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Fundulus heteroclitus is a well-characterized marine fish model for studying aryl hydrocarbon toxicity. The F. heteroclitus population in New Bedford Harbor (NBH), a Superfund site in southeastern Massachusetts, exhibits heritable resistance to the toxic effects of planar halogenated aromatic hydrocarbons (PHAHs), including 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) and polychlorinated biphenyls (PCBs). To investigate the role of the aryl hydrocarbon receptor (AHR) signal transduction pathway in PHAH resistance, we measured the relative levels of AHR1, AHR2, and ARNT2 mRNA in whole embryos at different developmental stages and in dissected tissues of adults, comparing expression of these genes in NBH fish with fish from a reference site (Scorton Creek, MA [SC]). Expression of both AHR1 and AHR2 mRNA increased during development, achieving maximum levels prior to hatching. Maximal embryonic expression of AHR1 was delayed relative to AHR2. Whole NBH and SC embryos exhibited no discernable differences in expression of these genes. As we have previously observed, adult SC fish expressed AHR2 and ARNT2 mRNA in all tissues examined, while AHR1 was expressed predominantly in brain, heart, and gonads. In contrast, AHR1 mRNA was widely expressed in NBH fish, appearing with unusual abundance in gill, gut, kidney, liver, and spleen. This AHR1 expression pattern was not observed in the lab-reared progeny of NBH fish, demonstrating that constitutive AHR1 expression in gill, gut, kidney, liver, and spleen is not a heritable phenotype. Furthermore, widespread AHR1 expression was not induced in reference-site fish by TCDD or PCB mixtures, suggesting that aberrant AHR1 expression is not simply a normal physiological response of contaminant exposure. These results identify ubiquitous AHR1 expression as an attribute unique to feral NBH F. heteroclitus, and they represent a first step in determining the regulatory mechanisms underlying this expression pattern and its possible role in TCDD resistance.

Bioflavonoids are plant compounds touted for their potential to treat or prevent several diseases including cancers induced by common environmental chemicals. Much of the biologic activity of one such class of pollutants, polycyclic aromatic hydrocarbons (PAH), is mediated by the aryl hydrocarbon receptor/transcription factor (AhR). For example, the AhR regulates PAH immunotoxicity that manifests as pre-B cell apoptosis in models of B cell development. Because bioflavonoids block PAH-induced cell transformation and are structurally similar to AhR ligands, it was postulated that some of them would suppress PAH-induced, AhR-dependent immunotoxicity, possibly through a direct AhR blockade. This hypothesis was tested using a model of B cell development in which pre-B cells are cultured with and are dependent on bone marrow stromal or hepatic parenchymal cell monolayers. Of seven bioflavonoids screened, galangin (3,5,7-trihydroxyflavone) blocked PAH-induced but not C(2)-ceramide- or H(2)O(2)-induced pre-B cell apoptosis. Because galangin blocked AhR-dependent reporter gene expression, AhR complex-DNA binding, and AhR nuclear translocation, inhibition of a relatively early step in AhR signaling was implicated. This hypothesis was supported by the ability of galangin to bind the AhR and stabilize AhR-90-kDa heat shock protein complexes in the presence of AhR agonists. These studies demonstrate the utility of pre-B cell culture systems in identifying compounds capable of blocking PAH immunotoxicity, define at least one mechanism of galangin activity (i.e., repression of AhR activation), and motivate the use of this and similar dietary bioflavonoids as relatively nontoxic inhibitors of AhR agonist activity and as pharmacologic agents with which to dissect AhR signaling pathways.

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.

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.

We measured rates of oxidative metabolism of two tetrachlorobiphenyl (TCB) congeners by hepatic microsomes of two marine mammal species, beluga whale and pilot whale, as related to content of selected cytochrome P450 (CYP) forms. Beluga liver microsomes oxidized 3,3',4,4'-TCB at rates averaging 21 and 5 pmol/min per mg for males and females, respectively, while pilot whale samples oxidized this congener at 0.3 pmol/min per mg or less. However, rates of 3,3',4,4'-TCB metabolism correlated with immunodetected CYP1A1 protein content in liver microsomes of both species. The CYP1A inhibitor alpha-naphthoflavone inhibited 3,3',4,4'-TCB metabolism by 40% in beluga, supporting a role for a cetacean CYP1A as a catalyst of this activity. Major metabolites of 3,3',4,4'-TCB generated by beluga liver microsomes were 4-OH-3,3',4',5-TCB and 5-OH-3,3',4,4'-TCB (98% of total), similar to metabolites formed by other species CYP1A1, and suggesting a 4,5-epoxide-TCB intermediate. Liver microsomes of both species metabolized 2,2',5,5'-TCB at rates of 0.2-1.5 pmol/min per mg. Both species also expressed microsomal proteins cross-reactive with antibodies raised against some mammalian CYP2Bs (rabbit; dog), but not others (rat; scup). Whether CYP2B homologues occur and function in cetaceans is uncertain. This study demonstrates that PCBs are metabolized to aqueous-soluble products by cetacean liver enzymes, and that in beluga, rates of metabolism of 3,3',4,4'-TCB are substantially greater than those of 2,2',5,5'-TCB. These directly measured rates generally support the view that PCB metabolism plays a role in shaping the distribution patterns of PCB residues found in cetacean tissue.

The effects of many chemicals on cellular processes are governed by their ability to enter the cell, which is in turn a function of the composition of the cell's external environment. To examine this relationship, the effect of serum in cell culture medium on the bioavailability of cytochrome P450 1A (CYP1A)-inducing compounds was determined in PLHC-1 (Poeciliopsis lucida hepatocellular carcinoma) cells. The presence of 10% calf serum in the medium increased the EC50 (effective concentration to achieve 50% maximal response) for induction of ethoxyresorufin O-deethylase (EROD) activity by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) 20-fold as compared to treatment in serum-free medium. Measurement of [3H]TCDD uptake and Ah receptor binding indicated that the apparent difference in potencies was a result of decreased bioavailability in the presence of serum, effectively reducing the concentration of TCDD within the cells. Induction of EROD and CYP1A protein in response to treatment with each of three coplanar polychlorinated biphenyls (PCB congeners 77, 126, and 169) was similarly affected by serum, although the magnitude varied among inducers and assays. Relative potencies (calculated as EC50TCDD / EC50PCB) for EROD induction by the three PCBs were significantly higher in the absence of serum. However, serum showed no significant effect on the relative potencies for CYP1A protein induction. These results demonstrate that measured inducing potencies, and relative potencies for EROD induction, by halogenated aromatic hydrocarbons are strongly dependent on the composition of culture medium, which can lead to artificial differences in comparisons among cell types.

