Article

Functional analysis of cis-regulatory regions within the dioxin-inducible CYP1A promoter/enhancer region from zebrafish (Danio rerio)

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Abstract

In vitro mutagenesis was utilized to render the various xenobiotic response elements (XREs) within the zebrafish CYP1A promoter/enhancer region non-functional either independently or in combination. Reporter gene assays revealed that only XRE4, XRE7, and XRE8 contributed to maximal TCDD-mediated induction of luciferase and that the contribution of each XRE to maximal induction was not equal. XRE4 and XRE7 were capable of functioning independently, while XRE8 alone could not support TCDD-mediated induction but was required for the ability of XRE4 and XRE7 to support maximal induction. These results were observed in cell lines derived from human, mouse and zebrafish. Mutagenesis of 3' nucleotides flanking the non-functional XRE5, and functional XRE4 did not alter the function of these XREs in cell culture. In silico analyses revealed the presence of putative Sp1, AP2, CREB, and two HNF-3 transcription factor binding sites that were localized to common positions within the enhancer region of both the mouse and zebrafish CYP1A genes. In vitro mutagenesis of the binding sites showed that loss of the Sp1 or AP2 sites had minimal impact on TCDD-mediated gene induction while loss of the putative CREB site resulted in a modest decrease in basal and inducible activity and mutation of the HNF-3 reduced inducible activity by >90% of controls. Collectively, these findings suggest that the presence of XREs is not the sole determinant for regulation of aryl hydrocarbon receptor (AHR)-mediated gene and do not function in an additive manner.

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... In silico promoter analysis of XREs. An in silico promoter analysis was carried out on 10 000 bp upstream of the transcriptional start site to identify potential XREs [KNGCGTG] (Lusska et al., 1993;ZeRuth and Pollenz, 2007) in the cis-promoter of nrf genes where AHR1b could potentially bind. Both strands of the DNA were searched using a fuzzy search algorithm, fuzznuc (Rice et al., 2000), as previously described in Williams et al. (2013). ...
... Primers for each XRE in the cis-promoter of all nrf genes were designed (Table 1) and used. For the positive control, primers were designed to amplify XRE 4 from cyp1a1 (ZeRuth et al., 2007), and the negative control primers amplified a segment of nrf1a cispromoter that was at least 5800 bp upstream from any of the 2 identified XREs. Promoter content was calculated as previously described in Hestermann and Brown (2003). ...
... qPCR of DNA from input fraction and AHR1b immunoprecipitation fraction are shown for samples treated with the control DMSO vehicle or TCDD. Shown in the nrf1a panel is the negative control which was an AHR1b IP followed by an amplification of a cis region of the nrf1a promoter lacking an XRE, and the positive control involved an AHR1b IP followed by an amplification of a cis region of the cyp1a promoter with XRE4 that has been shown to bind AHR2 (ZeRuth and Pollenz, 2007). Data are pooled from 3 experiments and presented as mean þ SD where different letters over bars indicate significant difference (2-way ANOVA with Sidak's multiple comparisons test, p ¼ .05). ...
Article
Interactions between regulatory pathways allow organisms to adapt to their environment and respond to stress. One interaction that has been recently identified occurs between the aryl hydrocarbon receptor (AHR) and the nuclear factor erythroid-2 related factor (NRF) family. Each transcription factor regulates numerous downstream genes involved in the cellular response to toxicants and oxidative stress; they are also implicated in normal developmental pathways. The zebrafish model was used to explore the role of AHR regulation of nrf genes during development and in response to toxicant exposure. To determine if AHR1b is responsible for transcriptional regulation of six nrf genes during development, a loss-of-function experiment using morpholino-modified oligonucleotides was conducted followed by a Chromatin Immunoprecipitation (ChIP) study at the beginning of the pharyngula period (24 hours post fertilization; hpf). The expression of nrf1a was AHR1b dependent and its expression was directly regulated through specific XREs in its cis-promoter. However, nrf1a expression was not altered by exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), a toxicant and prototypic AHR agonist. The expression of nrf1b, nrf2a, and nfe2 was induced by TCDD, and AHR1b directly regulated their expression by binding to cis-XRE promoter elements. Lastly, nrf2b and nrf3 were neither induced by TCDD nor regulated by AHR1b. These results show that AHR1b transcriptionally regulates nrf genes under toxicant modulation via binding to specific XREs. These data provide a better understanding of how combinatorial molecular signaling potentially protects embryos from embryotoxic events following toxicant exposure.
... In contrast, CYP1A has 22 core XREs within 10kb of the transcriptional start site. However, the presence of a core XRE sequence may not be sufficient to confer function to a putative XRE, and we did not find any regions in the CYP1D1 promoter that match the more extended positionspecific scoring matrix of ZeRuth and Pollenz (TYGCGTGMVMDS [39]), which they found in functional XREs. Other possible response elements found in the proximal promoter region of CYP1D1 include those for PPAR/RXR, RORa, and NRF1 (NFE2L1), but not RAR/RXR. ...
... The CYP1Cs have fewer (4) XREs than do CYP1A or CYP1B1, and although the function of these XREs has not been determined, the CYP1Cs are inducible in embryos by AHR agonists [17;18]. The lack of putative functional XREs, based on the more stringent approach of Zeruth and Pollenz [39], helps explain the lack of CYP1D1 induction by PCB126 or TCDD. The two core KNGCGTG motifs in the proximal CYP1D1 promoter do not match the extended XRE sequence shown to be functional with respect to TCDD-induced trans-activation [39]. ...
... The lack of putative functional XREs, based on the more stringent approach of Zeruth and Pollenz [39], helps explain the lack of CYP1D1 induction by PCB126 or TCDD. The two core KNGCGTG motifs in the proximal CYP1D1 promoter do not match the extended XRE sequence shown to be functional with respect to TCDD-induced trans-activation [39]. This suggests that CYP1D1 may play a limited role, if any, in adaptive response to dioxin-like compounds in zebrafish. ...
Article
Enzymes in the cytochrome P450 1 family oxidize many common environmental toxicants. We identified a new CYP1, termed CYP1D1, in zebrafish. Phylogenetically, CYP1D1 is paralogous to CYP1A and the two share 45% amino acid identity and similar gene structure. In adult zebrafish, CYP1D1 is most highly expressed in liver and is relatively highly expressed in brain. CYP1D1 transcript levels were higher at 9h post-fertilization than at later developmental times. Treatment of zebrafish with potent aryl hydrocarbon receptor (AHR) agonists (3,3',4,4',5-pentachlorobiphenyl or 2,3,7,8-tetrachlorodibenzo-p-dioxin) did not induce CYP1D1 transcript expression. Morpholino oligonucleotide knockdown of AHR2, which mediates induction of other CYP1s, did not affect CYP1D1 expression. Zebrafish CYP1D1 heterologously expressed in yeast exhibited ethoxyresorufin- and methoxyresorufin-O-dealkylase activities. Antibodies against a CYP1D1 peptide specifically detected a single electrophoretically-resolved protein band in zebrafish liver microsomes, distinct from CYP1A. CYP1D1 in zebrafish is a CYP1A-like gene that could have metabolic functions targeting endogenous compounds.
... A previous study showed that the XRE5 located in the distal cluster cyp1a1 promoter region conferred TCDD responsiveness with the greatest fold induction (Zeruth and Pollenz, 2007). Hence, complementary oligonucleotides of XRE5, 5-ACACATACACACCTTTGCA-CGCGATGCTTTACCTGTTGCT-3 and 5-AGCAA CAGGTAAAGCATCGC-GTGCAAAGGTGTGTATGTGT-3 were synthesized and annealed for the band-shift assay. ...
... This finding is in line with a study on the characterization of CYP1A1 in the Hepa-1c1c7 cell line in zebrafish Pollenz, 2005, 2007). Although the induction folds of these constructs were not sufficiently high in ZFL compared with the Hepa-1c1c7 cell line (Zeruth and Pollenz, 2007), they were useful in illustrating the transcriptional regulation mechanisms of Cd 2+ on CYP1A1 expression. Our results also showed that Cd 2+ inhibited the luciferase activity of those two TCDDresponsive constructs (P-2626/-2099 and 3XRE), indicating that Cd 2+ inhibited the transformation of AHR to its DNA-binding form and/or the nuclear accumulation of ligand-bound AHR, thus inhibiting AHR/ ARNT/XRE complex formation. ...
Article
We studied the effects of Cd(2+) on TCDD-mediated induction of the cytochrome P450 1A1 (cyp1a1) gene using a zebrafish liver cell line (ZFL). Our results showed that Cd(2+) inhibited the TCDD-mediated induction of the cyp1a1 protein, enzyme activity, and mRNA expression level. Cd(2+) also down-regulated levels of the aryl hydrocarbon receptor (ahr2) and the aryl hydrocarbon receptor nuclear translocator 2b (arnt2b) mRNAs. Compared with TCDD (3nM) treatment alone, co-treatment with Cd(2+) (0-30μM) and TCDD (3nM) significantly inhibited the activity of the luciferase reporter gene constructs harboring the distal promoter region (P-2626/-2009) of CYP1A1 and the synthetic 3XRE gene promoter. This indicates that Cd(2+) decreased the level of TCDD-induced cyp1a1 through transcriptional inhibition. Proteomic analysis was also used to evaluate the effect of Cd(2+) on TCDD-altered protein expression in ZFL cells. The identified proteins are mainly enzymes of the glycolysis pathway and proteasomes, and have anti-oxidative and anti-stress effects.
... Some putative PXR response elements (PXREs), including direct repeat 3 and 4 (DR3, DR4), everted repeat 6 and 8 (ER6, ER8), and inverted repeat 0 (IR0) Kast et al., 2002;Sonoda et al., 2002;Sueyoshi and Negishi, 2001) were identified using NHR scan (Sandelin and Wasserman, 2005). Putative xenobiotic response elements (XREs; also known as dioxin response elements DREs) also were searched using the XRE consensus sequence identified by Fujisawa-Sehara et al. (1987) and studied in zebrafish by Zeruth and Pollenz (2007). ...
... This suggestion that Ahr2 can up-regulate pxr expression and expression of Pxr target genes is supported by the presence of multiple XREs in the 10-kb upstream of the translation start sites of these genes. Notably, pxr and CYP3A65 both have clusters of XREs, similar to those found upstream of CYP1A (Zeruth and Pollenz, 2007). It could be that these XREs are involved in induction of pxr, CYP2AA12 and CYP3C1 by PCB126, in a common mechanism with CYP3A65 involving binding of Ahr-ligand complex to XREs (Chang et al., 2013). ...
Article
Full-text available
Ligand-activated receptors regulate numerous genes, and mediate effects of a broad set of endogenous and exogenous chemicals in vertebrates. Understanding the roles of these transcription factors in zebrafish (Danio rerio) is important to the use of this non-mammalian model in toxicological, pharmacological and carcinogenesis research. Response to a potential agonist for the pregnane X receptor (Pxr) (pregnenolone PN) was examined in developing zebrafish, to assess involvement of Pxr in regulation of selected genes, including genes in cytochrome P450 subfamilies CYP2 and CYP3. We also examined interaction of Pxr and the aryl hydrocarbon receptor (Ahr) signaling pathways. PN caused a dose-dependent increase in mRNA levels of pxr, ahr2, CYP1A, CYP2AA1, CYP2AA12, CYP3A65 and CYP3C1, most of which peaked at 3 μM PN. The well-known Ahr agonist 3,3',4,4',5-pentachlorobiphenyl (PCB126) also up-regulated expression of pxr, ahr2, CYP1A, CYP2AA12, CYP3A65 and CYP3C1 in a dose-dependent manner. Inhibition of pxr translation by morpholino antisense oligonucleotides (MO) suppressed PN-induced expression of pxr, ahr2, CYP3A65 and CYP3C1 genes. Levels of CYP2AA1 and CYP2AA12 mRNA were increased in the control-MO group exposed to PN; this was prevented by knocking down Pxr. Similarly, Ahr2-MO treatment blocked PCB126-induced mRNA expression of pxr, CYP1A, CYP2AA12, CYP3A65 and CYP3C1. The present study shows self-regulation of pxr by PN in developing zebrafish. Selected zebrafish CYP1, CYP2 (including several CYP2AAs) and CYP3 genes appear to be under the regulation of both Pxr and Ahr2. © The Author 2014. Published by Oxford University Press on behalf of the Society of Toxicology. All rights reserved. For permissions, please email: journals.permissions@oup.com.
... To determine whether Nrf2a or Nrf2b are directly involved in the transcriptional regulation of other nrf family members, in silico promoter analysis was carried out for AREs and XREs using a fuzzy search algorithm, fuzznuc [56]. 10,000 base pairs upstream of the start site and the entire length of the gene were examined for putative zebrafish AREs (TGA(G/C)nnnTC [57]) and XREs (KNGCGTG [58]). Additional searches were carried out for Nfe2 binding sites [59] determined from ChIP-Seq studies. ...
... Putative antioxidant response elements (ARE) and xenobiotic response elements (XRE) in the proximal regulatory region of zebrafish nfe2 and nfe2-related (nrf) genes. ARE and XRE positions were mapped using a fuzzy search for the core response elements determined in zebrafish[57,58]. Exon positions were exported from the Ensembl database (Zv9). ...
Article
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Transcription factors in the CNC-bZIP family (NFE2, NRF1, NRF2 and NRF3) regulate genes with a wide range of functions in response to both physiological and exogenous signals, including those indicating changes in cellular redox status. Given their role in helping to maintain cellular homeostasis, it is imperative to understand the expression, regulation, and function of CNC-bZIP genes during embryonic development. We explored the expression and function of six nrf genes (nfe2, nrf1a, nrf1b, nrf2a, nrf2b, and nrf3) using zebrafish embryos as a model system. Analysis by microarray and quantitative RT-PCR showed that genes in the nrf family were expressed throughout development from oocytes to larvae. The spatial expression of nrf3 suggested a role in regulating the development of the brain, brachia and pectoral fins. Knock-down by morpholino anti-sense oligonucleotides suggested that none of the genes were necessary for embryonic viability, but nfe2 was required for proper cellular organization in the pneumatic duct and subsequent swim bladder function, as well as for proper formation of the otic vesicles. nrf genes were induced by the oxidant tert-butylhydroperoxide, and some of this response was regulated through family members Nrf2a and Nrf2b. Our results provide a foundation for understanding the role of nrf genes in normal development and in regulating the response to oxidative stress in vertebrate embryos.
... Putative dioxin response elements (DREs) were sought in the promoter regions of the chicken, turkey, and mallard CYP1C genes, using the sequence 59-(T/G)NGCGTG-39 [26,27]. Within 10 kb upstream from the start codons of the CYP1C genes two putative DREs were found in chicken (at 2458 and 21671 bp) and one was found in turkey (at 29193 bp). ...
... Rather these differences could be related to differences in AHR affinity for PCB126 not compensated for by the higher dose given to quail. In addition to AHR affinity of the inducer, the level of CYP1 induction depends on the number of functional DREs in the gene promoters, epigenetic factors, interaction of the AHR with nuclear receptors (e.g., estrogen receptor), cofactors, the AHR repressor, etc. [26,51,52,53,54,55]. Because the CYP1s are likely to be expressed in different cell types, it would be informative to study cell-specific induction of the CYP1s, and CYP1C1 in particular, in chicken. ...
