Ah receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin: ontogeny in chick embryo liver

Molecular and functional characterization of aryl hydrocarbon receptor nuclear translocator 1 (ARNT1) and ARNT2 in chicken (Gallus gallus)

Our previous studies have provided evidence that birds have two isoforms of aryl hydrocarbon receptors (AHR1 and AHR2) and AHR nuclear translocators (ARNT1 and ARNT2) that potentially mediate toxic responses to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds. We have also shown that while both in vitro-expressed chicken AHR1 (ckAHR1) and AHR2 (ckAHR2) exhibit binding affinities to TCDD, only ckAHR1 but not ckAHR2 showed a TCDD-dose-dependent transactivation potency of chicken cytochrome P450 1A5 (ckCYP1A5) in in vitro reporter gene assays. To explore the molecular mechanism of functional difference in the two ckAHRs, the present study investigated the molecular characteristics and function of chicken ARNT (ckARNT) that is a potential dimerization partner for the activation of ckAHR. The full-length ckARNT1 and ckARNT2 cDNAs were isolated and their alternative splice variants were also identified. The ckARNT1 transcript was ubiquitously expressed in various tissues, but ckARNT2 showed restricted expressions in brain, kidney and eye, indicating a similar expression pattern to mammalian ARNTs. The expressions of tagged-ckARNT1 and -ckARNT2 were confirmed in a chicken hepatoma LMH cells by western blot analyses, and their interactions with each ckAHR and a specific recognition DNA element, xenobiotic response element (XRE), were examined by gel shift assays. The result showed that ckARNT1 and ckARNT2 dimerize with each ckAHR isoform and bind with the XRE in a TCDD-dependent manner. Hence, we conclude that functional loss on the dimerization with ckARNTs or the XRE binding is not the major cause of the deficient TCDD-dependency of ckAHR2 for the transactivation. Furthermore, in vitro reporter gene assays showed that transfected ckARNT1 failed to modulate the transcriptional induction of ckAHR-mediated ckCYP1A5 gene by TCDD in COS-7 and LMH cells, whereas ckARNT2 could potentiate the TCDD-dependent response in COS-7 but not in LMH cells. This suggests that ckARNT2 has a distinct role from ckARNT1 in AHR signaling pathway and in a cell-specific mode of action.

Effects of in ovo exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin on hepatic AHR/ARNT-CYP1A signaling pathways in common cormorants (Phalacrocorax carbo)

Our previous studies have isolated multiple isoforms of aryl hydrocarbon receptors (AHRs) and AHR nuclear translocators (ARNTs) in avian species. However, roles of such genes on cytochrome P450 1A (CYP1A) expression are not fully understood. To investigate the effects of dioxins on the hepatic expression profiles of AHR1, AHR2, ARNT1 and ARNT2 in avian species, and whether the expression levels of AHRs and ARNTs affect the transcriptions of CYP1A4 and CYP1A5 genes, the eggs of common (great) cormorants (Phalacrocorax carbo) collected from Lake Biwa, Japan, were in ovo administrated with 0, 1500 and 4500pg/g egg of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), and the hepatic expression levels of AHRs, ARNTs and CYP1As in embryos were monitored with two-step real-time RT-PCR. In young and adult cormorants collected from the same location, the hepatic expressions of these genes were also measured to understand the effects of growth stage. The residue levels of TCDD and other chlorinated dioxin-like congeners (DLCs) in the body of cormorants were quantified with high-resolution gas chromatography equipped with mass-spectrometry. There was no observable effect of in ovo TCDD treatment even at the highest dosage on mortality, body weight and morphology of the liver, heart, spleen, kidney and lung in the embryos. The mRNA expression of ARNT2 was slightly suppressed by the treatment with TCDD, while no alteration was observed for the expression of AHR1, AHR2 and ARNT1. Expressions of CYP1A4 and CYP1A5 were dose-dependently enhanced by TCDD, but CYP1A4 mRNA level increased more prominently than CYP1A5, indicating the difference in induction efficiency between the CYP1A isozymes. Comparison of hepatic mRNA levels of these genes among embryonic, young and adult cormorants revealed that young and adult cormorants had greater CYP1A5 expression levels than embryos, independently of the accumulation levels of DLCs. These results suggest that the hepatic induction of each CYP1A by DLCs in cormorants occurs in an isoform-specific manner and CYP1A5 expression, at least partially, depends on the factors related to the growth of cormorants, but the transcriptional processes of CYP1As are not related to the expression levels of AHRs and ARNTs. This study yielded results supporting our previous observations that in reality, high accumulation of DLCs induces hepatic CYP1A4 and 1A5 expressions in the wild cormorant population.

