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| Molecular Biology, Environmental Toxicology
Our research seeks to understand the molecular mechanisms of contaminant toxicity in aquatic and marine animals. Recent publications (underline indicates student co-author): Anna L. Zimmermann, Elizabeth A. King, Emelyne Dengler, Shana R. Scogin, and Wade H. Powell (2008) An Aryl Hydrocarbon Receptor Repressor from Xenopus laevis: Function, Expression and Role in Dioxin Responsiveness during Frog Development. Toxicol. Sci. in press. Philips, B.H., T.C. Susman, and W.H. Powell. (2006) Differences in elimination of 2,3,7,8-tetrachlorodibenzo-p-dioxin during Xenopus laevis development. Marine Environmental Research, 62:S34-S37. Lavine, J.A., A.J. Rowatt, T. Klimova, A.J. Whitington, E. Dengler, C. Beck, and W.H. Powell (2005) Aryl Hydrocarbon Receptors in the frog Xenopus laevis: Two AHR1 paralogs exhibit low affinity for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) Toxicol. Sci. 88:62-70. doi:10.1093/toxsci/kfi228. |
Kenyon Lab Group 2007-08 |
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Embryos of the African clawed frog, Xenopuslaevis, represent a long standing model of vertebrate development. They are also used in FETAX (Frog Embryos Teratogenesis Assay-Xenopus) and similar assays of the developmental toxicity of chemicals and environmental samples. 2,3,7,8 tetrachlorodibenzo-p-dioxin (TCDD) is a potent developmental toxicant in most vertebrates. However, frogs are generally insensitive to TCDD toxicity, especially at early life stages. Thus, FETAX and other frog embryo toxicity tests may be poorly suited for determining the developmental toxicity of samples containing dioxin-like compounds. Our research seeks to delineate the molecular mechanisms underlying TCDD insensitvity in frogs, using X. laevis as a model system. The aryl hydrocarbon receptor (AHR) is a ligand activated transcription factor that mediates the biological and toxicological effects of a broad range of structurally diverse chemicals, including TCDD. Inherent properties of the AHR signaling pathway, including AHR expression levels and the affinity of AHR for specific ligands, can underlie large variations in the relative potency of different ligands and the sensitivity of different animal groups. However, neither the exact mechanisms by which AHR activity leads to toxicity nor the endogenous, non-toxicological functions of AHR signaling are well understood. Our group has identified two AHRs from the African clawed frog (Xenopus laevis), recently duplicated paralogs called AHR1a and AHR1b. Both proteins bind TCDD with at least 25-fold lower affinity than the AHR from a highly sensitive strain of mouse, likely accounting for the dioxin-insensitive phenotype. Our research takes advantage of the unique amino acid sequence, functional properties, and phylogenetic position of the frog AHRs to probe their structural interactions with a range of xenobiotic and naturally occurring ligands and to contrast their function with AHRs from TCDD-sensitive species and with each other. We have three main goals:
Overall, this comparative approach in a novel model system will provide important basic information about the structure and function of all vertebrate AHRs. Understanding the differences between frog and human AHRs will also aid risk assessment by refining interpretation of toxicological data derived from FETAX (Frog Embryo Teratogenesis Assay-Xenopus) and similar developmental toxicity tests that employ frog embryos. development. [Supported by the National Institutes of Health, R15-ES011130] |
![]() 2,3,7,8 tetrachlorodibenzo-p-dioxin ("TCDD" or "dioxin") |
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