Printer Friendly

Green fluorescent protein (GFP) as a marker of aryl hydrocarbon receptor (AhR) function in developing zebrafish (danio rerio). (Articles).

We developed an inducible in vivo reporter system to examine expression of the aryl hydrocarbon receptor (AhR) during development in zebrafish (Danio rerio). AhR is a ligand-activated transcription factor that mediates the toxic actions of environmental contaminants such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Induction of cytochrome P4501A1 (CYP1A1) is an early biomarker of AhR activation. A 1905 base pair region of the human CYP1A1 promoter/enhancer region was regulated by AhR in zebrafish liver cells after exposure to TCDD (10 nM) in a transient transfection assay. This regulatory region was fused to the cDNA sequence encoding green fluorescent protein (GFP) of jellyfish (Aequorea victoria). Transgenic zebrafish were generated to express this AhR-regulated GFP construct. Injected fish exposed to TCDD exhibited induction of GFP in the eye, nose, and vertebrae of zebrafish embryos (48 and 72 hr after fertilization) compared to vehicle controls (DMSO), which did not express GFP. To investigate whether AhR-regulated GFP expression correlated with sites of TCDD toxicity, we exposed wild-type zebrafish to DMSO or TCDD and examined them for morphologic abnormalities. By 5 days after fertilization, TCDD-exposed fish exhibited gross dysmorphogenesis in cranio-facial and vertebral development. Key words, aryl hydrocarbon receptor, cytochrome P450, dioxin, green fluorescent protein, polychlorinated compounds.


The aryl hydrocarbon receptor (AhR) is a ligand-activated transcription factor that modulates the toxic actions of a class of environmental compounds including 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (1). Ligand-activated AhR forms a heterodimer with a second protein, aryl hydrocarbon nuclear translocator (Arnt), and binds to Ah response elements (AhREs) in the enhancer regions of AhR-regulated genes such as cytochrome P4501A1 (CYP1A1). An endogenous ligand for this receptor has not yet been identified. Several reports in the literature, however, suggest that AhR regulates proliferation and differentiation of many cell types (2-5).

That AhR plays an important role during development independent of environmental exposure is supported by AhR knockout mice, which exhibited poor survival, loss of body weight, and impaired liver and immune systems (6-9). To date, little information is known about the ontogenetic expression of this receptor. In this study, we examined the temporal expression pattern of AhR and its heterodimer partner, Arnt, during zebrafish development using reverse transcription polymerase chain reaction (RT-PCR). To determine the spatial expression of AhR, we developed an inducible reporter system designed to express green fluorescent protein (GFP) in response to ligand-activated AhR. Several reports in the literature have demonstrated that GFP can be used effectively to describe protein expression in live embryos and juvenile zebrafish (10-12). GFP offers several advantages over other reporter systems in that it is nontoxic and can be detected in living animals without the addition of exogenous substrates (10-12). We used AhR-regulated GFP expression as an in vivo reporter to detect AhR function and to determine whether AhR-regulated GFP expression accurately predicts sites of TCDD-induced dysmorphogenesis during zebrafish development.

Materials and Methods

Chemicals. We obtained TCDD from Cambridge Isotopes Laboratory (Andover, MA). We purchased restriction endonucleases from New England Biolabs (Beverly, MA). Unless specified otherwise, we purchased reagents from commercial sources and used them without further purification.

Zebrafish maintenance. Adult zebrafish were raised and maintained on a 14:10 hr light:dark cycle at 28.5 [degrees] C and bred in marbled tanks as described by Westerfield (13). We fed mature fish three times daily with a combination of Freshwater Aquarium Flakefood (Ocean Star International, Inc., Hayward, CA) and live brine shrimp (Carolina Biological Supply Co., Burlington, NC). Care and treatment of animals were conducted in accordance with guidelines established by the Tulane University Institutional Animal Care and Use Committee.

RNA preparation. We collected RNA from zebrafish embryos using TRI REAGENT RNA Isolation Reagent (Molecular Research Center, Inc., Cincinnati, OH). At targeted stages of development, embryos were frozen, rinsed twice in cold tank water, dissolved in 1 mL of TRI REAGENT, and transferred to a Dounce Homogenizer (Fisher Scientific, Pittsburgh, PA), previously washed with chloroform. Protective chorions surrounding embryos were broken by 10 strokes in the Dounce homogenizer. Embryos were transferred to RNase-free microcentrifuge tubes, and RNA was isolated according to a protocol supplied by the manufacturer.