The molecular basis for differential dioxin sensitivity in birds: role of the aryl hydrocarbon receptor

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and related halogenated aromatic hydrocarbons (HAHs) are highly toxic to most vertebrate animals, but there are dramatic differences in sensitivity among species and strains. Aquatic birds including the common tern (Sterna hirundo) are highly exposed to HAHs in the environment, but are up to 250-fold less sensitive to these compounds than the typical avian model, the domestic chicken (Gallus gallus). The mechanism of HAH toxicity involves altered gene expression subsequent to activation of the aryl hydrocarbon receptor (AHR), a basic helix-loop-helix-PAS transcription factor. AHR polymorphisms underlie mouse strain differences in sensitivity to HAHs and polynuclear aromatic hydrocarbons, but the role of the AHR in species differences in HAH sensitivity is not well understood. Here, we show that although chicken and tern AHRs both exhibit specific binding of [3H]TCDD, the tern AHR has a lower binding affinity and exhibits a reduced ability to support TCDD-dependent transactivation as compared to AHRs from chicken or mouse. We further show through use of chimeric AHR proteins and site-directed mutagenesis that the difference between the chicken and tern AHRs resides in the ligand-binding domain and that two amino acids (Val-325 and Ala-381) are responsible for the reduced activity of the tern AHR. Other avian species with reduced sensitivity to HAHs also possess these residues. These studies provide a molecular understanding of species differences in sensitivity to dioxin-like compounds and suggest an approach to using the AHR as a marker of dioxin susceptibility in wildlife.

Aryl hydrocarbon receptors: diversity and evolution

Animals have evolved inducible enzymatic defenses to facilitate the biotransformation and elimination of toxic compounds encountered in the environment. The sensory component of this system consists of soluble receptors that regulate the expression of certain isoforms of cytochrome P450, other enzymes, and transporters in response to environmental chemicals. These receptors include several members of the steroid/nuclear receptor superfamily as well as the aryl hydrocarbon receptor (AHR), a member of the bHLH-PAS gene superfamily. In addition to its adaptive functions, the AHR serves poorly understood physiological roles; interference with those roles by dioxins and related chemicals causes toxicity. One approach to understanding the physiological significance of the AHR is to characterize its structure, function, and regulation in diverse species, including mammals, birds, fish, and invertebrates. These animal groups include model species with unique features that can be exploited to broaden our understanding of AHR function. Studies carried out in diverse species also provide phylogenetic information that allows inferences about the evolutionary history of the AHR. This review summarizes the current understanding of AHR diversity among animal species and the evolution of the AHR signaling pathway, as inferred from molecular studies in vertebrate and invertebrate animals. The AHR gene has undergone duplication and diversification in vertebrate animals, resulting in at least three members of an AHR gene family: AHR1, AHR2, and AHR repressor. The inability of invertebrate AHR homologs to bind dioxins and related chemicals, along with other evidence, suggests that the adaptive role of the AHR as a regulator of xenobiotic metabolizing enzymes may have been a vertebrate innovation. The physiological functions of the AHR during development appear to be ancestral to the adaptive functions. Sensitivity to the developmental toxicity of dioxins and related chemicals may have had its origin in the evolution of dioxin-binding capacity of the AHR in the vertebrate lineage.

2,3,7,8-Tetrachlorodibenzo-p-dioxin alters melatonin metabolism in fish hepatocytes

Pineal hormone melatonin is an important regulator of endocrine and circadian rhythms in vertebrates. Since liver is assumed to be the major organ in the metabolism of this indole hormone, we investigated the effect of the known Ah-receptor agonist, 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) on melatonin metabolism in fish hepatocytes as well as the in vitro effect of melatonin on trout hepatic microsomal cytochrome P4501A (CYP1A) catalyst. Primary cell cultures of rainbow trout hepatocytes were exposed to [3H]melatonin (1 nM to 1 microM) alone and in combination with TCDD (50 pM) at 15 degrees C for 24 or 48 h. Analysis of melatonin and its metabolites in the culture medium and hepatocytes by HPLC revealed that about 96% of the added [3H]melatonin was metabolised after 24 h in both control and TCDD treated cultures. 3H-radioactivity was found mainly in the culture medium and less than 5% of the total 3H-radioactivity retained inside hepatocytes. Of the HPLC separated metabolites, one coeluted with 6-hydroxymelatonin and one unknown metabolite eluted after 6-hydroxymelatonin. In addition, two other metabolites were more water-soluble than 6-hydroxymelatonin and were considered to be conjugated products. Treatment of the hepatocytes with TCDD increased the amount of the major oxidated product, 6-hydroxymelatonin, about 2.5-fold after 24 h and 1.2-fold after 48 h exposure, respectively when compared with the control cultures. Whereas the amount of the unknown metabolite eluting after 6-hydroxymelatonin decreased about 1.3-fold after 24 h and 1.2-fold after 48 h exposure, respectively. Melatonin alone did not affect P4501A associated EROD-activity or CYP1AmRNA levels in the primary hepatocyte cultures. TCDD-treatment increased EROD-activity 3 to 5-fold and respective CYP1AmRNA content 6 to 14-fold, when compared with the control or melatonin-treated cultures. Furthermore, melatonin competitively inhibited EROD-activity in liver microsomes with a Ki value of 62.06+/-3.78 microM. The results show that TCDD alters metabolic degradation of melatonin in hepatocytes and suggest that P4501A may be an important P450 isoenzyme involved in oxidative metabolism of melatonin in fish liver.