The present study describes the use of a fish hepatoma cell line (PLHC-1) in monitoring the biological effects of sediments collected from recipient waters of the oil shale industry. Sampling sites were located in River Purtse and River Kohtla in northeast Estonia. The effects of pure oil shale on the PLHC-1 cells were also studied. The cells were exposed to n-hexane-extracted samples in 48-well plates for 24 h, and 7-ethoxyresorufin O-deethylase (EROD) activity, total protein, and porphyrin content were measured in the exposed cells. Polycyclic aromatic hydrocarbon (PAH) contents in the samples were measured by high-performance liquid chromatography (HPLC). All the sediment and oil shale samples induced CYP1A activity and led to porphyrin accumulation in the cells. The most potent inducers were the sediments collected near the oil shale processing plants (site Lüganuse in River Purtse and Kohtla in River Kohtla), as well as those at the most downstream site in River Purtse (Purtse). These samples possessed high total PAH contents, ranging from 4,270 to nearly 150,000 microg/kg dry sediment. The presence of other lipophilic organic contaminants in the samples was not determined in this study. Both EROD activity and porphyrin content exhibited biphasic induction curves, and the ED(50)(1) values for EROD activity were lower than the ED(50)s for porphyrin content. 2,3,7, 8-Tetrachlorodibenzo-p-dioxin induction equivalents (TCDD-EQs) calculated from EROD induction potencies correlated well with total PAHs (r(2) = 0.827 and p = 0.003 for log-transformed data) and also with individual PAHs. TCDD-EQs for porphyrin content did not correlate significantly with total PAHs (log-log r(2) = 0.785, p = 0. 116). The biological potency and PAH contamination of the samples showed the same rank order, except at Lüganuse, where sediment extracts induced CYP1A and porphyrins more than could have been expected based on PAH contents. Bioassay-derived induction EQs (normalized to dibenz(a,h)anthracene) were 20- to 3,200-fold greater than EQs calculated from the concentrations of five PAHs, suggesting important contributions from other compounds or nonadditive effects. The PLHC-1 cells proved to be a sensitive bioanalytical tool for sediments contaminated with PAH-type pollutants in the oil shale processing area. We suggest further use of this bioassay in screening and monitoring waters with similar background of pollution as in northeast Estonia.

The aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor through which 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds cause altered gene expression and toxicity. The AHR belongs to an emerging multigene family of transcription factors possessing basic helix loop helix (bHLH) and Per-ARNT-Sim (PAS) domains. Most bHLH-PAS proteins occur as duplicates or "paralog groups" in mammals, but only a single mammalian AHR has been identified. Here we report the cDNA cloning of two distinct AHRs, designated FhAHR1 and FhAHR2, from a single vertebrate species, the teleost Fundulus heteroclitus (Atlantic killifish). Both Fundulus AHR proteins possess bHLH and PAS domains that are closely related to those of the mammalian AHR. FhAHR1 and FhAHR2 are highly divergent (40% overall amino acid identity; 61% identity in the N-terminal half), suggesting that they arose from a gene duplication predating the divergence of mammals and fish. Photoaffinity labeling with 2-azido-3-[(125)I]iodo-7, 8-dibromodibenzo-p-dioxin and velocity sedimentation analysis using 2,3,7,8-[1,6-(3)H]TCDD showed that both FhAHR1 and FhAHR2 exhibit specific, high-affinity binding of dioxins. Both AHRs also showed specific, TCDD- and ARNT-dependent interactions with a mammalian xenobiotic response element. The two Fundulus AHR genes displayed different tissue-specific patterns of expression; FhAHR1 transcripts were primarily expressed in brain, heart, ovary, and testis, while FhAHR2 transcripts were equally abundant in many tissues. Phylogenetic analysis demonstrated that Fundulus AHR1 is an ortholog of mammalian AHRs, while AHR2 forms in Fundulus and other fish are paralogous to Fundulus AHR1 and the mammalian AHRs and thus represent a novel vertebrate subfamily of ligand-binding AHRs.

Previous studies indicated that two prototypic PAH, benzo[a]pyrene (B[a]P) and 7,12-dimethylbenz[a]anthracene (DMBA), suppress the developing immune system by inducing apoptosis in bone marrow pre-B lymphocytes. In bone marrow cultures consisting of pre-B cells growing on bone marrow stromal cell monolayers, pre-B cell apoptosis was shown to be dependent on the aryl hydrocarbon receptor/transcription factor (AhR) expressed in stromal cells. However, it was not determined if AhR activation alone is sufficient or if DMBA metabolism is required for induction of a stromal cell-derived apoptosis signal. To address these issues we assessed: 1) the ability of poorly metabolized AhR ligands to induce pre-B cell apoptosis and 2) the capacity for and the mechanism through which an early DMBA metabolite induces pre-B cell apoptosis. Three poorly metabolized AhR ligands, 2,3,7,8-tetrachlorodibenzo-p-dioxin, 3,3',4,4',5-pentachlorobiphenyl, and 3,3',4,4'-tetrachlorobiphenyl failed to induce pre-B cell apoptosis in bone marrow cultures, indicating that AhR activation alone is not sufficient to induce apoptosis and suggesting a role for PAH metabolism in induction of an apoptosis signal. Consistent with this hypothesis, DMBA-3, 4-dihydrodiol, an early DMBA metabolite, induced significant pre-B cell apoptosis. The ability of DMBA-3,4-dihydrodiol to activate the AhR, inhibition of DMBA-3,4-dihydrodiol-induced apoptosis by alpha-naphthoflavone, and the significantly lower levels of DMBA-3, 4-dihydrodiol-induced apoposis in pre-B cell populations maintained on AhR(-) stromal cells strongly support a role for the AhR in DMBA-3,4-dihydrodiol-induced apoptosis. Of two DMBA-metabolizing enzymes evaluated, CYP1A1 and CYP1B1, the latter appeared to be the more likely to play a role in DMBA-induced apoptosis. These data confirm a role for the AhR in PAH-induced pre-B cell apoptosis, indicate a role for DMBA metabolism, and suggest a feedback loop in which at least one product of DMBA metabolism augments AhR signaling, leading to induction of an apoptosis stimulus., (Copyright 1999 Academic Press.)

Two aryl hydrocarbon receptors (AhRs), rtAhR2alpha and rtAhR2beta, were cloned from rainbow trout (rt) cDNA libraries. The distribution of sequence differences, genomic Southern blot analysis, and the presence of both transcripts in all individual rainbow trout examined suggest that the two forms of rtAhR2 are derived from separate genes. The two rtAhR2s have significant sequence similarity with AhRs cloned from mammalian species, especially in the basic helix-loop-helix and PAS functional domains located in the amino-terminal 400 amino acids of the protein. In contrast, the Gln-rich transactivation domain found in the carboxyl-terminal half of mammalian AhRs is absent from both rtAhR2s. Both clones were expressed by in vitro transcription/translation and proteins of approximately 125 kDa were produced. These proteins bind 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) and are able to bind dioxin response elements in gel shift assays. rtAhR2alpha and rtAhR2beta are expressed in a tissue-specific manner with the highest expression of rtAhR2beta in the heart. Expression of rtAhR2alpha and rtAhR2beta mRNAs is positively regulated by TCDD. Both rtAhR2alpha and rtAhR2beta produced TCDD-dependent activation of a reporter gene driven by dioxin response elements. Surprisingly, the two receptors showed distinct preferences for different enhancer sequences. These results suggest that the two receptor forms may regulate different sets of genes, and may play different roles in the toxic responses produced by AhR agonists such as TCDD.

The aryl hydrocarbon receptor nuclear translocator (ARNT) is a member of the bHLH/PAS protein superfamily. ARNT dimerizes with several PAS superfamily members, including the ligand-activated aryl hydrocarbon receptor (AHR), forming a complex that alters transcription by binding specific elements within the promoters of target genes. Two genes encode different forms of the protein in rodents: ARNT1, which is widely expressed, and ARNT2, which is limited to the brain and kidneys of adults and specific neural and branchial tissues of embryos. In an effort to characterize aryl hydrocarbon signaling mechanisms in Fundulus heteroclitus, a marine teleost that can develop heritable xenobiotic resistance, we have isolated a liver cDNA encoding an ARNT homolog. The protein exhibits AHR-dependent DNA binding capability typical of other vertebrate ARNTs. Unexpectedly, phylogenetic analysis reveals that the cDNA encodes an ARNT2. This is the only detectable ARNT sequence in Fundulus liver, gill, ovary, and brain, suggesting that ARNT2 is the predominant form of ARNT in this species. Also surprising is the relative lack of sequence identity with another fish ARNT protein, rainbow trout ARNTb, which we show forms a distinct branch outside the ARNT1 and ARNT2 clades in phylogenetic analyses. Functional diversity of ARNT proteins in fish may have important implications for the assessment of aryl hydrocarbon effects on natural populations. The increasing use of fish models in developmental and toxicological studies underscores the importance of identifying taxon-specific roles of ARNT proteins and their potential dimeric partners in the PAS superfamily., (Copyright 1999 Academic Press.)

