Carbon stable isotope fractionation of tetrachloroethene (PCE) during reductive dechlorination by whole cells and crude extracts of Sulfurospirillum multivorans and Desulfitobacterium sp. strain PCE-S and the abiotic reaction with cyanocobalamin (vitamin B 12 ) was studied. Fractionation was largest during the reaction with cyanocobalamin with ␣C ؍ 1.0132. Stable isotope fractionation was lower but still in a similar order of magnitude for Desulfitobacterium sp. PCE-S (␣C ؍ 1.0052 to 1.0098). The isotope fractionation of PCE during dehalogenation by S. multivorans was lower by 1 order of magnitude (␣C ؍ 1.00042 to 1.0017). Additionally, an increase in isotope fractionation was observed with a decrease in cell integrity for both strains. For Desulfitobacterium sp. strain PCE-S, the carbon stable isotope fractionation factors were 1.0052 and 1.0089 for growing cells and crude extracts, respectively. For S. multivorans, ␣C values were 1.00042, 1.00097, and 1.0017 for growing cells, crude extracts, and the purified PCE reductive dehalogenase, respectively. For the field application of stable isotope fractionation, care is needed as fractionation may vary by more than an order of magnitude depending on the bacteria present, responsible for degradation.The chlorinated ethenes tetrachloroethene (PCE) and trichloroethene (TCE) have been used as solvents in the drycleaning industry and as metal degreasing agents and are among the most common groundwater contaminants due to spillage and leakage (12). The assessment of in situ biodegradation of groundwater contaminants is difficult since a decrease in the concentration can be a result of many factors, including dilution, sorption, and biological conversion. Monitoring and assessment of in situ microbial degradation activities of contaminants at polluted sites is therefore a major challenge. In the last few years, the application of stable isotope techniques has been suggested for assessment of the in situ biodegradation of contaminants (for a review, see references 17 and 33).Stable isotope fractionation of PCE and TCE has been observed under field conditions in contaminated aquifers as well as in laboratory studies by mixed microbial cultures and microcosms (2, 9, 39, 40); however, the factors affecting the isotope fractionation have not yet been studied systematically.Several factors may influence the degree of stable isotope fractionation, including biodegrading microorganisms, properties of the dehalogenating enzymes, and the reaction mechanism. Cobalamins are important cofactors of reductive dehalogenases in organisms capable of dehalorespiration (8,10,15,20,25,26). The microbial dehalogenation by cobalamin-containing dehalogenases has been proposed to proceed by alkylating a superreduced corrinoid containing a Co(I) species at the reactive site with the chloroethene (26). The chemical mechanism of the reductive dehalogenation of chlorinated ethenes catalyzed by cobalamin has been the subject of previous studies and has been suggested to occur via a single elect...