- Open Access
The aryl hydrocarbon receptor-mediated disruption of vitellogenin synthesis in the fish liver: Cross-talk between AHR- and ERα-signalling pathways
© Bemanian et al; licensee BioMed Central Ltd. 2004
- Received: 05 September 2003
- Accepted: 02 May 2004
- Published: 02 May 2004
In the fish liver, the synthesis of egg yolk protein precursor vitellogenin (VTG) is under control of the estrogen receptor alpha (ERα). Environmental contaminants such as 2,3,7,8-tetrachloro-dibenzo-p-dioxin (TCDD) are suspected to have antiestrogenic effects. The aryl hydrocarbon receptor (AHR) is the initial cellular target for TCDD and related compounds. The AHR is a ligand-activated transcription factor that stimulates the expression of the genes encoding xenobiotic metabolizing enzymes, such as cytochrome P450 1A (CYP1A). In this study, the effects of activation of AHR on the hepatic expression of VTG and ERα genes, in primary cultured salmon hepatocytes, have been investigated.
The expression of the genes encoding VTG and ERα were strongly induced by 17β-estradiol (E2). However, the expression of VTG was disrupted by exposure of the cells to TCDD while CYP1A expression was enhanced. The effect of TCDD on VTG and CYP1A expression was annulled by the AHR-inhibitor α-naphthoflavone. Furthermore, exposure of the cells to TCDD abolished E2-induced accumulation of ERα mRNA. The AHR-mediated inhibitory effects on the expression of the VTG and ERα genes may occur at transcriptional and/or post-transcriptional levels. Nuclear run-off experiments revealed that simultaneous exposure of the cells to E2 and TCDD strongly inhibited the initiation of transcription of the VTG and ERα genes. In addition, inhibition of RNA synthesis by actinomycin D treatment showed that post-transcriptional levels of VTG and ERα mRNAs were not significantly altered upon treatment of the cells with TCDD. These results suggested that activation of AHR may inhibit the transactivation capacity of the ERα. Further, electrophoretic mobility shift assays using nuclear extracts prepared from cells treated for one or two hours with E2, alone or in mixture with TCDD, showed a strong reduction in the DNA binding activities upon TCDD treatment. These results also suggested that activation of the AHR signalling pathway caused a marked decrease in the number of the nuclear ERα or that activated AHR blocked the ability of ERα to bind to its target DNA sequence. Finally, our results from Northern hybridizations indicated that E2 treatment of the cells did not cause any significant effect on the TCDD-induced levels of CYP1A mRNA.
In fish hepatocytes E2 induces ERα and VTG gene expression. The presence of dioxin (TCDD) abolishes this induction, probably through the action of AHR in complex with AHR nuclear translocator, and possibly by direct interference with the auto-regulatory transcriptional loop of ERα. Furthermore, E2 does not interfere with TCDD induced CYP1A gene expression, suggesting that cross-talk between the ERα- and AHR-signalling pathways is unidirectional.
- Aryl Hydrocarbon Receptor
- Aryl Hydrocarbon Receptor Ligand
- Antiestrogenic Effect
- TCDD Treatment
- Aryl Hydrocarbon Receptor Antagonist
The liver is a central organ for sexual reproduction and development of the embryo in oviparous vertebrates. In teleost fish, much of the yolk is synthesized by liver cells in the form of a protein precursor: the vitellogenin (VTG). VTG is a large phosphoglycolipoprotein which is synthesized in the liver under hormonal control and secreted into the bloodstream [1, 2]. The VTG is incorporated into the developing oocyte by receptor-mediated endocytosis [3, 4] and processed into three smaller proteins: phosvitin, a phosphorus containing protein, and two lipid containing proteins, lipovitellins I and II [5–7]. These become the primary substances stored as yolk. In the female fish, the induction of VTG synthesis (vitellogenesis) is under control of the hepatic estrogen receptor α (ERα). The induction of vitellogenesis is triggered by environmental cues and is regulated by coordinated endocrine feedback loops between the hypothalamus, pituitary, gonad and liver (HPGL axis) . Briefly, environmental signals induce the hypothalamus to release gonadotropin releasing hormones which stimulate the release of gonadotropins from the pituitary. The gonadotropin hormones, in turn, stimulate the follicle cells to synthesize 17β-estradiol (E2). The estradiol is released into the blood and transported into the liver where it enters the hepatocytes by diffusion and binds with high affinity to the ERα. The activated ERα triggers the expression of its own gene and subsequently that of the VTG.
Polycyclic aromatic hydrocarbons (PAHs) and polyhalogenated aromatic hydrocarbons (PHAHs) are suspected to have deleterious effects on fish vitellogenesis . A number of these compounds including polychlorinated dibenzo-p-dioxins such as 2,3,7,8-tetrachlorodibenzo-para-dioxin (TCDD) exert their effects through the aryl hydrocarbon receptor (AHR). The AHR is a ligand-activated transcription factor that regulates the activation of several genes that encode phase I and phase II drug metabolism enzymes in the liver (reviewed in ref. ). The AHR belongs to the family of basic helix-loop-helix (bHLH)/Per-Arnt-Sim (PAS) proteins which are characterized by two conserved domains, the N-terminal bHLH and the PAS domain (reviewed in ref. ).