RT-PCR. We reversed transcribed 10 [micro]g of total RNA according to manufacturer's recommendations (Promega, Madison, WI). Briefly, RNA or water, 20 units of RNasin Ribonuclease Inhibitor, and 1 unit RQ1 DNase (RNase-free) in a total volume of 10 [micro]L were heated to 37 [degrees] C for 15 min, 70 [degrees] C for 5 min, and cooled on ice. The reaction mixture was heated to 70 [degrees] C for 3 min with 200 pmol oligo d [(T).sub.16] and cooled on ice for 5 min. Reaction volume was increased to 40 [micro]L containing (final concentrations) 50 mM Tris-HC1 (pH 8.3.), 75 mM KCI, 8 mM Mg[Cl.sub.2], 10 mM DTT, 1 mM each of dATP, dCTP, dGTP, and dTTP, 20 units of RNase inhibitor, and 200 units of M-MLV reverse transcriptase. Reaction was incubated at 42 [degrees] C for 90 min, 70 [degrees] C for 10 min, placed on ice, and brought to 100 [micro]L in water. We used PCR to amplify zebrafish AhR and Arnt cDNA sequences. We designed AhR and Arnt primers according to published sequences (14). Primers used included AhR upper, 5'-CCAAGATTATC TAGGGTTCCATCAG; AhR lower, 5'-CTCCCACAGGCAGAGTATCGCACTGA; [beta]-actin upper, 5'- ATCTGGCACCA CACCTTCTACAATG; [beta]-actin lower, 5'- GGGGTGT TGAAGGTCTCAAACATGAT. We performed PCR reactions in a final volume of 50 [micro]L containing (final concentrations) 10 mM Tris-HCl (pH 9.0), 4.5 mM Mg[Cl.sub.2], 50 mM KCI, 0.1% Triton X-100, 0.5 mM each of dATP, dCTP, dGTP, dTTP, 2.5 units of Taq DNA Polymerase, 6 [micro]L of the reverse transcription reaction described above, and 20 pmol each of CYP1A1 primers. All components except enzyme were heated to 95 degrees] C for 2 min and cooled on ice for 5 min. Taq polymerase was added and samples were cycled 40 times through a 1 min 95 [degrees] C denaturation step, a 1 min 54 [degrees] C annealing step, and a 1 min 72 [degrees] C extension step. Cycling was followed by a 5 min final 72 [degrees] C extension step. Samples were coamplified with primers for the zebrafish [beta]-actin cDNA sequence for the purpose of a loading control.

Plasmid construction. We constructed two AhR-regulated reporter plasmids, p1A1Luc and plA1GFP, by fusing a portion of the 5' regulatory region (-1612/+292) of the AhR-regulated gene CYP1A1 to the cDNA sequences of firefly luciferase and jellyfish GFP, respectively. This region was previously shown to be regulated by activated AhR (15-19). We excised a 1904 base pair fragment from the phMC7.6 plasmid (a generous gift of Y. Fujii-Kuriyama, Sendai, Japan) by PvuII digestion, inserted it into the SmaI site of Bluescript (SK+) vector (Stratagene, La Jolla, CA), and designated it pBU1A1. This portion of the CYP1A15' regulatory region is AhR responsive and contains the promoter exon one as well as at least three functional AhREs (15-19). We excised this fragment from pBU1A1 by SacI-XhoI digestion and subcloned it into the pGL3-Basic Vector (Promega) upstream of the luciferase cDNA sequence to generate p lA1Luc. We excised the 5' regulatory region from pBU1A1 by SacI-PstI digestion and subcloned it into the corresponding sites of pEGFP-1 (Clontech, Palo Alto, CA) to generate plA1GFP.

Zebrafish liver cell culture. P. Collodi (Purdue University, West Lafayette, IN) provided adult zebrafish liver cells (ZFL). We cultivated the cells in ZFL medium consisting of Liebowitz L-15, Dulbecco's Modified Eagle's Medium (DMEM), and Ham's F 12 (50:35:15) supplemented with 10 mg/mL insulin, 5% fetal bovine serum (Hyclone, Salt Lake City, UT), and 0.1% trout serum (East Coast Biologics, Inc., New Berwick, ME) in an atmosphere of 5% C[O.sub.2]/95% air at 28.5 [degrees] C, as described by Collodi et al. (20).

Transient trasfections. We plated ZFL cells in 12-well dishes and transiently transfected them with 1 [micro]g of plA1Luc using TransFast Reagent (Promega) according to manufacturer's instructions. Following transfection incubation, we replaced ZFL medium with medium containing DMSO (0.1%) or TCDD (1 nM and 10 nM) at different time points. We selected these levels of TCDD because they are equivalent to levels at which humans are thought to be exposed (21). After a maximum 48-hr incubation, we rinsed cells twice in phosphate-buffered saline (PBS) (13.7 mM NaCI, 0.27 mM KCI, 0.43 mM sodium phosphate, 0.14 mM potassium phosphate) and lysed them on the plate by adding 60 [micro]L reporter lysis buffer 5X (Promega; 25 mM Tris-phosphate, pH 7.8, 2 mM DTT, 2 mM EDTA, 10% glycerol, 1% Triton X-100). Cell lysates were collected, vortexed, and centrifuged for 20 sec at 13,000 rpm in a microcentrifuge tube (Eppendorf; Brinkman Instruments, Westbury, NY). We added 100 [micro]L luciferase assay reagent (Promega) to supernatant (10 [micro]L) at 25 [degrees] C, and measured luciferase activity in a luminometer (Monolight 2010; Analytical Luminescence Laboratory, Ann Arbor, MI). We normalized assays to protein concentration estimated using the procedure of Lowry as modified by Peterson (22). Bovine serum albumin was the standard. The minimum detectable protein level for this assay was 1 ng.

