Aquatic Toxicity of Dioxins and Related Chemicals

Polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (PCBs) belong to a family of lipophilic halogenated aromatic hydrocarbons that have similar structures, resist chemical and biological degradation, and persist in the environment posing a potential risk to fish, wildlife, and human health. There are more than 400 possible polychlorinated dioxins, dibenzofuran, and biphenyl congeners; however, only 21 are considered highly toxic.1,2 The more potent congeners are planar or coplanar molecules with lateral chlorine substitutions, approximate isostereomers of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), the most potent PCDD, PCDF, or PCB congener.3 In mammals, TCDD and TCDD-like dioxin, dibenzofuran, and biphenyl congeners evoke similar patterns of toxic responses within a given species, and share a common mechanism of action mediated by binding the cellular aryl hydrocarbon (Ah) receptor and altering gene transcription.3,4 The ability of TCDD and TCDD-like congeners to produce toxicity in mammalian species correlates with their Ah receptor binding affinity and their ability to induce cytochrome P450IA enzyme activity, a gene subfamily that catalyzes monooxygenase reactions and whose expression is regulated by the Ah receptor.4−6

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