Blocking expression of AHR2 and ARNT1 in zebrafish larvae protects against cardiac toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin.

The zebrafish (Danio rerio) has become an attractive vertebrate model for studying developmental processes, and is emerging as a model system for studying the mechanisms by which xenobiotic compounds perturb normal development. Embryos treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) shortly after fertilization exhibit a range of adverse effects on the heart: an early reduction in cardiac myocyte number, followed by a change in heart looping and morphology, with an apparent compaction of the ventricle and overall decrease in heart size. These changes are accompanied by impaired cardiac function including a decrease in cardiac output and eventually irreversible ventricular standstill. The mechanisms involved in mediating effects of TCDD on the heart remain unknown. However, it is widely accepted that aryl hydrocarbon receptor (AHR) activation mediates endpoints of TCDD toxicity in vertebrates. In zebrafish, there are multiple forms of AHR and AHR nuclear translocator protein (ARNT) raising the question about whether different endpoints of TCDD toxicity are mediated by different components of the AHR/ARNT pathway. To address this question we used morpholino oligonucleotide technology to specifically block the expression of zfAHR2, zfARNT1, zfARNT2, and zfCYP1A, and assessed the previously described effects of TCDD on heart morphology, size, and function in the developing morphants. We report that blocking zfAHR2 and zfARNT1 expression provided protection against the TCDD-mediated alteration in heart morphology, reduced cardiac myocyte number, decreased cardiac output and ventricular standstill in zebrafish larvae, while the zfarnt2 and zfcyp1a morpholinos did not block the TCDD-induced cardiac toxicity.     

CYP1C1 messenger RNA expression is inducible by benzo[a]pyrene in Fundulus heteroclitus embryos and adults.

CYP1C is the newest member of the CYP1 family of P450s; however, its physiological significance, inducers, and metabolic functions are unknown. Two full-length alleles of Fundulus heteroclitus CYP1C1 complementary DNA were cloned. The 529 amino acid protein shared the highest amino acid identity with Stenotomus chrysops CYP1C1 (81%). To investigate whether the carcinogen benzo[a]pyrene (BaP) was a CYP1C1 inducer, we used real-time PCR to quantitatively measure tissue- and sex-specific expression of both CYP1C1 and CYP1A messenger RNAs (mRNAs) in BaP-exposed adult fish. CYP1C1 mRNA expression was constitutively higher than CYP1A in brain, spleen, eye, and gonad, while CYP1A was higher in gastrointestinal tract (GI), heart, gill, and liver. Kidney had equal but high expression of both CYP1s. There were sex differences in constitutive CYP1 expression in the GI, liver, gill, and eye. BaP exposure caused induction of CYP1C1 expression in female and male heart (31- and 17-fold), gill (seven- and four-fold), and liver (six- and five-fold), respectively. Embryo CYP1 expression was constitutively highest at 2 weeks posthatch, and whole embryos expressed 3- to 15-fold more CYP1C1 mRNA compared to CYP1A. BaP, 10 microg/l for 10 days, caused induction of both genes at 120 and 240 h postfertilization. Our results suggest that teleost CYP1C, in addition to CYP1A, is inducible by BaP, has a broad tissue distribution, and should be further investigated for its role in carcinogen bioactivation.     

Acquired resistance to Ah receptor agonists in a population of Atlantic killifish (Fundulus heteroclitus) inhabiting a marine superfund site: in vivo and in vitro studies on the inducibility of xenobiotic metabolizing enzymes.