The cytochrome P4501A (CYP1A) is an enzyme involved in the metabolism of many drugs and xenobiotics which is regulated by the AHR. The molecular mechanism involved in the activation of the CYP1A have been extensively studied . Prior to binding of the ligand the cytosolic form of the AHR is associated with a chaperoning complex consisting of heat shock protein 90 (HSP90) and several other co-chaperones . Upon binding of the ligand, the AHR is released from the HSP90 complex and translocated into the nucleus where it dimerizes with a structurally related protein, the Ah Receptor Nuclear Translocator (ARNT). The AHR/ARNT complex binds with high affinity to specific DNA sequences termed dioxin response elements (DREs) located in the regulatory regions of the target genes leading to activation of their expression.
TCDD has been shown to inhibit several estrogen-induced responses in the rodent uterus, mammary gland and in the mammalian cell cultures (reviewed in [12, 13]). The cross-talk between the ERα and AHR signalling pathway has not been extensively studied in the fish. However, recent studies using fish primary cultures of hepatocytes showed that AHR-ligands have an inhibitory effect on the estrogen-induced synthesis of VTG [14, 15]. On the other hand, conflicting findings were observed in in vivo exposures of fish to xenoestrogens and Ah-receptor ligands .
The efforts of this study have been concentrated on the mechanism behind cross-talk between the AHR- and ERα-signalling pathways in the fish liver. Our results show that activation of the AHR pathway has contradictory effects on the molecular functions of the ERα in the liver cells. Activation of the AHR inhibits the ERα to initiate transcription of the VTG gene and blocks the auto-regulatory loop of the ERα gene expression. The cross-talk between the two receptors, however, appears to be unidirectional, i.e., activation of the ERα has no significant inhibitory effect on the AHR-mediated induction of the CYP1A.
Effects of TCDD, β-naphthoflavone, and α-naphthoflavone on E2-induced vitellogenin gene expression
Down-regulation of the estradiol-induced ERα gene expression by TCDD
Effects of TCDD on the transcription initiation and turnover rates of vitellogenin and estrogen receptor mRNAs
Effects of TCDD on the DNA binding activities of the nuclear extracts
Reciprocal inhibitory effects of TCDD and E2 on the induction of vitellogenin and cytochrome P4501A1 gene expression
In the present work, the effects of TCDD on the estrogen-regulated gene expression in fish liver cells have been investigated. The results showed that TCDD can oppose E2-induced expression of the VTG gene in a concentration-dependent manner and exhibit a pronounced anti-estrogenic effect at higher doses. The inhibitory effects of TCDD on the E2-induced ERα signalling pathway were comparable to the effects of tamoxifen. The latter is an antagonistic ligand of ERα by competing with E2 in binding to the receptor and convert the receptor into an inactivated form . Our results, however, indicate that the mechanism behind the anti-estrogenic action of TCDD is completely different from those of tamoxifen and similar classes of anti-estrogens. Our studies provide several lines of evidence to establish the role of the AhR in mediating the anti-estrogenic effects of TCDD: The Northern hybridizations depicted in Figure 1 show that there is a clear negative relationship between the concentration-dependent induction of the CYP1A1 gene and inhibition of the E2-induced VTG gene expression. Other in vitro studies, using primary cultured rainbow trout hepatocytes, showed that the potency of the different classes of the AHR-ligands to inhibit the VTG synthesis was directly related to their capability to induce CYP1A1 protein levels and enzymatic activities [14, 15]. In addition, our results show that the AHR antagonist, α-NF, is capable of markedly inversing the inhibitory effects of the AHR ligands, TCDD and β-NF, on the E2-triggered expression of the VTG gene. These results supports previously reported studies using rat hepatoma cells  and rainbow trout hepatocytes .
Activation of AHR by TCDD resulted in a marked reduction of ERα mRNA levels. These results are interesting since ERα is the key regulator of the VTG gene expression. In vertebrate oviparous species the expression of ERα in the liver is induced by E2 [20–23]. Regulation of the ER gene expression is an important aspect of the vitellogenesis, since the sensitivity of the target gene is directly dependent on the cellular concentration of ER, i.e., the estrogen receptor number is a rate-limiting factor in the expression of the VTG gene . There are several reports suggesting that the AHR-ligands exert their inhibitory effects on ER signalling by decreasing the levels of ER; for example, treatment of mice with TCDD induced a decrease in hepatic levels of ER mRNA levels . Recent studies using human breast cancer cell line T47D showed that activation of the AHR by TCDD caused a specific proteasome-dependent degradation of ERα [25, 26]. Nevertheless, the inhibitory effects of TCDD on the ERα gene expression appear to be cell-type specific. For example, treatment of the human breast cancer cell line MCF-7 with TCDD did not have any influence on the ERα mRNA levels while it significantly down-regulated the expression of the cathepsin D gene which is under the control of ERα . In another report, the effect of TCDD on the expression of a reporter gene under the control of the Xenopus vitellogenin A2 regulatory sequences was studied. The study revealed that TCDD could prevent reporter-gene expression also when the cells transiently overexpressed ER. These results suggested that the mechanism did not involve downregulation of the ER by TCDD .
The negative effects of TCDD on the expression of ERα and VTG genes, as indicated by decreasing of the levels of their respective mRNAs, might be exerted at transcriptional or post-transcriptional stages. Our results indicate strongly that these effects are mediated through a mechanism which blocks the activation of those genes.