Basal and induced EROD activity in the chorioallantoic membrane during chicken embryo development

The chorioallantoic membrane (CAM) is a highly vascularized tissue that takes part in the respiratory exchange of gases through the eggshell. Although the CAM may be exposed to environmental contaminants, its response to pollutants has not been studied. We examined the cytochrome P4501A (CYP1A)-catalyzed deethylation of 7-ethoxyresorufin (EROD) in the CAM during chicken embryo development. EROD was constitutively present and was inducible by the aryl hydrocarbon (Ah) receptor agonist 3,3',4,4',5-pentachlorobiphenyl (PCB 126). Our results suggest the CAM as a first line of defence of the avian embryo against toxic compounds, but also as a target for CYP1A-activated chemicals.

The existence of the 4S polycyclic aromatic hydrocarbon-protein binding in 14-day-old chick embryo liver

Cytochrome P-450IA1, the isozyme most closely associated with aryl hydrocarbon hydroxylase (AHH), is regulated by two high-affinity binding proteins, the 4S polycyclic aromatic hydrocarbon (PAH)-binding protein which primarily binds PAHs and the 8S Ah (dioxin) receptor which binds 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and like congeners. The present study was conducted to determine whether the 4S protein existed in 14-day-old chick embryo liver when AHH activity is maximal to determine if they are linked as is the 8S Ah receptor and to confirm the existence of the dioxin receptor by investigating their ligand binding characteristics in the presence and absence of sodium molybdate, an agent that stabilizes steroid hormone receptors and partially stabilizes the dioxin receptor. Competitive ligand binding studies were performed with liver cytosol from livers of male 14-day-old chick embryos using [3H]-benzo[a]pyrene (B[a]P) or [3H]-TCDD in the presence and absence of a 200-fold excess of B[a]P, benzo[e]pyrene (B[e]P), 3-methylcholanthrene (3-MC), and tetrachlorodibenzofuran (TCDBF). Specific PAH-binding activity was assayed using sucrose gradient analysis. In the absence of molybdate, the 4S PAH-binding protein had high affinity for B[a]P, B[e]P, 3-MC, but very low affinity for TCDBF; the Ah receptor exhibited high affinity for TCDBF. In the presence of sodium molybdate, the Ah receptor was stabilized while the 4S PAH-binding protein was relatively unaffected. These results affirm the existence of two distinct PAH-binding proteins in 14-day-old chick embryo liver cytosol and suggest a linkage of the 4S protein to AHH.

The aryl hydrocarbon receptor: a comparative perspective

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.

Molecular basis for effects of carcinogenic heavy metals on inducible gene expression

Certain forms of the heavy metals arsenic and chromium are considered human carcinogens, although they are believed to act through very different mechanisms. Chromium(VI) is believed to act as a classic and mutagenic agent, and DNA/chromatin appears to be the principal target for its effects. In contrast, arsenic(III) is considered nongenotoxic, but is able to target specific cellular proteins, principally through sulfhydryl interactions. We had previously shown that various genotoxic chemical carcinogens, including chromium (VI), preferentially altered expression of several inducible genes but had little or no effect on constitutive gene expression. We were therefore interested in whether these carcinogenic heavy metals might target specific but distinct sites within cells, leading to alterations in gene expression that might contribute to the carcinogenic process. Arsenic(III) and chromium(VI) each significantly altered both basal and hormone-inducible expression of a model inducible gene, phosphoenolpyruvate carboxykinase (PEPCK), at nonovertly toxic doses in the chick embryo in vivo and rat hepatoma H411E cells in culture. We have recently developed two parallel cell culture approaches for examining the molecular basis for these effects. First, we are examining the effects of heavy metals on expression and activation of specific transcription factors known to be involved in regulation of susceptible inducible genes, and have recently observed significant but different effects of arsenic(III) and chromium(VI) on nuclear transcription factor binding. Second, we have developed cell lines with stably integrated PEPCK promoter-luciferase reporter gene constructs to examine effects of heavy metals on promoter function, and have also recently seen profound effects induced by both chromium(VI) and arsenic(III) in this system. These model systems should enable us to be able to identify the critical cis (DNA) and trans (protein) cellular targets of heavy metal exposure leading to alterations in expression of specific susceptible genes. It is anticipated that such information will provide valuable insight into the mechanistic basis for these effects as well as provide sensitive molecular biomarkers for evaluating human exposure.

