1,2-Dichloropropane (1,2-D), a widespread groundwater contaminant, can be reductively dechlorinated to propene by anaerobic bacteria. To shed light on the populations involved in the detoxification process, a comprehensive 16S rRNA gene-based bacterial community analysis of two enrichment cultures derived from geographically distinct locations was performed. Analysis of terminal restriction fragments, amplicons obtained with dechlorinator-specific PCR primers, and enumeration with quantitative real-time PCR as well as screening clone libraries all implied that Dehalococcoides populations were involved in 1,2-D dechlorination in both enrichment cultures. Physiological traits (e.g., dechlorination in the presence of ampicillin and a requirement for hydrogen as the electron donor) supported the involvement of Dehalococcoides populations in the dechlorination process. These findings expand the spectrum of chloroorganic compounds used by Dehalococcoides species as growth-supporting electron acceptors. The combined molecular approach allowed a comparison between different 16S rRNA gene-based approaches for the detection of Dehalococcoides populations.The short-chain chlorinated aliphatic compound 1,2-dichloropropane (1,2-D) has been used as a fumigant to fight rootparasitic nematodes in the production of high-value crops, as an insecticide, and in numerous industrial applications (17). Although 1,2-D is no longer employed in agricultural applications and its industrial use has been reduced, these practices lead to substantial groundwater contamination. Thus, many sites with 1,2-D concentrations exceeding the U.S. Environmental Protection Agency enforced maximum concentration level of 5 ppb (www.epa.gov/safewater/dwh/c-voc.html) exist. Due to the toxicity (and potential for carcinogenicity) of 1,2-D to the liver, kidneys, adrenal glands, bladder, and gastrointestinal and respiratory tracts, its presence in the environment is of genuine public concern, and many of the existing contaminated sites require remedial action.No naturally occurring aerobic microbial pathways that efficiently transform 1,2-D to nontoxic products have been described (11), although enzymes that transform polychlorinated propanes were generated by in vitro molecular evolution (3, 32). Most of the contamination with 1,2-D has occurred in oxygen-limited or anaerobic subsurface environments, where reductive processes are more probable (17, 34). In a previous study, the reductive dechlorination (i.e., hydrogenolysis) of 1,2-D to monochlorinated propanes and subsequent dehydrochlorination to propene was demonstrated in microcosms derived from river sediment (17). Interestingly, in sediment-free, nonmethanogenic enrichment cultures derived from these microcosms, only vicinal reduction (dichloroelimination) of 1,2-D to propene without the intermediate formation of monochlorinated propanes occurred (17). Hydrogen consumption threshold measurements provided circumstantial evidence for the presence of populations in the enrichment cultures that gain energy ...