The nuclear run-off transcription assays showed that E2 treatment induced the transcriptional activities of the ERα and VTG genes while TCDD-treatment had a marked inhibitory effect on the activation of these genes. One important issue to be considered here is that the expression of the ERα and VTG genes in the fish liver are differentially regulated [23, 29]. The nuclear run-off transcription studies showed that the expression of the ERα gene reaches a plateau in about 10–12 hours while the expression of the VTG gene continues to increase during the 24 hours after the E2 treatment. These results suggest that the auto-regulation loop of the ERα provides a quick response to estrogen stimuli and subsequently triggers the activation of the VTG gene. In this way, the ERα provides the proper hepatic function necessary to meet the challenging period of vitellogenesis. Our results, however, suggest that despite their different transcriptional rates, the activities of the ERα and VTG genes are both significantly down-regulated by TCDD.
Post-transcriptional events including degradation and/or stabilization of mRNA species are important mechanisms for gene expression. Flouriot and co-workers showed that, in fish liver, the E2-mediated induction of VTG mRNA was brought about by an increase in the rate of VTG gene transcription and by stabilization of cytoplasmic VTG mRNA . Further, these studies indicated that the process of ERα mRNA stabilization was dependent on the presence of an uncharacterized E2-induced protein factor. In general, the stability of the mRNA has been determined by site-specific mRNA endonucleases. Endonuclease-catalyzed mRNA decay is regulated by RNA-binding proteins which specifically bind to the target mRNAs and block their cleavage by endonucleases (reviewed in ). For example, stability of the hepatic VTG mRNA in Xenopus laevis is regulated by an E2-induced RNA-binding protein, vigilin, which binds specifically to a segment of the 3'-UTR of the VTG mRNA and protects it from degradation [31–33]. The results depicted in Figure 4 showed that treatment of hepatocytes with 10 nM TCDD caused a significant reduction the VTG and ERα mRNA levels. Therefore, we performed an assay to investigate whether activation of AHR could increase the turnover rate of VTG and ERα mRNAs, i.e., whether activation of the AHR signalling pathway would trigger any VTG and/or ERα specific mRNA endonuclease activity. As the results presented in Figure 6 show, exposure of the cells to TCDD had no significant effect on the destabilization of VTG and ERα mRNAs.
Electrophoretic mobility shift assays showed that the nuclear extracts prepared from hepatocytes treated with E2 specifically bound to the ERE, i.e., the nuclei were enriched in the activated estrogen receptor. On the other hand, the DNA binding activity of the nuclear extracts from cells co-treated with estradiol and TCDD was markedly decreased. The nature of this pronounced reduction remains unknown. Nonetheless, our results indicate that TCDD treatment may cause a marked depletion of the nuclear ERα. Recently, Wormke et al. suggested a mechanism for the inhibitory AHR-ERα cross-talk in breast cancer cells . These authors showed that ligand activated AHR recruits both ERα and proteasomes which results in the degradation of both AHR and ERα. Due to lack of specific antibodies raised against salmon ERα protein, we were not able to examine this mechanism in the salmon liver cells.
Another interesting issue is whether cross-talk between the two receptors is bidirectional. A bidirectional inhibitory mechanism could arise from competition between the two receptors for a common co-activator. For instance, squelching of the nuclear factor-1 has been described ; in addition, it has been shown that both AHR/ARNT complex  and ERα are able to interact with general transcription factor Sp1 [36, 37]. Our experimental data indicate that squelching would not primarily account for cross-talk between the AHR- and ERα-signalling pathways, as E2 did not exert any inhibitory effect on the expression of the CYP1A gene (Figure 8). These results confirm data from experiments using primary cultured rainbow trout hepatocytes . However, Ricci et al.  using several E2-sensitive human cells lines showed that E2 treatment decreased the TCDD-induced CYP1A1 mRNA levels and transcriptional activities. A similar effect has been reported in the human breast cancer cell line, MCF-7 ; however, conflicting results has also appeared . Thus, the mutual interactions between the ERα- and AHR-mediated signalling pathways appears to be cell-type specific and to be regulated by specific protein factors (co-activators or co-repressors) restricted to each cell type. In our own laboratory, in vivo experiments with salmon have indicated that AHR agonists, such as PCB-77, can act both antagonistic and synergistic to xenoestrogen (nonylphenol) stimulation on vitellogenesis and zonagenesis, whereas no effect of the xenoestrogen was observed on CYP1A levels [2, 16]. Nevertheless, we have also observed that prolonged treatment with high doses of E2 or nonylphenol will provoke reduced CYP1A mRNA levels in the liver of juvenile Atlantic salmon . Activation of the mammalian ER-signalling pathway by the AHR/ARNT complex or ARNT alone has been described recently [41, 42]. It has been shown that upon ligand binding and nuclear translocation the AHR heterodimerize with nuclear ARNT, and then associates with the unliganded ERα or ERβ. The resulting complex recruits the co-activator p300 to the promoter of the E2-responsive genes leading to an E2-independent activation of the genes . ERα or ERβ can also interact with the ARNT via their ligand-binding domains and activate the target genes. This kind of interaction is E2-dependent and involves physical interaction of the ERs with C-terminal trans-activation domain of ARNT .
TCDD and other AH receptor ligands are capable to disrupt E2-induced expression of the VTG gene. The negative effect of TCDD on the expression of VTG gene is accompanied by a reduction in ERα levels. Our results provide evidence that this effect is mediated through a direct interference with the auto-regulatory transcriptional loop of ERα. Additionally, E2 does not interfere with TCDD induced CYP1A gene expression, suggesting that cross-talk between the ERα- and AHR-signalling pathways is unidirectional.
