial program such <br />that organelle and ATP-ADP formation is not limited throughout the microbial respiratory <br />process. <br />