The aryl hydrocarbon receptor (Ah receptor or AHR) is a ligand-activated transcription factor involved in the regulation of several genes, including those for xenobiotic-metabolizing enzymes such as cytochrome P450 1A and 1B forms. Ligands for the AHR include a variety of aromatic hydrocarbons, including the chlorinated dioxins and related halogenated aromatic hydrocarbons whose toxicity occurs through activation of the AHR. The AHR and its dimerization partner ARNT are members of the emerging bHLH-PAS family of transcriptional regulatory proteins. In this review, our current understanding of the AHR signal transduction pathway in non-mammalian and other non-traditional species is summarized, with an emphasis on similarities and differences in comparison to the AHR pathway in rodents and humans. Evidence and prospects for the presence of a functional AHR in early vertebrates and invertebrates are also examined. An overview of the bHLH-PAS family is presented in relation to the diversity of bHLH-PAS proteins and the functional and evolutionary relationships of the AHR and ARNT to the other members of this family. Finally, some of the most promising directions for future research on the comparative biochemistry and molecular biology of the AHR and ARNT are discussed.

The mammalian aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor that controls the expression of cytochrome P450 1A (CYP1A) genes in response to halogenated aromatic hydrocarbons such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The natural ligand and normal physiologic function of this protein are as yet unknown. One approach to understanding AHR function and significance is to determine the evolutionary history of this receptor and of processes such as CYP1A induction that are controlled by the AHR in mammals. In these studies, AHR function was evaluated in representative cartilaginous fish (little skate, Raja erinacea) and jawless fish (sea lamprey, Petromyzon marinus and Atlantic hagfish, Myxine glutinosa), using CYP1A induction as a model AHR-dependent response. Treatment of skate with beta-naphthoflavone (BNF) caused an 8-fold increase in hepatic ethoxyresorufin O-deethylase (EROD) activity as well as a 37-fold increase in the content of immunodetectable CYP1A protein. Evidence of CYP1A inducibility was also obtained for another cartilaginous fish, the smooth dogfish Mustelus canis. In contrast, hepatic EROD activity was not detected in untreated lamprey nor in lamprey treated with 3,3'4,4'-tetrachlorobiphenyl (TCB), a potent AHR agonist in teleosts. A possible CYP1A homolog was detected in lamprey hepatic microsomes by one of three antibodies to teleost CYP1A, but expression of this protein was not altered by TCB treatment. CYP1A protein and catalytic activity were measurable in hagfish, but neither was induced after treatment with TCB. These results suggest that the AHR-CYP1A signal transduction pathway is highly conserved in gnathostomes, but that there may be fundamental differences in AHR signaling or AHR-CYP1A coupling in agnathan fish. Agnathan fish such as hagfish and lamprey may be interesting model species for examining possible ancestral AHR functions not related to CYP1A regulation.

Infant house mice, Mus musculus, produce ultrasonic calls that reliably lead to retrieval by adult mice. While individual differences in calls have been demonstrated both among and within species, the influences of age and sex on call characteristics have not been systematically investigated in mice. This study examined the influences of age, sex, and genotype (inbred versus hybrid) on the rate, length, and frequency characteristics of the calls of 486 male and female mice from 2 to 12 days of age. Rate of calling followed a shallow inverted U-shaped function across days. Call lengths decreased and call frequency characteristics increased, in a linear manner, with age. Females emitted fewer calls, with a smaller bandwidth, at some ages than males. Hybrid pups produced more calls of greater length and a lower frequency than inbred pups. These results indicate the presence of cues that could allow adult mice to behave differentially toward pups as a function of their age and sex.

Cytotoxicity and CYP1A induction properties of celluloses and wood chips were studied with a teleost liver cell line, PLHC-1. Cells were exposed to acetone extracts of celluloses produced using new bleaching techniques (elemental chlorine free, ECF; totally chlorine free, TCF) in two sulphate mills or without any bleaching (unbleached, UB) in a sulphite mill. In another set of exposures, celluloses (ECF and TCF bleached) and wood chips (from pine and birch) were collected from a sulphate mill, extracted with acetone, and the extracts used to treat the cells. After exposure, O-deethylation of 7-ethoxyresorufin (EROD, a measure of cytochrome P4501A (CYP1A) catalytic activity), and total protein content, a measure of cytotoxicity, were assayed. The presence of the CYP1A protein in the exposed cells was assessed by immunoblotting. The cellulose and wood chip extracts were able to cause both cytotoxicity and EROD induction in the PLHC-1 cells. In the exposures conducted with the material from three different mills, the celluloses made of birch were more cytotoxic and more potent inducers of EROD activity than were the celluloses of pine. Further, UB celluloses increased EROD activity and caused cytotoxicity at lower doses than material bleached with modern bleaching techniques. In the exposures made with material from one single mill, there were no clear trends between the celluloses made of pine or birch. Wood chips of pine, however, were more cytotoxic than wood chips of birch. Especially with pine wood chips, cytotoxicity interfered with the induction of EROD activity, thus complicating the evaluation of CYP1A induction. CYP1A protein content was not detected in cells exposed to extracts of celluloses or wood chips, possibly due to low amounts of protein available for the assay. Wood and pulp processing, like bleaching, may change the chemical composition of the raw material in a way that reduces the potency for biological effects of the final product, cellulose. This could explain why both UB celluloses and wood chips were more potent in the cells than ECF or TCF bleached celluloses. In this study the PLHC-1 cell line showed its potential for use in evaluating the biological activity existing in pulp and paper mill products and raw materials. The identity and source of the compounds that were able to affect the PLHC-1 cell line remain to be determined.

Several studies have reported a low inducibility of hepatic cytochrome P4501A (CYP1A) activity in European flounder (Platichthys flesus) following exposure to mixtures of polychlorinated biphenyls (PCBs). Here we report on mechanistic studies toward understanding this low CYP1A inducibility of flounder, involving molecular characterization of the Ah receptor (AhR) pathway as well as inhibition of the CYP1A catalytic activity by PCB congeners. Hepatic cytosolic AhR levels in flounder were determined using hydroxylapatite, protamine sulfate adsorption analysis, or velocity sedimentation on sucrose gradients. AhR levels in flounder (approximately 2-7 fmol/mg protein) were much lower than observed generally in rodents (approximately 50-300 fmol/mg protein). Molecular characterization of the flounder AhR was provided by first-strand cDNA synthesis and amplification of flounder hepatic poly(A)+ RNA using RT-PCR. A 690-bp product was found, similar in size to a Fundulus AhR cDNA. The specificity of the 690-bp band was established by Southern blotting and hybridization with a degenerate AhR oligonucleotide. The deduced amino acid sequence of the flounder AhR fragment was 59-60% identical to mammalian AhR sequences. Although the AhR is present in flounder cytosol, we were unable to demonstrate detectable amounts of inducible TCDD-AhR-DRE complex in gel-retardation assays. High induction levels of CYP1A protein and associated EROD activity have been previously found in flounder following exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In contrast, the induction of CYP1A catalytic activity by PCB mixtures remains unexpectedly low. Therefore, we further characterized the inhibitory potential of PCB congeners on CYP1A activity in flounder and compared this with inhibitory effects of PCB congeners on rat CYP1A activity. Analysis in vitro demonstrated that 3,3',4,4'-tetraCB, 3,3',4,4',5-pentaCB, 2,2',4,4',5,5'-hexaCB, 3,3',4,4',5,5'-hexaCB, and the commercial PCB mixture Clophen A50 are potent competitive inhibitors of hepatic microsomal CYP1A catalytic activity in flounder and rat. The K(m) for ethoxyresorufin (0.095 microM) in flounder is strikingly close to Ki's found for the tested PCBs. This emphasizes the possible involvement of PCB congeners in inhibition of EROD activity in PHAH exposed fish. Finally, our data indicate that flounder CYP1A is more efficient in metabolizing ethoxyresorufin than that of rat CYP1A.

The aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor through which halogenated aromatic hydrocarbons such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) cause altered gene expression and toxicity. The AHR belongs to the basic helix-loop-helix/Per-ARNT-Sim (bHLH-PAS) family of transcriptional regulatory proteins, whose members play key roles in development, circadian rhythmicity, and environmental homeostasis; however, the normal cellular function of the AHR is not yet known. As part of a phylogenetic approach to understanding the function and evolutionary origin of the AHR, we sequenced the PAS homology domain of AHRs from several species of early vertebrates and performed phylogenetic analyses of these AHR amino acid sequences in relation to mammalian AHRs and 24 other members of the PAS family. AHR sequences were identified in a teleost (the killifish Fundulus heteroclitus), two elasmobranch species (the skate Raja erinacea and the dogfish Mustelus canis), and a jawless fish (the lamprey Petromyzon marinus). Two putative AHR genes, designated AHR1 and AHR2, were found both in Fundulus and Mustelus. Phylogenetic analyses indicate that the AHR2 genes in these two species are orthologous, suggesting that an AHR gene duplication occurred early in vertebrate evolution and that multiple AHR genes may be present in other vertebrates. Database searches and phylogenetic analyses identified four putative PAS proteins in the nematode Caenorhabditis elegans, including possible AHR and ARNT homologs. Phylogenetic analysis of the PAS gene family reveals distinct clades containing both invertebrate and vertebrate PAS family members; the latter include paralogous sequences that we propose have arisen by gene duplication early in vertebrate evolution. Overall, our analyses indicate that the AHR is a phylogenetically ancient protein present in all living vertebrate groups (with a possible invertebrate homolog), thus providing an evolutionary perspective to the study of dioxin toxicity and AHR function.

Ultrasonic calls produced by young mice reliably elicit investigation and retrieval by adults. While there are large individual differences in the characteristics of these calls, little work has been done to partition that variation. We completed a 4 x 4 diallel cross and Hayman analyses on several characteristics of these cries. The major result was the detection of directional dominance toward a higher rate of calling, longer calls, and calls of lower overall frequency with a greater bandwidth. Within the context of biometrical genetic theory, we conclude that calls with such characteristics may have important fitness value. Extending this idea, we propose that within the population sampled for this study (the animals of the four inbred strains and 12 F1 hybrid groups), the calls most effectively eliciting investigation and retrieval would be calls with the average hybrid values of the diallel cross.

Concentration-dependent induction of cytochrome P4501A (CYP1A) and intracellular porphyrin accumulation were observed following treatment of chicken embryo hepatocyte (CEH) cultures with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 3,3',4,4'-tetrachlorobiphenyl (PCB 77, IUPAC nomenclature), 2,3',4,4',5-pentachlorobiphenyl (PCB 118), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), 3,3',4,4',5,5'-hexachlorobiphenyl (PCB 169), and a commercial mixture of PCBs (Aroclor 1254). For these halogenated aromatic hydrocarbons (HAHs), or mixture, maximal CYP1A activity [measured as ethoxyresorufin-O-deethylase (EROD) activity] and immunodetectable protein were observed at concentrations just prior to, or coincident with, the concentrations at which porphyrin accumulation became evident. Both immunodetectable CYP1A protein and catalytic activity decreased at high concentrations of these compounds, but the rate and extent of decrease of immunodetectable CYP1A protein varied. Time-course studies with PCB 77 indicated a decrease in potency and an increase in maximal CYP1A induction between 24 and 48 hr of exposure which may indicate in vitro metabolism of this HAH. Intracellular accumulation of total porphyrins without CYP1A induction, was observed for 2,2',5,5'-tetrachlorobiphenyl (PCB 52), 2,2',6,6'-tetrachlorobiphenyl (PCB 54), 2,2',3,5',6-pentachlorobiphenyl (PCB 95), 2,2',4,5,5'-pentachlorobiphenyl (PCB 101), 2,2',3,3',6,6'-hexachlorobiphenyl (PCB 136), and 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153). Overall, these results are consistent with a role for CYP1A induction and/or Ah receptor activation in porphyrin accumulation mediated by HAHs with a planar configuration, whereas those that are not planar may mediate porphyrin accumulation by a mechanism not involving induction of CYP1A.

Concentration-dependent effects of halogenated aromatic hydrocarbons (HAHs) on cytochrome P4501A (CYP1A) induction in primary hepatocyte cultures prepared from embryos of chickens (four breeds), pheasants, turkeys, ducks (three breeds), and herring gulls were determined. CYP1A activity was estimated by measuring ethoxyresorufin O-deethylase (EROD) activity and the concentration of immunodetectable CYP1A was estimated using mouse monoclonal antibody 1-12-3 that was prepared against scup (Stenotomus chrysops) CYP1A1. The HAHs studies were 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 3,3',4,4'-tetrachlorobiphenyl (PCB 77, IUPAC nomenclature), 3,4,4',5-tetrachlorobiphenyl (PCB 81), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), 3,3',4,4',5,5'-hexachlorobiphenyl (PCB 169), 2,3,3',4,4'-pentachlorobiphenyl (PCB 105), and 2,3',4,4',5-pentachlorobiphenyl (PCB 118). Two general types of comparisons were made: (1) relative potencies of compounds within a species (expressed relative to TCDD as induction equivalency factors, IEFs) and (2) relative sensitivity of each species to EROD induction by each compound. Three methods for estimating potency were compared. These were: (1) the concentration of inducer that produced a half-maximal (EC50) EROD response, (2) the concentration producing a response equivalent to 10% of the maximal response produced by TCDD (ECTCDD 10%), and (3) a slope ratio method. For each method, the rank order in potency was TCDD > or = TCDF > PCB 126 > PCB 81 > PCB 77 > PCB 169 in chicken, pheasant, and turkey hepatocytes. The rank order was similar in duck and herring gull hepatocytes with the following exceptions: TCDF was approximately 2- to 4-fold more potent than TCDD in duck hepatocytes; PCB 169 induced EROD in gulls, but PCB 77 had no measurable effect in this species. PCB 118 was a relatively weak EROD inducer in most species/breeds, but it did not induce EROD in Pekin ducks or gulls. PCB 105 was a weak inducer in White Leghorn chicken and turkey hepatocytes, but it did not induce EROD in other species. The EC50, ECTCDD10% and slope ratio methods for estimating potencies generally gave similar IEFs for compounds that produced a maximal response that was at least 60% of the maximal response produced by TCDD. For compounds that caused a response that was 50% or lower than that produced by TCDD, EC50-based IEFs were greater (10- to 100-fold) than ECTCDD10%-based IEFs or slope-ratio-based IEFs. Among species, the rank order in sensitivity to EROD induction was chicken > pheasant > turkey > or = duck > or = herring gull. The relative sensitivity of avian hepatocyte cultures to EROD induction by PCB 77 was similar to the relative sensitivity of these species (reported elsewhere) to lethality after in ovo injection of PCB 77. Chicken hepatocyte cultures were 5-10 times more sensitive to EROD induction by TCDD than were pheasant hepatocyte cultures, which is identical to the difference in sensitivity of these species to the lethal effect of TCDD after in ovo injection. Measuring the sensitivity of hepatocyte cultures to EROD induction might be useful for estimating the sensitivity of avian species (including rare or endangered species, where it is impossible to conduct in vivo studies) to the embryotoxic effects of TCDD, non-ortho substituted PCBs, and other aryl hydrocarbon receptor agonists.