Collagenase, 17β-estradiol, and testosterone were purchased from Sigma (USA). 2,3,7,8-tetrachloro-dibenzo-p-dioxin was purchased from Cambridge Isotope Laboratories, Inc. (UK).
Preparation and culture of hepatocytes
Juvenile Atlantic salmon (Salmo salar), with approximately 500–700 g in weight, were kept in running seawater at a constant temperature of 12°C, at the Industrial Laboratory (ILAB), HIB, Bergen, Norway. Hepatocytes were isolated by a two-step perfusion described by Berry and Friend , and modified by Andersson et al. . Briefly, the liver was first perfused in situ with a calcium-free solution containing NaCl (7.14 g/l); KCl (0.36 g/l), MgSO4 (0.15 g/l); Na2 HPO4 (1.6 g/l); NaH2PO4 (0.4 g/l); NaHCO3 (0.31 g/l) and EGTA (20 mg/l), at approximately 20°C. The liver was then perfused for about 10 min with the same buffer, but with calcium (0.22 g/l) instead of EGTA, and with collagenase A (EC 220.127.116.11, Sigma) (80 mg/150 ml). The cell suspension was filtered through a 150 μm nylon monofilament filter and centrifuged at 50 g for 5 min. Cells were washed with serum-free medium three times and finally resuspended in the complete medium. Viability of the cells was determined by Trypan blue exclusion. The cells were plated on 35 mm Primaria plates (Becto Dickinson Labware, USA) at a density of about 5 × 106 per plate, in Minimum Essential Medium with Earle's salts (EMEM), without phenol red (Gibco, Invitrogen Corp. USA), and containing 2.5% (v/v) foetal bovine serum, glutamine (0.3 g/l medium) and 1% (v/v) antibiotic mixture (Penicillin, Streptomycin, Amphotericin B). The cells were kept at 12°C in a humid atmosphere containing 5% CO2 and 95% air. The cells were kept in culture for, at least, 48 hours prior to treatment with chemicals. The viability of the cells after each treatment was always over 90%, as determined by the Trypan blue exclusion assay.
RNA purification, Northern and slot blot analysis
Total cellular RNA was isolated using Trizol reagent, according to the manufacturer's protocol (Invitrogen). For Northern blot analysis, the samples were separated on a 1% formaldehyde-containing agarose gel, and transferred to a nylon membrane by vacuum blotting. The RNA samples were immobilized on the membranes by UV-cross-linking. The membranes were prehybridized at 42°C, for about 12 hrs, in prehybridization solution containing 50% formamide, 5 X Denhardt's solution, 6 X SSPE (1xSSPE equals 0.15 M NaCl, 10 mM sodium dihydrophosphate and 5 mM EDTA pH 7.2), 0.5% SDS, and 100 μg denatured herring sperm DNA, and hybridized with the respective probe at 42°C for about 12 hrs in the same hybridization solution. The membranes were washed 2 times (20 min/wash) in 1X SSPE/0.1% SDS at 42°C and 2 times (15 min/wash) at high stringency in 2 X SSPE/0.1% SDS at 55°C. For slot blot analysis, total RNA was applied to a nylon membrane using a slot blot apparatus, immobilized, hybridized and washed by the same conditions as described for Northern blot membranes.
Probes and labelling
The ERα probe was prepared by PCR amplification of the hinge region of the ERα cDNA (accession number X89959) obtained from Dr S.A. Rogers, School of Molecular and Medical Biosciences, University of Wales, UK. The primers used for amplification were ELaA (5'-AGG-CAC-TTT-GTT-CTT-ACA-TTT-3') and ELaS (5'-TGG-TGC-CTT-CTC-CTT-CTG-TT-3'). The PCR reaction was run using AmpliTaq (Applied Biosystems) by the following conditions: 1 cycle at 94°C for 5 min, 30 cycles at 94°C/30 sec, 55°C/30 sec, 72°C/45 sec., 1 cycle at 72°C for 7 min. The VTG probe was derived from a VTG cDNA isolated in our laboratory (Yadetie F., Goksøyr A. and Male R., unpublished). The CYP1A1 probe was a NheI restriction fragment from the plasmid pSG-15 containing 2553 base pairs of the rainbow trout CYP1A1 (accession number M21310). The plasmid was a gift from Dr. D.W. Nebert, Laboratory of Developmental Pharmacology, NICHD; Bethesda, MD, USA. The β-actin probe was prepared by PCR amplification of a region spanning nucleotides 225–724 of the Atlantic salmon β-actin cDNA (accession number AF012125). The primers used for amplification were ActinF (5'-CGT-CAC-CAA-CTG-GGA-CGA-CA-3') and ActinR (5'-GCT-CGT-AGC-TCT-TCT-CCA-G-3'). The PCR conditions were as described for preparation of ERα probe. All probes were labelled by random priming method using [α-32P]dCTP (3000 Ci/mmol)(Amersham) according to Ausubel et al. . The images were scanned using Phosphoimager FLA-2000 (Fuji Photo Film CO. Ltd, Japan). Radioactivity was quantified using Phosphoimager FLA-2000 as photo stimulated luminescence (PSL).
Nuclear run-off transcription assay
Preparation of the active nuclei and performance of the run-off transcription assay was performed following an established protocol , with some modifications.