Article
Full-text available
Cytochrome P450 1 (CYP1) genes are biomarkers for aryl hydrocarbon receptor (AHR) agonists and may be involved in some of their toxic effects. CYP1s other than the CYP1As are poorly studied in birds. Here we characterize avian CYP1B and CYP1C genes and the expression of the identified CYP1 genes and AHR1, comparing basal and induced levels in chicken and quail embryos. We cloned cDNAs of chicken CYP1C1 and quail CYP1B1 and AHR1. CYP1Cs occur in several bird genomes, but we found no CYP1C gene in quail. The CYP1C genomic region is highly conserved among vertebrates. This region also shares some synteny with the CYP1B region, consistent with CYP1B and CYP1C genes deriving from duplication of a common ancestor gene. Real-time RT-PCR analyses revealed similar tissue distribution patterns for CYP1A4, CYP1A5, CYP1B1, and AHR1 mRNA in chicken and quail embryos, with the highest basal expression of the CYP1As in liver, and of CYP1B1 in eye, brain, and heart. Chicken CYP1C1 mRNA levels were appreciable in eye and heart but relatively low in other organs. Basal transcript levels of the CYP1As were higher in quail than in chicken, while CYP1B1 levels were similar in the two species. 3,3',4,5,5'-Pentachlorobiphenyl induced all CYP1s in chicken; in quail a 1000-fold higher dose induced the CYP1As, but not CYP1B1. The apparent absence of CYP1C1 in quail, and weak expression and induction of CYP1C1 in chicken suggest that CYP1Cs have diminishing roles in tetrapods; similar tissue expression suggests that such roles may be met by CYP1B1. Tissue distribution of CYP1B and CYP1C transcripts in birds resembles that previously found in zebrafish, suggesting that these genes serve similar functions in diverse vertebrates. Determining CYP1 catalytic functions in different species should indicate the evolving roles of these duplicated genes in physiological and toxicological processes.
... Dioxin response elements (DREs) are DNA regions where the AHR/ARNT transcription factor complex binds to induce gene expression. Consensus DRE core sequences, defined as (T/G)NGCGTG (Zeruth and Pollenz, 2007), were searched for in the 20-kb regions upstream from the clawed frog CYP1 gene start codons (using the X. tropicalis genome assembly 4.1, ENSEMBL version 58), and the locations of such sequences are depicted in Fig. 2. The gene having the greatest abundance of putative DRE sequences was CYP1A in which 13 such sequences were found, whereas CYP1B1 and CYP1C had 6 and 7, and CYP1D1 had only 1 putative DREs, respectively in the regions examined (Fig. 2). The CYP1A gene had a cluster of 5 DREs located about 5 kb upstream of the transcription start site (~9.5 kb upstream of the translation start site). ...
... However, which DREs are functional in frog CYP1 genes is not known. Functional studies of putative DREs in CYP1A genes in mammals and fish have shown that not all DREs can initiate gene expression, and induction also depends on the occurrence of binding sites for other transcription factors and co-activators in the vicinity of the DREs (Zeruth and Pollenz, 2007). Conceivably, there could be fewer functional DREs in the clawed frog CYP1A than in CYP1A in many fish species, e.g., zebrafish (Jönsson et al., 2007b). ...
Article
The Xenopus tropicalis genome shows a single gene in each of the four cytochrome P450 1 (CYP1) subfamilies that occur in vertebrates, designated as CYP1A, CYP1B1, CYP1C1, and CYP1D1. We cloned the cDNAs of these genes and examined their expression in untreated tadpoles and in tadpoles exposed to waterborne aryl hydrocarbon receptor agonists, 3,3',4,4',5-pentachlorobiphenyl (PCB126), β-naphthoflavone (βNF), or indigo. We also examined the effects of PCB126 on expression of genes involved in stress response, cell proliferation, thyroid homeostasis, and prostaglandin synthesis. PCB126 induced CYP1A, CYP1B1, and CYP1C1 but had little effect on CYP1D1 (77-, 1.7-, 4.6- and 1.4-fold induction versus the control, respectively). βNF induced CYP1A and CYP1C1 (26- and 2.5-fold), while, under conditions used, indigo tended to induce only CYP1A (1.9-fold). The extent of CYP1 induction by PCB126 and βNF was positively correlated to the number of putative dioxin response elements 0-20 kb upstream of the start codons. No morphological effect was observed in tadpoles exposed to 1 nM-10 μM PCB126 at two days post-fertilization (dpf) and screened 20 days later. However, in 14-dpf tadpoles a slight up-regulation of the genes for PCNA, transthyretin, HSC70, Cu-Zn SOD, and Cox-2 was observed two days after exposure to 1 μM PCB126. This study of the full suite of CYP1 genes in an amphibian species reveals gene- and AHR agonist-specific differences in response, as well as a much lower sensitivity to CYP1 induction and short-term toxicity by PCB126 compared with in fish larvae. The single genes in each CYP1 subfamily may make X. tropicalis a useful model for mechanistic studies of CYP1 functions.
... AHRE clusters have also been identified in the regulatory region of other dioxin-induced genes, most notably mouse Cyp1a1 and Cyp1a2 (Nukaya et al., 2009). The variable degree of functionality of individual AHREs in the X. tropicalis cluster ( Figure 4) appears to be common to AHRE clusters in other genes, including mouse Cyp1a2 (Kawasaki et al., 2010) and zebrafish cyp1a (Zeruth and Pollenz, 2007). ...
Article
Frog metamorphosis, the development of an air-breathing froglet from an aquatic tadpole, is controlled by thyroid hormone (TH) and glucocorticoids (GC). Metamorphosis is susceptible to disruption by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), an aryl hydrocarbon receptor (AHR) agonist. Krüppel-Like Factor 9 (klf9), an immediate early gene in the endocrine-controlled cascade of expression changes governing metamorphosis, can be synergistically induced by both hormones. This process is mediated by an upstream enhancer cluster, the klf9 synergy module (KSM). klf9 is also an AHR target. We measured klf9 mRNA following exposures to triiodothyronine (T3), corticosterone (CORT), and TCDD in the Xenopus laevis cell line XLK-WG. klf9 was induced 6-fold by 50 nM T3, 4-fold by 100 nM CORT, and 3-fold by 175 nM TCDD. Co-treatments of CORT and TCDD or T3 and TCDD induced klf9 7- and 11-fold, respectively, while treatment with all 3 agents induced a 15-fold increase. Transactivation assays examined enhancers from the Xenopus tropicalis klf9 upstream region. KSM-containing segments mediated a strong T3 response and a larger T3/CORT response, while induction by TCDD was mediated by a region ∼1 kb farther upstream containing 5 AHR response elements (AHREs). This region also supported a CORT response in the absence of readily-identifiable glucocorticoid responsive elements, suggesting mediation by protein-protein interactions. A functional AHRE cluster is positionally conserved in the human genome, and klf9 was induced by TCDD and TH in HepG2 cells. These results indicate that AHR binding to upstream AHREs represents an early key event in TCDD’s disruption of endocrine-regulated klf9 expression and metamorphosis.
... Interestingly, not all DREs are able to initiate gene expression. Gary Zeruth studied the function of putative DREs in CYP1A genes in mammals and fish and showed that induction also depends on the occurrence of binding sites for other transcription factors and coactivators in the vicinity of the DREs [94]. ...
Article
Full-text available
The aryl hydrocarbon receptor (AhR) is a transcription factor that regulates a wide range of biological and toxicological effects by binding to specific ligands. AhR ligands exist in various internal and external ecological systems, such as in a wide variety of hydrophobic environmental contaminants and naturally occurring chemicals. Most of these ligands have shown differential responses among different species. Understanding the differences and their mechanisms helps in designing better experimental animal models, improves our understanding of the environmental toxicants related to AhR, and helps to screen and develop new drugs. This review systematically discusses the species differences in AhR activation effects and their modes of action. We focus on the species differences following AhR activation from two aspects: (1) the molecular configuration and activation of AhR and (2) the contrast of cis-acting elements corresponding to AhR. The variations in the responses seen in humans and other species following the activation of the AhR signaling pathway can be attributed to both factors.
... The lack of effect of PCB126 on Cyp3a56 in SC fish gill suggests that Ahr is not involved in Cyp3a56 regulation in killifish, at least not in in gills. This hypothesis is supported by the lack of any xenobiotic (dioxin) response elements (XRE/DRE) within 2 kb of the start site of Cyp3a56 gene, and only 2 DRE sequences in the 5 kb cis regulatory region, in distinct contrast to zebrafish (Zeruth and Pollenz, 2007). The lack of a clear-cut effect of PCB153 on Pxr expression in gills further suggests that the regulation is different from the action of pregnenolone in zebrafish. ...
Article
Full-text available
Previous reports suggested that non-dioxin-like (NDL) PCB153 effects on cytochrome P450 3A (Cyp3a) expression in Atlantic killifish (Fundulus heteroclitus) gills differed between F0 generation fish from a PCB site (New Bedford Harbor; NBH) and a reference site (Scorton Creek; SC). Here, we examined effects of PCB153, dioxin-like (DL) PCB126, or a mixture, on Cyp3a56 mRNA in killifish generations removed from the wild, without environmental PCB exposures. PCB126 effects in liver and gills differed between populations, as expected. Gill Cyp3a56 was not affected by either congener in NBH F2 generation fish, but was induced by PCB153 in SC F1 fish, with females showing a greater response. PCB153 did not affect Cyp3a56 in liver of either population. Results suggest a heritable resistance to NDL-PCBs in killifish from NBH, in addition to that reported for DL PCBs. Induction of Cyp3a56 in gills may be a biomarker of exposure to NDL PCBs in fish populations that are not resistant to PCBs.
... One cluster of DREs is located between À2700 and À2100, and the other is located between À580 and À180. A subset of DREs is capable of promoting TCDD-inducible expression (Zeruth and Pollenz, 2007). Therefore, the zebrafish cyp1a1 gene expression level is the best biological marker for indicating the activity of the AhR agonist . ...
... Reporter gene assays revealed that only DRE4, DRE7, and DRE8 could contribute to the maximal TCDDmediated induction of luciferase, and the contribution of each XRE to the maximal subsequent induction was not equal. Consistent results have also been observed in cell lines derived from zebrafish, mouse and human (Zeruth and Pollenz, 2007). Xie et al. (2018) compared the intact cyp1a promoter with three different truncated promoters in a dualluciferase reporter assay in vitro and found that increasing the quantity of DREs increased the sensitivity of the cyp1a promoter for AHR ligands. ...
Article
Dioxin-like compounds (DLCs) are extremely stable toxic organic compounds and can cause serious health risks. To develop a convenient biomonitoring tool for the detection of DLCs in the environment, we generated a transgenic line—Tg(cyp1a-12DRE:EGFP)—with a zebrafish cyp1a promoter recombined with multiple dioxin-responsive elements (DREs) that drive EGFP expression. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD)-induced EGFP expression was observed in the head cartilage (most sensitive), gut, otic vesicle, pectoral fin bud and eye of larvae. The lowest observed effect concentration of TCDD was estimated to be approximately 1 ng/L. Compared with existing zebrafish lines, our transgenic fish displayed comparable or even higher detection sensitivity to DLCs and could serve as an improved and rapid assay in an in vivo context. The Tg(cyp1a-12DRE:EGFP) transgenic zebrafish line also had higher stability for inducing EGFP expression (nearly 100% of our zebrafish induced EGFP at approximately 1 ng/L TCDD) than other lines. In addition, Tg(cyp1a-12DRE:EGFP) zebrafish could serve as a convenient and straightforward tool to assess potential cranial malformations and related health effects.
... These results show that the three active PXR-specific REs determined for human CYP3A4 34 are not conserved between these species, including mouse ( Supplementary Fig. 2). The clusters of known XREs in human CYP1A1, mouse Cyp1a1 and zebrafish cyp1a orthologs [35][36][37] , however, appear to be conserved and coincide position-wise. Importantly, whereas NR REs dominate the promoter regions of mammalian CYP3A genes, the promoter regions of the fish cyp3a orthologs have a higher number of potential XREs (Fig. 6c). ...
Article
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Sensitivity to environmental stressors largely depend on the genetic complement of the organism. Recent sequencing and assembly of teleost fish genomes enable us to trace the evolution of defense genes in the largest and most diverse group of vertebrates. Through genomic searches and in-depth analysis of gene loci in 76 teleost genomes, we show here that the xenosensor pregnane X receptor (Pxr, Nr1i2) is absent in more than half of these species. Notably, out of the 27 genome assemblies that belong to the Gadiformes order, the pxr gene was only retained in the Merluccidae family (hakes) and Pelagic cod (Melanonus zugmayeri). As an important receptor for a wide range of drugs and environmental pollutants, vertebrate PXR regulate the transcription of a number of genes involved in the biotransformation of xenobiotics, including cytochrome P450 enzymes (CYP). In the absence of Pxr, we suggest that the aryl hydrocarbon receptor (Ahr) have evolved an extended regulatory role by governing the expression of certain Pxr target genes, such as cyp3a, in Atlantic cod (Gadus morhua). However, as several independent losses of pxr have occurred during teleost evolution, other lineages and species may have adapted alternative compensating mechanisms for controlling crucial cellular defense mechanisms.
... However, the most sensitive promoter was the truncated 8XRE promoter when treated with 0.1 nM TCDD, which showed the Fluc/Rluc value 7 times higher than that obtained using the intact promoter. These results were similar to the findings descibed by Zeruth et al [40]. Therefore, the sensitivity of the intact and modified promoters was in the order: ...
Article
The polycyclic aromatic hydrocarbons (PAHs) and 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) are classified as human carcinogens, and can also cause serious health problems. To develop a convenient bio-monitoring tool for the detection of PAHs and TCDD in the environment, we generated a transgenic zebrafish line Tg(cyp1a:mCherry) with cyp1a promoter driving mCherry expression. Here, Tg(cyp1a:mCherry) embryos were treated with different concentrations of TCDD and five US EPA priority PAHs congeners. The results showed that the expressions of mCherry and endogenous cyp1a were consistent with the PAHs exposure concentrations and were largely induced by TCDD and ≥4-ring PAHs. Moreover, the sensitivity of Tg(cyp1a:mCherry) embryos was also evaluated through monitoring of the PAHs contamination in the water and soil samples. The elevated red fluorescent signals and cyp1a expression levels were observed in Tg(cyp1a:mCherry) zebrafish after exposure to water samples and soil organic extracts with higher concentrations of ≥4-ring PAHs. These results further strengthen our findings of concentration- and congener-dependent response of the newly established zebrafish. Taken together, the newly established zebrafish line will prove as a sensitive, efficient and convenient tool for monitoring PAHs and TCDD contamination in the environment.
... To construct the 3XRE-luc reporter, the following single-strand oligonucleotide (oligo) containing three repeated core sequences of zfXRE (bold) (Zeruth and Pollenz, 2007) was designed: 5′-CGGGGTACCGCTAAAGCATCGCGTGCAAAGGTGT GCTAAAGCATCGCGTGCAAAGGTGTGCTAAAGCATCGCGTGCAAAGGTGT-CCGCTCGAG-3′. The oligo and its complementary strand were synthesized by Tech Dragon Limited, Hong Kong. ...
