The effects of polychlorinated biphenyls (PCBs) on nitrification were examined for pure cultures and natural reservoir samples. PCBs at concentrations greater than 10 ,ug liter-' inhibited nitrification, principally ammonium oxidation, in one of two natural reservoir environments. However, this inhibition could not be reproduced in pure high-cell-density cultures or in previously contaminated reservoir waters. A PCB environmental biotransformation product, p-chlorophenylglyoxylic acid, and p-chloromandelic acid had no effect on nitrification. Polychlorinated biphenyls (PCBs) are recognized as toxic environmental contaminants with near global distribution (16). PCBs are dispersed in the environment principally through industrial use, manufacturing, product and waste disposal, accidential spills, and deliberate discharge. These industrial chemicals, manufactured under the trade name Aroclor (Monsanto Industrial Chemicals Co.) in the United States, are complex mixtures of various chlorinated biphenyl congeners. Because of the environmental distribution, stability of the chlorinated biphenylic ring system (resistance to physical, chemical, and biological degradation), bioaccumulation, toxicity, and mutagenic properties, a federal ban has been placed on their manufacture and use in open-system applications. Evidence indicates that PCBs are subject to microbial biotransformation and metabolism (1, 4, 7, 8, 11, 22, 24, 25; Shiaris and Sayler, Environ. Sci. Technol., in press). We have demonstrated that environmental biotransformation of the lesser chlorinated biphenyls results in the accumulation of chlorobenzoic acids and chlorophenylglyoxylic acid (CPGA) in the environment (Shiaris and Sayler, Environ. Sci. Technol., in press). These chlorinated biotransformation products lack the apparent mutagenicity of the parent PCB residue (Sayler et al., Arch. Environ. Contam. Toxicol., in press). Although PCB toxicity to animal populations and movement in the environment are well doc