New Bedford Harbor (NBH), MA, is a federal Superfund site that is heavily contaminated with polychlorinated biphenyls (PCBs) and other halogenated aromatic hydrocarbons (HAHs), including some potent aryl hydrocarbon receptor (AhR) agonists. A population of Atlantic killifish (Fundulus heteroclitus) continues to inhabit this site, despite accumulating extraordinarily high concentrations of PCBs (272 microg/g dry weight). To determine if NBH killifish have developed resistance to HAHs that act through the AhR, we examined the inducibility of cytochrome P4501A1 (CYP1A1), UDP glucuronosyl transferase (UGT), and glutathione S-transferase (GST) in fish from NBH and a reference site, Scorton Creek (SC, Cape Cod, MA; PCB concentrations 0.177 microg/g dry weight). 2,3,7,8-Tetrachlorodibenzofuran (TCDF) induced CYP1A1 mRNA, protein, and activity in SC fish in all tissues examined (liver, heart, gut, gill, kidney, spleen, and gonad). In contrast, NBH fish expressed low levels of CYP1A1 and showed no induction of CYP1A1 mRNA, protein, or activity by TCDF, or induction that was lower in magnitude or required higher doses of inducer. p-Nitrophenol UGT activity was not induced by TCDF in either population, while GST activity with 1-chloro-2,4-dinitrobenzene as substrate was induced only in NBH fish in one experiment. Inducibility of CYP1A1 by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or beta-naphthoflavone (BNF) was measured in primary hepatocyte cultures prepared from SC and NBH fish. TCDD induced CYP1A1 activity (ethoxyresorufin O-deethylase) to the same degree in hepatocytes from both populations, demonstrating the functionality of the AhR signaling pathway in NBH fish. However, hepatocytes from NBH fish were 14-fold less sensitive to TCDD than were those from SC fish. The nonhalogenated AhR agonist BNF also induced CYP1A1 in cells from both populations, although with only a 3-fold difference in sensitivity (NBH < SC). These results indicate that chronic exposure to high levels of HAHs has led to a reduction in the sensitivity of NBH killifish to AhR agonists. The resistance is systemic and pretranslational, and exhibits compound-specific differences in magnitude. These findings suggest an alteration in the AhR signal transduction pathway in NBH fish.     

Molecular and histological evaluation of tributyltin toxicity on spermatogenesis in a marine fish, the mummichog (Fundulus heteroclitus)

There is still concern about the effects of organotin compounds (OTs) on marine organisms, and especially on their reproductive systems. We investigated the toxicity of tributyltin oxide (TBTO) on spermatogenesis in a marine fish, mummichog, Fundulus heteroclitus. TBTO exposure caused serious histological damage to the testis, including reduction in counts of spermatids and spermatozoa and malformation of somatic cells around the seminal duct. Analysis of the incorporation of bromodeoxyuridine into spermatogenic cells revealed inhibition of the proliferation of germ cells. To find a biomarker for evaluation of the effects of TBTO on fish spermatogenesis, we cloned genes downregulated by TBTO exposure in the mummichog testis, and identified mummichog creatine kinase (mCK). The cDNA sequence of mCK contained an open reading frame encoding 387 amino acid residues (M(r)=43,344). The derived amino acid sequence of mCK was very similar to that of the testicular-type CK of the rainbow trout, Oncorhynchus mykiss. Furthermore, Northern blot analysis revealed that mCK was produced specifically in the testis. We therefore identified mCK in the mummichog as a testicular-type CK. Real-time PCR revealed that exposure of the fish to TBTO significantly reduced mCK expression in the testis. To some extent, this reduction was coincident with that of bromodeoxyuridine incorporation into spermatogenic cells. The mCK gene can therefore be used as a biomarker for evaluating the effects of TBTO on fish spermatogenesis. In addition, levels of expression of the mCK gene in control fish were well correlated with increments in the gonad somatic index (GSI) below 4%. Individuals that were thought to have testicular damage caused by TBTO could be discriminated from those considered normal. The results suggest that TBTO is involved in the suppression of fish spermatogenesis and that analysis of both GSI values and mCK gene expression is useful for evaluating the levels of xenobiotic pollution in coastal areas.     

Linked expression of Ah receptor, ARNT, CYP1A1, and CYP1B1 in rat mammary epithelia, in vitro, is each substantially elevated by specific extracellular matrix interactions that precede branching morphogenesis.

Cytochrome P4501B1 (CYP1B1), the major constitutively expressed CYP in the rat mammary gland, is induced by Ah-receptor (AhR) ligands, while CYP1A1 is predominantly expressed only after induction. These CYPs contribute to carcinogenic activation of polycyclic aromatic hydrocarbons (PAHs). AhR, ARNT, and CYP1B1 were only weakly expressed, even after 2,3,7,8-tetrachlorodibenzo-p-dioxin induction, when rat mammary epithelial cells (RMEC) were cultured on plastic. RMEC cultured on the extracellular matrix (ECM), Matrigel, or on a floating gel of collagen I demonstrated branching morphogenesis and substantially increased basal CYP1B1 and induced CYP1A1 expression, in parallel with large increases in AhR and ARNT expression. Branching was more pronounced in the Wistar Kyoto than in the Wistar Furth rat strain. Although EGF enhanced branching, neither strain nor growth factor treatment substantially impacted CYP expression. Increased AhR and ARNT expression is observed within 24 h of dispersal on Matrigel, substantially prior to branch formation. Culture on thin layers of collagen I, collagen IV, and laminin, respectively, failed to reproduce the branching morphogenesis or increases in AhR, ARNT, or CYP expression. However, adherent, gelled collagen I recapitulated the increased protein expression, without supporting branching. This increased protein expression was closely paralleled by enhanced expression of beta-catenin and E-cadherin, components of cell-cell adhesion complexes. A synthetic peptide that selectively antagonizes integrin-ECM interactions reduced branch formation, without diminishing AhR, ARNT, and CYP expression. These data demonstrate that early ECM surface adhesion interactions mediate AhR and ARNT expression, which enhances CYP expression, independent of branching morphogenesis.     