A pharmacodynamic analysis of TCDD-induced cytochrome P450 gene expression in multiple tissues: dose- and time-dependent effects

The ability of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, dioxin) to alter gene expression and the demonstration that the induction of CYP1A2 is responsible for hepatic TCDD sequestration suggest that both pharmacokinetic and pharmacodynamic events must be incorporated for a quantitative description of TCDD disposition. In this paper, a biologically based pharmacodynamic (BBPD) model for TCDD-induced biochemical responses in multiple tissues was developed. The parameters responsible for tissue response were estimated simultaneously with a refined physiologically based pharmacokinetic (PBPK) model developed by Wang et al. (1997a), by using the time-dependent effects of TCDD on induced CYP1A1/CYP1A2 gene expression in multiple target tissues (liver, lungs, kidneys, and skin) of female Sprague-Dawley rats treated with 10 microgram TCDD/kg for 30 min, 1, 3, 8, or 24 h, or 7, 14, or 35 days. This refined BBPD model developed based on the time-course of TCDD-induced CYP1A1/CYP1A2 protein expression, and associated enzymatic activities well described the dose-dependent effects of TCDD on cytochrome P450 protein expression and associated enzyme activities in the multiple tissues of female Sprague-Dawley rats at 3 days following a single exposure to TCDD (0.01-30.0 micromgram TCDD/kg). This is the first BBPD model to quantitatively describe the time- and dose-dependent effects of TCDD on induced CYP1A1/CYP1A2 protein expression and associated enzyme activities in multiple target tissues for TCDD-induced biochemical responses.

Developmental regulation of the 3-methylcholanthrene- and dioxin-inducible CYP1A5 gene in chick embryo liver in vivo

The cDNA sequences for two dioxin-inducible cytochrome P450s in chicken, CYP1A4 and CYP1A5, have recently been reported which correspond to two dioxin-inducible forms of P450 previously designated as TCDDAHH and TCDDAA, respectively. The developmental expression of CYP1A4-associated aryl hydrocarbon (benzo[a]pyrene) hydroxylase (AHH) activity and its association with expression of the Ah receptor had previously been characterized in chick embryo liver. The purpose of this study was to examine the developmental regulation of the second dioxin-inducible P450 gene, CYP1A5, in chick embryo liver. A partial gene sequence for CYP1A5 indicated that the intron/exon organization of this gene was identical to that of the CYP1A1 and CYP1A2 mammalian genes and was present in a single copy in the genome. CYP1A5 mRNA was expressed basally in chick embryo liver and was highly inducible by the Ah receptor ligands, 3-methylcholanthrene, beta-naphthoflavone, and 3,4,3', 4'-tetrachlorobiphenyl (TCB), but not by the phenobarbital analog, glutethimide. CYP1A5 mRNA levels were increased 40- to 50-fold within 5 h after a single TCB treatment, corresponding to a 30- to 40-fold increase in the transcription rate of the CYP1A5 gene at this time point. In contrast to a previous report that CYP1A5 mRNA expression was inducible by estradiol, we observed no effects of estradiol or dexamethasone on CYP1A5 mRNA expression, either alone or in combination with TCB. Basal and TCB-inducible CYP1A5 mRNA expression was maximal in liver at 8 days of development and remained high throughout the remainder of embryonic development. Thus, CYP1A5 appears to be regulated in a very similar manner to CYP1A4 in chick embryo liver.

Expression of the aryl hydrocarbon receptor (AhR) and AhR nuclear translocator during chick cardiogenesis is consistent with 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced heart defects

We examined cardiotoxicity induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the chick embryo and the cardiac expression of transcription factors, the aryl hydrocarbon receptor (AhR) which binds TCDD, and its dimer partner, the AhR nuclear translocator (Arnt). Chicken eggs were injected with control (triolein) or 1.0 pmol TCDD/g egg prior to incubation and collected on Day 10 when cardiomorphogenesis is complete. Relative to controls, TCDD increased heart wet weight (27.2 +/- 0.5 versus 36.6 +/- 1.3 mg, p < 0.001) and dry weight (2.7 +/- 0.1 versus 3.1 +/- 0.1 mg, p < 0.01), and tended to increase heart myosin content (3.5 +/- 0.6 versus 6.3 +/- 2.5 microg, p < 0.07), suggesting an increase in cardiac muscle mass and edema. Histologic and morphometric analyses revealed that 10/13 TCDD-exposed hearts exhibited enlarged right and left ventricles, thickened ventricular septum, and a thinner left ventricular wall with increased trabeculation, and 4/13 exhibited ventricular septal defects compared to controls (0/23). To evaluate AhR and Arnt expression, untreated chick embryos were collected on Days 2.2, 3, 4, 5, and 8 of incubation, preserved in Bouin's fixative, sectioned, and stained with AhR and Arnt antibodies. The AhR was expressed ubiquitously in cardiac myocytes, while Arnt expression was restricted to myocytes overlying developing septa: atrioventricular canal, outflow tract, and atrial and ventricular septa. Both proteins were absent from endocardium and endocardial-derived mesenchyme. In addition, cardiac expression of an AhR/Arnt target, cytochrome P4501A1, was restricted to myocardium coexpressing AhR and Arnt. Thus, the spatial and temporal expression of AhR and Arnt suggests that the developing myocardium and cardiac septa are potential targets of TCDD-induced teratogenicity, and such targets are also consistent with cardiac hypertrophy and septal defects observed following TCDD exposure.

