Industrial chemicals known as polychlorinated biphenyls (PCBs) were widely used for decades until their production was banned worldwide due to their persistence and toxicities to humans and other animals. Upon oxidative metabolism by cytochrome P450, hydroxylated metabolites of PCBs (OHPCBs) are formed. OHPCBs have been shown to competitively displace thyroxine from transthyretin, block normal hormonal activity, and inhibit phenol or family 1 sulfotransferases (SULTs) which catalyze sulfation of thyroid hormones and estrogens. Recently, three OHPCBs were shown to also interact with hydroxysteroid or family 2 sulfotransferases that play a role in the homeostasis of steroid hormones such as dehydroepiandrosterone (DHEA). The objectives of the studies presented in this thesis were to further examine the effects of selected OHPCBs on the activity of human hydroxysteroid sulfotransferase (hSULT2A1), to develop a three-dimensional quantitative structure activity relationship (3D-QSAR) model for OHPCBs as inhibitors of DHEA-sulfation catalyzed by this enzyme, and to investigate the mechanism of inhibition and binding of OHPCBs to hSULT2A1. All 15 OHPCBs examined inhibited the sulfation of 1 μ M [3H] DHEA, catalyzed by hSULT2A1 with IC50 values ranging from 0.6 to 96 μ M. The OHPCBs with a 3, 5-dichloro-4-hydroxy substitution were the most potent inhibitors of DHEA sulfation, and they were also shown to be substrates for hSULT2A1. Eight OHPCBs were substrates for hSULT2A1, and seven were solely inhibitors (i.e. they inhibited the sulfation of DHEA, yet they were not themselves sulfuryl-acceptors in hSULT2A1-catalyzed reactions). A 3D-QSAR model was developed utilizing comparative molecular field analysis (CoMFA). The model fit the data well and also had good predictability. The kinetics of inhibition showed that these OHPCBs were noncompetitive inhibitors of hSULT2A1. Binding studies utilizing the displacement of a fluorescent probe, 8-anilino-1-naphthalene sulfonic acid, revealed that several of the OHPCBs interact either at more than one binding site or with more than one enzyme conformation. Further exploration of this binding by molecular modeling showed that OHPCBs bind similarly to different conformations of the enzyme. This work has helped in our understanding of the roles of sulfotransferases in the metabolism and toxicities of OHPCBs, and it opens new avenues for future work.

Polychlorinated biphenyls (PCBs) are persistent organic pollutants. Due to their properties, PCBs accumulate in the food-chain and post a threat to the health of human beings and wildlife. Hydroxylated PCBs (OH-PCBs) are oxidative metabolites of PCBs and are more hydrophilic than their parent PCBs. One of the best approaches to break down these contaminants is through bioremediation, which is an environmental friendly process that uses microorganisms to restore natural environment. Towards this goal, we have investigated the toxicity and accumulation of PCBs and OH-PCBs in a Gram-negative bacterium, Escherichia coli. We have also determined the role played by a primary multidrug efflux transporter AcrB on the accumulation of PCBs and OH-PCBs in bacterial cell. We found that one of the PCBs tested was toxic to E. coli, while different OH-PCBs have different levels of toxicity; the acrB knockout strain accumulated significantly more PCBs and OH-PCBs than the wild-type strain, suggesting that these compounds are substrates of the efflux pump; higher cytoplasmic concentrations of OH-PCBs were also observed in the acrB knockout strain using the biosensors. Based on these observations, we conclude that both PCBs and OH-PCBs are substrates of protein AcrB. Therefore the efflux activities of multidrug resistant pumps in Gram-negative bacteria should be considered while designing bioremediation approaches.

Polychlorinated biphenyls (PCBs) are toxic and persistent chemicals that have been largely dispersed into the environment. The biological and abiotic transformations of PCBs often generate hydroxylated derivatives, which have been detected in a variety of environmental samples, including animal tissues and feces, water, and sediments. Because of their toxicity and widespread dispersion in the environment, hydroxylated PCBs (OH-PCBs) are today increasingly considered as a new class of environmental contaminants. Although PCBs are known to be susceptible to microbial degradation under both aerobic and anaerobic conditions, bacterial degradation of OH-PCBs has received little attention. The overall objective of this study is therefore to evaluate the transformation of mono-hydroxylated PCBs by the well characterized aerobic PCB-degrading bacterium, Burkholderia xenovorans LB400. In order to achieve our overall objective, a series of model mono-hydroxylated PCBs have been selected and they are used to determine the toxicity of hydroxylated congeners toward the bacterium B. xenovorans LB400. The biodegradation kinetics and metabolic pathways of the selected OH-PCBs by B. xenovorans LB400 are then characterized using GC/MS. To understand further the molecular basis of the metabolism of OH-PCBs by B. xenovorans LB400, gene expression analyses are conducted using reverse-transcription real-time (quantitative) polymerase chain reaction (RT-qPCR) and microarray technology. More formally, the specific aims of the proposed research are stated as follows: (1) To evaluate the toxicity of selected mono-hydroxylated derivatives of lesser-chlorinated PCBs toward the bacterium B. xenovorans LB400. (2) To assess the degradation of the selected OH-PCBs by B. xenovorans LB400. (3) To gain further understanding of the molecular bases of the metabolism of the selected OH-PCBs by B. xenovorans LB400. Three hydroxylated derivatives of 4-chlorobiphenyl and 2,5-dichlorobiphenyl, including 2'-hydroxy-, 3'-hydroxy-, and 4'-hydroxy- congeners, were significantly transformed by Burkholderia xenovorans LB400 when the bacterium was growing on biphenyl (biphenyl pathway-inducing conditions). On the contrary, only 2'-OH-4-chlorobiphenyl and 2'-OH-2,5-dichlorobiphenyl were transformed by the bacterium growing on succinate (conditions non-inductive of the biphenyl pathway). Gene expression analyses showed that only exposure to 2'-OH-4-chlorobiphenyl and 2'-OH-2,5-dichlorobiphneyl resulted in induction of key genes of the biphenyl pathway, when cells grown on succinate. These observations suggest that 2'OH-PCBs were capable of inducing the genes of biphenyl pathway. These results provide the first evidence that bacteria are able to cometabolize PCB derivatives hydroxylated on the non-chlorinated ring. Genome-wide transcriptional analyses using microarrays showed that 134 genes were differentially expressed in cells exposed to biphenyl, 2,5-dichlorobiphenyl, and 2'-OH-2,5-dichlorobiphneyl as compared to non-exposed cells. A significant proportion of differentially expressed genes were simultaneously expressed or down regulated by exposure to the three target compounds i.e., biphenyl, 2,5-DCB, and 2'-OH-2,5-DCB, which suggests that these structurally similar compounds induce similar transcriptional response of B.xenovorans LB400. Results of this study may have important implications for the natural attenuation of PCBs and fate of OH-PCBs in the environment. The recalcitrance to biodegradation and the high toxicity of some OH-PCBs may provide a partial explanation for the persistence of PCBs in the environment. / Civil Engineering