Role of AHR2 in the expression of novel cytochrome P450 1 family genes, cell cycle genes, and morphological defects in developing zebra fish exposed to 3,3',4,4',5-pentachlorobiphenyl or 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Halogenated agonists for the aryl hydrocarbon receptor (AHR), such as 3,3',4,4',5-pentachlorobiphenyl (PCB126) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), cause developmental toxicity in fish. AHR dependence of these effects is known for TCDD but only presumed for PCB126, and the AHR-regulated genes involved are known only in part. We defined the role of AHR in regulation of four cytochrome P450 1 (CYP1) genes and the effect of PCB126 on cell cycle genes (i.e., PCNA and cyclin E) in zebra fish (Danio rerio) embryos. Basal and PCB126-induced expression of CYP1A, CYP1B1, CYP1C1, and CYP1C2 was examined over time as well as in relation to cell cycle gene expression and morphological effects of PCB126 in developing zebra fish. The four CYP1 genes differed in the time for maximal basal and induced expression, i.e., CYP1B1 peaked within 2 days postfertilization (dpf), the CYP1Cs around hatching (3 dpf), and CYP1A after hatching (14-21 dpf). These results indicate developmental periods when the CYP1s may play physiological roles. PCB126 (0.3-100nM) caused concentration-dependent CYP1 gene induction (EC50: 1.4-2.7nM, Lowest observed effect concentration [LOEC]: 0.3-1nM) and pericardial edema (EC50: 4.4nM, LOEC: 3nM) in 3-dpf embryos. Blockage of AHR2 translation significantly inhibited these effects of PCB126 and TCDD. PCNA gene expression was reduced by PCB126 in a concentration-dependent manner, suggesting that PCB126 could suppress cell proliferation. Our results indicate that the four CYP1 genes examined are regulated by AHR2 and that the effect of PCB126 on morphology in zebra fish embryos is AHR2 dependent. Moreover, the developmental patterns of expression and induction suggest that CYP1 enzymes could function in normal development and in developmental toxicity of PCB126 in fish embryos.     

MRP2 and acquired tolerance to inorganic arsenic in the kidney of killifish (Fundulus heteroclitus).

We used proximal tubules isolated from the killifish, Fundulus heteroclitus, to examine the effect of environmentally relevant, sublethal levels of arsenic on the function and expression of MRP2, an ABC transporter that transports xenobiotics into urine, including arsenic-glutathione conjugates. Exposure of fish to arsenic as sodium arsenite (4-14 days) increased both MRP2 expression in the apical membrane of proximal tubules and MRP2-mediated transport activity. The level of MRP2 mRNA was not affected, suggesting a posttranslational mechanism of action. Acute exposure of proximal tubules isolated from control fish to 75-375 ppb arsenic decreased mitochondrial function (inner membrane electrical potential). However, in tubules from fish that were preexposed to arsenic (4-14 days), no such effect on mitochondrial function was observed. Thus, chronic in vivo exposure to arsenic induces mechanisms that protect proximal tubules during subsequent arsenic exposure. Upregulation of MRP2 expression and activity is one likely contributing factor.     

Response of the incisor tooth to 2,3,7,8-tetrachlorodibenzo-p-dioxin in a dioxin-resistant and a dioxin-sensitive rat strain.