Preferential effects of the chemotherapeutic DNA crosslinking agent mitomycin C on inducible gene expression in vivo

The immediate effects of a single dose of the chemotherapeutic DNA crosslinking agent, mitomycin C (MMC), on the expression of several constitutive and drug-inducible genes were examined in a simple in vivo system, the 14 day chick embryo. We observed no effect of MMC on the steady-state mRNA expression of the constitutively expressed beta-actin, transferrin, or albumin genes. In contrast, MMC treatment significantly altered both the basal and drug-inducible mRNA expression of two glutethimide-inducible genes, 5-aminolevulinic acid (ALA) synthase and cytochrome P450 CYP2H1. The basal expression of these genes was transiently but significantly increased over a 24 hr period following a single dose of MMC. Conversely, MMC significantly suppressed the glutethimide-inducible expression of these genes when administered 1 to 24 hr prior to the inducing drug. The effects of MMC on both basal and drug-inducible ALA synthase and CYP2H1 mRNA expression were principally a result of changes in the transcription rates of these genes. In contrast, MMC treatment had little or no effect on glutethimide-induced expression of ALA synthase or CYP2H1 when administered 1 hr after the inducing drug, suggesting that a very early event in the induction process represents the target for these MMC effects. Covalent binding studies demonstrated that the effects of MMC on gene expression were closely correlated temporally with formation of [3H]-porfiromycin-DNA adducts. These results support the hypothesis that genotoxic chemicals specifically target their effects to inducible genes in vivo.

Modulation of gene expression and endocrine response pathways by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds

The aryl hydrocarbon (Ah) receptor binds several different structural classes of chemicals, including halogenated aromatics, typified by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), polynuclear aromatic and heteropolynuclear aromatic hydrocarbons. TCDD induces expression of several genes including CYP1A1, and molecular biology studies show that the Ah receptor acts as a nuclear ligand-induced transcription factor that interacts with xenobiotic or dioxin responsive elements located in 5'-flanking regions of responsive genes. TCDD also elicits diverse toxic effects, modulates endocrine pathways and inhibits a broad spectrum of estrogen (17 beta-estradiol)-induced responses in rodents and human breast cancer cell lines. Molecular biology studies show that TCDD inhibited 17 beta-estradiol-induced cathepsin D gene expression by targeted interaction of the nuclear Ah receptor with imperfect dioxin responsive elements strategically located within the estrogen receptor-Sp1 enhancer sequence of this gene.

Effects of the genotoxic carcinogen chromium(VI) on basal and hormone-inducible phosphoenolpyruvate carboxykinase gene expression in vivo: correlation with glucocorticoid- and developmentally regulated expression

Previous studies have shown that a number of different genotoxic carcinogens that induce different types of DNA damage preferentially alter the expression of inducible genes in vivo. To investigate further the mechanistic basis for these effects, we examined the effects of the human lung carcinogen chromium(VI) on expression of the hormone-inducible cytosolic phosphoenolpyruvate carboxykinase (PEPCK) gene in chick embryo liver. Chromium(VI) pretreatment had significant effects on both basal and glucocorticoid-inducible PEPCK expression in 14-d-old embryo liver. These effects were principally a result of changes in PEPCK transcription. In contrast, treatment with chromium(VI) 1 h after treatment with glucocorticoid had no effect on PEPCK induction, suggesting that an early event in the induction process is the target for carcinogen effects. In 16-d-old liver, in which PEPCK expression is no longer responsive to glucocorticoid induction, both basal and inducible PEPCK expression were also refractory to chromium(VI) effects, indicating that carcinogen responsiveness is a phenotypic rather than an inherent property of inducible genes and is related to their competence for induction. Chromium(VI) had no effect on cAMP induction of PEPCK expression, demonstrating that carcinogens target their effects to specific regulatory pathways. Comparison of the effects of chromium(VI) with those of cycloheximide suggests that chromium(VI) targets its effects to a labile, constitutively expressed repressor involved in PEPCK gene regulation.

Developmental and reproductive toxicity of dioxins and related compounds: cross-species comparisons

Developmental toxicity to TCDD-like congeners in fish, birds, and mammals, and reproductive toxicity in mammals are reviewed. In fish and bird species, the developmental lesions observed are species dependent, but any given species responds similarly to different TCDD-like congeners. Developmental toxicity in fish resembles "blue sac disease," whereas structural malformations can occur in at least one bird species. In mammals, developmental toxicity includes decreased growth, structural malformations, functional alterations, and prenatal mortality. At relatively low exposure levels, structural malformations are not common in mammalian species. In contrast, functional alterations are the most sensitive signs of developmental toxicity. These include effects on the male reproductive system and male reproductive behavior in rats, and neurobehavioral effects in monkeys. Human infants exposed during the Yusho and Yu-Cheng episodes, and monkeys and mice exposed perinatally to TCDD developed an ectodermal dysplasia syndrome that includes toxicity to the skin and teeth. Toxicity to the central nervous system in monkey and human infants is a potential part of the ectodermal dysplasia syndrome. Decreases in spermatogenesis and the ability to conceive and carry a pregnancy to term are the most sensitive signs of reproductive toxicity in male and female mammals, respectively.

