Role of aryl hydrocarbon receptor in mesencephalic circulation failure and apoptosis in zebrafish embryos exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a persistent and potent developmental toxicant in various animals, with developing fish being the most sensitive organisms. Although the expression of aryl hydrocarbon receptor (AHR) as well as the partner molecule, AHR nuclear translocator (ARNT) in the brain has been reported, the effect of TCDD on the brain remains to be clarified in detail. Previously, we reported local circulation failure and apoptosis in dorsal midbrain caused by TCDD in developing zebrafish. In the present experiments, we investigated the effects of morpholino antisense oligos against aryl hydrocarbon receptor 2 (zfAHR2) (AHR2-MO) on toxicological endpoints caused by TCDD in developing zebrafish. AHR2-MO but not its negative homologue (4mis-AHR2-MO) improved TCDD-evoked circulation failure in mesencephalic vein and reduced the occurrence of apoptosis in dorsal midbrain, with concomitant inhibition of CYP1A induction in vascular endothelium. Injection of bovine serum albumin (BSA) into the general circulation, followed by immunohistochemistry with anti-BSA, showed that TCDD raised vascular permeability to albumin in dorsal midbrain, which was blocked by AHR2-MO and N-acetlycystein. In the absence of TCDD, development of embryos injected with AHR2-MO appeared normal at least until 60 h after fertilization. It is concluded that AHR2 activation in the vascular endothelium of the zebrafish embryo midbrain is involved in the mesencephalic circulation failure and apoptosis elicited by TCDD. This is the further evidence that vascular endothelium is the target of TCDD in relation to local circulation failure and apoptosis in dorsal midbrain.     

An uncommon phenotype of poor inducibility of CYP1A1 in human lung is not ascribable to polymorphisms in the AHR, ARNT, or CYP1A1 genes

Cigarette smoking can induce CYP1A1 in the lung. Induction requires the aryl hydrocarbon receptor (AHR) and aryl hydrocarbon receptor nuclear translocator (ARNT) proteins. Lung samples from seven of 75 Finnish patients who smoked until the time of surgery exhibited absent or low levels of CYP1A1 protein, mRNA and enzymatic activity, suggesting that these individuals might be genetically non or poorly inducible for CYP1A1. All seven lung samples expressed normal levels of AHR mRNA and ARNT mRNA, indicating that they did not carry inactivating polymorphisms in the 5' upstream regulatory regions of these genes. Sequencing of cDNAs encompassing the complete coding regions of AHR and ARNT identified a previously known codon 554 polymorphism in AHR, which was present in the homozygous state in one individual. This polymorphism, which leads to an amino acid substitution, has previously been reported either to have no effect or to enhance CYP1A1 induction. Previously unreported silent single nucleotide polymorphisms were identified in codon 44 of AHR and codon 189 of ARNT. 1500 bp of genomic sequence from the 5' upstream regulatory sequence of the CYP1A1 gene was also sequenced in the non-inducible individuals. A nucleotide substitution polymorphism at position -459 was detected in the heterozygous state in two individuals. This polymorphic site does not reside in any known regulatory sequence. The complete CYP1A1 coding sequence and intron/exon boundaries were then sequenced. None of the non or poorly inducible individuals exhibited any polymorphisms, either homozygous or heterozygous compared to representative inducible individuals or the previously published CYP1A1 sequence. Thus, no polymorphisms in the AHR, ARNT or CYP1A1 genes were identified that could be responsible for the non/low inducibility phenotype observed.     

In vivo up-regulation of aryl hydrocarbon receptor expression by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in a dioxin-resistant rat model.

The aryl hydrocarbon receptor (AHR) mediates toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and regulates expression of several genes such as CYP1A1. Little is known about what regulates expression of the AHR itself. We tested the ability of TCDD to alter in vivo expression of its own receptor in rat strains that are susceptible to TCDD lethality [Long-Evans (Turku AB) (L-E) and Sprague Dawley (SD)] and in a rat strain that is remarkably resistant to TCDD lethality [Han/Wistar (Kuopio) (H/W)]. Rats were administered a single, intragastric dose of 5 or 50 microg/kg of TCDD. Hepatic cytosol, nuclear extract, and RNA were prepared at 1, 4, and 10 days after TCDD exposure. AHR expression was assessed at three levels: ligand binding function, immunoreactive protein and mRNA. TCDD at 5 microg/kg produced a 2- to 3-fold increase in cytosolic AHR in all strains; 50 microg/kg produced depletion at day 1 followed by recovery in SD and H/W but not L-E rats. Both the increase in AHR above basal levels and the recovery from initial depletion were accompanied by elevations in steady-state AHR mRNA, suggesting a pre-translational mechanism for AHR regulation by its own ligand. This up-regulation in vivo is in contrast to the sustained depletion of AHR caused by TCDD in cell culture. There was no clear relationship between AHR regulation and strain sensitivity; thus, the large inherent strain differences in susceptibility to TCDD lethality probably are not explained by differential regulation of AHR by TCDD.     

