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      Coupling Aggressive Mass Removal with Microbial Reductive Dechlorination for Remediation of DNAPL Source Zones: A Review and Assessment

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          Abstract

          The infiltration of dense non-aqueous-phase liquids (DNAPLs) into the saturated subsurface typically produces a highly contaminated zone that serves as a long-term source of dissolved-phase groundwater contamination. Applications of aggressive physical–chemical technologies to such source zones may remove > 90% of the contaminant mass under favorable conditions. The remaining contaminant mass, however, can create a rebounding of aqueous-phase concentrations within the treated zone. Stimulation of microbial reductive dechlorination within the source zone after aggressive mass removal has recently been proposed as a promising staged-treatment remediation technology for transforming the remaining contaminant mass. This article reviews available laboratory and field evidence that supports the development of a treatment strategy that combines aggressive source-zone removal technologies with subsequent promotion of sustained microbial reductive dechlorination. Physical–chemical source-zone treatment technologies compatible with posttreatment stimulation of microbial activity are identified, and studies examining the requirements and controls (i.e., limits) of reductive dechlorination of chlorinated ethenes are investigated. Illustrative calculations are presented to explore the potential effects of source-zone management alternatives. Results suggest that, for the favorable conditions assumed in these calculations (i.e., statistical homogeneity of aquifer properties, known source-zone DNAPL distribution, and successful bioenhancement in the source zone), source longevity may be reduced by as much as an order of magnitude when physical–chemical source-zone treatment is coupled with reductive dechlorination.

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          Most cited references140

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          Groundwater contamination: pump-and-treat remediation

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            Anaerobic microbial dehalogenation.

            The natural production and anthropogenic release of halogenated hydrocarbons into the environment has been the likely driving force for the evolution of an unexpectedly high microbial capacity to dehalogenate different classes of xenobiotic haloorganics. This contribution provides an update on the current knowledge on metabolic and phylogenetic diversity of anaerobic microorganisms that are capable of dehalogenating--or completely mineralizing--halogenated hydrocarbons by fermentative, oxidative, or reductive pathways. In particular, research of the past decade has focused on halorespiring anaerobes, which couple the dehalogenation by dedicated enzyme systems to the generation of energy by electron transport-driven phosphorylation. Significant advances in the biochemistry and molecular genetics of degradation pathways have revealed mechanistic and structural similarities between dehalogenating enzymes from phylogenetically distinct anaerobes. The availability of two almost complete genome sequences of halorespiring isolates recently enabled comparative and functional genomics approaches, setting the stage for the further exploitation of halorespiring and other anaerobic dehalogenating microbes as dedicated degraders in biological remediation processes.
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              Detoxification of vinyl chloride to ethene coupled to growth of an anaerobic bacterium.

              Tetrachloroethene (PCE) and trichloroethene (TCE) are ideal solvents for numerous applications, and their widespread use makes them prominent groundwater pollutants. Even more troubling, natural biotic and abiotic processes acting on these solvents lead to the accumulation of toxic intermediates (such as dichloroethenes) and carcinogenic intermediates (such as vinyl chloride). Vinyl chloride was found in at least 496 of the 1,430 National Priorities List sites identified by the US Environmental Protection Agency, and its precursors PCE and TCE are present in at least 771 and 852 of these sites, respectively. Here we describe an unusual, strictly anaerobic bacterium that destroys dichloroethenes and vinyl chloride as part of its energy metabolism, generating environmentally benign products (biomass, ethene and inorganic chloride). This organism might be useful for cleaning contaminated subsurface environments and restoring drinking-water reservoirs.
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                Author and article information

                Journal
                Environ Health Perspect
                Environmental Health Perspectives
                National Institute of Environmental Health Sciences
                0091-6765
                April 2005
                8 December 2004
                : 113
                : 4
                : 465-477
                Affiliations
                1Environmental and Water Resources Engineering Program, University of Michigan, Ann Arbor, Michigan, USA
                2Department of Civil and Environmental Engineering, Tufts University, Medford, Massachusetts, USA
                3School of Civil and Environmental Engineering, Georgia Institute of Technology, Atlanta, Georgia, USA
                Author notes
                Address correspondence to L.M. Abriola, Department of Civil and Environmental Engineering, Tufts University, 105 Anderson Hall, 200 College Ave., Medford, MA 02155 USA. Telephone: (617) 627-3237. Fax: (617) 627-3819. E-mail: linda.abriola@tufts.edu

                This article is based on a presentation at the conference “Bioremediation and Biodegradation: Current Advances in Reducing Toxicity, Exposure and Environmental Consequences” ( http://www-apps.niehs.nih.gov/sbrp/bioremediation.html) held 9–12 June 2002 in Pacific Grove, California, and sponsored by the NIEHS Superfund Basic Research Program. The overall focus of this conference was on exploring the research interfaces of toxicity reduction, exposure assessment, and evaluation of environmental consequences in the context of using state-of-the-art approaches to bioremediation and biodegradation. The Superfund Basic Research Program has a legacy of supporting research conferences designed to integrate the broad spectrum of disciplines related to hazardous substances.

                This research was sponsored by the U.S. Environmental Protection Agency Great Lakes & Mid-Atlantic Hazardous Substance Research Center (R-825540), Michigan Department of Environmental Quality Emergency Response Division (Y80011), Strategic Environmental Research and Development Program (contract DACA72-00-C-0023), and a National Science Foundation CAREER award to F.E.L. (award 0090496). The content of this manuscript has not been subject to agency review and does not necessarily represent the views of the agency sponsors.

                The authors declare they have no competing financial interests.

                Article
                ehp0113-000465
                10.1289/ehp.6932
                1278488
                15811838
                68e5b8b0-53e1-44b5-92e5-19a63bfc6ada
                This is an Open Access article: verbatim copying and redistribution of this article are permitted in all media for any purpose, provided this notice is preserved along with the article's original DOI.
                History
                : 23 December 2003
                : 16 August 2004
                Categories
                Research
                Articles

                Public health
                aquifer,source zone,innovative technologies,post-treatment,dnapl,physical–chemical,remediation,microbial degradation,reductive dechlorination,bioremediation

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