Release of 3,3'-dichlorobenzidine (DCB), an intermediate in dye manufa
cturing, and its congeners are of environmental concern due to their c
arcinogenic nature. To elucidate the fate of these compounds in sedime
nt/water systems, sediment/water mixtures were spiked with DCB and inc
ubated at 20 degrees C for 12 months under anaerobic conditions. The s
ediments used in this study were collected from Lake Macatawa (Holland
, MI) and ranged in composition from silty-clay to sandy. Dehalogenati
on of DCB to benzidine appeared to take place through a transient inte
rmediate, 3-monochlorobenzidine, which was observed in timecourse anal
yses of the sediment/water mixtures. No metabolites were observed in a
utoclaved samples, suggesting that dehalogenation of DCB in anaerobic
sediment/water systems was mediated by microbial activity. The product
of dehalogenation (benzidine) is more toxic to humans than the parent
compound, DCB. From sediment/water distribution experiments, DCB show
ed greater affinity for the sediment phase than its non-chlorinated de
rivative, benzidine. Therefore, progressive dehalogenation of DCB in a
naerobic lake sediments is expected to yield a greater total concentra
tion of aromatic amines in the solution phase, a shift to a more toxic
form, and greater potential for transport in the environment.