Dioxins are ubiquitous environmental pollutants that afflict developing teeth. To find out if the effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the continuously erupting rat incisor is associated with the sensitivity to TCDD acute lethality and to see the histological basis for any macroscopic findings, we exposed 25 resistant Han/Wistar (Kuopio; H/W) and 20 sensitive Long-Evans (Turku/AB; L-E) female rats to total doses of 0.17, 1.7, 17, and 170 (only H/W rats) micro g/kg TCDD. Each dose group comprised five animals. The treatment was started when the rats were 10 weeks old and continued for 20 weeks. The exposure time covered two life cycles of the incisor. Stereomicroscopic examination of the dissected mandibles showed color defects and pulpal perforation of the lower incisors at 17 and 170 micro g/kg TCDD. Tissue sections revealed odontoblastic and pulpal cell death and the consequent arrest of dentin formation at the incisal tooth end at the same doses. H/W rat incisors were affected closer to the germinative tooth end at 170 than at 17 micro g/kg TCDD, resulting in a larger perforation. In accordance with the enamel discoloration, the postsecretory enamel organ underwent, albeit inconsistently, precocious squamous metaplasia with pronounced proliferation. Thus, both the mesenchymal and, to a lesser extent, epithelial elements of the forming tooth were affected dose-dependently at relatively high doses of TCDD. Similar responses in both strains implied that the impaired formation of the incisor tooth, at least of its mesenchymal elements, is not associated with the differential resistance of H/W and L-E rats to TCDD acute lethality.     

Microsomal electron transport and xenobiotic monooxygenase activities during the embryonic period of development in the killifish,Fundulus heteroclitus

The developmental patterns of aryl hydrocarbon hydroxylase (AHH) activity and NADPH-cytochrome c reductase activity were followed during embryonic development in Fundulus. AHH activity was localized in microsomal fractions prepared from whole Fundulus embryos and eleutheroembryos. On the basis of this subcellular localization, the requirements of O₂ and NADPH for activity, and sensitivity to carbon monoxide and cytochrome c inhibition, the AHH activity in Fundulus embryos and eleutheroembryos appeared to be cytochrome P-450 dependent. AHH activity was measurable in stages prior to the appearance of the liver rudiment, and during subsequent embryonic development the extrahepatic tissues were likely to have contributed substantially to the AHH activity measured. At all stages assayed before hatching, microsomal AHH specific activity remained uniformly low, but within 24 hr of hatching, AHH specific activity increased about ninefold. This posthatching increase in AHH activity was not age dependent, nor developmental stage dependent, but rather required hatching, and was not due to the presence of endogenous inhibitors in prehatching stages. The levels of NADPH-cytochrome c reductase activity and AHH activity were not closely correlated in whole embryo and eleutheroembryo microsomes, but the AHH activity in these preparations apparently was not limited by the levels of the NADPH-cytochrome c (P-450) reductase. The presence of AHH activity in Fundulus embryos during the period of active organogenesis, prior to hatching, indicates that this species is likely to be susceptible to a variety of teratogens requiring metabolic activation, and this may be the case for other species of fish as well.     

Inhibition of human and rat CYP1A2 by TCDD and dioxin-like chemicals.

Dioxins have been shown to bind and induce rodent CYP1A2, producing a dose-dependent hepatic sequestration in vivo. The induction of CYP1A2 activity has been used as a noninvasive biomarker for human exposure to dioxins; while there is a consistent relationship between exposure and hepatic CYP1A2 induction in rodents, this relationship has only been observed in some of the highest exposed human populations. This may be explained by inhibition of CYP1A2 activity by dioxins as some rodent studies demonstrate that rodent CYP1A2 activity can in fact be inhibited by dioxins in vitro. CYP1A2 activity was examined using a series of dioxins to inhibit human and rat CYP1A2 activity in species-specific CYP1A2 SUPERSOMES using three common CYP1A2 substrates. Methoxyresorufin was a more efficient substrate than acetanalide or caffeine in this in vitro system. Rat and human CYP1A2 enzymatic activity is inhibited by TCDD, PCDD, TCDF, 4-PeCDF, and PCBs 126, 169, 105, 118, and 156 in a concentration-dependent manner. These data demonstrate that the in vitro metabolism of prototype substrates is similar between the rat and human CYP1A2 SUPERSOME preparations and that dioxins inhibit CYP1A2 activity in both species. Because of the potential for inhibition of CYP1A2 activity by TCDD and other dioxins, studies examining CYP1A2 induction in dioxin-exposed populations using these substrates should be viewed cautiously.     

In vivo and in vitro inhibition of CYP1A-dependent activity in Fundulus heteroclitus by the polynuclear aromatic hydrocarbon fluoranthene.

