Contamination of soils and sediments with the highly persistent hexachlorocyclohexanes (HCHs) continues to be a threat for humans and the environment. Despite the existence of bacteria capable of biodegradation and cometabolic transformation of HCH isomers, such processes occur over time scales of decades and are thus challenging to assess. Here, we explored the use of compound-specific isotope analysis (CSIA) to track the aerobic biodegradation and biotransformation pathways of the most prominent isomers, namely, (-)-alpha-, (+)-alpha-, beta-, gamma-, and delta-HCH, through changes of their C and H isotope composition in assays of LinA2 and LinB enzymes. Dehydrochlorination of (+)-alpha-, gamma-, and delta-HCH catalyzed by LinA2 was subject to substantial C and H isotope fraction with apparent C-13- and H-2-kinetic isotope effects (AKIEs) of up to 1.029 +/- 0.001 and 6.7 +/- 2.9, respectively, which are indicative of bimolecular eliminations. Hydrolytic dechlorination of delta-HCH by LinB exhibited even larger C but substantially smaller H isotope fractionation with C-13- and H-2-AKIEs of 1.073 +/- 0.006 and 1.41 +/- 0.04, respectively, which are typical for nucleophilic substitutions. The systematic evaluation of isomer-specific phenomena showed that, in addition to contaminant uptake limitations, diffusion-limited turnover ((-)-alpha-HCH), substrate dissolution (beta-HCH), and potentially competing reactions catalyzed by constitutively expressed enzymes might bias the assessment of HCH biodegradation by CSIA at contaminated sites.