Preparation of the active nuclei
The cells were treated with E2, TCDD or a combination of these chemicals for 8 hrs. The medium was removed and the cells were washed two times with 2 ml of ice-cold phosphate-buffered saline (PBS). The cells were gently dislodged from the plastic surface by scraping with a rubber policeman. The cells were collected by centrifugation at 500 g for 5 min, at 4°C, and lysed using 1% Nonidet-40 buffer (10 mM Tris-HCl pH 7.4, 10 mM NaCl, 3 mM MgCl2, 1% V/V NP-40). The nuclei were isolated by centrifugation at 2500 rpm in an Eppendorf centrifuge and resuspended in 100 μl of glycerol storage buffer (50 mM Tris-HCl pH 8.3, 40% glycerol, 5 mM MgCl2, 0.1 mM EDTA) by gently vortexing. The prepared nuclei were immediately frozen and kept at -80°C.
Binding of plasmid DNA to nylon membrane
200 ng of each the respective plasmid DNA was linearized with appropriate restriction enzyme, and denatured by adding 1 M NaOH to a final concentration 0.1 M and by incubation at room temperature, for 30 min. 10 X vol of 6 X SSC (1 X SSC contains 0.15 M NaCl and 0.015 M trisodium citrate pH 7.0) per sample was added and the plasmid DNA was spotted onto the membrane using a slot blot apparatus (Schleicher & Schuell, Germany).
In vitro transcription assay
An aliquot of 100 μl of frozen nuclei was thawed at room temperature and mixed with 100 μl of freshly prepared 2 X reaction buffer containing nucleotides (10 mM Tris-HCl, pH 8.0, 5 mM MgCl2, 300 mM KCl, 5 mM dithiothreitol, and 0.5 nM of GTP, CTP, ATP and [α-32P]UTP (800 μCi/mmol)) and incubated for 30 min at 30°C. Following in vitro transcription 1 X vol. of Trizol reagent was added and the total RNA was isolated following the instructions of the manufacturer. The yield of labelled RNA was determined using a scintillation counter. The membranes were hybridized to 1 × 106 cpm labelled RNA. Prehybridization, hybridization and wash of the membranes were performed by the same conditions as described for Northern blot membranes.
Electrophoretic mobility shift assay (EMSA)
Preparation of nuclear extracts
The nuclear extracts were prepared by a previously described protocol , with some modifications. A triplet of cells cultured on 35 mm dishes was used in each assay. After exposure of the cultured cells to the appropriate chemicals the dishes were washed two times with ice-cold PBS and the cells were harvested by trypsinization, collected in 15-ml Falcon tubes by centrifuge at 500 g at 4°C, for 5 min, and washed 3 X with ice-cold PBS. After the final wash, the cells were resuspended in 5 ml of homogenization buffer (10 mM HEPES, pH 7.6, 10 mM KCl, 1.5 mM MgCl2, 0.5 mM DTT) and incubated on ice for 10 min. The cell suspensions were transferred to a precooled 7 ml tissue homogenizer and homogenized by 10 strokes. The homogenized cell suspensions were centrifuged at 500 g for 5 min. The pellet (enriched nuclei) was resuspended in 3 ml of S1 solution (0.25 M sucrose, 10 mM MgCl2). The resuspended pellet was carefully layered over 3 ml of S2 solution (0.35 M sucrose, 0.5 mM MgCl2) and centrifuged at 4000 g, for 5 min, at 4°C. This step resulted in a cleaner preparation of the nuclei. The nuclear pellet was resuspended in 50 μl of nuclear lysis buffer (10 mM HEPES, pH 7.6, 100 mM KCl, 0.1 mM EDTA pH 8.0, 3 mM MgCl2, 10% glycerol and 1% NP-40 including a protease inhibitor cocktail, 1 mM phenylmethylsulfonyl fluoride (PMSF), pepstatin A, leupeptin, antipain, and aprotinin) and transferred to an Eppendorf tube. The resuspended pellet was incubated, on ice, for 10 min and then centrifuged at 13000 rpm (12000 g), at 4°C, for 10 min. The supernatant was dialyzed against 1000 X volume of the same buffer without NP-40, for 30 min, using a Slide-A-Lyzer MINI dialysis unit (Pierce, USA) at 4°C. The protein concentration in the samples were determined by the method of Bradford  and the extracts were kept at -80°C until use.
Performance of the EMSA
The complementary oligonucleotides (Medprobe, Oslo, Norway) were mixed and annealed by incubation at 100°C, for 10 min, and slowly cooling to the room temperature (for 1 hr). The probes used were a 3'-end biotin-labelled DNA duplex of the sequence 5'-CATTCTGTTTGCTGTGTCATGTTGACCTGCTCTAGA-3', containing a putative ERE derived from the proximal promoter region of the Atlantic salmon ERα gene (Hanne Ravneberg and Rune Male, unpublished), or a radioactive labelled ERE oligo (ERE-sense oligo: 5'-CGGGGATCCTAGTAGGTCACAGTGACCTCATGGATCC-3', ERE-antisense oligo: 5'-GGGGATCCATGAGGTCAGTGTGACCTACTAGGATCC-3'). The radioactive probe was labelled by end-filling reaction using DNA polymerase (Klenow fragment), and [α-32P]dCTP (3000 Ci/mmol) according to the standard protocols . The Oct probe was composed of a sense oligonucleotide Oct-1: 5'-CGGGGATCCTGATCCATGCAAATCGACGACT-3' and antisense oligonucleotide Oct-1: 5'-GGGGATCCAGTCGTCGATTTGCATGGATCAG-3'. The binding reaction with the biotinylated probe was performed according to the instructions of the manufacturer, using the LightShift Chemiluminescent EMSA kit (Pierce) and 1 μg of nuclear extracts per reaction. The DNA-protein complexes were electrophoresed through a 6% native polyacrylamide gel, and transferred to a nylon membrane electrophoretically. The samples were fixed to the membrane by UV-cross-linking. The chemiluminescent detection was performed as described by the manufacturer. The membranes were exposed to an enhanced chemiluminescence film (Kodak), for 5 seconds, before developing or scanned using Phosphoimager FLA-2000 (Fuji Photo Film CO. Ltd, Japan). Alternatively, 3 μl of nuclear extract was mixed with 1 μg poly (dI-dC) in binding buffer (10 mM Tris-HCl, pH 7.5, 100 mM NaCl, 1 mM DTT, 1 mM EDTA and 4% glycerol), and incubated at room temperature for 15 min. The radio-labelled probe was subsequently added to the mixture, and the binding reaction was further incubated, at room temperature, for an additional 20 min period, before fractionation by electrophoresis. The gels were subsequently dried and exposed to phosphoimager plates, overnight, before scanning.