Article
Polybrominated diphenyl ethers (PBDEs) are endocrine-disrupting chemicals that affect the environment and the health of humans and wildlife. In this study, the zebrafish liver (ZFL) cell line was used in vitro to investigate two major PBDE contaminants: 2, 2’, 4, 4’, 5-pentabromodiphenyl ether (BDE-99) and 2, 2’, 4, 4’-tetrabromodiphenyl ether (BDE-47). BDE-99 was found to significantly induce cytochrome P450 (CYP1A), uridine diphosphate glucuronosyl transferase 1 family a, b (ugt1ab), 7-ethoxyresorufin-O-deethylase activity and an aryl hydrocarbon receptor (Ahr) dependent xenobiotic response element luciferase reporter system, confirming the Ahr-mediated activation of CYP1A by BDE-99. The time-course effect indicated that the role of BDE-99 in Ahr-mediated signaling is likely to be transient and highly dependent on the ability of BDE-99 to induce CYP1A and ugt1ab, and presumably its metabolism. BDE-99 also exhibited a significant dose-response effect on a developed zebrafish pregnane X receptor luciferase reporter gene system. However, the other abundant contaminant under study, BDE-47, did not exhibit the above effects. Together, these results indicated that the molecular mechanism of PBDEs induced in ZFL cells is a chemically specific process that differs between members of the PBDE family. CYP1A induction derived by BDE-99 warrants further risk assessment as the humans, wildlife and environment are exposed to a complex mixture including dioxin-like compounds and carcinogenic compounds.
... Upon ligand binding, the ligand-receptor complex dissociates from the heat shock protein HSP90 and migrates to the nucleus with the aryl hydrocarbon receptor nuclear translocator (ARNT). 4 The entire complex then acts as a transcription factor that binds to xenobiotic responsive elements (XREs) located in the promoter region of the cyp1a1 gene to activate its transcription. 5 In zebrafish, there are several isoforms of CYP1, AHR, and ARNT proteins. ...
Article
We evaluated the individual and joint estrogenic effects of cadmium (Cd2+) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the zebrafish liver (ZFL) cell line, zebrafish embryo, larvae and the liver of adult zebrafish. The mRNA expression of vtg1 was inhibited by Cd2+, but unaffected by TCDD in ZFL cells. Similar changes in the mRNA levels of ERα, ERβ1, ERβ2 and GPER (G protein coupled estrogen receptor) in ZFL cells were also observed. Deletion mutants of vtg1 gene promoters were constructed to investigate transcriptional regulation, and we found that all of the constructs failed to respond to TCDD or Cd2+. However, after co-transfection with a vtg1 promoter-luciferase construct to the ERα, ERβ1, ERβ2 and GPER expression vectors, decreased luciferase activity was observed in the ERα co-transfection group after treatment with Cd2+, suggesting that ERα participates in vtg1 transcriptional regulation and is affected by Cd2+. Differences in the regulation of the mRNA levels of these genes were also observed between different developmental stages and between the livers of male and female zebrafish.
... Upon ligand binding, the ligand-receptor complex dissociates from the heat shock protein HSP90 and migrates to the nucleus with the aryl hydrocarbon receptor nuclear translocator (ARNT). 4 The entire complex then acts as a transcription factor that binds to xenobiotic responsive elements (XREs) located in the promoter region of the cyp1a1 gene to activate its transcription. 5 In zebrafish, there are several isoforms of CYP1, AHR, and ARNT proteins. ...
Article
Trace metal ions and trace organic compounds are common co-contaminants in the environment that pose risks to human health. We evaluated the effects of four metal ions (As(3+), Cu(2+), Hg(2+), and Zn(2+)) on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) induced cytotoxicity and the expression of the cytochrome P4501A1 gene (cyp1a1) in the zebrafish liver (ZFL) cell line. A metal accumulation study showed that Cu and Zn did not accumulate in ZFL cells. However, As and Hg did accumulate, which resulted in the inhibition of TCDD-mediated induction of cyp1a1 mRNA and protein expression, and 7-ethoxyresorufin O-deethylase activity. A luciferase assay showed that both As(3+) and Hg(2+) inhibited the TCDD-induced activity of gene constructs containing either synthetic 3XRE or a distal cyp1a1 promoter region, implying that the decreased levels of TCDD-induced cyp1a1 were due to transcriptional effects. A proteomic study showed that the toxic effects of As(3+) might be due to changes in cellular metabolic processes, the cellular stimulation response and the cellular redox state in ZFL cells.
... In zebrafish, AHR2B (zfAHR2B) is a predominant form involved in TCDD toxicity, whereas zfAHR1A is nonfunctional (Andreasen et al., 2002). In in vitro experiments, the zfAHR2B isoform exhibits high-affinity binding of TCDD, XRE binding via dimerization with ARNT in a ligand-dependent manner, and transactivation potency of a reporter gene under the transcriptional control of an XRE-containing promoter (Karchner et al., 2005;Tanguay et al., 1999;ZeRuth and Pollenz, 2007). Moreover, protection against several endpoints of TCDD toxicity was observed by the functional knockdown of zfAHR2B with an antisense morpholino oligonucleotide in vivo and the functional loss of dominant negative AHR2B in transgenic zebrafish (Antkiewicz et al., 2006;Lanham et al., 2011;Prasch et al., [ / Quantity (g) Chicken CYP1A4 (ckCYP1A4) mRNA levels in chicken embryos were also quantified using real-time RT-PCR. ...
Article
Dioxins including 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) cause toxic effects through activation of the aryl hydrocarbon receptor (AHR)–mediated signaling pathway. Our previous studies have investigated the function of 2 AHR isoforms (AHR1 and AHR2) in avian species and identified a third AHR in the chicken (Gallus gallus) genome. Knowledge of multiple avian AHRs is indispensable to understand molecular mechanisms of AHR-mediated toxic effects and establish risk assessment framework for environmental AHR ligands in avian species. In this study, we successfully isolated a third novel AHR1-like cDNA from chicken and designated it as chicken AHR1 beta (ckAHR1β). The mRNA expression of ckAHR1β was primarily detected in the liver, and the hepatic protein expression was confirmed by Western blotting. Although mRNA expression of ckAHR1β was not altered by in ovo TCDD exposure, ckAHR1β exhibited specific binding to [3H]TCDD, TCDD-dependent nuclear translocation, and interaction with xenobiotic responsive elements (XREs) and AHR nuclear translocators (ARNTs). In vitro XRE-driven reporter gene assays revealed ckAHR1β-mediated transactivation of TCDD in a dose-dependent manner, showing a 10-fold reduced sensitivity (high EC50) compared with that mediated by ckAHR1. The mutation of Val371 to Ser371 in the ligand-binding domain of ckAHR1β shifted the TCDD-EC50 toward the value observed in ckAHR1, indicating the critical roles of the amino acid in sensitivity. Furthermore, ckAHR1β-mediated transactivation of TCDD was enhanced by 17β-estradiol (E2)-activated chicken estrogen receptor α (ckERα), suggesting a positive cross talk between ckERα and ckAHR1β signaling pathway. Both TCDD-induced and its enhanced activities by E2 were suppressed by the ckAHR repressor in a manner similar to ckAHR1. Collectively, our findings discover the role of ckAHR1β in dioxin toxicity and give an insight into the evolutionary history of the AHR signaling pathway.
... We also searched the zebrafish genome for putative DREs in the cox-2a, cox-2b, myca, and axin2 genes. As previously reported there are a large number of putative DREs in the zebrafish CYP1A gene promoter (Jönsson et al., 2007b;Zeruth and Pollenz, 2007). Data for putative DREs in the CYP1B1, CYP1C1, CYP1C2, and CYP1D1 promoters have also been published (Jönsson et al., 2007a;Goldstone et al., 2009). ...
Article
The teleost swim bladder is assumed a homolog of the tetrapod lung. Both swim bladder and lung are developmental targets of persistent aryl hydrocarbon receptor (AHR(2)) agonists; in zebrafish (Danio rerio) the swim bladder fails to inflate with exposure to 3,3',4,4',5-pentachlorobiphenyl (PCB126). The mechanism for this effect is unknown, but studies have suggested roles of cytochrome P4501 (CYP1) and cyclooxygenase 2 (Cox-2) in some Ahr-mediated developmental effects in zebrafish. We determined relationships between swim bladder inflation and CYP1 and Cox-2 mRNA expression in PCB126-exposed zebrafish embryos. We also examined effects on β-catenin dependent transcription, histological effects, and Ahr2 dependance of the effect of PCB126 on swim bladder using morpholinos targeting ahr2. One-day-old embryos were exposed to waterborne PCB126 or carrier (DMSO) for 24h and then held in clean water until day 4, a normal time for swim bladder inflation. The effects of PCB126 were concentration-dependent with EC50 values of 1.4 to 2.0nM for induction of the CYP1s, 3.7 and 5.1nM (or higher) for cox-2a and cox-2b induction, and 2.5nM for inhibition of swim bladder inflation. Histological defects included a compaction of the developing bladder. Ahr2-morpholino treatment rescued the effect of PCB126 (5nM) on swim bladder inflation and blocked induction of CYP1A, cox-2a, and cox-2b. With 2nM PCB126 approximately 30% of eleutheroembryos(3) failed to inflate the swim bladder, but there was no difference in CYP1 or cox-2 mRNA expression between those embryos and embryos showing inflated swim bladder. Our results indicate that PCB126 blocks swim bladder inflation via an Ahr2-mediated mechanism. This mechanism seems independent of CYP1 or cox-2 mRNA induction but may involve abnormal development of swim bladder cells.
... In addition, the putative DREs were found only in the distal site (from -5.0 to -4.0 kb) of X. tropicalis CYP1A upstream sequence. It has been reported that functional DREs exist within the -2.0 kb sequences of CYP1A genes in human, mouse, chicken, and zebrafish (ZeRuth and Pollenz, 2007;Lee et al., 2009;Nukaya and Bradfield, 2009). In X. laevis, a closely related species to X. tropicalis, AHR exhibits a low binding ability to TCDD and much higher requirement of TCDD dosage for the induction of CYP1A gene than those of other vertebrates (Lavine et al., 2005). ...
Article
Cytochrome P450 family 1 (CYP1) genes are involved in the metabolism of chemical pollutants including halogenated aromatic hydrocarbons such as 2,3,7,8-terachlorodibenzo-p-dioxin (TCDD). Whereas the molecular characterization of CYP1 genes has been well investigated in various vertebrates, information on CYP1 genes in amphibians is relatively scarce. In the present study, we attempt to characterize CYP1 genes in Xenopus tropicalis, the only amphibian species whose genome has been sequenced. A novel CYP1 gene, CYP1D was identified in the X. tropicalis genome sequence, besides the genes of CYP1A, 1B, and 1C subfamilies that have been so far reported. Moreover, by a bioinformatics approach, three putative dioxin responsive elements (DREs) were found in the 5′-flanking regions of the X. tropicalis CYP1 genes, but the number of DREs and their localization within the 5 kb upstream sequences were different from those of other vertebrates. These findings provide new insights into the evolutionary and functional diversity of CYP1 genes in vertebrates and less susceptibility of amphibians to TCDD.
... However, the CYP1A gene of killifish contains three consensus XREs (5 0 CACGC3 0 ) within 1.6 kb of the putative transcriptional start site (Powell et al., 2004), in addition, two XREs at À613 bp and À1585 bp in common cormorant CYP1A5, and one XRE at À262 bp in chicken CYP1A5 conferred TCDD-responsiveness (Lee et al., 2009). Study of ZeRuth and Pollenz (2007) shows that XREs is not the sole determinant for regulation of aryl hydrocarbon receptor (AhR)-mediated gene and their function does not appear in an additive manner. In mouse, seven out of eight DREs are located 1.4 kb upstream of the CYP1A1 transcriptional start site and 12.6 kb upstream of the CYP1A2 start site. ...
Article
Phylogenetic analysis of AhR pathway genes and their evolutionary rate variations were studied on aquatic animals. The gene sequences for the proteins involved in this pathway were obtained from four major phylogenetic groups, including bivalvia, amphibian, teleostei and mammalia. These genes were distributed under four major steps of toxicology regulation: formation of cytosolic complex, translocation of AhR, heterodimerization of AhR and induction of CYP1A. The NJ, MP, and ML algorithm were used on protein coding DNA sequences to deduce the evolutionary relationship for the respective AhR pathway gene among different aquatic animals. The rate of non-synonymous nucleotide substitutions per non-synonymous site (d(N)) and synonymous nucleotide substitutions per synonymous site (d(S)) were calculated for different clade of the respective phylogenetic tree for each AhR pathway gene. The phylogenetic analysis suggests that evolutionary pattern of AhR pathway genes in aquatic animals is characterized mainly through gene duplication events or alterative splicing. The d(N) values indicate that all AhR pathway genes are well conserved in aquatic animals, except for CYP1A gene. Furthermore, compare with other aquatic animals, the d(N) value indicates that AhR pathway genes of fish are less conserved, and these genes likely go through an adaptive evolution within aquatic animals.
... However, the lack of induction of CYP1D1 in zebrafish was suggested to be related to a lack of functional AHR response elements (AHREs), which are binding sites for the AHR/ARNT in the promoter regions . In zebrafish, there are only two putative AHREs (of unproven function) in the promoter of zebrafish CYP1D1, in contrast to the 22 putative AHREs and three proven functional AHREs for CYP1A (ZeRuth and Pollenz, 2007;Goldstone et al., 2009). A variety of other response elements were identified in the promoter region of zebrafish CYP1D1 ) and thus the possibility of induction via other receptors and agonists still remains to be elucidated, both for the CYP1Cs and CYP1D1 in Fundulus and in zebrafish. ...
Article
Knowledge of the complement of cytochrome P450 (CYP) genes is essential to understanding detoxification and bioactivation mechanisms for organic contaminants. We cloned three new CYP1 genes, CYP1B1, CYP1C2 and CYP1D1, from the killifish Fundulus heteroclitus, an important model in environmental toxicology. Expression of the new CYP1s along with previously known CYP1A and CYP1C1 was measured by qPCR in eight different organs. Organ distribution was similar for the two CYP1Cs, but otherwise patterns and extent of expression differed among the genes. The AHR agonist 3,3',4,4',5-pentachlorobiphenyl (PCB126) (31 pmol/g fish) induced expression of CYP1A and CYP1B1 in all organs examined, while CYP1C1 was induced in all organs except testis. The largest changes in response to PCB126 were induction of CYP1A in testis (approximately 700-fold) and induction of CYP1C1 in liver (approximately 500-fold). CYP1B1 in liver and gut, CYP1A in brain and CYP1C1 in gill also were induced strongly by PCB126 (> 100-fold). CYP1C1 expression levels were higher than CYP1C2 in almost all tissues and CYP1C2 was much less responsive to PCB126. In contrast to the other genes, CYP1D1 was not induced by PCB126 in any of the organs. The organ-specific response of CYP1s to PCB126 implies differential involvement in effects of halogenated aromatic hydrocarbons in different organs. The suite of inducible CYP1s could enhance the use of F. heteroclitus in assessing aquatic contamination by AHR agonists. Determining basal and induced levels of protein and the substrate specificity for all five CYP1s will be necessary to better understand their roles in chemical effects and physiology.