Histological analysis of acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in zebrafish

Previous studies have demonstrated that acute exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) by injection leads to inhibition of caudal fin regeneration in zebrafish. Since the TCDD exposure in these studies is systemic, it is possible that pathology in organs other than the fin could result in inhibition of fin regeneration. Therefore, histopathology of adult zebrafish (Danio rerio) organs was characterized following abdominal cavity injection of a TCDD dose (70ng/g). The most pronounced histopathologic changes 5 days post-injection included lipidosis and hypertrophy of liver hepatocytes and hypertrophy of gill lamellae. Effects of TCDD exposure on immunolocalization of the zebrafish aryl hydrocarbon receptor nuclear translocator (ARNT2), the heterodimer partner of the aryl hydrocarbon receptor (AHR2), and an AHR regulated gene cytochrome P450 1A (CYP1A) was also determined. ARNT2 was immunolocalized to the gastrointestinal tract, gill lamellae, kidney, ventricle of the heart, caudal fin, brain and liver of zebrafish. TCDD exposure had no measurable effect on ARNT2 abundance or localization. CYP1A was immunolocalized in TCDD exposed fish as a biomarker for cells with an activated AHR pathway. CYP1A was not detected in any tissue from vehicle exposed fish. Significant TCDD-dependent induction of CYP1A was detected in the proximal tubules of the kidney, in liver hepatocytes and in the gastrointestinal tract of TCDD exposed fish. Significant but lower TCDD-dependent CYP1A expression was evident in the gill, caudal fin and ventricle of the heart. Overall, TCDD exposure in adult zebrafish leads to histopathology similar to that reported in other fish species, and it appears unlikely that the histopathology in these organs completely explains the inhibition of fin regeneration.     

Serum withdrawal leads to reduced aryl hydrocarbon receptor expression and loss of cytochrome P4501A inducibility in PLHC-1 cells

Changes in the expression of the aryl hydrocarbon receptor (AHR) have been documented in several systems and in response to a variety of treatments. The significance of these findings is unclear, because the effects of such changes on subsequent responses to AHR ligands seldom have been measured. We tested the ability of changes in serum used in cell culture medium to alter expression of the AHR and induction of cytochrome P4501A (CYP1A) in PLHC-1 teleost hepatoma cells. Culture of early-passage cells in serum-free medium for 2 days led to a loss of CYP1A inducibility by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In contrast, culture in 10% delipidated calf serum increased the TCDD-induced levels of both CYP1A protein and enzymatic activity relative to levels in cells cultured in 10% complete calf serum. These effects were consistent between 8 and 24hr post-treatment, indicating that the kinetics of induction were unaffected. In cells cultured in serum-free medium for 1 and 2 days there was a progressive loss of CYP1A inducibility. This loss of response paralleled a time-dependent decline in AHR protein, as measured by specific binding of [3H]TCDD. Using an operational model for AHR action in PLHC-1 cells, the measured reduction in AHR could be shown to predict the loss of CYP1A induction. Expression of AHR protein was unaffected by culture in 10% delipidated serum. The effects of serum-free medium and delipidated serum were found only in early-passage cells; inducibility of CYP1A and expression of AHR protein in late-passage cells were unaffected by serum withdrawal. Comparison of early- and late-passage cells revealed a 2-fold greater rate of proliferation in the latter, suggesting that a growth advantage is coincident with loss of the serum-dependency of AHR expression. These results provide a quantitative link between changes in receptor expression and a downstream response, establishing a foundation for future studies of receptor expression and sensitivity to toxic responses in vitro and in vivo.     

Developmental and tissue-specific expression of AHR1, AHR2, and ARNT2 in dioxin-sensitive and -resistant populations of the marine fish Fundulus heteroclitus.

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.     

Regulation of cytochrome P-450 (CYP) 1B1 in mouse Hepa-1 variant cell lines: A possible role for aryl hydrocarbon receptor nuclear translocator (ARNT) as a suppressor of CYP1B1 gene expression