Statistical analysis was performed by one-way ANOVA (n = 3 in each group, unless otherwise indicated) using JMP (version 5.0), SAS Institute Inc., USA. Data were tested for normal distribution (Shapiro-Wilk W test) and for homogeneity of variance. Sets with homogeneous variances were analysed by Dunnett's test to determine which means were significantly different from a reference group (P < 0.05).
This study was supported by the Norwegian Research Council (NFR grants 125692/720 and 156166/130) and Biosense Laboratories AS (Bergen, Norway). The authors would like to thank Wenche Telle, for technical assistance. We are also most grateful to Dr. B.E. Grøsvik, for his advise about statistical analysis of data.
- Mommsen TP, Walsh PJ: Vitellogenesis and oocyte assembly. Fish Physiology. Edited by: Hoar W S and Randall D J. 1988, London, Academic Press, 11: 347-406.Google Scholar
- Arukwe A, Goksøyr A: Eggshell and egg yolk proteins in fish: Hepatic proteins for the next generation: Oogenetic, population, and evolutionary implications of endocrine disruption. Comp Hepatol. 2003, 2: 4-10.1186/1476-5926-2-4.PubMed CentralView ArticlePubMedGoogle Scholar
- Davail B, Pakdel F, Bujo H, Perazzolo LM, Waclawek M, Schneider WJ, Le Menn F: Evolution of oogenesis: The receptor for vitellogenin from the rainbow trout. J Lipid Res. 1998, 39: 1929-1937.PubMedGoogle Scholar
- Stifani S, Le Menn F, Rodriguez JN, Schneider WJ: Regulation of oogenesis: The piscine receptor for vitellogenin. Biochim Biophys Acta. 1990, 1045: 271-279. 10.1016/0005-2760(90)90130-P.View ArticlePubMedGoogle Scholar
- Byrne BM, Gruber M, Ab G: The evolution of egg yolk proteins. Prog Biophys Mol Biol. 1989, 53: 33-69. 10.1016/0079-6107(89)90005-9.View ArticlePubMedGoogle Scholar
- Wahli W: Evolution and expression of vitellogenin genes. Trends Genet. 1988, 4: 227-232. 10.1016/0168-9525(88)90155-2.View ArticlePubMedGoogle Scholar
- Mouchel N, Trichet V, Betz A, Le Pennec JP, Wolff J: Characterization of vitellogenin from rainbow trout (Oncorhynchus mykiss). Gene. 1996, 174: 59-64. 10.1016/0378-1119(96)00336-8.View ArticlePubMedGoogle Scholar
- Nicolas J-M: Vitellogenesis in fish and the effects of polycyclic aromatic hydrocarbon contaminants. Aquatic Toxicology. 1999, 45: 77-90. 10.1016/S0166-445X(98)00095-2.View ArticleGoogle Scholar
- Rowlands JC, Gustafsson JA: Aryl hydrocarbon receptor-mediated signal transduction. Critical Reviews In Toxicology. 1997, 27: 109-134.View ArticlePubMedGoogle Scholar
- Gu YZ, Hogenesch JB, Bradfield CA: The pas superfamily: Sensors of environmental and developmental signals. Annual Review Of Pharmacology And Toxicology. 2000, 40: 519-561. 10.1146/annurev.pharmtox.40.1.519.View ArticlePubMedGoogle Scholar
- Whitlock JP: Induction of cytochrome p4501a1. Annual Review Of Pharmacology And Toxicology. 1999, 39: 103-125. 10.1146/annurev.pharmtox.39.1.103.View ArticlePubMedGoogle Scholar
- Safe SH: Modulation of gene-expression and endocrine response pathways by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related-compounds. Pharmacology & Therapeutics. 1995, 67: 247-281. 10.1016/0163-7258(95)00017-B.View ArticleGoogle Scholar
- Safe S: Molecular biology of the ah receptor and its role in carcinogenesis. Toxicology Letters. 2001, 120: 1-7. 10.1016/S0378-4274(01)00301-0.View ArticlePubMedGoogle Scholar
- Anderson MJ, Miller MR, Hinton DE: In vitro modulation of 17-beta-estradiol-induced vitellogenin synthesis: Effects of cytochrome p4501a1 inducing compounds on rainbow trout (Oncorhynchus mykiss) liver cells. Aquatic Toxicology. 1996, 34: 327-350. 10.1016/0166-445X(95)00047-8.View ArticleGoogle Scholar
- Navas JM, Segner H: Antiestrogenicity of [beta]-naphthoflavone and pahs in cultured rainbow trout hepatocytes: Evidence for a role of the arylhydrocarbon receptor. Aquatic Toxicology. 2000, 51: 79-92. 10.1016/S0166-445X(00)00100-4.View ArticlePubMedGoogle Scholar
- Arukwe A, Yadetie F, Male R, Goksøyr A: In vivo modulation of nonylphenol-induced zonagenesis and vitellogenesis by the antiestrogen, 3,3'4,4'-tetrachlorobiphenyl (pcb-77) in juvenile fish. Environmental Toxicology and Pharmacology. 2001, 10: 5-15. 10.1016/S1382-6689(01)00063-1.View ArticlePubMedGoogle Scholar