Certainpolynuclear aromatic hydrocarbons (PAHs) such as benzo[a]pyrene (BaP) induce CYP1A-dependent enzyme activities. Because PAHs are ubiquitous environmental contaminants, and some are aryl hydrocarbon agonists, CYP1A has been used as a biomarker for PAH exposure. However, PAHs exist in the environment in complex mixtures that may confound biomarker results. In in vitro studies, the PAH fluoranthene (FL) failed to increase or enhance CYP1A1-dependent ethoxyresorufin-O-deethylase (EROD) activity in cells, but rather inhibited activities induced by AhR agonists such as 2,3,7,8-tetrachlorodibenzo-p-dioxin and benzo(k)fluoranthene. In order to determine the in vivo effects of FL on CYP1A and DNA adduct levels, Fundulus heteroclitus were given single ip injections of either BaP (5 mg/kg), BaP + FL (5 mg/kg each), BaP + FL (5 and 50 mg/kg, respectively), FL (5 mg/kg), FL (50 mg/kg), or corn oil control. BaP-treated fish had liver microsome EROD activities significantly higher than controls, whereas FL-treated fish were not different from controls. EROD activities in BaP + FL cotreatments were significantly lower compared to fish treated with BaP alone. When FL was incubated with BaP-induced microsomes, the IC50 for inhibition of EROD activity was 1.4 x 10(-5) M FL. Kinetic studies indicated a significant noncompetitive component to the FL inhibition. When fish were treated with [(14)C]FL, the concentration of radiolabel associated with microsomal preparations was four orders of magnitude lower than the IC50. Therefore, the presence of FL or a FL metabolite was insufficient to account for the inhibition by a kinetic mechanism. In contrast to cell studies, CYP1A immunoreactive protein was significantly decreased in vivo by FL cotreatment, indicating that FL may inhibit EROD activity by down-regulating the CYP1A protein. A covalent interaction of [(14)C]FL with CYP1A was not detected. Total (32)P-postlabeled DNA adducts were not significantly changed by cotreatment of FL and BaP; however, cotreatment with 50 mg/kg FL decreased one adduct and increased another significantly. Because FL and perhaps other inhibitory PAHs, co-occur in the environment with CYP1A inducers, CYP1A-dependent bioassays may cause an underestimation of PAH exposures.     

Effects of 2,2',4,4'-tetrachlorobiphenyl on granulocytic HL-60 cell function and expression of cyclooxygenase-2.

Polychlorinated biphenyls (PCBs) are persistent environmental contaminants that affect a number of cellular systems, including neutrophils. It has been demonstrated that noncoplanar PCBs (i.e., ortho- substituted PCBs) alter function of primary rat neutrophils. The objectives of these experiments were to determine if responses in a human, neutrophil-like cell line exposed to PCBs were similar to those reported for rat neutrophils and to explore further PCB-mediated alterations in neutrophil function. The human promyelocytic leukemia cell line (HL-60) was differentiated with DMSO to a neutrophil-like phenotype. Treatment of differentiated HL-60 cells with 2,2',4,4'-tetrachlorobiphenyl, a noncoplanar, ortho-substituted PCB congener, caused an increase in f-Met-Leu-Phe-induced degranulation, as measured by release of myeloperoxidase (MPO). Treatment with the coplanar, non-ortho-substituted congener 3,3',4,4'-tetrachlorobiphenyl had no effect on MPO release. 2,2',4,4'-Tetrachlorobiphenyl caused a time- and dose-dependent release of [3H]-arachidonic acid (3H-AA). A significant increase in 3H-AA release was observed after 60 min of exposure, and concentrations of 10 microM or larger increased 3H-AA release. In contrast, 3,3',4,4'-tetrachlorobiphenyl had no effect on 3H-AA release. The effect of PCBs on mRNA levels for cyclooxygenase-2 (COX-2) was examined using semiquantitative RT-PCR. COX-2 mRNA was significantly elevated in response to 2,2',4,4'-tetrachlorobiphenyl in a concentration-dependent manner. COX-2 expression was maximal by 30 min of exposure to 2,2',4,4'-tetrachlorobiphenyl. COX-2 protein and activity were also increased after exposure to 2,2',4,4'-tetrachlorobiphenyl; COX-1 protein and activity were unaffected. 3,3',4,4'-Tetrachlorobiphenyl did not increase COX-2 mRNA levels. These results demonstrate that a noncoplanar PCB alters the functional status of granulocytic HL-60 cells, causing enhanced degranulation and upregulation of COX-2, whereas a coplanar PCB lacks this activity. These data suggest that noncoplanar PCBs alter HL-60 cell function and COX-2 expression via an Ah-receptor-independent mechanism.