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The “toxicology in the twenty-first century” paradigm shift demands the development of alternative in vitro test systems. Especially in the field of ecotoxicology, coverage of aquatic species-specific assays is relatively scarce. Transient reporter gene assays could be a quick, economical, and reliable bridging technology. However, the user should be aware of potential pitfalls that are influenced by reporter vector geometry. Here, we report the development of an AhR-responsive transient reporter-gene assay in the permanent zebrafish hepatocytes cell line (ZFL). Additionally, we disclose how viral, constitutive promoters within reporter-gene assay cassettes induce squelching of the primary signal. To counter this, we designed a novel normalization vector, bearing an endogenous zebrafish-derived genomic promoter (zfEF1aPro), which rescues the squelching-delimited system, thus, giving new insights into the modulation of transient reporter systems under xenobiotic stress. Finally, we uncovered how the ubiquitously used ligand BNF promiscuously activates multiple toxicity pathways of the xenobiotic metabolism and cellular stress response in an orchestral manner, presumably leading to a concentration-related inhibition of the AhR/ARNT/XRE-toxicity pathway and non-monotonous concentration–response curves. We named such a multi-level inhibitory mechanism that might mask effects as “maisonette squelching . ” Graphical abstract A transient reporter gene assay in zebrafish cell lines utilizing endogenous regulatory gene elements shows increased in vitro toxicity testing performance. Synthetic and constitutive promotors interfere with signal transduction (“squelching”) and might increase cellular stress (cytotoxicity). The squelching phenomenon might occur on multiple levels (toxicity pathway crosstalk and normalization vector), leading to a complete silencing of the reporter signal.
Article
A new series of 1,3-diketone, heterocyclic and α,β-unsaturated derivatives were synthesized and evaluated for their AhR antagonist activity using zebrafish and mammalian cells. Compounds 1b, 2c, 3b and 5b showed significant AhR antagonist activity in a transgenic zebrafish model. Among them, compound 3b, and 5b were found to have excellent AhR antagonist activity with IC50 of 3.36 nM and 8.3 nM in a luciferase reporter gene assay. In stem cell proliferation assay, compound 5b elicited marked HSC expansion.
Article
2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a persistent organic pollutant (POP), an unintentional byproduct of various industrial processes and a human carcinogen. The expression of the cytochrome P450 1A (cyp1a) gene is upregulated in the presence of TCDD through activating the aryl hydrocarbon receptor (AhR) pathway in a dose-dependent manner. Several essential response elements, including the eight potential xenobiotic response elements (XREs) in the cyp1a promoter region, have been identified to be the main functional parts for the response to TCDD. Thus, we aimed to develop a convenient and sensitive bio-monitoring tool to examine the level of POPs in the environment and evaluate its potential human health risks by TCDD. Here, we established a transgenic zebrafish model with a red fluorescent reporter gene (mCherry) using the truncated cyp1a (T-cyp1a) promoter. Under exposure to TCDD, the expression pattern of mCherry in the reporter zebrafish mirrored that of endogenous cyp1a mRNA, and the primary target tissues for TCDD were the brain vessels, liver, gut, cloaca and skin. Our results indicated that exposure of the embryos to TCDD at concentrations as low as 0.005 nM for 48 h, which did not elicit morphological abnormalities in the embryos, markedly increased mCherry expression. In addition, the reporter embryos responded to other POPs, and primary liver cell culture of zebrafish revealed that Cyp1a protein was mainly expressed in the cytoplasm of liver cells. Furthermore, our transgenic fish embryos demonstrated that TCDD exposure can regulate the expression levels of several tumor-related factors, including EGF, TNF-α, C-myc, PCNA, TGF-β, Akt and pAkt, suggesting our transgenic fish can be used as a sensitive model to evaluate the carcinogenicity induced by TCDD exposure.
Chapter
It is a challenge to determine how best to protect aquatic biota from pollution within the context of the increasing pressures on our planetary freshwater resources. Aquatic environmental regulations based on single toxicant concentrations have helped protect biota. There are concerns, however, that these regulations do not adequately protect against chronic exposure to toxicant mixtures. Advances have been made to assist regulators in identifying chemicals of concern, as well as the construction of conceptual frameworks for mixture and ecosystem risk assessment. The basis of these new initiatives is a greater understanding of the biological effects of toxicants on individuals, populations and ecosystems. This chapter focuses on bioavailability, uptake, metabolism, excretion and mode of action of toxicants (metal, pharmaceuticals, organic pollutants, pesticides and nanomaterial) and how knowledge of these processes assists environmental risk assessment. There is an urgent need for guidance on allowable toxicant loads to protect freshwater biota before irreparable damage is done.
Article
2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the unintentional byproduct of various industrial processes, is classified as human carcinogen and could disrupt reproductive, developmental and endocrine systems. Induction of cyp1a1 is used as an indicator of TCDD exposure. We sought to determine tissues that are vulnerable to TCDD toxicity using a transgenic zebrafish (Danio rerio) model. We inserted a nuclear enhanced green fluorescent protein gene (EGFP) into the start codon of a zebrafish cyp1a gene in a fosmid clone using DNA recombineering. The resulting recombineered fosmid was then used to generate cyp1a reporter zebrafish, embryos of which were exposed to TCDD. Expression pattern of EGFP in the reporter zebrafish mirrored that of endogenous cyp1a mRNA. In addition, exposure of the embryos to TCDD at as low as 10pM for 72h, which does not elicit morphological abnormalities of embryos, markedly increased GFP expression. Furthermore, the reporter embryos responded to other AhR ligands as well. Exposure of the embryos to TCDD revealed previously reported (the cardiovascular system, liver, pancreas, kidney, swim bladder and skin) and unreported target tissues (retinal bipolar cells, otic vesicle, lateral line, cloaca and pectoral fin bud) for TCDD. Transgenic cyp1a reporter zebrafish we have developed can further understanding of ecotoxicological relevance and human health risks by TCDD. In addition, they could be used to identify agonists of AhR and antidotes to TCDD toxicity.
Article
Cytochrome P450 1 (CYP1) mRNA induction patterns in three-spined stickleback (Gasterosteus aculeatus) were explored for use in environmental monitoring of aryl hydrocarbon receptor (AHR) agonists. The cDNAs of stickleback CYP1A, CYP1B1, CYP1C1, and CYP1C2 were cloned and their basal and induced expression patterns were determined in the brain, gill, liver and kidney. Also, their induction time courses were compared after waterborne exposure to a transient (indigo) or a persistent (3,3',4,4',5-pentacholorbiphenyl PCB 126) AHR agonist. The cloned stickleback CYP1s exhibited a high amino acid sequence identity compared with their zebrafish orthologs and their constitutive tissue distribution patterns largely agreed with those reported in other species. PCB 126 (100 nM) induced different CYP1 expression patterns in the four tissues, suggesting tissue-specific regulation. Both indigo (1 nM) and PCB 126 (10 nM) induced a strong CYP1 expression in gills. However, while PCB 126 gave rise to a high and persistent induction in gills and liver, induction by indigo was transient in both organs. The number of putative dioxin response elements found in each CYP1 gene promoter roughly reflected the induction levels of the genes. The high responsiveness of CYP1A, CYP1B1, and CYP1C1 observed in several organs suggests that three-spined stickleback is suitable for monitoring of pollution with AHR agonists.
Article
Arylhydrocarbon receptor (Ahr) and cytochrome P4501a1 (Cyp1a1) are members of the Ahr/Cyp1a1 pathway that oxygenates various toxic chemicals including aryl hydrocarbons. To elucidate Ahr/Cyp1a1 pathway responses in teleost fish tissues, we examined the effects of 3,4-dichloroaniline (3,4-DCA), a reference toxic compound known to activate the Ahr/Cyp1a1 pathway, on the expression of arh and cyp1a1 in zebrafish tissues and embryos by means of in situ hybridization (ISH). Our ISH analysis showed that cyp1a1 expression was markedly activated by 3,4-DCA in the gill and intestinal epithelia, skin epidermis, and liver parenchymal cells of adult zebrafish. Before differentiation of the gill, intestine, and liver, skin was the site of cyp1a1 activation in embryos. Unlike the cyp1a1 response, 3,4-DCA-mediated ahr activation was not marked in either adults or embryos, indicating a possibility that stable ahr transcripts persist in the cytoplasm of these cells to induce cyp1a1. Young oocytes (previtellogenic to early vitellogic stage) express ahr; however activation of cyp1a1 by 3,4-DCA was negligible in these oocytes, suggesting that ahr expression in oocytes is not directly linked to cyp1a1 activation. Based on our finding that skin epidermis up-regulates cyp1a1 in response to 3,4-DCA, we demonstrated that fin explants, which can be harvested without sacrificing fish, can be used as a standard for assaying cyp1a1 activation in addition to embryos that are now used.
Article
The present study focuses on the molecular mechanism and interspecies differences in susceptibility of avian aryl hydrocarbon receptor (AHR)-cytochrome P4501A (CYP1A) signaling pathway. By the cloning of 5'-flanking regions of CYP1A5 gene from common cormorant (Phalacrocorax carbo) and chicken (Gallus gallus), seven putative xenobiotic response elements (XREs) were identified within 2.7 kb upstream region of common cormorant CYP1A5 (ccCYP1A5), and six XREs were found within 0.9 kb of chicken CYP1A5 (ckCYP1A5). Analysis of sequential deletion and mutagenesis of the binding sites in avian CYP1A5 genes by in vitro reporter gene assays revealed that two XREs at -613 bp and -1585 bp in ccCYP1A5, and one XRE at -262 bp in ckCYP1A5 conferred TCDD-responsiveness. The binding of AHR1 with AHR nuclear translocator 1 (ARNT1) to the functional XRE in a TCDD-dependent manner was verified with gel shift assays, suggesting that avian CYP1A5 is induced by TCDD through AHR1/ARNT1 signaling pathway as well as mammalian CYP1A1 but through a distinct pathway from mammalian CYP1A2, an ortholog of the CYP1A5. TCDD-EC(50) for the transcriptional activity in both cormorant AHR1- and AHR2-ccCYP1A5 reporter construct was 10-fold higher than that in chicken AHR1-ckCYP1A5 reporter construct. In contrast, chicken AHR2 showed no TCDD-dependent response. The TCDD-EC(50) for CYP1A5 transactivation was altered by switching AHR1 between the two avian species, irrespective of the species from which the regulatory region of CYP1A5 gene originates. Therefore, the structural difference in AHR, not the CYP1A5 regulatory region may be a major factor to account for the dioxin susceptibility in avian species.
Article
Hepatocyte nuclear factor 3 (HNF3) recognizes two apparently distinct classes of sequence. However, a detailed mutational analysis of a representative binding site of each class reveals that these sequences display common features. We propose a unified consensus sequence for HNF3-binding sites. The basis of the sequence specificity of the interaction of HNF3 with DNA is analyzed in light of the recently determined structure of an HNF3-DNA complex (Clark et al., Nature 364, 412-420, 1993). Particularly, our study reveals that the DNA site used for this structural analysis is too short to account for all HNF3-DNA interactions. The better knowledge of the sequence determinant recognized by HNF3 has allowed us to analyze its function in the glucocorticoid response of the rat tyrosine aminotransferase (TAT) gene. This response is mediated through a complex array of neighboring and overlapping transcription factor binding sites. Selective inactivation of the HNF3-binding sites in this glucocorticoid response unit (GRU) allows us to demonstrate unambiguously that they play a major role in the amplitude of the glucocorticoid response. Furthermore, HNF3 beta overexpression results in a stimulation of the glucocorticoid response that is dependent on the integrity of its binding sites. We also show that the relative level of HNF3 determines the extent of the contribution of one of the glucocorticoid receptor binding sites. Our results indicate that HNF3 accounts for most of the liver-specific activity of this GRU.
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The cytochrome P450 1 (CYP1) family has expanded with the addition of the CYP1B and CYP1C subfamilies. We recently identified a new CYP1 subfamily in zebrafish, CYP1D, with a single gene, CYP1D1. Here we examined sequences found in other fish genomes, i.e., stickleback (Gasterosteus aculeatus) and medaka (Oryzias latipes), for similarities among fish CYP1D1 genes. The full-length deduced amino acid sequences for CYP1D1 in these two species averaged about 43% identity to the CYP1As, but nearly 50% when sequence alignment ambiguities were masked. CYP1D1 has seven exons, similar in size and position to the exons in CYP1D1 and CYP1A in zebrafish. However, the intronic distances were substantially smaller in the medaka and stickleback. There also were differing numbers of putative xenobiotic response elements in the CYP1D1 of the various species. Whether the stickleback or medaka genes are inducible by aryl hydrocarbon receptor (AHR) agonists is yet to be determined.
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The liganded Ah receptor activates transcription by binding to a specific DNA-recognition motif within a dioxin-responsive enhancer upstream of the CYP1A1 gene. Analyses of mutant enhancers by gel retardation reveal that each base pair within the domain 5'CGTG(GCAC)3' is essential to the receptor-enhancer interaction. The three base pairs immediately flanking each end of the essential domain contribute less strongly to receptor binding. Analyses of enhancer function by transfection reveal that a mutation in the essential domain, which abolishes receptor-DNA binding, obliterates enhancer function. Mutations outside the essential domain, which diminish, but do not abolish, receptor-DNA binding, also obliterate enhancer function. Additionally, one mutation adjacent to the essential binding motif does not affect receptor-DNA binding, but destroys enhancer activity. These findings imply that transcriptional enhancement by the dioxin-responsive system cannot be predicted solely by the strength of the receptor-enhancer interaction.
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The environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin produces its biological effects by binding to an intracellular protein, the Ah receptor. The liganded receptor activates transcription by binding to a specific recognition motif within a dioxin-responsive enhancer upstream of the target CYP1A1 gene. Here, we have used gel retardation to analyze the interaction between the liganded Ah receptor and five circularly permuted DNA fragments that contain a receptor recognition motif. Our findings indicate that the binding of the liganded receptor to its recognition motif bends the DNA at (or near) the site of the protein-DNA interaction. This observation implies that Ah receptor-induced DNA distortion may contribute to the activation of CYP1A1 transcription by 2,3,7,8-tetrachlorodibenzo-p-dioxin.
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The dioxin-responsive enhancer upstream of the CYP1A1 gene contains four copies of the recognition motif for the liganded Ah receptor. The results of deletion analyses, linker-scanning analyses, and the analysis of individual enhancer subdomains reveal that each copy of the motif contributes to the response of the enhancer to 2,3,7,8-tetrachlorodibenzo-p-dioxin. In the context of the dioxin-responsive enhancer, a GC box, representing the DNA binding site for Sp1 (or a related transcription factor), has no detectable intrinsic activity but enhances gene expression when linked to a recognition motif for the liganded Ah receptor, thereby producing a synergistic effect on enhancer function.