The interactions of 2,3,7,8-tetrachlorodibenzo-p-dioxin and 6-methyl-1,3,8-trichlorodibenzofuran in chick embryo hepatocytes

Treatment of chick embryo hepatocytes in ovo and in culture with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in a dose-dependent induction of microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities. Significant induction was observed in the hepatocytes at TCDD doses as low as 10(-11) mol/egg (in ovo) and 10(-10)m (in culture). In contrast, 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) was a relatively weak inducer of these activities and only 10-20% of the induction responses observed for TCDD were elicited by MCDF at doses of 10(-6) mol/egg or 10(-7)m in culture. Co-treatment of the chick embryo hepatocytes with TCDD (10(-10) mol/egg in ovo; 10(-10)m in culture) and different concentrations of MCDF (10(-6) to 10(-8) mol/egg in ovo and 10(-7) and 10(-8)m in culture) resulted in minimal inhibition of TCDD-induced enzyme activities in ovo and a 37 to 50% inhibition in culture. The partial antagonist activity of MCDF in the chick embryo hepatocytes in culture paralleled the interactive effects previously reported in rodent liver and transformed rodent cell lines. TCDD (10(-7) to 10(-10)m) also caused an accumulation of hepta- and octacarboxyporphyrins in chick embryo hepatocytes (10(-7) to 10(-9)m); however, MCDF (10(-6) and 10(-5)m) elicited similar responses and MCDF did not significantly decrease the TCDD-induced porphyrogenic response in these cells. These results suggest that chick embryo hepatocytes in culture will serve as a useful model for investigating TCDD-induced gene transcription and the effects and mechanism of action of antagonists.

Embryolethality and induction of 7-ethoxyresorufin O-deethylase in chick embryos by polychlorinated biphenyls and polycyclic aromatic hydrocarbons having Ah receptor affinity

The lethality and 7-ethoxyresorufin O-deethylase (EROD)-inducing potency of some individual polycyclic aromatic hydrocarbons (PAHs) and coplanar polychlorinated biphenyls (PCBs) in chick embryos were measured in order to compare the mechanisms of action of these compounds. In previous studies it was found that coplanar PCBs and certain PAHs have a high embryolethality in the chicken and that they induce embryonic EROD activity. Although the most potent PAHs were almost as embryolethal as the PCBs when injected into hens' eggs 72 h prior to measurement, they were considerably less potent EROD inducers. In the present study, three coplanar PCBs (3,3',4,4'-tetrachlorobiphenyl (TCB), 3,3',4,4',5-pentachlorobiphenyl (PeCB) and 3,3',4,4',5,5'-hexachlorobiphenyl (HCB)) and four of the most toxic PAHs (benzo[a]anthracene (BaA), benzo[k]fluoranthene (BkF), indeno[1,2,3-cd]pyrene (IP) and dibenzo[a, h]-anthracene (DBahA] were administered to chick embryos in different ways, including co-administration. Additive embryolethality was found when BkF and PeCB were co-administered as well as when BaA and DBahA were given simultaneously. The PAHs were more effective as EROD inducers when injected on day 9 (24 h prior to measurement) than when injected on day 7 (72 h prior to measurement). The opposite was found for PeCB and HCB, whereas no difference in potency was noted when comparing TCB injected 24 and 72 h before EROD determination. These substance-related differences were probably due, at least partly, to differences in biotransformation rates. EROD activities found after treatment with high doses of BkF, IP, or DBahA on day 9 were similar to those measured after treatment with PeCB in doses high enough to give maximal induction. Co-administration of high doses of BkF and PeCB did not further increase the activity, indicating that the PAHs and coplanar PCBs induce EROD to a common maximal value. To decrease the influence of metabolization of the PAHs on their EROD-inducing potency, EROD was determined early in development (day 8) and soon after treatment (24 h) in one experiment. In that experiment, the PAHs proved to be only a few times less potent EROD inducers in relation to their embryolethalities compared with the PCBs. The results of the present study, a previously observed similarity in pathology between chick embryos treated with PAHs and embryos treated with coplanar PCBs, and the fact that the most toxic PAHs also are the most avid Ah receptor binders suggest that the coplanar PCBs and the PAHs largely exert their toxicity in chick embryos via an Ah receptor-mediated mechanism. The differences between the compounds in their EROD-inducing potency/embryolethality ratios could probably be explained by their different rates of biotransformation.

