Two tetrachlorethene (PCE)-dechlorinating populations, designated strains BB1 and BRS1, were isolated from pristine river sediment and chloroethene-contaminated aquifer material, respectively. PCE-to-cis-1,2-dichloroethene-dechlorinating activity could be transferred in defined basal salts medium with acetate as the electron donor and PCE as the electron acceptor. Taxonomic analysis based on 16S rRNA gene sequencing placed both isolates within the Desulfuromonas cluster in the ⊠subdivision of the Proteobacteria. PCE was dechlorinated at rates of at least 139 nmol min Ű1 mg of protein Ű1 at pH values between 7.0 and 7.5 and temperatures between 25 and 30°C. Dechlorination also occurred at 10°C. The electron donors that supported dechlorination included acetate, lactate, pyruvate, succinate, malate, and fumarate but not hydrogen, formate, ethanol, propionate, or sulfide. Growth occurred with malate or fumarate alone, whereas oxidation of the other electron donors depended strictly on the presence of fumarate, malate, ferric iron, sulfur, PCE, or TCE as an electron acceptor. Nitrate, sulfate, sulfite, thiosulfate, and other chlorinated compounds were not used as electron acceptors. Sulfite had a strong inhibitory effect on growth and dechlorination. Alternate electron acceptors (e.g., fumarate or ferric iron) did not inhibit PCE dechlorination and were consumed concomitantly. The putative fumarate, PCE, and ferric iron reductases were induced by their respective substrates and were not constitutively present. Sulfide was required for growth. Both strains tolerated high concentrations of PCE, and dechlorination occurred in the presence of free-phase PCE (dense non-aqueous-phase liquids). Repeated growth with acetate and fumarate as substrates yielded a BB1 variant that had lost the ability to dechlorinate PCE. Due to the 16S rRNA gene sequence differences with the closest relatives and the unique phenotypic characteristics, we propose that the new isolates are members of a new species, Desulfuromonas michiganensis, within the Desulfuromonas cluster of the Geobacteraceae.The first reported anthropogenic production of tetrachloroethene (PCE) dates back to 1821, when Faraday produced PCE by thermal decomposition of hexachloroethane (15). Starting at the beginning of the 20th century, increasing amounts of PCE and trichloroethene (TCE) were manufactured due to the extensive use of these compounds in industry, in the military, and in private households, mainly as nonflammable solvents (summarized in reference 9). This widespread use, along with careless handling and storage, made chlorinated ethenes abundant groundwater pollutants. Often, PCE and TCE contamination coincided with spills of other organic compounds, such as crude oil constituents, other solvents (often seen at industrial and military sites), or starch (at dry cleaning operations). Aerobic microorganisms rapidly degrade the nonchlorinated contaminants, thereby depleting oxygen. Under anaerobic conditions PCE and TCE can be used as alternate growth-supportin...