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Three nuclear factors, the Ah receptor, XF1, and XF2, bind sequence specifically to the Ah response elements or xenobiotic response elements (XREs) of the cytochrome P450IA1 (P450c) gene. The interactions of these factors with the Ah response element XRE1 were compared by three independent methods, methylation interference footprinting, orthophenanthroline-Cu+ footprinting, and mobility shift competition experiments, using a series of synthetic oligonucleotides with systematic alterations in the XRE core sequence. These studies established the following (i) all three factors interact sequence specifically with the core sequence of XRE1; (ii) the pattern of contacts made with this sequence by the Ah receptor are different from those made by XF1 and XF2; and (iii) although XF1 and XF2 can be distinguished by the mobility shift assay, the sequence specificities of their interactions with XRE1 are indistinguishable. Further characterization revealed the following additional differences among these three factors: (i) XF1 and XF2 could be extracted from nuclei under conditions quite different from those required for extraction of the Ah receptor; (ii) XF1 and XF2 were present in the nuclei of untreated cells and did not respond to polycyclic compounds, such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and beta-napthoflavone, while nuclear Ah receptor was undetectable in untreated cells and rapidly increased in response to TCDD; (iii) inhibition of protein synthesis did not affect the TCDD-induced appearance of the Ah receptor but substantially decreased the constitutive activities of XF1 and XF2, suggesting that the Ah receptor must be present in untreated cells in an inactive form that can be rapidly activated by polycyclic compounds, while the constitutive expression of XF1 and XF2 depends on the continued synthesis of a relatively unstable protein; (iv) the receptor-deficient and nuclear translocation-defective mutants of the hepatoma cell line Hepa1, which are known to lack nuclear Ah receptor, expressed normal levels of XF1 and XF2, suggesting that the former factor is genetically distinct from the latter two; and (v) a divalent metal ion, probably Zn2+, is known to be an essential cofactor for the Ah receptor but was not required for the DNA-binding activities of XF1 and XF2. Together, these findings indicate that the Ah receptor is distinct from XF1 and XF2, while the latter two activities may be related. Because the DNA-binding domains of these three factors overlap substantially, their binding to XREs is probably mutually exclusive, which suggests that the interplay of these factors at Ah response elements may be important to the regulation of CYP1A1 gene transcription. The results of preliminary transfection experiments with constructs harboring XREs upstream of the chloramphenicol acetyltransferase gene driven by a minimal simian virus 40 promoter are presented that are consistent with this hypothesis.
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Gel retardation analyses reveal a cluster of six binding sites for the liganded Ah receptor within a 700-base pair DNA domain upstream of the mouse CYP1A1 gene. The nucleotide sequences of the binding sites define a consensus recognition motif for the liganded receptor. The consensus motif is not symmetric. Alteration of the consensus motif produces a decrease in the receptor-DNA interaction. The ligand receptor binds as a monomer to its recognition motif and preferentially binds to double-stranded DNA. These observations reveal apparent differences between 2,3,7,8-tetrachlorodibenzo-p-dioxin and steroid hormones in their respective mechanisms of action.
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The environmental contaminant 2,3,7,8-tetra-chlorodibenzo-p-dioxin produces its biological effects by binding to an intracellular protein (the Ah receptor). The dioxin-Ah receptor complex activates cytochrome P1-450 gene transcription by interacting with dioxin-responsive enhancers. Here, we report that the dioxin-Ah receptor complex binds to DNA containing the "core" sequence 5'-TA/TGCGTG-3', which is present in each of three receptor-dependent enhancers. Functional analyses indicate that binding of the liganded Ah receptor to the core sequence fails to generate an active enhancer and that nucleotides flanking the core sequence must contribute to enhancer function and dioxin action.
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The synthesis of cytochrome P-450c is induced remarkably in cultured cells as well as animal tissues in response to added chemicals such as 3-methylcholanthrene and 2,3,7,8-tetrachlorodibenzodioxin. To study this mechanism, we joined the sequence of 5'-flanking and upstream regions of the P-450c gene to the structural gene for chloramphenicol acetyltransferase. The fusion gene was introduced into Hepa-1 cells for the assay of the expressed acetyltransferase activity. At least three cis-acting regulatory regions that are responsible for the inductive expression were determined in the sequences from nucleotide -3674 to -3067, from -1682 to -1429, and from -1139 to -1029, relative to the transcription start site, by external deletion analysis. Further detailed analysis of the region (nucleotides -1139 to -1029) most influential on the inducibility revealed that a regulatory element consisting of 10 base pairs termed a drug regulatory element (DRE) and its homologues were tandemly arranged in this region. The consensus sequence deduced from DREs is 5'-GCNTGAGGCTGGG-3'. The regulatory sequence from nucleotide -1140 to -844 is capable of conferring inducibility on a heterologous promoter in a manner independent of its orientation and distance from the subordinate promoter.
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The DNA element governing the inducible expression of drug-metabolizing P-450c gene by xenobiotic treatments was investigated by gene transfer methods. A variety of dissected fragments from -844 to -1140bp region which was essential for the inducibility of P-450c gene were placed on the hetero-logous SV40 promoter for testing the inducibility. Mapping studies in combination with gel retardation assay defined the presence of the two xenobiotic responsive elements(XRE, XRE1, -1007 - -1021bp; XRE2, -1088 - -1092bp) composed of about 15 nucleotides which expressed the enhancer activity in response to xenobiotic inducers. The two XREs share 10 nucleotides in common out of 15 as expressed in the sequence CG/CTG/CC/TTG/CTCACGCT/AA and are arranged in the inverse orientation. They are different from DREs(drug responsive element) proposed previously(Sogawa, K. et al. Proc. Natl. Acad. Sci. 83, 8044–8048(1986)) and expressed a strong enhancer activity in response to 3-methylcholanthrene. The XRE shows a significant homology with glucocort.icoid regulatory elements and apparently needs normal functions of a putative xenobiotic receptor for the inducible enhancer activity.
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The Ah receptor (AHR), the Ah receptor nuclear translocator protein (ARNT), and single-minded protein (SIM) are members of the basic helix-loop-helix-PAS (bHLH-PAS) family of regulatory proteins. In this study, we examine the DNA half-site recognition and pairing rules for these proteins using oligonucleotide selection-amplification and coprecipitation protocols. Oligonucleotide selection-amplification revealed that a variety of bHLH-PAS protein combinations could interact, with each generating a unique DNA binding specificity. To validate the selection-amplification protocol, we demonstrated the preference of the AHR.ARNT complex for the sequence commonly found in dioxin-responsive enhancers in vivo (TNGCGTG). We then demonstrated that the ARNT protein is capable of forming a homodimer with a binding preference for the palindromic E-box sequence, CACGTG. Further examination indicated that ARNT may have a relaxed partner specificity, since it was also capable of forming a heterodimer with SIM and recognizing the sequence GT(G/A)CGTG. Coprecipitation experiments using various PAS proteins and ARNT were consistent with the idea that the ARNT protein has a broad range of interactions among the bHLH-PAS proteins, while the other members appear more restricted in their interactions. Comparison of this in vitro data with sites known to be bound in vivo suggests that the high affinity half-site recognition sequences for the AHR, SIM, and ARNT are T(C/T)GC, GT(G/A)C (5'-half-sites), and GTG (3'-half-sites), respectively.
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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.
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The DNA upstream of the dioxin-inducible CYP1A1 gene contains six distinct sites to which the liganded Ah receptor binds in intact mouse hepatoma cells. Here, we have analyzed these six bona fide receptor-binding sites in order to study the relationships between DNA sequence, receptor binding, and dioxin responsiveness. Gel retardation studies reveal that the sites vary by about 7-fold in their relative affinities for the liganded receptor. Within this range, there is no obvious association between the strength of receptor binding and the degree of dioxin responsiveness, as measured in transfection experiments. In fact, one site binds the receptor well but fails to respond to dioxin. This observation implies that the receptor-DNA binding event per se is not sufficient to confer dioxin responsiveness upon a linked gene. Comparison of the DNA sequences of the six receptor-binding sites permits the derivation of a "functional consensus" recognition sequence, which is more extended in length than the "core"-binding sequence previously described. In corroboration of these results, protein-DNA cross-linking studies indicate that the liganded receptor contacts base pairs beyond the core sequence. Our observations also indicate that the liganded receptor can tolerate limited sequence heterogeneity at its DNA-binding site and still elicit a response to dioxin. This finding might reflect corresponding heterogeneity in the amino acid sequence of the liganded receptor's DNA-binding domain.
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The liver-specific enhancer of the serum albumin gene contains an essential segment, designated eH, which binds the hepatocyte nuclear factor 3 alpha (HNF3 alpha) and ubiquitous nuclear factor 1/CCAAT transcription factor (NF1/CTF) proteins in tight apposition. We previously showed that activation of transcription by the eH site was correlated with an increase in intracellular HNF3 alpha levels during the in vitro differentiation of the hepatic cell line H2.35. We now show that transfection of an HNF3 alpha cDNA expression vector into dedifferentiated H2.35 cells is sufficient to induce transcription from the eH site. Mutational analysis of the enhancer demonstrates that NF1/CTF cooperates with HNF3 alpha to induce enhancer activity. However, when the eH site is removed from the context of the enhancer, NF1/CTF can inhibit transcriptional activation by HNF3 alpha. We conclude that the ternary complex of HNF3 alpha, NF1/CTF, and the eH site forms a novel, composite regulatory element that is sensitive to the local DNA sequence environment and suggest that the transcriptional stimulatory activity of NF1/CTF depends on its higher-order interactions with other proteins during hepatocyte differentiation.
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cDNAs encoding two distinct basic helix-loop-helix/PER-ARNT-SIM (bHLH/PAS) proteins with similarity to the mammalian aryl hydrocarbon nuclear translocator (ARNT) protein were isolated from RTG-2 rainbow trout gonad cells. The deduced proteins, termed rtARNTa and rtARNTb, are identical over the first 533 amino acids and contain a basic helix-loop-helix domain that is 100% identical to human ARNT. rtARNTa and rtARNTb differ in their COOH-terminal domains due to the presence of an additional 373 base pairs of sequence that have the characteristics of an alternatively spliced exon. The presence of the 373-base pair region causes a shift in the reading frame. rtARNTa lacks the sequence and has a COOH-terminal domain of 104 residues rich in proline, serine, and threonine. rtARNTb contains the sequence and has a COOH-terminal domain of 190 residues rich in glutamine and asparagine. mRNAs for both rtARNT splice variants were detected in RTG-2 gonad cells, trout liver, and gonad tissue. rtARNTa and rtARNb protein were identified in cell lysates from RTG-2 cells. Transfection of rtARNT expression vectors into murine Hepa-1 cells that are defective in ARNT function (type II) result in rtARNT protein expression localized to the nucleus. Treatment of these cells with 2,3,7,8-tetrachlorodibenzo-p-dioxin results in a 20-fold greater induction of endogenous P4501A1 protein in cells expressing rtARNTb when compared with rtARNTa, even though both proteins effectively dimerize with the aryl hydrocarbon receptor. The decreased function of rtARNTa appears to be due to inefficient binding of rtARNTa.AHR complexes to DNA. In addition, the presence of rtARNTa can reduce the aryl hydrocarbon receptor-dependent function of rtARNTb in vivo and in vitro.
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The aryl hydrocarbon (Ah) receptor has occupied the attention of toxicologists for over two decades. Interest arose from the early observation that this soluble protein played key roles in the adaptive metabolic response to polycyclic aromatic hydrocarbons and in the toxic mechanism of halogenated dioxins and dibenzofurans. More recent investigations have provided a fairly clear picture of the primary adaptive signaling pathway, from agonist binding to the transcriptional activation of genes involved in the metabolism of xenobiotics. Structure-activity studies have provided an understanding of the pharmacology of this receptor; recombinant DNA approaches have identified the enhancer sequences through which this factor regulates gene expression; and functional analysis of cloned cDNAs has allowed the characterization of the major signaling components in this pathway. Our objective is to review the Ah receptor's role in regulation of xenobiotic metabolism and use this model as a framework for understanding the less well-characterized mechanism of dioxin toxicity. In addition, it is hoped that this information can serve as a model for future efforts to understand an emerging superfamily of related signaling pathways that control biological responses to an array of environmental stimuli.
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Toxicity and histopathology of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in zebrafish (Danio rerio) early life stages was characterized from 12 to 240 hr postfertilization (hpf) following water-borne exposure of newly fertilized eggs. TCDD did not increase egg mortality (0-48 hpf), nor did it affect time to hatching (48-96 hpf). Egg doses of 1.5 ng [3H]TCDD/g or greater elicited toxic responses in zebrafish larvae. Pericardial edema and craniofacial malformations were first observed at 72 hpf, followed by the onset of yolk sac edema (96 hpf) and mortality (132 hpf). At 240 hpf the ED50s for pericardial edema, yolk sac edema, and craniofacial malformations were 2.2, 2.1, and 1.9 ng [3H]TCDD/g egg, respectively. The LD50, determined at 240 hpf, was 2.5 ng [3H]TCDD/g egg. Severe hemodynamic changes, observed as slowed blood flow in vascular beds of the trunk, head, and gills and slowed heart rate, occurred in TCDD-treated zebrafish prior to or coincident with the onset of gross signs of toxicity. Histological examination of TCDD-treated zebrafish revealed a variety of epithelial tissue lesions including arrested gill development and ballooning degeneration and/or necrosis of the renal tubules, hepatocytes, pancreas, and all major brain regions. Mesenchymal tissue lesions included subcutaneous edema in the head, trunk, and yolk sac, edema of the pericardium and skeletal muscle, and underdevelopment of the swim bladder. This demonstration of zebrafish responsiveness to TCDD early life stage toxicity coupled with the considerable information on developmental biology and genetics of zebrafish provides a foundation for future investigations into the mechanism of TCDD developmental toxicity.
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The effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure on regional red blood cell (RBC) perfusion rate, as an index of blood flow, and lower jaw development were investigated quantitatively in zebrafish embryos (Danio rerio) during early development. As revealed by observation of live embryos and alcian-blue staining, TCDD retarded lower jaw development in a concentration-dependent manner with only a minor inhibitory effect on total body length. Both inhibitory effects were significant as early as 60 h postfertilization (hpf), at which time the area of goosecoid (gsc) mRNA expression was clearly reduced in the lower jaw. To examine effects of TCDD on RBC perfusion rate, time-lapse recording was performed using a digital video camera attached to a light microscope. TCDD did not show marked effects on RBC perfusion rate until 72 hpf, when vessel-specific effects emerged. TCDD severely inhibited RBC perfusion rate in intersegmental arteries of the trunk, but only modestly and slightly inhibited RBC perfusion rate in certain vessels of the head such as the central arteries and optic vein. Conversely, at both 72 and 84 hpf, TCDD significantly increased RBC perfusion rate in the hypobranchial artery branching to the lower jaw primordia, and then reduced it at 96 hpf. RBC perfusion rate in all vessels examined in TCDD-exposed embryos was inhibited at 96 hpf. The zebrafish aryl hydrocarbon receptor 2 (zfAhR2) mRNA was strongly expressed in the lower jaw primordia at 48 hpf, and expression of this transcript was augmented by TCDD treatment. Thus, TCDD exposure of the zebrafish embryo has a disruptive effect on local circulation and lower jaw cartilage growth. Initially, TCDD may act directly on the lower jaw primordia to impair lower jaw development. Reductions in hypobranchial RBC perfusion rate occurred well after the initial retardation in lower jaw development had become apparent, and may contribute further to the effect.