Cyclophosphamide metabolism in the primary immune organs of the chick: assays of drug activation, P450 expression, and aldehyde dehydrogenase

Several diagnostic catalytic assays were used to determine whether organ-specific metabolic activation or detoxification of cyclophosphamide (CP) contributes to the selective toxicity of CP directed towards differentiating B cells as compared to T cells in the developing chicken. An assay for the alkylation of 4-[p-nitrobenzyl] pyridine (NBP) was used to assess comparative levels of CP activation products generated from microsomal preparations from liver, bursa of Fabricius (B cells), and thymus (T cells) of day-old chicks. Three catalytic assays were used to characterize and compare cytochrome P450-associated enzyme activities in neonatal hepatic and lymphoid tissues. Aldrin epoxidase (AE) was used to detect phenobarbital (PB)-inducible P450 activity. Ethoxyresorufin-O-deethylase (EROD) and aryl hydrocarbon hydroxylase (AHH) were used for the evaluation of polycyclic aromatic hydrocarbon (PAH)-inducible P450 activities in control and PB- or 3,3',4,4'-tetrachlorobiphenyl (TCB)-induced animals. Using the NBP assay, basal and PB-induced CP activation were observed using chick liver microsomes. However, no evidence of CP activation from immune organ microsomes was observed in control, PB-, or TCB-induced chicks. Basal and PB-induced AE activities were observed in thymus, but not bursa, and represented less than 1% of basal liver activity. EROD activity was detected in TCB-induced samples from both thymus and bursa, the thymus having the greater activity. Activities of aldehyde dehydrogenase (ALDH), an enzyme involved in CP detoxification, were about equal in cytosolic fractions from the bursa and thymus. These studies suggest strongly that tissue-specific differences in metabolic capacities are not the major factors governing the selective toxicity of CP directed towards differentiating B lymphocytes in vivo.

Mono-ortho-chlorinated chlorobiphenyls: toxicity and induction of 7-ethoxyresorufin O-deethylase (EROD) activity in chick embryos

Six mono-ortho-chlorinated chlorobiphenyls were compared regarding their toxicity and 7-ethoxyresorufin O-deethylase (EROD)-inducing potency in chick embryos. Three of the tested chlorobiphenyls have a chloro substituent adjacent to the ortho-chlorine, and these congeners were about ten times more potent than the three having a meta-hydrogen adjacent to the ortho-chlorine. These more toxic mono-ortho-chlorinated congeners were, however, about three orders of magnitude less toxic and less potent as EROD inducers in chick embryos than 3,3',4,4',5-pentachlorobiphenyl in a previous similar study. Malformed eyes and beaks, degenerative hepatic lesions and subcutaneous as well as pericardial edema were detected in embryos exposed to the mono-ortho-chlorine-substituted congeners, as was previously found after exposure to the most toxic non-ortho-chlorinated, coplanar chlorobiphenyls. It is concluded that the mono-ortho-chlorinated chlorobiphenyls are considerably less toxic and less potent as EROD inducers than the most toxic coplanar ones. Owing to their relatively high concentrations in technical preparations of polychlorinated biphenyls (PCBs) the mono-ortho-chlorine-substituted congeners may, however, contribute to the overall toxicity of PCBs.

3,3',4,4'-tetrachlorobiphenyl: metabolism by the chick embryo in ovo and toxicity of hydroxylated metabolites

The metabolism of 3,3',4,4'-tetrachlorobiphenyl (TCB) has been studied in the chicken in ovo by analysis of bile from chick embryos. Four percent of the [14C]TCB dose injected into the air sac on day 13 of incubation was detected in the bile by day 19. An increase of more lipophilic TCB metabolites was observed by HPLC analysis after hydrolysis of the bile. TCB and three phenolic TCB metabolites were identified and quantified in the hydrolyzed bile: TCB (14 ng/gall bladder), 5-hydroxy-3,3',4,4'-tetrachlorobiphenyl (234 ng/gall bladder), 4-hydroxy-3,3',4',5-tetrachlorobiphenyl (45 ng/gall bladder) and 2-hydroxy-3,3',4,4'-tetrachlorobiphenyl (3 ng/gall bladder). The presence of two other TCB metabolites in the bile, a dihydroxy-tetrachlorobiphenyl and a dihydroxy-trichlorobiphenyl was also indicated. The method used in the present study is well suited for studies of metabolism in avian embryos in ovo. The three TCB metabolites identified all proved to be at least two orders of magnitude less toxic than TCB in a chick embryo test. These metabolites were also shown to bind with significantly lower affinity than TCB to the Ah receptor. TCB, 5-hydroxy-3,3',4,4'-tetrachlorobiphenyl, 4-hydroxy-3,3',4',5-tetrachlorobiphenyl and 2-hydroxy-3,3',4,4'-tetrachlorobiphenyl gave Kd values of 16, 33, 45 and 37 nM, respectively, in the Ah receptor test.

