Abstract

Chlorinated ethenes are toxic groundwater contaminants. Although they can be dechlorinated by microorganisms, reductive dehalogenases, and their corrinoid cofactor, biochemical reaction mechanisms remain unsolved. This study uncovers a mechanistic shift revealed by contrasting compound-specific carbon (e13C) and chlorine (e37Cl) isotope effects between perchloroethene, PCE (e37Cl = −4.0‰) and cis-dichloroethene, cis-DCE (e37Cl = −1.5‰), and a pH-dependent shift for trichloroethene, TCE (from e37Cl = −5.2‰ at pH 12 to e37Cl = −1.2‰ at pH 5). Different pathways are supported also by pH-dependent reaction rates, TCE product distribution, and hydrogen isotope effects. Mass balance deficits revealed reversible and irreversible cobalamin-substrate association, whereas high-resolution mass spectrometry narrowed down possible structures to chloroalkyl and chlorovinyl cobalamin complexes. Combined experimental evidence is inconsistent with initial electron transfer or alkyl or vinyl complexes as shared intermediat...

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