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Cytochrome P450 3A4 (CYP3A4) is involved in the metabolism of more than 50% of currently used therapeutic drugs, yet the mechanisms that control CYP3A4 basal expression in liver are poorly understood. Several putative binding sites for CCAAT/enhancer-binding protein (C/EBP) and hepatic nuclear factor 3 (HNF-3) were found by computer analysis in CYP3A4 promoter. The use of reporter gene assays, electrophoretic mobility shift assays, and site-directed mutagenesis revealed that one proximal and two distal C/EBP alpha binding sites are essential sites for the trans-activation of CYP3A4 promoter. No trans-activation was found in similar reporter gene experiments with a HNF-3 gamma expression vector. The relevance of these findings was further explored in the more complex DNA/chromatin structure within endogenous CYP3A4 gene. Using appropriate adenoviral expression vectors, we found that both hepatic and nonhepatic cells overexpressing C/EBP alpha had increased CYP3A4 mRNA levels, but no effect was observed when HNF-3 gamma was overexpressed. In contrast, overexpression of HNF-3 gamma simultaneously with C/EBP alpha resulted in a greater activation of the CYP3A4 gene. This cooperative effect was hepatic-specific and also occurred in CYP3A5 and CYP3A7 genes. To investigate the mechanism for HNF-3 gamma action, we studied its binding to CYP3A4 promoter and the effect of the deacetylase inhibitor trichostatin A. HNF-3 gamma was able to bind CYP3A4 promoter at a distal position, near the most distal C/EBP alpha binding site. Trichostatin A increased C/EBP alpha effect but abolished HNF-3 gamma cooperative action. These findings revealed that C/EBP alpha and HNF-3 gamma cooperatively regulate CYP3A4 expression in hepatic cells by a mechanism that probably involves chromatin remodeling.
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In order to use the zebrafish as a model vertebrate to investigate the developmental toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), it is essential to know whether one or both forms of the zebrafish aryl hydrocarbon receptor (AHR), zfAHR1 or zfAHR2, mediate toxicity. To determine the role of zfAHR2, an antisense morpholino approach was used to knock down translation of the protein. No effect of the zfahr2 morpholino (zfahr2-MO) was seen on normal development in embryos not treated with TCDD. Injection of embryos at the 1-2 cell stage with zfahr2-MO decreased TCDD-induced transcription of zfCYP1A mRNA until 96 h post fertilization (hpf), and immuno-histochemical detection of zfCYP1A protein in embryos at 72 hpf revealed a dramatic decrease in expression. The zfahr2-MO completely protected embryos from TCDD-induced edema and anemia and provided protection against TCDD-induced reductions in peripheral blood flow initially; however, a slight reduction in blood flow was observed at later times when the morpholino was no longer effective. Due to persistence of TCDD and decreasing effectiveness of the zfahr2-MO over time, the morpholino provided only transient protection against TCDD-induced inhibition of chondrogenesis of the lower jaw, and no protection against an effect of TCDD that was initiated late in development, blockade of swimbladder inflation. The zfahr2-MO did not protect embryos from TCDD-induced mortality but did produce a 48 h delay in its onset. Endpoints of TCDD developmental toxicity manifested in zfahr2 morphants at late stages of development, beyond 144 hpf, were clearly different from TCDD-exposed embryos injected with a control morpholino. Most strikingly, zfahr2 morphants exposed to TCDD never developed edema. Taken together, these results demonstrate that zfAHR2 mediates several endpoints of TCDD developmental toxicity in zebrafish.
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Aryl hydrocarbon receptor (AHR) is a transcription factor whose activity is regulated by environmental agents, including several carcinogenic agonists. We measured recruitment of AHR and associated proteins to the human cytochrome P4501A1 gene promoter in vivo. Upon treatment with the agonist β-naphthoflavone, AHR is rapidly associated with the promoter and recruits the three members of the p160 family of coactivators as well as the p300 histone acetyltransferase, leading to recruitment of RNA polymerase II (Pol II) and induction of gene transcription. AHR, coactivators, and Pol II cycle on and off the promoter, with a period of ∼60 min. In contrast, the chemopreventative AHR ligand 3,3′-diindolylmethane promotes AHR nuclear translocation and p160 coactivator recruitment but, remarkably, fails to recruit Pol II or cause histone acetylation. This novel mechanism of receptor antagonism may account for the antitumor properties of chemopreventative compounds targeting the AHR.
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Enzymes in the cytochrome P450 gene family 1 (CYP1) catalyze the metabolic activation of numerous hydrocarbon carcinogens and various natural compounds. CYP1 family members have been identified in several vertebrates, including fish, amphibians, birds, and mammals, and are inducible by aromatic hydrocarbons acting through the aryl hydrocarbon receptor (AHR). Together with its heterodimeric partner ARNT, the ligand-bound AHR binds conserved xenobiotic response elements (XREs) near the promoter of CYP1A and other genes. However, some populations of the Atlantic killifish Fundulus heteroclitus inhabiting highly contaminated sites are refractory to CYP1A induction by aromatic hydrocarbons. To better understand the mechanisms underlying this phenomenon, we are characterizing the AHR-CYP1A signaling pathway in this species. We report here the characterization of a genomic clone containing the 5(') end of the wild-type F. heteroclitus CYP1A gene. The 5(') coding sequence matches that of the F. heteroclitus CYP1A cDNA reported earlier [Comp. Biochem. Physiol. 121C (1998) 231]. Consistent with its inducibility by AHR agonists, the CYP1A gene contains three consensus XREs (5(')CACGC3(')) within 1.6 kb of the putative transcriptional start site. When oligonucleotides containing each of these sites were analyzed in an electrophoretic mobility shift assay, one of these showed a strong, TCDD-inducible mobility shift in the presence of in vitro expressed mouse AHR protein. These sequence data and initial functional characterization provide a valuable tool for the study of genetic variations in CYP1A expression and activity in sensitive and resistant populations. These studies may ultimately shed light on the importance of P4501A activity in xenobiotic toxicity.
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Comparative approaches were used to identify human, mouse and rat dioxin response elements (DREs) in genomic sequences unambiguously assigned to a nucleotide RefSeq accession number. A total of 13 bona fide DREs, all including the substitution intolerant core sequence (GCGTG) and adjacent variable sequences, were used to establish a position weight matrix and a matrix similarity (MS) score threshold to rank identified DREs. DREs with MS scores above the threshold were disproportionately distributed in close proximity to the transcription start site in all three species. Gene expression assays in hepatic mouse tissue confirmed the responsiveness of 192 genes possessing a putative DRE. Previously identified functional DREs in well-characterized AhR-regulated genes including Cyp1a1 and Cyp1b1 were corroborated. Putative DREs were identified in 48 out of 2437 human–mouse–rat orthologous genes between −1500 and the transcriptional start site, of which 19 of these genes possessed positionally conserved DREs as determined by multiple sequence alignment. Seven of these nineteen genes exhibited 2,3,7,8-tetrachlorodibenzo-p-dioxin-mediated regulation, although there were significant discrepancies between in vivo and in vitro results. Interestingly, of the mouse–rat orthologous genes with a DRE between −1500 and +1500, only 37% had an equivalent human ortholog. These results suggest that AhR-mediated gene expression may not be well conserved across species, which could have significant implications in human risk assessment.
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Studies using transient expression systems have implicated the XAP2 protein in the control of aryl hydrocarbon receptor (AHR) stability and subcellular location. Thus, studies were performed in cell lines that expressed endogenous rat or mouse Ahb-1 (C57BL/6) or Ahb-2 (C3H) AHRs with similar levels of endogenous XAP2. Unliganded rat and mouse Ahb-2 receptor complexes associated with reduced levels of XAP2 and exhibited dynamic nucleocytoplasmic shuttling in comparison with Ahb-1 receptors. Rat and mouse Ahb-2 receptors also exhibited a greater magnitude of ligand-induced degradation than Ahb-1 receptors. Small interfering RNA reduction of endogenous XAP2 by >80% had minimal impact on the level of Ahb-2 receptors but resulted in a 25–30% reduction of Ahb-1 receptors. XAP2 reduction resulted in increased susceptibility of the Ahb-1 receptor to ligand-induced degradation yet produced higher levels of endogenous CYP1A1 induction. Stable expression of the Ahb-2 receptor in the C57BL/6 background resulted in a protein with reduced association with XAP2, dynamic nucleocytoplasmic shuttling, and increased levels of ligand-induced degradation. Small interfering RNA reduction of endogenous XAP2 in a C-terminal hsp70-interacting protein knockout mouse cell line, exhibited a 25–30% reduction in the level of endogenous Ahb-1 AHR and showed high levels of ligand-induced degradation. Thus, endogenous XAP2 exerts a negative function on a small fraction of the endogenous Ahb-1 receptor complex but appears to have a minimal impact on endogenous rat or Ahb-2 receptors. This implies that the analysis of the AHR-mediated signaling via rat and mouse Ahb-2 receptors may better represent the physiology of this signal transduction pathway.
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To use the zebrafish (Danio rerio) as a model to study 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) developmental toxicity, it is essential to know which proteins are involved in mediating toxicity. Previous work has identified zfAHR2 as the receptor that binds TCDD mediating downstream responses. Although zfARNT2b can form a functional heterodimer with zfAHR2 in vitro, zfarnt2 null mutants show no protection against endpoints of TCDD developmental toxicity, demonstrating that zfARNT2b cannot be the physiological dimerization partner for zfAHR2 mediating responses to TCDD in zebrafish embryos. The purpose of the current study was to identify an alternate dimerization partner(s) for zfAHR2 that may function to mediate TCDD developmental toxicity. By searching zebrafish genomic sequence and using the polymerase chain reaction-based rapid amplification of cDNA ends technique, three forms of cDNA that seem to be alternate mRNA splice variants of a zebrafish homolog of ARNT1 were detected. Analysis of the zfARNT1 proteins in vitro demonstrates that the two longest forms of zfARNT1, zfARNT1b and zfARNT1c, can form functional heterodimers with zfAHR2. However, the shortest form, zfARNT1a, seems to be nonfunctional with zfAHR2 in vitro. To determine whether a zfARNT1 protein functions with zfAHR2 in vivo, a morpholino targeted against the 5' end of zfARNT1 (zfarnt1-MO) was used. Injection of the zfarnt1-MO before TCDD treatment significantly decreases the induction of zfCYP1A mRNA and protein. In addition, zfarnt1 morphants show complete protection against TCDD-induced pericardial edema and show partial protection against reduced blood flow and craniofacial malformations caused by TCDD, demonstrating the role of zfARNT1 proteins in mediating these responses.
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CYP1A1 and CYP1B1 metabolically activate many polycyclic aromatic hydrocarbons (PAHs), including benzo[a]pyrene, to reactive intermediates associated with toxicity, mutagenesis, and carcinogenesis. Paradoxically, however, Cyp1a1-/- knockout mice are more sensitive to oral benzo[a]pyrene exposure, compared with wild-type Cyp1a1+/+ mice (Mol Pharmacol 65:1225, 2004). To further investigate the mechanism for this enhanced sensitivity, Cyp1a1-/-, Cyp1a2-/-, and Cyp1b1-/- single-knockout, Cyp1a1/1b1-/- and Cyp1a2/1b1-/- double-knockout, and Cyp1+/+ wild-type mice were analyzed. After administration of oral benzo[a]pyrene (125 mg/kg/day) for 18 days, Cyp1a1-/- mice showed marked wasting, immunosuppression, and bone marrow hypocellularity, whereas the other five genotypes did not. After 5 days of feeding, steady-state blood levels of benzo[a]pyrene were approximately 25 and approximately 75 times higher in Cyp1a1-/- and Cyp1a1/1b1-/- mice, respectively, than in wild-type mice. Benzo[a]pyrene-DNA adduct levels were highest in liver, spleen, and marrow of Cyp1a1-/- and Cyp1a1/1b1-/- mice. Many lines of convergent data obtained with oral benzo[a]pyrene dosing suggest that: 1) inducible CYP1A1, probably in both intestine and liver, is most important in detoxication; 2) CYP1B1 in spleen and marrow is responsible for metabolic activation of benzo[a]pyrene, which results in immune damage in the absence of CYP1A1; 3) both thymus atrophy and hepatocyte hypertrophy are independent of CYP1B1 metabolism but rather may reflect long-term activation of the aryl hydrocarbon receptor; and 4) the magnitude of immune damage in Cyp1a1-/- and Cyp1a1/1b1-/- mice is independent of plasma benzo[a]pyrene and total-body burden and clearance. Thus, a balance between tissue-specific expression of the CYP1A1 and CYP1B1 enzymes governs sensitivity of benzo[a]pyrene toxicity and, possibly, carcinogenicity.
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Dioxin (2,3,7,8-tetrachlorodibenzo-p-dioxin) induces cleft palate and hydronephrosis in mice, when exposed in utero; these effects are mediated by the aryl hydrocarbon receptor. The Cyp1a1, Cyp1a2, and Cyp1b1 genes are up-regulated by the aryl hydrocarbon receptor. To elucidate their roles in dioxin-induced teratogenesis, we compared Cyp1a1(-/-), Cyp1a2(-/-), and Cyp1b1(-/-) knock-out mice with Cyp1(+/+) wild-type mice. Dioxin was administered (25 μg/kg, gavage) on gestational day 10, and embryos were examined on gestational day 18. The incidence of cleft palate and hydronephrosis was not significantly different in fetuses from Cyp1a1(-/-), Cyp1b1(-/-), and Cyp1(+/+) wild-type mice. To fetuses carried by Cyp1a2(-/-) dams, however, this dose of dioxin was lethal; this effect was absolutely dependent on the maternal Cyp1a2 genotype and independent of the embryonic Cyp1a2 genotype. Dioxin levels were highest in adipose tissue, mammary gland, and circulating blood of Cyp1a2(-/-) mothers, compared with that in the Cyp1(+/+) mothers, who showed highest dioxin levels in liver. More dioxin reached the embryos from Cyp1a2(-/-) dams, compared with that from Cyp1(+/+) dams. Fetuses from Cyp1a2(-/-) dams exhibited a ∼6-fold increased sensitivity to cleft palate, hydronephrosis, and lethality. Using the humanized hCYP1A1_1A2 transgenic mouse (expressing the human CYP1A1 and CYP1A2 genes in the absence of mouse Cyp1a2 gene), the teratogenic effects of dioxin reverted to the wild-type phenotype. These data indicate that maternal mouse hepatic CYP1A2, by sequestering dioxin and thus altering the pharmacokinetics, protects the embryos from toxicity and birth defects; substitution of the human CYP1A2 trans-gene provides the same protection. In contrast, neither CYP1A1 nor CYP1B1 appears to play a role in dioxin-mediated teratogenesis.