Though social behavior has not been overlooked by behavior geneticists, the number of studies is small when compared to those on individual traits. One reason for the neglect may be the difficulty of making connections between genes and social behaviors, which by definition involve the interaction of two or more organisms. Fuller and Hahn (1976) addressed this issue and described three means of establishing social groups that would facilitate genetic analysis. We survey the literature on agonistic behavior in mice from 1976 through 1994 and describe interesting uses of those three methods. One of those methods (the standard tester design) often employs a "noninteractive" social partner. We present data showing that the standard tester design may be more valuable when using an evocative and interactive standard tester.

Hepatic uroporphyria is a well-known effect of halo- genated aromatic hydrocarbons in mammalian and avian systems, including primary cell cultures, but attempts to produce uroporphyria in vertebrate (mammalian) hepatoma lines have been unsuccessful. In this study, the ability of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), and selected chlorobiphenyl congeners to cause uroporphyria was examined in a fish hepatoma cell line (PLHC-1) that expresses aryl hydrocarbon (Ah) receptors and an inducible cytochrome P4501A (CYP1A). Dose-dependent accumulation of porphyrins was observed in cells treated for 48 h with TCDD or 3,3',4,4'-tetrachlorobiphenyl (3,3',4,4'-TCB; IUPAC 77) when the heme precursor delta-aminolevulinic acid (ALA) was present during the last 5 h of treatment. HPLC analysis identified the porphyrins as uroporphyrin (approximately 80%) and heptacarboxylporphyrin (approximately 20%). Uroporphyria did not occur in cells treated with TCDD or 3,3',4,4'-TCB in the absence of added ALA. ALA-dependent porphyrin accumulation was also seen following treatment of PLHC-1 cells with TCDF or with the non-ortho-substituted chlorobiphenyls 3,4,4',5-tetrachlorobiphenyl (IUPAC 81) and 3,3',4,4',5-pentachlorobiphenyl (IUPAC 126). Neither of the mono-ortho-substituted chlorobiphenyls 2,3,3',4,4'-pentachlorobiphenyl (IUPAC 105) or 2,3',4,4'5-pentachlorobiphenyl (IUPAC 118) increased the porphyrin content of PLHC-1 cells. The ability of the PCB congeners to cause porphyria correlated with their ability to induce the CYP1A catalytic activity ethoxyresorufin 0-deethylase (EROD) and immunodetectable CYP1A protein in these cells, suggesting direct or indirect regulation of porphyrin accumulation via the Ah receptor and/or the induced CYP1A. Induction of EROD activity by TCDD, TCDF, and the planar polychlorinated biphenyls was biphasic, with increases at lower concentrations of inducer followed by decreased induction at higher concentrations, as seen previously. EC50 values for porphyrin accumulation were similar to, or slightly higher than, the concentrations at which peak EROD activities were obtained, suggesting a relationship between the decline in EROD activity and enhanced porphyrin accumulation. alpha-Naphthoflavone inhibited TCDD-induced EROD activity and porphyrin accumulation, providing further evidence for the involvement of a fish CYP1A in the mechanism of this prophyria. Addition of 3,3',4,4'-TCB to TCDD-treated cells also inhibited EROD activity, but enhanced porphyrin accumulation, suggesting that an interaction between the halogenated inducer and the induced CYP1A is necessary for the porphyrogenic response. PLHC-1 cells grown in medium supplemented with ALA may be a useful model System for studying mechanisms of chemical uroporphyria induced by Ah receptor agonists.

Glucocorticoids are being found to influence expression of cytochrome P450 (CYP) genes in multiple subfamilies in mammals (J.S. Sidhu, and C.J. Omiecinski (1995) Pharmacogenetics 5, 24--36). In the present study we investigated CYP1A and CYP3A expression in the fish Poeciliopsis lucida hepatocellular carcinoma cell line (PLHC-1) after coadministration of CYP1A and CYP3A inducers, including glucocorticoids. A putative CYP3A protein is expressed in PLHC-1 cells but its content was not altered by exposure of cultures to the prototypical mammalian CYP3A inducers dexamethasone (DEX), pregnenolone-16 alpha-carbonitrile (PCN), or rifampicin (RIF). However, when coadministered with 3,3', 4,4'-tetrachlorobiphenyl or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), DEX but not PCN or RIF caused increases in the degree of CYP1A induction by these aryl hydrocarbon receptor (AHR) agonists. This increase was seen both in CYP1A protein content and rates of ethoxyresorufin-O-deethylase (EROD) activity. DEX alone caused no induction of CYP1A, indicating that the enhancement of CYP1A induction caused by DEX + AHR agonists was not an additive effect but rather a potentiation. The dose of DEX required for maximal potentiation was three orders of magnitude greater at 48 h than the dose required at 24 h. Moreover, the degree of potentiation of CYP1A induction was much greater at the lower doses than at the highest doses of TCDD. There was up to 20-fold potentiation of EROD induction in cultures exposed to 0.1 nM TCDD. Two other glucocorticoid receptor (GR) agonists, cortisol and prednisone, also produced a strong potentiation of CYP1A induction, but other mammalian CYP3A inducers that are not GR agonists, such as the anti-glucocorticoid PCN, the anti-mineralocorticoid spironolactone, or the macrolide antibiotics RIF and troleandomycin, did not potentiate the CYP1A induction in PLHC-1 cells. Addition of the mammalian GR antagonists PCN or RU 38486 reduced the DEX-mediated potentiation of CYP1A induction, whereas spironolactone had no effect on the potentiation. RU 38486 also potentiated the induction of EROD activity by the TCDD, which suggests that RU 38486 acts as a partial GR agonist in PLHC-1 cells. These results suggest that potentiation of CYP1A induction in this nonmammalian cell line proceeds by a classical GR-mediated pathway, independently of the expression of CYP3A. However, the complex interaction between doses of both GR and AHR agonists and duration of exposure, suggests that additional processes influence this potentiation. The unusually strong potentiation at lower doses of TCDD may make PLHC-1 cells particularly suitable in exploring further the consequences of this potentiation.

The PAS domain of a teleost Ah receptor was amplified using reverse transcription-PCR with degenerate primers containing inosine. The deduced amino acid sequence of the amplified cDNA fragment was 62-64% identical with the PAS domains of mammalian Ah receptors. These data demonstrate the homology of Ah receptors in mammals and fish, and reveal regions of this protein that are highly conserved between these diverse vertebrate groups.