Effects of TCDD and its congeners 3,3',4,4'-tetrachloroazoxybenzene and 3,3',4,4'-tetrachlorobiphenyl on lymphoid development in the thymus of avian embryos

Thymus anlagen from 11-day-old chick and 14-day-old turkey and duck embryos were cultured in media containing 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin (TCDD) for 5 days. The maximal TCDD-induced decrease in lymphoid cell number of chick embryo thymus (to about 60% of the control number) occurred at concentrations of 10(-10) M and above. To produce the same effect on lymphoid cell number in the cultures of thymus anlagen from turkey and duck embryos, about a 100-fold higher concentration of TCDD was needed. The toxicity of the TCDD congeners 3,3'4,4'-tetrachloroazoxybenzene (TCAOB) and 3,3',4,4'-tetrachlorobiphenyl (TCB) to embryonic chicken thymus was tested in vitro and in ovo. In chick embryo thymus cultures, TCAOB and TCB were about two orders of magnitude less toxic than TCDD. Injection of TCAOB and TCB into chicken eggs preincubated for 11 days resulted in a dose-dependent decrease in thymic lymphoid cell number 5 days later, declining to about 14% of the controls at 10 micrograms TCAOB/kg egg. The ED50 value was estimated to be 3.6 and 60 micrograms/kg egg for TCAOB and TCB, respectively.

Effects of the TCDD congeners 3,3',4,4'-tetrachlorobiphenyl and 3,3',4,4'-tetrachloroazoxybenzene on lymphoid development in the bursa of Fabricius of the chick embryo

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and its congeners, such as 3,3',4,4'-tetrachlorobiphenyl (TCB) and 3,3',4,4'-tetrachloroazoxybenzene (TCAOB), act on targets in the immune system, probably by interacting with the Ah-receptor, causing a characteristic pattern of effects typified by inhibition of lymphoid development in the thymus. There are, however, also reports of effects on B cells. Birds have a well-defined site of B-lymphocyte development, the bursa of Fabricius, analogous to the thymus for T cells. Thus, we wanted to determine whether this organ is suitable for studying effects on B-cell development. TCB and TCAOB were administered by injection into the air sacs of White Leghorn eggs on Day 13 of incubation. Effects observed on Day 19 were as follows: (1) There was a reduction in bursal dry weight but not in body weight in the treated groups. (2) The number of lymphoid cells in the bursae decreased in a dose-dependent manner, and bursae from high-dose groups (300 and 30 micrograms/kg egg of TCB and TCAOB, respectively) were almost completely devoid of lymphoid cells. For the reduction of lymphoid cell number, the ED50 for TCB and TCAOB was approximately 45 and 1.4 micrograms/kg egg, respectively. (3) Histological sections showed that embryos from treated egges contained fewer bursal follicles and that follicles contained fewer lymphoid cells compared with controls. (4) Aryl hydrocarbon hydroxylase activity was 30 and 50 times that of the control at high doses of TCB and TCAOB (estimated ED50: 200-300 and 4 micrograms/kg egg, respectively). These findings suggest that lymphoid development in the bursa of Fabricius of the chick embryo is inhibited by TCDD congeners.

Differences between chick and turkey embryos in sensitivity to 3,3',4,4'-tetrachloro-biphenyl and in concentration/affinity of the hepatic receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin

1. 3,3',4,4'-Tetrachlorobiphenyl (TCB) was 20-100 times more toxic in chick embryos than in turkey embryos when injected into eggs. 2. The ED50-value for induction of AHH activity by TCB in the liver of early chick and turkey embryos was estimated to be 0.6 and 6 micrograms/kg egg, respectively. 3. In both species alpha-naphthoflavone was more effective than metyrapone at inhibiting basal and TCB-induced AHH activities. 4. The TCDD receptor was detected in the liver of 7-day-old chick embryos, while it was not found in 9-day-old turkey embryo liver.

Ontogeny of the chicken cytochrome P-450 enzyme system. Expression and development of responsiveness to phenobarbital induction

The sensitivity of the developing embryo to toxins and drugs is highly dependent on the state of development of the cytochrome P-450 system. Previous work in this laboratory has demonstrated the genotoxicity of aflatoxin B1 (AFB1) to the chicken embryo at 3 days of incubation (DI) and induction of AFB1 genotoxicity by phenobarbital at 7 DI. In this study, the basal and 24-hr phenobarbital (PB) induced levels of aminopyrine-N-demethylase (AMPD) and cytochrome P-450 were assayed in hepatic microsomes from 7 DI to 36 days posthatching (PH) and in microsomes from whole embryos at 5 DI. A dose-response for induction by PB was observed in embryonic hepatic microsomes as early as 7 DI, whereas a low level of cytochrome P-450 was detected in control 7 DI microsomes using the reduced CO vs oxidized CO difference spectrum. Basal levels of AMPD and cytochrome P-450 in hepatic microsomes increased steadily throughout development as did the responsiveness of the embryonic liver to induction with PB. Hepatic microsomes from control and PB-induced chickens had the highest AMPD activities posthatching particularly from 1 to 3 days PH. Maximal induced levels, which were 2- to 3-fold over control throughout development, ranged from 1.22 at 7 DI to 12.72 nmol HCHO/mg protein/min at 2 days PH. The potency of PB as an inducer increased about 1000-fold between 7 DI and hatching. PB induction did not increase the specific activity of AMPD at any period of development. The specific activity of AMPD posthatching increased about 3-fold above embryonic levels, indicating the development of a cytochrome P-450 complex more active toward aminopyrine in the neonatal period.