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The basic-helix-loop-helix/PAS (bHLH/PAS) family of proteins is a group of transcription factors that regulate key pathways during normal development and in the response to stress. The aryl hydrocarbon receptor (AHR) is a member of this family. Recently, Danio rerio (zebrafish) has become an important model system in the study of the signal transduction pathway and complements the results seen in mammalian models. However, studies of the AHR protein have been limited by the lack of antibody reagents and thus, little is known concerning the localization and degradation of the zebrafish AHR (zfAHR). In this report, we describe the production and characterization of specific polyclonal antibodies to the zfAHR2 protein and the analysis of AHR-mediated signal transduction in the zebrafish liver cell line (ZFL). The results show that the zfAHR2 is degraded via the 26S proteasome following exposure of cells to beta-naphthoflavone (BNF). Interestingly, the time course is slower and the magnitude of zfAHR2 degradation is not as great as seen for the mammalian AHR. Studies also show that the zfAHR2 is rapidly degraded in a ligand-independent manner by exposure of cells to geldanamycin (GA) to levels consistent with mammalian AHR. Finally, immunohistochemical staining of the ZFL cells suggest that the unliganded AHR resides in both the cytoplasm and nucleus and undergoes active nucleocytoplasmic shuttling in the absence of ligand. These results suggest that there is conservation of function between fish and mammals with respect to ligand-dependent and -independent degradation of the AHR and that the zfAHR2 is degraded via the 26S proteasome.
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2,3,7,8-Tetrachlorodibenzo-p- dioxin (TCDD, or dioxin) causes early life stage mortality in a variety of fish species. We have used the zebrafish (Danio rerio) to study the cardiovascular effects of TCDD treatment over the time course of zebrafish development. Early TCDD exposure (6 ng/ml) starting at 4 hr postfertilization (hpf) produced reductions in blood flow and in the number of circulating erythrocytes. These defects were consistently observable by 72 hpf. However, these responses were not observed when TCDD exposure was delayed until 96 hpf or later. These results suggest a model in which TCDD interferes with cardiovascular and erythropoietic developmental processes that are normally completed by 96 hpf. This model is strengthened by the finding that TCDD exposure blocks the step in hematopoiesis in which developing zebrafish switch from the primitive phase to the definitive phase of erythropoiesis. We observed no effect of TCDD on the levels of circulating primitive erythrocytes before 72 hpf and the expression of markers for early hematopoiesis, GATA-1 and GATA-2. However, early TCDD exposure prevented the appearance of definitive phase erythrocytes. TCDD produced a small delay in the migration of blood cells expressing SCL from the intermediate cell mass to the dorsal mesentery and dorsal aorta. Despite the decrease in blood flow produced by TCDD, confocal microscopy of the trunk vasculature by using a Tie2/green fluorescence protein endothelial marker at 48, 60, 72, and 96 hpf of TCDD-exposed (4 hpf) revealed no apparent defects in blood vessel structure. © 2001 Wiley-Liss, Inc.
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Transcriptional up-regulation of mammalian CYP1A1 genes by dioxin is known to require binding of dioxin to the Ah receptor (AHR), subsequent interaction of this ligand-receptor complex with the AHR nuclear translocator (ARNT), and binding of this heterodimer to aromatic hydrocarbon response elements (AHREs) located in the 5′ flanking sequences. From the rainbow trout (Oncorhyncus mykiss), we have isolated and sequenced the CYP1A3 gene—spanning 4.0 kb and containing seven exons and six introns—and 1897 bp of the 5′ flanking region. The transcription start site was determined by primer extension analysis. Five putative AHREs were found between −451 and −1820, with an overlap of AHRE3 and AHRE4 sharing 1 bp. The 5′ flanking region of the trout CYP1A3 gene was fused to the firefly luciferase (luc) reporter gene and transiently transfected into mouse hepatoma Hepa-1c1c7 wild-type (wt) cell cultures and three benzo[a]pyrene-resistant mutant lines: c2, containing less than 10% levels of functional AHR; c4, defective in ARNT; and c37, deficient in CYP1A1 metabolism. We compared the trout CYP1A3 promoter-luc constructs with mouse and human CYP1A1 promoter-luc constructs. All of our trout CYP1A3 promoter data are consistent with dioxin-inducible luciferase activity being controlled by two or more AHREs via cooperativity with a GC-rich region (−1852)—as has previously been demonstrated for AHREs in mammalian CYP1A1 promoters. The dependence of trout CYP1A3 promoter activity on the AHR and on the ARNT, and the enhancement of CYP1A3 promoter activity in the absence of CYP1A1 metabolic capacity, are all similar to that with mammalian CYP1A promoters. These findings indicate that the DNA motifs in trout, and the mouse liver proteins that bind to these motifs, are evolutionarily conserved elements.
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The nucleotide sequence of the 5'-upstream region up to about -4.1 kb of the human P-450c gene was determined. Two kinds of repetitive sequences were located; one was the Alu sequence which was inserted at three positions (-3127 to -3038, -3017 to -2770, and -2167 to -1851), and the other was the SINE-R element located just upstream of the most distal Alu sequences. The region other than the two repeated sequences showed an overall similarity of 70% to that of the rat P-450c gene. Survey of XRE or its homologues, responsible for the inducible expression of the rat P-450c gene, revealed eight XRE core sequences in this region of the human P-450c gene. Three of them were carried in the Alu sequences. A fusion gene which was constructed by ligating the upstream region of the human P-450c gene to the chloramphenicol acetyltransferase (CAT) gene expressed the CAT activity in response to the inducer, methylcholanthrene, when transfected into Hepa-1 cells. Stepwise decrease in CAT activity in three regions was observed as the 5'-upstream sequence containing XRE motifs was removed. However, the XRE core sequence in the Alu sequences seemed inactive, because elimination of the three elements in the Alu sequences did not affect the expressed CAT activity. In accordance with this observation, competition experiments using gel mobility shift assay showed that XRE core sequences in the Alu sequences could not compete with the XRE sequence for the inducer-bound receptor.(ABSTRACT TRUNCATED AT 250 WORDS)
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In mouse hepatoma cells, the environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) increases the transcription rate of the CYP1A1 gene, which encodes a cytochrome P-450 enzyme. In this study, we analyzed the DNA region immediately upstream of the CYP1A1 gene. A domain that extends upstream to nucleotide--166 was found to function as a transcriptional promoter. The promoter was silent when uncoupled from the dioxin-responsive enhancer located farther upstream. DNase footprinting experiments indicated that nuclear proteins interact with distinct domains of the promoter in a TCDD-independent fashion. Mutational analyses indicated that the CYP1A1 promoter contains at least three functional domains, including a TATAAA sequence, a CCAAT box transcription factor/nuclear factor I-like recognition motif, and a guanine-rich G box.
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We analyzed the function and sequence of a dioxin-responsive genomic element flanking the 5' end of the cytochrome P1-450 gene in high-activity variant mouse hepatoma cells. The element can regulate the mouse mammary tumor virus promoter. The element retains responsiveness to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) when the distance, the 5' or 3' position, and/or the 5' or 3' orientation with respect to the promoter are varied. The function of the element requires TCDD-receptor complexes. The element remains responsive to TCDD when transfected into cells from either a heterologous mouse tissue or a heterologous species (human). The DNA element and TCDD receptors together constitute a dioxin-responsive enhancer system.
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In this review, we have examined the biochemical and toxic responses produced by halogenated aromatic hydrocarbons and have tried to develop a model for their mechanism of action. These compounds bind to a cellular receptor and evoke a sustained pleiotropic response. In many tissues this response consists of the expression of a battery of enzymes which are, for the most part, involved in drug metabolism, but in other tissues, those which develop toxicity, an additional set of genes is expressed which effects cellular involution, division, and/or differentiation. The toxicity of these compounds appears to be due to the sustained expression of a normal cellular regulatory system, of which we were previously unaware. In future investigations it is hoped that we will learn the nature and physiologic role of this regulatory system. Only then can we hope to understand the mechanism of toxicity of these compounds.
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Hepatocyte nuclear factor 3 (HNF3) recognizes two apparently distinct classes of sequence. However, a detailed mutational analysis of a representative binding site of each class reveals that these sequences display common features. We propose a unified consensus sequence for HNF3-binding sites. The basis of the sequence specificity of the interaction of HNF3 with DNA is analyzed in light of the recently determined structure of an HNF3-DNA complex (Clark et al., Nature 364, 412-420, 1993). Particularly, our study reveals that the DNA site used for this structural analysis is too short to account for all HNF3-DNA interactions. The better knowledge of the sequence determinant recognized by HNF3 has allowed us to analyze its function in the glucocorticoid response of the rat tyrosine aminotransferase (TAT) gene. This response is mediated through a complex array of neighboring and overlapping transcription factor binding sites. Selective inactivation of the HNF3-binding sites in this glucocorticoid response unit (GRU) allows us to demonstrate unambiguously that they play a major role in the amplitude of the glucocorticoid response. Furthermore, HNF3 beta overexpression results in a stimulation of the glucocorticoid response that is dependent on the integrity of its binding sites. We also show that the relative level of HNF3 determines the extent of the contribution of one of the glucocorticoid receptor binding sites. Our results indicate that HNF3 accounts for most of the liver-specific activity of this GRU.
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In mouse hepatoma cells, the environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, or dioxin) induces Cyp1A1 gene transcription, a process that requires two basic helix-loop-helix regulatory proteins, the aromatic hydrocarbon receptor (AhR) and the aromatic hydrocarbon receptor nuclear translocator (Arnt). We have used a ligation-mediated PCR technique to analyze dioxin-induced changes in protein-DNA interactions and chromatin structure of the Cyp1A1 enhancer-promoter in its native chromosomal setting. Dioxin-induced binding of the AhR/Arnt heteromer to enhancer chromatin is associated with a localized (about 200 bp) alteration in chromatin structure that is manifested by increased accessibility of the DNA; these changes probably reflect direct disruption of a nucleosome by AhR/Arnt. Dioxin induces analogous AhR/Arnt-dependent changes in chromatin structure and accessibility at the Cyp1A1 promoter. However, the changes at the promoter must occur by a different, more indirect mechanism, because they are induced from a distance and do not reflect a local effect of AhR/Arnt binding. Dose-response experiments indicate that the changes in chromatin structure at the enhancer and promoter are graded and mirror the graded induction of Cyp1A1 transcription by dioxin. We discuss these results in terms of a TCDD-induced shift in an equilibrium between nucleosomal and nonnucleosomal chromatin configurations.
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The expression and induction of cytochrome P450 by 2,3,7,8-tetrachlordibenzo-p-dioxin (TCDD) and beta-naphthoflavone (BNF) in a new liver cell line from adult zebrafish (Brachydanio rerio) were studied. Subcellular fractions from control, BNF- or TCDD-treated cells did not show detectable bands in immunoblots probed with antibodies to the constitutive forms of trout P450 (LMC1, LMC2, LMC3, LMC4, and LMC5), suggesting that either zebrafish liver cells lack P450s closely related to those constitutively expressed in trout or that the concentrations of the orthologous P450s were too low to be detected. However, upon exposure to TCDD, the cells expressed a major immunoreactive 54-kDa protein and a minor 50-kDa protein recognized by antibodies to rainbow trout P4501A1. These immunoreactive proteins were observed in microsomal and mitochondrial fractions of TCDD-treated cells but were not detected in cell cultures treated with dimethyl sulfoxide (DMSO) (vehicle control) or BNF. The activities of ethoxyresorufin O-deethylase (EROD) and 7,12-dimethylbenzanthracene (DMBA) hydroxylase were markedly increased by TCDD but not by BNF in this cell line. EROD activity was more sensitive than DMBA hydroxylase activity of TCDD-treated liver cells to diagnostic inhibitors such as alpha-naphthoflavone and anti-trout P4501A1 IgG. The TCDD-treated cells converted DMBA to various metabolites, one of which is the putative proximate carcinogen, DMBA-3,4-diol. These results suggest that TCDD, but not BNF, induces one or possibly two forms of P450 immunochemically and functionally related to trout P4501A1, in cultured zebrafish liver cells.
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Nucleosome positioning at genetic regulatory sequences is not well understood. The transcriptional enhancer of the mouse serum albumin gene is active in liver, where regulatory factors occupy their target sites on three nucleosome-like particles designated N1, N2, and N3. The winged helix transcription factor HNF3 binds to two sites near the center of the N1 particle. We created dinucleosome templates using the albumin enhancer sequence and found that site-specific binding of HNF3 protein resulted in nucleosome positioning in vitro similar to that seen in liver nuclei. Thus, binding of a transcription factor can position an underlying nucleosome core.
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A single far-upstream enhancer is sufficient to confer hepatocyte-specific, glucocorticoid- and cyclic AMP-inducible periportal expression to the carbamoylphosphate synthetase I (CPS) gene. To identify the mechanism of hormone-dependent activation, the composition and function of the enhancer have been analyzed. DNase I protection and gel mobility shift assays revealed the presence of a cyclic AMP response element, a glucocorticoid response element (GRE), and several sites for the liver-enriched transcription factor families HNF3 and C/EBP. The in vivo relevance of the transcription factors interacting with the enhancer in the regulation of CPS expression in the liver was assessed by the analysis of knockout mice. A strong reduction of CPS mRNA levels was observed in glucocorticoid receptor- and C/EBPalpha-deficient mice, whereas the CPS mRNA was normally expressed in C/EBPbeta knockout mice and in HNF3alpha and -gamma double-knockout mice. (The role of HNFbeta could not be assessed, because the corresponding knockout mice die at embryonic day 10). In hepatoma cells, most of the activity of the enhancer is contained within a 103-bp fragment, which depends for its activity on the simultaneous occupation of the GRE, HNF3, and C/EBP sites, thus meeting the requirement of a glucocorticoid response unit. In fibroblast-like CHO cells, on the other hand, the GRE in the CPS enhancer does not cooperate with the C/EBP and HNF3 elements in transactivation of the CPS promoter. In both hepatoma and CHO cells, stimulation of expression by cyclic AMP depends mainly on the integrity of the glucocorticoid pathway, demonstrating cross talk between this pathway and the cyclic AMP (protein kinase A) pathway.
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Cytochrome P4501A1 is a substrate-inducible microsomal enzyme that oxygenates polycyclic aromatic hydrocarbons, such as the carcinogen benzo(a)pyrene, as the initial step in their metabolic processing to water-soluble derivatives. Enzyme induction reflects increased transcription of the cognate CYP1A1 gene. The environmental toxicant 2,3,7,8-tetrachlorodibenzo-p-dioxin is the most potent known cytochrome P4501A1 inducer. Two regulatory proteins, the aromatic (aryl) hydrocarbon receptor (AhR) and the AhR nuclear translocator (Arnt), mediate induction. AhR and Arnt are prototypical members of the basic helix-loop-helix/Per-Arnt-Sim class of transcription factors. Mechanistic analyses of cytochrome P4501A1 induction provide insights into ligand-dependent mammalian gene expression, basic helix-loop-helix/Per-Arnt-Sim protein function, and dioxin action; such studies also impact public health issues concerned with molecular epidemiology, carcinogenesis, and risk assessment.