Endothelium is a single-cell layer lining blood vessels and constituting capillaries and could be a primary site of chemical effects in the cardiovasculature and systemically. Cytochrome P4501A1 (CYP1A1) is strongly inducible in vertebrate endothelium in vivo by aryl hydrocarbon receptor (AhR) agonists [Mol. Pharmacol. 36:723-729 (1989); Mol. Pharmacol. 41:1039-1046 (1992)]. We investigated CYP1A expression and activity in porcine aorta endothelial cells (PAEC) exposed in culture to the AhR agonists 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3,3',4,4'-tetrachlorobiphenyl (TCB), benzo[a]pyrene (BP), or beta-naphthoflavone (BNF). Immunoblotting with monoclonal anti-CYP1A1 and polyclonal anti-CYP1A1 and anti-CYP1A2 antibodies showed that CYP1A1 was induced in cultures exposed to TCDD, TCB, BP, or BNF but was not detectable in untreated or dimethylsulfoxide-exposed cultures. CYP1A1 was strongly induced at intermediate concentrations (0.1 microM or 1.0 microM) of TCB, BP, or BNF, but induction was suppressed by higher concentrations, a response not due to general toxicity; cell viability (trypan blue exclusion) was > 97% with BNF or TCB at up to 10 microM. CYP1A1 induction by TCDD was maximal at 0.3-1.0 nM. ED50 values for induction of CYP1A1 by TCDD, TCB, and BP were 0.016 nM, 3-10 nM, and 180 nM, respectively. Immunohistochemical analysis confirmed CYP1A1 induction in PAEC but also showed that only some cells in the cultures were induced. Subcellular fractionation, marker enzyme analysis, and immunoblot analysis showed that PAEC had a typical complement of microsomal electron-transport components. NADPH-cytochrome P450 reductase showed comparable rates (approximately 40 nmol/min/mg) in induced and control cultures. Cultures maximally induced by 0.1 microM TCB had microsomal CYP1A1 [ethoxyresorufin-O-deethylase (EROD)] activity averaging 25 pmol/min/mg. Addition of purified rat reductase to PAEC microsomes increased the EROD rates 3-fold. EROD rates measured in intact cells maximally induced by BP, TCB, or TCDD ranged from 15 to 30 pmol/min/mg of whole-cell protein. Methoxyresorufin O-demethylase activity induced by TCDD was 2 pmol/min/mg, i.e., < 10% of the EROD activity. In cultures in which CYP1A1 was strongly induced, CYP1A2 was not detectably expressed. The CYP1A2 inducer acenaphthylene did not induce EROD or methoxyresorufin O-demethylase in intact cells. The results show that CYP1A1 but not CYP1A2 is strongly induced in mammalian endothelial cells in culture and that CYP1A1 is active in intact cells, although the catalytic rates are low.(ABSTRACT TRUNCATED AT 400 WORDS)

Cytochrome P4501A1 (CYP1A1) is known to play important roles in the activation and detoxification of carcinogens and other toxicants in vertebrate animals, including fish. Although extensively studied in mammalian systems, the regulation of CYP1A forms in other vertebrates is less well understood. We examined the time course and dose-response relationships for induction of CYP1A1 mRNA, protein, and catalytic activity by 2,3,7,8-tetrachlorodibenzofuran (TCDF) in the marine fish Stenotomus chrysops (scup). The time course of CYP1A1 induction was determined following a single ip dose (10 nmol/kg) of 2,3,7,8-TCDF. Hepatic ethoxyresorufin O-deethylase activity was increased after 1 day, reached a maximum by 8 days, and was still elevated 14 days after treatment. The content of immunodetectable CYP1A1 protein in liver was elevated on Day 1 and continued to increase through 14 days. CYP1A1 protein content was also strongly induced in heart and gill beginning at 2 days after treatment and extending through Day 14. Hepatic CYP1A1 mRNA was strongly induced by 1 day after dosing and remained elevated through 14 days. The sustained induction of CYP1A1 mRNA by 2,3,7,8-TCDF contrasts with the transient induction seen previously in fish treated with nonhalogenated inducers and most likely reflects differences in persistence of the inducers. Dose-response studies indicated that induction of CYP1A1 mRNA, protein, and catalytic activity occurred following doses of 2,3,7,8-TCDF as low as 0.4 nmol/kg (120 ng/kg), within the range of whole-body contents of this congener measured in fish from contaminated environments. The estimated dose producing half-maximal CYP1A1 induction in scup was approximately 2-10 nmol/kg, suggesting that the sensitivity of these fish to induction may be as great as or greater than that of rats. In contrast to previous results obtained with 3,3',4,4'-tetrachlorobiphenyl (TCB) and beta-naphthoflavone, which appear to inhibit or inactivate CYP1A1 in fish and other vertebrates, there was a good correlation among levels of CYP1A1 mRNA, protein, and catalytic activity in individual fish following various doses of 2,3,7,8-TCDF. The difference in response to 2,3,7,8-TCDF versus 3,3',4,4'-TCB may reflect differences in the inducing potencies of the two compounds relative to their similar potencies as inhibitors of CYP1A1 catalytic activity. In additional studies to evaluate structure-activity relationships for CYP1A1 induction by chlorinated dibenzofurans in fish, scup were treated with 2,3,6,8-tetrachlorodibenzofuran (2,3,6,8-TCDF). At 10 or 50 nmol/kg, 2,3,6,8-TCDF was inactive as an inducer of CYP1A1 mRNA, protein, or catalytic activity.(ABSTRACT TRUNCATED AT 400 WORDS)

Understanding the effects of environmental contaminants on cetaceans and other marine mammals will require information on the biochemistry of xenobiotic metabolism in these species. We characterized the hepatic microsomal cytochrome P450 system in beluga whales (Delphinapterus leucas) from the Canadian Arctic. The content of native P450 averaged 0.203 and 0.319 nmol/mg microsomal protein, cytochrome b5 content averaged 0.199 and 0.236 nmol/mg, and rates of NADPH-cytochrome c reductase were 79 and 76 nmol/min/mg, for females and males respectively. Ethoxyresorufin O-deethylase (EROD), pentoxyresorufin O-depentylase (PROD), and benzo[a]pyrene (BP) hydroxylase (AHH) activities were significantly greater in males than in females, and were highly correlated with one another (r2 between 0.853 and 0.912). HPLC analysis of in vitro BP metabolites revealed benzo-ring (7,8- and 9,10-) dihydrodiols, consistent with activation of this compound, as well as 4,5-dihydrodiol,3-OH-, 7-OH-, and 9-OH-BP and 1,6- and 3,6-quinones. Estradiol 2-hydroxylase activity did not differ between sexes, and rates did not correlate with those of the other activities. Antibodies against scup P450B (an apparent teleost CYP2B) and rat CYP2B1 did not recognize proteins in beluga liver microsomes, but there was a protein detected by antibodies to PB-inducible rabbit CYP2B4. Antibodies to ethanol and ketone-inducible rat CYP2E1 reacted with two proteins in beluga liver microsomes. Antibodies specific to hydrocarbon-inducible CYP1A1 and/or CYP1A2 forms showed a single protein band, apparently more closely related to CYP1A1. The content of CYP1A was fivefold greater in male than in female beluga. CYP1A content was highly correlated with EROD, PROD, and AHH activities, suggesting that this P450 form is a primary catalyst for these reactions in beluga. CYP1A content and activity were highly correlated with the concentrations in blubber of non-ortho and mono-ortho PCB congeners, compounds that induce CYP1A in other mammals. These results indicate that a CYP1A is a catalyst for the metabolism of aromatic hydrocarbon pollutants in the beluga whale, and strongly suggest that this protein is induced in these organisms by environmental contaminants, including PCBs. The results support the measurement of CYP1A expression as a biomarker of exposure to inducers in marine mammals. The full functional and evolutionary relationships of beluga CYP1A and of beluga proteins immunologically related to other P450 forms are uncertain.

