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M E Hahn

Publications and source records attributed to M E Hahn.

58 records · Page 4Linked to original sources

Towards molecular understanding of species differences in dioxin sensitivity: initial characterization of Ah receptor cDNAs in birds and an amphibian.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and related planar halogenated aromatic hydrocarbons (PHAHs) are highly toxic to most vertebrate animals, but there are dramatic species differences in sensitivity, both within and among vertebrate classes. For example, studies in cultured avian hepatocytes have revealed differential sensitivity of birds to PHAHs [Kennedy et al. (1996). Toxicol. Appl. Pharmacol., 141, 214-230]. Differences in the characteristics or expression of the aryl hydrocarbon receptor (AHR) could contribute to these species differences in PHAH responsiveness. To investigate the molecular mechanism of differential PHAH sensitivity, we have begun to characterize the AHR in white leghorn chicken (Gallus gallus), Pekin duck (Anas platyrhynchos), and common tern (Sterna hirundo), as well as an amphibian, mudpuppy (Necturus maculosus). Partial AHR cDNAs encompassing the helix-loop-helix and PAS domains were cloned and sequenced. Comparison of amino acid sequences in this region indicated a high degree of sequence conservation among the bird species (97% amino acid identity). The percent identity between bird sequences and either mouse or mudpuppy was lower (79%); the mudpuppy AHR was 74% identical to the mouse AHR. Phylogenetic analysis of these and other AHR amino acid sequences showed that the bird and mudpuppy AHRs were more closely related to mammalian and fish AHR1 forms than to fish AHR2. Future studies include the in vitro expression and functional characterization of AHRs from these and other non-mammalian vertebrates.

Amino Acid Sequence↗

The evolution of aryl hydrocarbon signaling proteins: diversity of ARNT isoforms among fish species.

The aryl hydrocarbon receptor nuclear translocator (ARNT) mediates aryl hydrocarbon signaling and toxicity by dimerizing with the ligand-activated aryl hydrocarbon receptor (AHR), forming a complex that binds specific DNA elements and alters transcription of target genes. Two genes encode different forms of ARNT in rodents: ARNT1, which is widely expressed, and ARNT2, which exhibits a very restricted expression pattern. In an effort to characterize aryl hydrocarbon signaling mechanisms in fishes, we previously isolated an ARNT cDNA from Fundulus heteroclitus and discovered that this species expresses ARNT2 ubiquitously. This situation differs not only from mammals, but also from rainbow trout, which expresses a divergent ARNT gene that we hypothesized was peculiar to salmonids (rtARNTa/b). In this communication, we examine the ARNT sequences of multiple fish species, including a newly isolated cDNA from scup (Stenotomus chrysops). Our phylogenetic analysis demonstrates that zebrafish ARNT, like the Fundulus protein, is an ARNT2. Contrary to expectations, the scup ARNT is closely related to the rainbow trout protein, demonstrating that the existence of this ARNT isoform predates the divergence of salmonids from the other teleosts. Thus, different species of fish express distinct and highly conserved isoforms of ARNT. The number, type, and expression pattern of ARNT proteins may contribute to interspecies differences in aryl hydrocarbon toxicity, possibly through distinct interactions with additional PAS-family proteins.

Animals↗

Immunohistochemical localization of cytochrome P-450IA1 induced by 3,3',4,4'-tetrachlorobiphenyl and by 2,3,7,8-tetrachlorodibenzoafuran in liver and extrahepatic tissues of the teleost Stenotomus chrysops (scup).

The regulation of different cytochrome P-450 forms and their functions in different organs and cell types could determine the susceptibility of those cells and organs to toxic effects of xenobiotics, including chemical carcinogenesis. Here we describe the cellular localization of cytochrome P-450E (P-450IA1) induced in 10 major organs or organ systems of a marine vertebrate species, the fish, Stenotomus chrysops (scup). Scup were injected ip with 3,3',4,4'-tetrachlorobiphenyl (TCB) at 1 mg/kg, or with 2,3,7,8-tetrachlorodibenzofuran (TCDF) at 3 micrograms/kg. Induction was verified by Western blot analysis of microsomes from selected organs (liver, kidney, and gill) using monoclonal antibody (MAb) 1-12-3 to scup P-450IA1. The localization of P-450IA1 was subsequently determined in sections prepared by standard histological methods (10% buffered formalin fixation, paraffin embedding), and stained with MAb 1-12-3 and peroxidase-labeled second antibody. P-450IA1 was induced in epithelial and endothelial cells in liver (including pancreatic tissue), kidney, gill, gut, spleen, testis, and ovary. Induction also was detected in endothelial cells, but not other types, in heart, brain, and red muscle. In heart, the staining was present in the endocardium as well as in the endothelium of the coronary vasculature and great vessels. Although TCDF and TCB both induced P-450IA1 in various cells of all organs examined, the effect of TCB was in most cases greater than that of TCDF. This may be due to a relatively higher TCB dosage. A wider staining distribution was seen in gut, gill, kidney, and gonad of TCB-treated fish, which might be explained by a greater penetration, or by excretion of parent TCB, as opposed to TCDF. In any case, the results show that these important environmental agents induce P-450IA1 in generally similar patterns in all organs examined. The common finding of a strong induction of P-450IA1 in endothelial cells in all organs examined supports the suggestion that the endothelium may be a primary site of P-450IA1 induction.

Animals↗