- Larsen EL, Celander M, Goksøyr A: The cytochrome P450 system of Atlantic salmon (salmo salar): II. Variations in hepatic catalytic activities and isozyme patterns during an annual reproductive cycle. Fish Physiology and Biochemistry. 1992, 10: 291-301.View ArticlePubMedGoogle Scholar
- Macgregor JI, Jordan VC: Basic guide to the mechanisms of antiestrogen action. Pharmacol Rev. 1998, 50: 151-196.PubMedGoogle Scholar
- Merchant M, Arellano L, Safe S: The mechanism of action of alpha-naphthoflavone as an inhibitor of 2,3,7,8-tetrachlorodibenzo-para-dioxin-induced cyp1a1 gene-expression. Archives Of Biochemistry And Biophysics. 1990, 281: 84-89.View ArticlePubMedGoogle Scholar
- Barton MC, Shapiro DJ: Transient administration of estradiol-17 beta establishes an autoregulatory loop permanently inducing estrogen receptor mRNA. Proc Natl Acad Sci U S A. 1988, 85: 7119-7123.PubMed CentralView ArticlePubMedGoogle Scholar
- Evans MI, O'Malley PJ, Krust A, Burch JB: Developmental regulation of the estrogen receptor and the estrogen responsiveness of five yolk protein genes in the avian liver. Proc Natl Acad Sci U S A. 1987, 84: 8493-8497.PubMed CentralView ArticlePubMedGoogle Scholar
- Flouriot G, Pakdel F, Ducouret B, Ledrean Y, Valotaire Y: Differential regulation of two genes implicated in fish reproduction: Vitellogenin and estrogen receptor genes. Mol Reprod Dev. 1997, 48: 317-323. 10.1002/(SICI)1098-2795(199711)48:3<317::AID-MRD3>3.0.CO;2-U.View ArticlePubMedGoogle Scholar
- Flouriot G, Pakdel F, Valotaire Y: Transcriptional and post-transcriptional regulation of rainbow trout estrogen receptor and vitellogenin gene expression. Mol Cell Endocrinol. 1996, 124: 173-183. 10.1016/S0303-7207(96)03960-3.View ArticlePubMedGoogle Scholar
- Tian Y, Ke S, Thomas T, Meeker RJ, Gallo MA: Transcriptional suppression of estrogen receptor gene expression by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). J Steroid Biochem Mol Biol. 1998, 67: 17-24. 10.1016/S0960-0760(98)00067-3.View ArticlePubMedGoogle Scholar
- Wormke M, Stoner M, Saville B, Safe S: Crosstalk between estrogen receptor alpha and the aryl hydrocarbon receptor in breast cancer cells involves unidirectional activation of proteasomes. FEBS Letters. 2000, 478: 109-112. 10.1016/S0014-5793(00)01830-5.View ArticlePubMedGoogle Scholar
- Wormke M,M, Stoner B, Saville K, Walker M, Abdelrahim R, Burghardt and, S. Safe : The aryl hydrocarbon receptor mediates degradation of estrogen receptor alpha through activation of proteasomes. Molecular Cell Biology. 2003, 23: 1843-1855. 10.1128/MCB.23.6.1843-1855.2003.View ArticleGoogle Scholar
- Kharat I, Saatcioglu F: Antiestrogenic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin are mediated by direct transcriptional interference with the liganded estrogen receptor - cross-talk between aryl hydrocarbon- and estrogen-mediated signaling. Journal of Biological Chemistry. 1996, 271: 10533-10537. 10.1074/jbc.271.18.10533.View ArticlePubMedGoogle Scholar
- Nodland KI, Wormke M, Safe S: Inhibition of estrogen-induced activity by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the MCF-7 human breast cancer and other cell lines transfected with vitellogenin A2 gene promoter constructs. Arch Biochem Biophys. 1997, 338: 67-72. 10.1006/abbi.1996.9806.View ArticlePubMedGoogle Scholar
- Pakdel F, Delaunay F, Ducouret B, Flouriot G, Kern L, Lazennec G, LeDrean Y, Petit F, Salbert G, Saligaut D, Tujague M, Valotaire Y: Regulation of gene expression and biological activity of rainbow trout estrogen receptor. Fish Physiology and Biochemistry. 1997, 17: 123-133. 10.1023/A:1007706207857.View ArticleGoogle Scholar
- Ostareck-Lederer A, Ostareck DH, Hentze MW: Cytoplasmic regulatory functions of the KH-domain proteins hnRNPs K and E1/E2. Trends in Biochemical Sciences. 1998, 23: 409-411. 10.1016/S0968-0004(98)01301-2.View ArticlePubMedGoogle Scholar