The mammalian aromatic hydrocarbon (Ah) receptor is a soluble protein involved in the regulation of gene expression by halogenated aromatic hydrocarbons such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Little is known, however, about the presence and properties of this receptor in nonmammalian species. In these studies, we sought evidence for an Ah receptor in the liver or liver-equivalent of diverse species of invertebrate and vertebrate animals. Velocity sedimentation analysis of hepatic cytosol labeled with [3H]TCDD gave equivocal results with three species of marine fish. In subsequent studies, photoaffinity labeling with 2-azido-3-[125I]iodo-7,8-dibromodibenzo-p-dioxin was used to identify the Ah receptor. Specific labeling (labeling that could be displaced by an excess of unlabeled ligand) was observed in seven species of teleost and elasmobranch fish, including winter flounder (Pleuronectes americanus), killifish (Fundulus heteroclitus), scup (Stenotomus chrysops), rainbow trout (Oncorhynchus mykiss), brown trout (Salmo trutta), and dogfish (Mustelus canis and Squalus acanthias). Specific labeling was also found in cytosolic fractions prepared from PLHC-1 fish hepatoma cells and livers of a turtle (Chrysemys picta) and a cetacean, the beluga whale Delphinapterus leucas. The fish Ah receptor was sensitive to conditions of tissue preparation; inclusion of proteinase inhibitors in the homogenization buffer stabilized the receptor in some species. There was heterogeneity in the apparent molecular mass of the largest specifically labeled band in each species; these ranged from 105 to 146 kDa, slightly larger on average than mammalian Ah receptors (95-130 kDa). In contrast to the results obtained with teleost and elasmobranch fish, no specifically labeled polypeptides were detectable in cytosol from two agnathan fish species (hagfish Myxine glutinosa and sea lamprey Petromyzon marinus), the tunicate Ciona intestinalis, or any of nine other invertebrate species representing eight classes in four phyla. Overall these results suggest that the Ah receptor evolved at least 450 million years ago, prior to the divergence of bony and cartilaginous fishes. Although the exact relationship between receptor presence and dioxin responsiveness in these species is uncertain, our data predict that the invertebrate species examined in this study, which appear to lack an Ah receptor protein like that seen in mammals and fish, may be less sensitive than vertebrates to the effects of environmental contaminants that act through this transcriptional regulator.

The ubiquity of lead in our environment, its toxic nature and its potential to alter behavior of humans and animals has stimulated much research. In addition to the well known, but complex, changes in activity and performance of learned tasks following exposure to lead, an increasing body of literature suggests that changes in social behavior also occur. This study examined the impact of ingesting a 0.5% lead acetate solution (as the only available fluid)--a protocol that results in ca. 100 micrograms/dl blood-levels in our Binghamton Heterogenous (HET) mice--on food competition in both male and female HET mice. Effects of this lead exposure on cricket predation by the same HET mice also were observed. Our results from the food competition study (Experiment I) show, compared with water controls, that such exposure to lead increases both food possession time and amount of social contact after food consumption; but very little agonistic behavior took place in either the water control or lead-exposed competition testing sessions. In the cricket predation observations (Experiment II) there was a tendency for lead exposure to reduce the latency of males to attack, and the indication that lead-exposed females initially attacked a cricket's legs more often than any of the other groups. In fact, suggestions of such gender x treatment interactions occurred in both the food competition and the predation work. Overall, we believe our results, in conjunction with other relevant literature, suggest that exposure to lead reduced the individual's general fitness, even when levels are relatively low.

Differences in expression of cytochrome P450 forms and their functions in different organs and cell types could determine the response of those cells and organs to xenobiotics. Recently, we described the cellular localization of cytochrome P450IA1 (P450E) induced in 10 organs or organ systems of the fish, Stenotomus chrysops (scup) treated with 3,3',4,4'-tetrachlorobiphenyl or with 2,3,7,8-tetrachlorodibenzofuran. (R.M. Smolowitz, M.E. Hahn, and J.J. Stegeman, Drug Metab. Dispos. 19, 113, 1991). Here we describe the presence and localization of P450IA1 in organs of scup sampled directly from an environment contaminated by chlorinated biphenyls and bibenzofurans, the outer New Bedford Harbor of Massachusetts. Western blot analysis of microsomes from selected organs (liver, kidney, gill, and heart), using monoclonal antibody 1-12-3, revealed induced levels of P450IA1 in each. The localization of P450IA1 in these and other organs was determined in sections prepared by standard histological methods and stained with MAb 1-12-3 in an indirect peroxidase labeling method. P450IA1 was detected in multiple cell types in liver, including hepatic, pancreatic, and vascular tissue. Kidney and gut also showed prominent P450IA1 levels in epithelial structures and in vascular endothelial cells. Specific staining was detected in endothelial cells, but not other cell types, in heart, gill, spleen, testis, ovary, nose, and brain. In heart, the staining was present in the endocardium of atrium and ventricle, and endothelium of the coronary vasculature and great vessels. The results demonstrate that P450IA proteins are induced in many organs of fish exposed to environmental chemicals in the wild, with patterns of cellular localization like those seen in fish experimentally treated with known inducers. The strong staining of P450IA1 in endothelial cells in all organs examined supports experimental results indicating that endothelium is a major site of P450IA1 induction. Our results indicate further that immunohistochemistry is a useful method for detecting P450 induction as a biomarker for exposure.

Four inbred strains of mice, DBA/2J, C57BL/10J, BALB/cJ, and SJL/J, were mated in a diallel cross. The cerebella of the F1 generation were examined for the presence (Type I) or absence (Type II) of an intraculminate fissure between vermian lobule IV and vermian lobule V (the ventral and dorsal lobules of the culmen). One strain (DBA/2J) consistently expressed the Type I pattern. Another strain (SJL/J) expressed predominantly the Type II pattern. The other two strains (C57BL/10J and BALB/cJ) and many of the hybrids exhibited variability in their expression of the foliation patterns. The results were analyzed using biometrical genetic procedures and showed significant additive and dominance genetic effects and a maternal effect. Correlations of these cerebellar anatomical variants with the development of behavior are discussed.

Ethanol (ETOH)-induced locomotor activation and depression were studied in 23 genotypes of mice. This included a diallel cross of four inbred strains tested with a range of ETOH doses from 0 to 2.75 g/kg. The diversity in shapes of the biphasic ETOH dose-response curves was both qualitative and quantitative, and additive gene action characterized the genetic control of the dose-response curve. Small dominance effects were typically directional in the direction of more activation, or resistance to sedation. No evidence was found for maternal effects, sex linkage, or epistasis. Sex differences were seen in the increased susceptibility of male mice to locomotor sedation at higher ETOH doses. In the diallel cross, there was no correlation between the degree of activation produced by low ETOH doses and sedation produced by higher doses. This indicates that while considerable genetic influences exist for both activational and sedative domains of ETOH effects, these genetic influences are relatively independent.

We describe a method for the rapid clean-up of rodent urine samples prior to the analysis of porphyrin carboxylic acids by reversed-phase high-performance liquid chromatography (HPLC) with fluorescence detection. A simple pretreatment step using chromatography on a Dowex 1X8 anion-exchange resin effectively removes fluorescent substances that are present in rodent urine and would otherwise interfere with the detection and quantitation of urinary porphyrins by HPLC. Recovery of porphyrins with four to eight carboxyl groups (coproporphyrin to uroporphyrin) averaged 93% using this procedure. The use of this method to determine the amount of individual porphyrins present in the urine of hexachlorobenzene-treated mice is illustrated.

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.

