Effects of polychlorinated biphenyls and environmental biotransformation products on aquatic nitrification

Impact of coplanar PCBs on microbial communities in anaerobic estuarine sediments

The toxicity of three coplanar PCBs on microbial communities of an estuarine sediment were assessed. Sediment slurries were amended with 2, 10 and 50 mg/L of 345-4 CB, 345-34 CB and 345-345 CB, respectively under anaerobic conditions. The fate and effects of these coplanar PCBs were studied over 250 days. Bacterial communities in sediment slurries were described by dehrdogenase activity and by bacterial populations deduced from the clone libraries. Dechlorination of 345-4 CB and 345-34 CB occurred at least after 100 days of incubation, but dechlorination of 345-345 CB was not observed over the entire incubation period. However, time profiles of dehydrogenase activity were similar in sediment slurries amended with 345-4 CB, 345-34 CB or 345-345 CB. After normalization of the effect of acetone we found that dehydrogenase activity was increased in sediment slurries amended with 50 mg/L, but were inhibited in those amended with 2 and 10 mg/L of coplanar PCBs. Extra addition of electron donors plus sulfate or sulfate could increase dehydrogenase activity significantly. The major microbial populations in the sediment slurries incubated with 2, 10, and 50 mg/L of 345-4 CB were delta-Proteobacteria, Chloroflexi, and epsilon-Proteobacteria, respectively. This study shows that (1) dechlorination of coplanar PCBs did not change their effects on microbial metabolic activities, (2) concentration of coplanar PCBs had effects on microbial metabolic activities and community composition, (3) extra addition of electron donors plus sulfate or sulfate could increase dehydrogenase activity significantly, but this did not always lead to higher dechlorination rates, (4) coplanar PCBs induced perturbations of sediment microbial communities in terms of population structures (but not always as an inhibition).

Plasmid-mediated biodegradative fate of monohalogenated biphenyls in facultatively anaerobic sediments

The results of these studies have demonstrated that model PCB substrates can be mineralized by indigenous microbial population in contaminated sediments. This catabolic function can be rate limited at the microenvironmental level by physical-chemical processes such as physical partitioning and accumulation. At the biochemical level, this catabolic function is determined by the existence of plasmid borne genes that, under laboratory conditions, can be maintained and expressed in pure or mixed culture. Numerous limitations are encountered in establishing the significance of these biodegradative bacteria and the catabolic plasmids at the environmental level. Relatively little information is available concerning frequencies and stability of the bacteria or the plasmid encoded genes within the community. There is no information on the incompatibility grouping of the isolated plasmid relative to other plasmids maintained within the populations. Such factors will influence the development of gene screening techniques to monitor gene frequency distributions in the sediment community. Although mineralization of 4CBP was observed under moderately reducing conditions, it remains suspect that transient or trace levels of dissolved oxygen may have permitted conventional aerobic metabolism of the substrate. If this is true, demonstrating anaerobic metabolism of environmental contaminants will require strict and tedious cultivation under highly reduced conditions (approximately-300 mV). Large deletions of cryptic DNA observed under laboratory conditions may affect bacterial survival and gene maintenance and transfer under environmental conditions. Little information exists on regulation of catabolic activity of selective pressures required to maintain the degradative genes under environmental conditions. Such limitation encountered in these studies are shared by virtually all attempts to utilize genetically manipulated bacteria or newly isolated strains and plasmids. Perhaps the fundamental question is whether the catabolic genes are maintained and expressed within the community rather than whether the host bacterium can survive in the environment.

Heterotrophic bacterial guild structure: Relationship to biodegradative populations

Numerical taxonomic analysis of a freshwater bacterial guild demonstrated that the bacteria capable of growth on phenanthrene and polychlorinated biphenyl media were representative of the taxa obtained from low nutrient oligotrophic media. The diversity of heterotrophic bacteria and members of new taxa recovered from the guild followed a poisson distribution relative to the number of isolation media used. Moderately high nutrient, yeast extract peptone and glucose agar was found to be the most selective isolation medium relative to the total number of taxa recovered whereas low nutrient, lake water agar was the least selective medium used. Carbon source utilization patterns of the isolated taxa indicated that taxa within the guild had broad niche ranges and could potentially occupy many niches within a dynamic environment. The structure of the bacterial guild was dominated by mesophilic oligotrophs.The results of this investigation demonstrate that potential biodegradative populations are representative of the diverse taxa found in uncontaminated freshwater environments.

Impact of Coal-Coking Effluent on Sediment Microbial Communities: a Multivariate Approach

The functional response to and recovery from coal-coking waste effluent was evaluated for sediment microbial communities. Twenty estimates of microbial population density, biomass, and activity were measured five times during a 15-month period. Significant effects on microbial communities were observed in response to both wastewater contamination and diversion of the wastewater. Multivariate analysis of variance and discriminant analysis indicated that accurate differentiation between uncontaminated and contaminated sediments required a minimum of nine estimates of community response. Total viable population density, ATP, alkaline phosphatase, naphthalene, and phenanthrene mineralization rates were found to be highly weighted variables in site discrimination. Lipid and glucose mineralization, nitrogen fixation, and sediment protein also contributed significantly to explaining variation among sites. Estimates of anaerobic population densities and rates of methane production contributed little to discrimination among sites in the environment examined. In general, total viable population density, ATP, and alkaline phosphatase activity were significantly depressed in contaminated sediments. However, after removal of this contamination, the previously affected sites demonstrated greater temporal variability but a closer approximation of the mean response at the control site. Naphthalene and phenanthrene mineralization did not follow the general trend and were elevated at the contaminated sites throughout the investigation. Results of the investigation supported the hypothesis that multiple functional measures of microbial community response are required to evaluate the effect of and recovery from environmental contamination. In addition, when long-term effects are evaluated, select physiological traits, i.e., polyaromatic hydrocarbon mineralization, may not reflect population and biomass estimates of community response.