Article
: Transcriptional up-regulation of mammalian CYP1A1 genes by dioxin is known to require binding of dioxin to the Ah receptor (AHR), subsequent interaction of this ligand-receptor complex with the AHR nuclear translocator (ARNT), and binding of this heterodimer to aromatic hydrocarbon response elements (AHREs) located in the 5' flanking sequences. From the rainbow trout (Oncorhyncus mykiss), we have isolated and sequenced the CYP1A3 gene-spanning 4.0 kb and containing seven exons and six introns-and 1897 bp of the 5' flanking region. The transcription start site was determined by primer extension analysis. Five putative AHREs were found between -451 and -1820, with an overlap of AHRE3 and AHRE4 sharing 1 bp. The 5' flanking region of the trout CYP1A3 gene was fused to the firefly luciferase (luc) reporter gene and transiently transfected into mouse hepatoma Hepa-1c1c7 wild-type (wt) cell cultures and three benzo[a]pyrene-resistant mutant lines: c2, containing less than 10% levels of functional AHR; c4, defective in ARNT; and c37, deficient in CYP1A1 metabolism. We compared the trout CYP1A3 promoter-luc constructs with mouse and human CYP1A1 promoter-luc constructs. All of our trout CYP1A3 promoter data are consistent with dioxin-inducible luciferase activity being controlled by two or more AHREs via cooperativity with a GC-rich region (-1852)-as has previously been demonstrated for AHREs in mammalian CYP1A1 promoters. The dependence of trout CYP1A3 promoter activity on the AHR and on the ARNT, and the enhancement of CYP1A3 promoter activity in the absence of CYP1A1 metabolic capacity, are all similar to that with mammalian CYP1A promoters. These findings indicate that the DNA motifs in trout, and the mouse liver proteins that bind to these motifs, are evolutionarily conserved elements.
Article
Many classes of environmental pollutants are found at significant levels in the aquatic environment. We are designing a fish model as an inexpensive and efficient system for the assessment of aquatic pollution. Three classes of environmental pollutants-halogenated and nonhalogenated aromatic hydrocarbons, heavy metals, and potent electrophiles-are known to upregulate particular mammalian genes via the activation of specific DNA motifs called aromatic hydrocarbon (AHREs), heavy metal (MREs), and electrophile (EPREs) response elements, respectively. We have made plasmid constructs, using these mammalian or trout response elements to drive the luciferase reporter gene. Here we show that transient transfection of the zebrafish ZEM2S cell line with these reporter constructs imparts dose-dependent gene induction upon exposure to a variety of chemicals within each of these three classes of inducers: [a] (AHRE-mediated) 2,3,7,8-tetrachlorodibenzo-p-dioxin, 3-methylcholanthrene, 3,4,5,3',4',5'-hexabromobiphenyl, Aroclor 1254, and benzo[a]pyrene; [b] (MRE-mediated) Cd(2+), Zn(2+), Hg(2+), and Al(3+); and [c] (EPRE-mediated) tert-butylhydroquinone, Hg(2+), Pb(2+), As(3+), Cu(2+), and Cd(2+). As expected, some agents gave a response to only one of the three classes, whereas others gave a mixed (AHRE- plus EPRE-mediated or MRE- plus EPRE-mediated) response. In response to several environmental agents, we found that differences in the electrophoretic mobility shift assay, using the AHRE or MRE as probe, were consistent with the degree of transcriptional activation seen with the reporter constructs. Our data suggest that these reporter constructs might be valuable for the generation of transgenic zebrafish in order to carry out mechanistic and developmental studies of transcriptional activation by environmental contaminants; moreover, such transgenic zebrafish lines might be useful as a sentinel for assessing aquatic pollution.
Article
The aryl hydrocarbon receptor nuclear translocator (ARNT) protein is involved in many signaling pathways. Rainbow trout express isoforms of ARNT protein that are divergent in their C-terminal domains due to alternative RNA splicing. Rainbow trout ARNT(b) (rtARNT(b)) contains a C-terminal domain rich in glutamine and asparagine (QN), whereas the C-terminal domain of rtARNT(a) is rich in proline, serine, and threonine (PST). rtARNT(b) functions positively in AH receptor-mediated signaling, whereas rtARNT(a) functions negatively. Studies were performed to understand how changes in the C-terminal domains of the two rtARNT isoforms affect function. Deletion of the QN-rich C-terminal domain of rtARNT(b) did not affect function in aryl hydrocarbon receptor (AHR)-mediated signaling, whereas deletion of the PST-rich domain of rtARNT(a) restored function. Expression of the PST-rich domain on truncated rtARNT(b) or mouse ARNT (mARNT) reduced function of this protein by 50-80%. Gel shift assays revealed that the PST-rich domain affected AHR-mediated signaling by inhibiting DNA binding of the AHR*ARNT heterodimer. Gal4 transactivation assays revealed a potent transactivation domain in the QN-rich domain of rtARNT(b). In contrast, Gal4 proteins containing the PST-rich domain of rtARNT(a) did not transactivate because the proteins did not bind to DNA. Secondary structure analysis of the PST-rich domain revealed hydrophilic and hydrophobic regions. Truncation of the hydrophobic domain that spanned the final 20-40 amino acids of the rtARNT(a) restored function to the protein, suggesting that repressor function was related to protein misfolding or masking of the basic DNA binding domain. Functional diversity within the C-terminal domain is consistent with other negatively acting transcription factors and illustrates a common biological theme.
Article
Rainbow trout aryl hydrocarbon receptor (AHR) nuclear translocator isoform a (rtARNTa) has a negative function in AHR-mediated signal transduction. Previous analyses suggest that the negative function is at the level of DNA binding and may be due to the presence of 57 C-terminal amino acids that are strongly hydrophobic. To assess the negative activity of rtARNTa at the molecular level, hydrophobic-rich domains corresponding to amino acids 601-637, 601-631, and 616-631 were analyzed for the ability to affect the function of truncated rtARNT proteins in complementation and gel shift assays. Addition of the hydrophobic-rich domains to these proteins reduced their ability to complement AHR-mediated signal transduction in mouse hepatoma cells by 65-95%. The decrease in function was related to a reduced ability of the AHR. rtARNT complex to bind DNA and not due to a lack of dimerization with AHR. Expression of the hydrophobic-rich domains on Gal4 proteins showed that the C-terminal domain of rtARNTa was unlikely to contain transactivation function; however, the hydrophobic domains reduced the ability of the Gal4 proteins to bind DNA. Immunoprecipitation and mutational experiments indicate that the hydrophobic-rich domains do not interact with the bHLH motif of AHR. Interestingly, immunoprecipitation experiments also revealed that the C-terminal hydrophobic-rich region of rtARNTa could oligomerize in vitro in a chimera with the Gal4 DNA binding domain. These findings indicate that the C-terminal hydrophobic amino acids are critical for the negative function of rtARNTa in AHR-mediated signaling and suggest that multiple mechanisms may be involved in the repression of DNA binding.
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Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on local circulation and apoptosis in the midbrain were investigated in zebrafish (Danio rerio) embryos during early development. Embryos were exposed to TCDD from 24 h post fertilization (hpf) until observation, in water maintained at 28.5 degrees C. TCDD decreased blood flow in the mesencephalic vein, the only vessel perfusing the dorsal midbrain of the embryo. At 50 hpf, blood flow was maximally reduced in this vessel and gradually returned to the control level at 60 hpf. In contrast, blood flows in the trunk and in other vessels of the head of the embryo did not significantly change until 72 hpf. Furthermore, TCDD exposure caused apoptosis in the midbrain at 60 hpf, and the TCDD dose response relationship for this effect was similar to that for reduced blood flow in the mesencephalic vein at 50 hpf. The effects of TCDD on apoptosis in the midbrain, but not on blood flow, were abolished by Z-VAD-FMK, a general caspase inhibitor. TCDD effects on both endpoints were mimicked by beta-naphthoflavone (BNF), an aryl hydrocarbon receptor (AHR) agonist, and almost abolished by concomitant exposure to TCDD and alpha-naphthoflavone (ANF), an AHR antagonist. Concomitant exposure to TCDD and either an inhibitor of cytochrome P450 (CYP) (SKF525A or miconazole) or an antioxidant (N-acetylcysteine or ascorbic acid) inhibited these effects of TCDD. The incidence of apoptosis in the midbrain was inversely related to blood flow in this brain region following these various treatments and graded TCDD exposure concentrations (r = -0.91). The same range of TCDD exposure concentrations that reduced blood flow and increased apoptosis in the midbrain greatly enhanced CYP1A mRNA expression and immunoreactivity at 50 hpf in endothelial cells of blood vessels including the mesencephalic vein and the heart, but not the brain parenchyma. Taken together, these results suggest that TCDD induces apoptosis in the midbrain of the zebrafish embryo secondary to local circulation failure, which could be related to AHR activation, induction of CYP1A, and oxidative stress.
Article
The mechanism of toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is thought to result from changes in gene expression via the aryl hydrocarbon receptor (AHR). The induction of cytochrome P450 1A (CYP1A) in various organs is a cardinal effect of TCDD. However, whether CYP1A is involved in endpoints of TCDD toxicity is controversial. We investigated the role of CYP1A in TCDD-induced developmental toxicities using gene knock-down with morpholino antisense oligos. Exposure of zebrafish embryos to TCDD, at concentrations eliciting the hallmark endpoints of developmental toxicity, induced CYP1A in the heart and vascular endothelium throughout the body. This induction by TCDD was markedly inhibited by morpholinos to zebrafish arylhydrocarbon receptor 2 (zfAHR2-MO) and to zebrafish CYP1A (zfCYP1A-MO). The zfAHR2-MO but not the zfCYP1A-MO inhibited zfCYP1A mRNA expression, indicating the specificities of these morpholinos. Injection of either zfAHR2-MO or zfCYP1A-MO blocked the representative signs of TCDD developmental toxicity in zebrafish, pericardial edema and trunk circulation failure. The morpholinos appeared do not affect normal development in TCDD-untreated embryos. These results suggest a mediatory role of zfCYP1A induction through zfAHR2 activation in causing circulation failure by TCDD in zebrafish. This is the first molecular evidence demonstrating an essential requirement for CYP1A induction in TCDD-evoked developmental toxicities in any vertebrate species.
Article
Cytochrome P450 3A4 (CYP3A4) is the major cytochrome P450 present in adult human liver and is involved in the metabolism of over 50% of therapeutic compounds currently in use. Since expression levels of CYP3A4 are regulated by many of these compounds, this raises the potential for drug-drug interactions and subsequent altered efficacy or toxicity of the individual compounds at the dose prescribed. Hence, understanding the molecular mechanisms of CYP3A4 regulation is of key importance in predicting and understanding such interactions. To examine this we have used DNase I footprinting and bioinformatic analysis to identify putative transcription factor binding sites within the 250 base pairs of promoter proximal to the transcription start site. We identified several protected fragments within this region that corresponded to putative binding sites for Sp1, AP2, CCAAT/enhancer binding protein (C/EBPalpha), and hepatic nuclear factor-3 (HNF3), as well as confirming previously identified C/EBPalpha, pregnane X receptor (PXR), and HNF3 binding sites. Sequential site-directed mutagenesis of C/EBPalpha, Sp1, HNF3, and PXR binding sites was next used to examine the role of these sites in basal CYP3A4 expression. Disruption of the C/EBPalpha, HNF3, and PXR binding sites all affected basal expression. Finally, the role of these sites was examined in activation of CYP3A4 expression by rifampicin, metyrapone, clotrimazole, and phenobarbital. Disruption of any of these sites either led to an altered pattern of activation by the xenobiotic, as altered maximal activation, or altered the EC(50) value of activation. Such effects were xenobiotic-specific, with each disrupted site playing a role in the activation of some of the xenobiotics.
Article
The aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor that dimerizes with ARNT to mediate responses to compounds such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). TCDD and other AHR agonists cause toxic responses in early life stages of fish, including the zebrafish, Danio rerio. The most well characterized target gene for the AHR/aryl hydrocarbon receptor nuclear translocator (ARNT) dimer is a cytochrome P450, CYP1A. Induction of CYP1A by TCDD has been correlated with certain toxic responses in developing zebrafish and has been postulated to mediate these responses. To determine whether CYP1A is the important downstream effector enzyme for the AHR/ARNT pathway, we used morpholino oligonucleotides (MOs) to block induction of CYP1A in response to TCDD in zebrafish embryos. Although the zfcyp1a-MO effectively prevented CYP1A up-regulation, it did not prevent the signs of developmental toxicity, including pericardial edema, slowed blood flow, craniofacial malformation, and defects in erythropoiesis. We conclude that the important target for the AHR/ARNT pathway in developing zebrafish exposed to TCDD is not zfcyp1a. This suggests an alternative model in which TCDD-activated AHR/ARNT disrupts the normal process of growth and development by altering programs of gene expression or function.
Article
The aryl hydrocarbon receptor (AHR) mediates the carcinogenic and other toxic effects of a variety of environmental pollutants, including 2,37,8-tetrachlorodibenzo-p-dioxin (TCDD), and some polycyclic aromatic hydrocarbons (PAHs). In most if not all cases, these deleterious effects depend upon modulation of gene transcription effected by the ligand-bound AHR. The responsive genes required for toxicity of TCDD have yet to be defined. However, induction of Cyp1a1 is known to represent a significant event in the toxicity of PAHs. Furthermore, the Cyp1a1 gene provides a model system for studying the mechanism of gene transcription by AHR. This review discusses the roles of transcriptional coactivator proteins in induction of Cyp1a1 by AHR ligands. Coactivators physically associate with the gene upon induction, and provide a bridge between AHR molecules, located at 5'enhancer elements, and general transcription factors, located at the promoter of the gene. Studies on the endogenous Cyp1a1 gene in its natural chromosomal setting are emphasized. The recent development of several new experimental techniques including the chromatin immunoprecipitation (ChIP) assay, RNA interference, and real-time PCR has provided a major boost to such studies. Future directions for research are also discussed. Since variations in coactivator expression or activity may result in inter-individual differences in response to AHR ligands, and may also underlie tissue-specific differences in sensitivity to such ligands during development, and in adulthood, the role of coactivators in transcriptional activation by AHR constitutes a very important area of research.
Article
Zebrafish (Danio rerio) have advantages over mammals as an animal model for investigating developmental toxicity. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (dioxin, TCDD), a persistent global contaminant, is the most comprehensively studied developmental toxicant in zebrafish. The hallmark responses of TCDD developmental toxicity manifested in zebrafish larvae include edema, anemia, hemorrhage, and ischemia associated with arrested growth and development. Heart and vasculature development and function are severely impaired, and jaw malformations occur secondary to inhibited chondrogenesis. The swim bladder fails to inflate, and the switch from embryonic to adult erythropoiesis is blocked. This profile of developmental toxicity responses, commonly referred to as "blue sac syndrome" because the edematous yolk sac appears blue, is observed in the larval form of all freshwater fish species exposed to TCDD at the embryonic stage of development. Components of the aryl hydrocarbon receptor/aryl hydrocarbon receptor nuclear translocator (AHR/ARNT) signaling pathway in zebrafish have been identified and functionally characterized. Their role in mediating TCDD toxicity has been determined using morpholinos to specifically knockdown the translation of zfAHR1, zfAHR2, zfARNT1, and zfARNT2 mRNAs, respectively, and a line of zfARNT2 null mutant zebrafish has provided further insight. These studies have shown that zfAHR2 and zfARNT1 mediate TCDD developmental toxicity. In addition, the growing use of molecular and genomic tools for research on zebrafish have led to advances in our understanding of the mechanism of TCDD developmental toxicity at the molecular level, including the recent finding that toxicity is not mediated by increased cytochrome P4501A (zfCYP1A) expression.