The role of the Ah locus in hexachlorobenzene (HCB)-induced porphyria and the possible involvement of P-450 cytochromes P(1)450 and P(3)450 in the pathogenesis of this disease were investigated in two congenic strains of C57BL/6J mice that differ only at this locus. Female B6-Ahb mice (Ah receptor: approximately 30-70 fmol/mg of cytosolic protein) and B6-Ahd mice (Ah receptor: undetectable) were pretreated with iron (500 mg/kg) and then fed a diet containing 0 or 200 p.p.m. of HCB for up to 17 weeks. Mice from the two strains consumed similar amounts of HCB. Urinary excretion of porphyrins was increased after 7 weeks of HCB treatment in B6-Ahb mice, and after 15 weeks was over 200 times greater than that of mice given iron only. In B6-Ahd mice, porphyrin excretion did not begin to increase until after 13 weeks, and after 15 weeks was only six times greater than that of controls. Similar differences were seen in the 15-week hepatic porphyrin concentrations (B6-Ahb: 1110 +/- 393; B6-Ahd: 17.6 +/- 14.5; controls: approximately 0.20 nmol/g). Uroporphyrinogen decarboxylase (EC 4.1.1.37) activity was diminished by 70 and 20% in B6-Ahb B6-Ahd mice respectively after 15 weeks of treatment with HCB. Cytochromes P(1)450 and P(3)450 were measured in hepatic microsomes (microsomal fractions) by radioimmunoassay and immunoblotting, using antisera raised against the orthologous rat isoenzymes P450c and P450d. HCB induced small amounts of a protein recognized by anti-P450c (P(1)450) in B6-Ahd mice, but not in B6-Ahd mice. Relatively large amounts of a protein recognized by anti-P450d (P(3)450) were induced in both strains, but to a somewhat greater extent in the B6-Ahb mice. The hepatic accumulation of HCB at 15 weeks was greater in B6-Ahb than in B6-Ahd mice, in association with elevated hepatic lipid levels in the former strain. The results of this experiment indicate that the Ah locus influences the susceptibility of C57BL/6J mice to HCB-induced porphyria and are consistent with the suggestion that the sustained induction of P(3)450 and/or P(1)450 may be a causative factor in the development of this disease.

Hexachlorobenzene (HCB) produces hepatic porphyria and induces the hepatic cytochrome P450 isozymes P450c (P450IA1) and P450d (P450IA2) in rodents. These and other effects of HCB resemble those of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), which acts via its binding to the aromatic hydrocarbon (Ah) receptor. We therefore examined the ability of HCB to interact with this receptor in vitro and in vivo. HCB, at concentrations of 1 microM or higher, inhibited the specific binding of [3H]TCDD (0.3 nM) to the Ah receptor in vitro, whereas the solubility of [3H]TCDD was affected only at 100 microM HCB. The inhibition was competitive, with a KI of approximately 2.1 microM. In rats fed a diet containing 3000 ppm HCB for varying times (4 h to 7 days), the specific binding of [3H]TCDD in hepatic cytosol was reduced by up to 40%, as observed previously for known Ah receptor agonists. The decrease in [3H]TCDD specific binding in cytosol of HCB-treated rats was due principally to a decrease in the number of binding sites for [3H]TCDD rather than competition from residual HCB. As shown by immunoblotting and radioimmunoassay, HCB induced the cytochrome P450 isozymes P450c and P450d, which are regulated by the Ah receptor, as well as the phenobarbital-inducible isozymes P450b and P450e. Together these results indicate that HCB is a weak agonist for the Ah receptor, and suggest that some of its effects may be mediated by its interaction with this gene-regulatory protein.

Polychlorinated biphenyl congeners that are abundant in environmental samples, and known to induce hepatic monooxygenase isozymes in the P450IA gene subfamily in mammals, were examined for their ability to induce hepatic monooxygenase activity in scup, a marine teleost. Scup were dosed ip with 3,3',4,4'-tetrachlorobiphenyl (congener 77), 2,3,3',4,4'-pentachlorobiphenyl (congener 105), 2,3',4,4',5-pentachlorobiphenyl (congener 118), 2,2',3,4,4',5'-hexachlorobiphenyl (congener 138), 2,2',3,3',4,4'-hexachlorobiphenyl (congener 128), or beta-naphthoflavone and examined for increases in ethoxyresorufin O-deethylase (EROD) activity, immunodetectable cytochrome P450E (the EROD catalyst in scup), and in vitro translatable mRNA for P450E. Monooxygenase parameters were significantly induced only by 3,3',4,4'-tetrachlorobiphenyl (TCB). However, while translatable mRNA for P450E was induced at all doses (1, 5, and 10 mg/kg), EROD activity and P450E were decreased at the 5 and 10 mg/kg doses, relative to the response at 1 mg/kg. A strong relationship between residual TCB concentration in the liver and the decreased EROD activity was evident at the higher doses of TCB. Aminopyrine N-demethylase, a monooxygenase activity not catalyzed by P450E, was unaffected by TCB treatment, indicating a specificity in the TCB effect. Analysis in vitro revealed that TCB was a potent competitive inhibitor of EROD activity, with half-maximal inhibition at 0.3 microM, near the Km for ethoxyresorufin, suggesting one mechanism for the in vivo effect of TCB. These results demonstrate that PCB congeners with ortho-chlorine substitution, and which are effective inducers of AHH and EROD activity in mammals, are ineffective, at the doses tested, as inducers in the teleost scup.

Fuller Brain Weight Selection lines are well differentiated for 42-day brain weight and a high degree of genetic homogeneity for trait-relevant genes is indicated. Using these lines, random bred descendants of the foundation population and an inbred line, biometrical analysis of brain growth from birth to 23 days was attempted. While strain means differ as expected, within and between litter variances for genetically heterogeneous mice were typically no greater than for more genetically homogeneous selected lines. Possible explanations involving gestational age, intra-uterine and postnatal competition and ontogenetic buffering are discussed.

The genetics of social behavior presents special difficulties because the phenotype is the product of an interaction between two or more individuals. Social interactions are of two kinds: (1) cooperative, in which the probabilities of transmission of the genes of all participants are similarly affected by the outcome, and (2) agonistic, in which the probabilities for the participants are affected in opposite directions. The latter are of particular interest for evolutionary theory. Three major types of designs for measuring social behavior in genetic experiments are available: (1) homogeneous sets, (2) standard tester, and (3) tester panel representing a reference population. The advantages and limitations of each method are discussed. Important areas for future development include the relationship of genetic and experiential factors in early life to social status as an adult and the extension of the genetic analysis of social behavior to natural populations.

Brain growth was studied from day of birth through 23 days of age in three outbred and one inbred groups of mice. The results showed that the brain grows rapidly from Birth through 11 days and quite slowly thereafter. We found no evidence of the several spurts and plateaus in growth that are central to the theory of phrenoblysis (correlated brain and mind growth). Our results show the main features of mouse brain growth to parallel those of human brain growth except for timing of rapid and slow growth.

This study compared the ability of hexachlorobenzene (HCB) and of other chlorinated benzenes to induce cytochrome P-450 isozymes in rat liver. HCB (greater than 99% pure) induced both the phenobarbital-inducible forms (cytochrome P-450b and P-450e) and the 3-methylcholanthrene (3-MC)-inducible forms (P-450c and P-450d) of cytochrome P-450. However, HCB differed from many 3-MC-type inducers by inducing P-450d preferentially over P-450c. In contrast to HCB, the lower chlorinated benzenes did not induce significant amounts of P-450c or P-450d in the rat, but were phenobarbital-type inducers, inducing P-450b and P-450e. These data indicate that the hepatic effects of HCB differ markedly from those of other chlorinated benzenes. However, chlorinated dibenzodioxins also induce P-450c and P-450d in the rat, and although chlorinated dibenzodioxins and dibenzofurans contaminate certain commercial products, none were detected by gas chromatography/mass spectrometry (detection limit 0.5 ppm) in the HCB used in this study. The evidence that HCB interacted with the receptor for 2,3,7,8-tetrachlorodibenzo-para-dioxin (TCDD) was equivocal. At a concentration of 10(-6) M, HCB produced a slight decrease (18%) in the binding of 3H-TCDD to this protein in vitro, but had no effect at lower concentrations. However, as an inducer of two 3-MC-inducible isozymes of P-450, HCB was clearly more effective in aromatic-hydrocarbon-responsive mice (C57Bl/6J) than in non-responsive mice (DBA/2J), suggesting that HCB may act through the Ah receptor.