- Dodson RE, Shapiro DJ: Vigilin, a ubiquitous protein with 14 K homology domains, is the estrogen-inducible vitellogenin mRNA 3'-untranslated region-binding protein. J Biol Chem. 1997, 272: 12249-12252. 10.1074/jbc.272.19.12249.View ArticlePubMedGoogle Scholar
- Kanamori H, Dodson RE, Shapiro DJ: In vitro genetic analysis of the rna binding site of vigilin, a multi-kh-domain protein. Mol Cell Biol. 1998, 18: 3991-4003.PubMed CentralView ArticlePubMedGoogle Scholar
- Cunningham KS, Dodson RE, Nagel MA, Shapiro DJ, Schoenberg DR: Vigilin binding selectively inhibits cleavage of the vitellogenin mRNA 3'-untranslated region by the mRNA endonuclease polysomal ribonuclease 1. Proc Natl Acad Sci U S A. 2000, 97: 12498-12502. 10.1073/pnas.220425497.PubMed CentralView ArticlePubMedGoogle Scholar
- Ricci MS, Toscano DG, Mattingly CJ, Toscano WA: Estrogen receptor reduces cyp1A1 induction in cultured human endometrial cells. Journal of Biological Chemistry. 1999, 274: 3430-3438. 10.1074/jbc.274.6.3430.View ArticlePubMedGoogle Scholar
- Kobayashi A, Sogawa K, Fujii-Kuriyama Y: Cooperative interaction between AhR.Arnt and Sp1 for the drug-inducible expression of CYP1A1 gene. J Biol Chem. 1996, 271: 12310-12316. 10.1074/jbc.271.21.12310.View ArticlePubMedGoogle Scholar
- Batistuzzo de Medeiros SR, Krey G, Hihi AK, Wahli W: Functional interactions between the estrogen receptor and the transcription activator Sp1 regulate the estrogen-dependent transcriptional activity of the vitellogenin A1 io promoter. J Biol Chem. 1997, 272: 18250-18260. 10.1074/jbc.272.29.18250.View ArticlePubMedGoogle Scholar
- Porter W, Saville B, Hoivik D, Safe S: Functional synergy between the transcription factor Sp1 and the estrogen receptor. Mol Endocrinol. 1997, 11: 1569-1580. 10.1210/me.11.11.1569.View ArticlePubMedGoogle Scholar
- Navas JM, Segner H: Estrogen-mediated suppression of cytochrome P4501A (CYP1A) expression in rainbow trout hepatocytes: role of estrogen receptor. Chemico-Biological Interactions. 2001, 138: 285-298. 10.1016/S0009-2797(01)00280-0.View ArticlePubMedGoogle Scholar
- Hoivik D, Willett K, Wilson C, Safe S: Estrogen does not inhibit 2,3,7, 8-tetrachlorodibenzo-p-dioxin-mediated effects in MCF-7 and Hepa 1c1c7 cells. Journal of Biological Chemistry. 1997, 272: 30270-30274. 10.1074/jbc.272.48.30270.View ArticlePubMedGoogle Scholar
- Oppen-Berntsen DO,, Arukwe A,, Yadetie F,, Lorens JB,, Male R: Salmon eggshell protein expression: a marker for environmental estrogens. Marine Biotechnology. 1999, 1: 252-260.View ArticlePubMedGoogle Scholar
- Ohtake F, Takeyama K, Matsumoto T, Kitagawa H, Yamamoto Y, Nohara K, Tohyama C, Krust A, Mimura J, Chambon P, Yanagisawa J, Fujii-Kuriyama Y, Kato S: Modulation of oestrogen receptor signalling by association with the activated dioxin receptor. Nature. 2003, 423: 545-550. 10.1038/nature01606.View ArticlePubMedGoogle Scholar
- Brunnberg S, Pettersson K, Rydin E, Matthews J, Hanberg A, Pongratz I: The basic helix-loop-helix-PAS protein ARNT functions as a potent coactivator of estrogen receptor-dependent transcription. Proc Natl Acad Sci U S A. 2003, 100: 6517-2652. 10.1073/pnas.1136688100.PubMed CentralView ArticlePubMedGoogle Scholar
- Berry MN, Friend DS: High-yield preparation of isolated rat liver parenchymal cells: A biochemical and fine structural study. J Cell Biol. 1969, 43: 506-520. 10.1083/jcb.43.3.506.PubMed CentralView ArticlePubMedGoogle Scholar
- Andersson T, Forlin L, Hansson T: Biotransformation of 7-ethoxycoumarin in isolated perfused rainbow trout liver. Drug Metab Dispos. 1983, 11: 494-498.PubMedGoogle Scholar
- Ausubel F, Brent R, Kingstone RE, Moore DD, Seidman JG, Smith J, Stuhl K: Current protocols in molecular biology. 1997, Boston, MA, John Wiley and Sons IncGoogle Scholar
- Delaunay F, Pakdel F, Valotaire Y: Effect of in vivo oestradiol treatment on cell-free transcription in trout liver nuclear extracts. J Mol Endocrinol. 1994, 13: 137-147.View ArticlePubMedGoogle Scholar
- Bradford MM: A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal Biochem. 1976, 72: 248-254. 10.1006/abio.1976.9999.View ArticlePubMedGoogle Scholar
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