Cytochrome P-450 (CYP) 1B1 expression in mouse hepatoma (Hepa-1) wild-type (WT) cells was compared with responses in Hepa-1 variants LA1 and LA2, which, respectively, exhibit low aryl hydrocarbon receptor (AhR) level and defective AhR nuclear translocator (ARNT) protein. 10T1/2 mouse embryo fibroblasts express predominantly CYP1B1 and at a 100 times higher level than in Hepa-1 cells, whereas they express about 300-fold lower CYP1A1 than Hepa-1 cells. The expression of CYP1B1 in WT and LA1 variant, although at a much lower level, follows that of CYP1A1, reflecting their common regulation through the AhR. The LA2 (ARNT-defective) cells showed a major difference between CYP1B1 and CYP1A1 expression. Although CYP1A1 mRNA levels in LA2 were extremely low and unresponsive to 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD), basal CYP1B1 mRNA and protein were expressed at levels similar to those seen in TCDD-induced WT. The elevated basal CYP1B1 mRNA in LA2 cells decreased by 50% after transient transfection of ARNT cDNA, in parallel with substantial restoration of CYP1A1 induction. This implicates ARNT as a suppressor of CYP1B1 basal expression in Hepa cells. In transient CYP1B1-luciferase constructs in LA2 cells, ARNT shows stimulatory effects in the enhancer region but an inhibitory effect on the proximal promoter. Two CYP1B1 enhancer elements [xenobiotic-responsive element (XRE) 1/2 and XRE4] formed TCDD-unresponsive complexes of similar mobility to TCDD-stimulated AhR-ARNT complex with XRE5. However, because these two complexes were formed to the same extent in LA2 as in WT cells, they cannot be due to ARNT or contribute to ARNT-regulated suppression.     

Correlation of cardiotoxicity mediated by halogenated aromatic hydrocarbons to aryl hydrocarbon receptor activation.

In mammals, the toxicity of halogenated aromatic hydrocarbons (HAH) correlates with their ability to activate the aryl hydrocarbon receptor (AHR). To test this correlation in an avian model, we selected six HAHs based on their affinity for the mammalian AHR, including: 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD); 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PCDD); 2,3,7,8-tetrachlorodibenzofuran (TCDF); 2,3,4,7,8-pentachlorodibenzofuran (PCDF); 3,3',4,4'-tetrachlorobiphenyl (PCB 77); and 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153). We determined the ability of these compounds to induce cardiotoxicity, as measured by an increase in heart wet weight on incubation day 10 in the chick embryo (Gallus gallus) and formation of the avian AHR/ARNT/DNA binding complex in chicken hepatoma cells. Relative potency values (RPs) were calculated by dividing the TCDD EC(50) (AHR/ARNT/DNA binding) or ED(50) (15% increase in day-10 heart wet weight) by the HAH congeners EC(50) or ED(50), respectively. The rank order of potencies for inducing cardiotoxicity were TCDD > PCDD = PCDF = TCDF > PCDF > PCB77, PCB 153, no effect. The RP values for inducing AHR/ARNT DNA binding were then correlated with those for inducing cardiotoxicity (the RP values of PCDD were determined to be statistical outliers). This correlation was found to be highly significant (r = 0.94, p = 0.017). The ability of PCDD to act as an AHR agonist was verified using luciferase reporter assays and analysis of cytochrome P4501A1 protein levels. These results indicate that the ability of HAHs to activate the avian AHR signaling pathway, in general, correlates with their ability to mediate cardiotoxicity in the chick embryo.     

Persistent, low-dose 2,3,7,8-tetrachlorodibenzo-p-dioxin exposure: effect on aryl hydrocarbon receptor expression in a dioxin-resistance model

Most toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) are mediated by the aryl hydrocarbon receptor (AHR). A single, acute dose of TCDD can alter its own receptor levels thus complicating evaluation of dose-response relationships for AHR-mediated events. Since environmental exposure to dioxins is typically of a repeated low-dose nature, we examined the effect of such exposure on AHR expression. Three rat strains differing greatly in their sensitivity to acute TCDD lethality, Long-Evans (Turku AB) (L-E) (LD50 approximately 10 microg/kg); Sprague Dawley (SD) (LD50 approximately 50 microg/kg); and Han/Wistar (Kuopio) (H/W) (LD50 > 9600 microg/kg), were administered TCDD intragastrically, biweekly for 22 weeks producing doses equivalent to 0, 10, 30, and 100 ng/kg/day. Changes in hepatic AHR levels were quantitated at the protein level by radioligand binding and immunoblotting and at the mRNA level by RT-PCR. Cytosolic AHR protein was elevated at 10 or 30 ng/kg/day TCDD in SD and L-E rats; AHR mRNA was also elevated at these doses, suggesting a pretranslational mechanism. There was no apparent relationship between TCDD-induced AHR regulation and strain sensitivity to TCDD. Overall, "subchronic" TCDD did not greatly perturb AHR expression. The maintenance of relatively constant receptor levels in the face of persistent agonist stimulation is in contrast to the sustained depletion of AHR by TCDD observed in cell culture and to the fluctuations in AHR observed hours to days following acute TCDD exposure in vivo. Changes in AHR levels may affect dose-response relationships; the effect of TCDD on its own receptor at environmentally relevant dosing schemes is therefore important to risk assessment.