Microinjection of zebrafish embryos and GFP detection. We micro-injected single-cell zebrafish embryos with plA1GFP as described (13). Briefly, plA1GFP was linearized with PvuII, purified from an agarose gel, and suspended at 75 [micro]g/mL in TE buffer (10 mM Tris-HCl, 1 mM EDTA, pH 7.8) and phenol red (2%) (23). We constructed agarose ramps for injections as described (24). We transferred eggs to the agarose ramps and injected them with DNA/phenol red solution using a micropipet secured in a micromanipulator (Zeiss, Jena, Germany). We transferred injected eggs to Petri dishes and exposed them to DMSO (0.1%) or TCDD (10 nM) immediately following injection or at 48 hr after fertilization for 24 hr. We monitored embryos for expression of GFP using a Zeiss microscope equipped with a fluorescein isothiocyanate (FITC) filter ([lambda] ex = 470 nm, [lambda] em = 515 nm). We processed images with help from D. Biggs, using the AutoDeblur 2D blind deconvolution algorithm from AutoQuant Imaging, Inc. (Watervliet, NY).

Results and Discussion

Temporal expression of AhR in developing zebrafish. Understanding the role of AhR during development has been limited by the lack of information about the spatio-temporal expression patterns of AhR transcriptional machinery. Difficulties associated with defining AhR and Arnt expression are related partly to limitations posed by mammalian systems, which include the difficulty of reproducible staging and limiting numbers of embryos (25). Thus zebrafish provide distinct advantages over other systems in the availability and transparency of eggs.

It was first important to determine whether AhR and Arnt were expressed during development. Because AhR is present in low abundance (5,000-33,000 molecules/cell), RT-PCR was used to amplify AhR mRNA (26). Primers were designed based on a portion of published zebrafish AhR cDNA sequences (14). We isolated RNA from unfertilized eggs and embryos at several stages during development. We detected AhR mRNA at low levels in the unfertilized egg and in the embryo at 1 and 2 hr after fertilization (data not shown). At 4 hr after fertilization, mRNA levels increased (Figure 1), correlating with the estimated onset of zygotic transcription (27,28). We detected AhR transcript at all stages examined (4, 12, 24, 28, 33, 48, and 120 hr after fertilization), although levels appeared to fluctuate, suggesting that this gene is regulated during development.

Design and construction of AhR-responsive constructs. Induction of CYP1A1 mRNA is an early biochemical marker of ligand-activated AhR. The CYP1A1 cDNA sequence is highly conserved among vertebrates and invertebrates (29,30). The 5' regulatory region of the human CYP1A1 gene has been well characterized (15,12). Several studies have identified elements of the CYP1A1 regulatory region that are involved in AhR-mediated transcriptional activation of this gene, including a TATA box, an NF-1 binding site, and eight AhR response elements (AhREs) (1,15,17). AhR activates transcription of CYP1A1 by binding as a heterodimer to one or more of the eight AhREs in combination with other factors of the basal transcriptional machinery (1,18,19). Because CYP1A1 monooxygenase activity depends on AhR activation, we used the CYP1A1 promoter/enhancer region to design an AhR-responsive reporter construct.

Previous reports have indicated that the first 1905 base pairs of the 5' regulatory region are sufficient for transcriptional activation of CYP1A1 by AhR (1,16,18,19). This region includes the TATA box, the NF-1 binding site, and three of the eight AhR response elements (1,16,18,19). Before injecting zebrafish eggs with a GFP reporter construct under regulatory control of the human CYP1A1 promoter/enhancer region, we had to determine whether this 5' regulatory region of CYP1A1 was responsive to AhR ligands in zebrafish. To test this, we constructed a plasmid by ligating the human CYP1A1 regulatory region to the cDNA sequence encoding firefly luciferase (Figure 2). This construct was transiently transfected into adult zebrafish liver cells (ZFL)(20). Cells were exposed to either DMSO (0.01%) or environmentally relevant concentrations of TCDD (1 nM and 10 nM) for 18, 24, or 48 hr. We determined luciferase activity fluorometrically. Induction of luciferase activity was concentration dependent and reached steady state by 24 hr (Figure 3). These results were consistent with activation observed in human systems using this 5' regulatory region of CYP1A1, and showed that this region was responsive to AhR-mediated induction in the zebrafish system (2).


AhR-mediated GFP expression in developing zebrafish. We constructed a second AhR-dependent reporter plasmid for injection into zebrafish embryos. We fused the identical 1905 base pair 5' regulatory region of the human CYP1A1 gene to the cDNA sequence encoding GFP (Figure 2). This construct was linearized by digestion with PvuII and microinjected into zebrafish embryos at the one-cell stage as described by Westerfield (13). Embryos were immediately exposed to DMSO (0.01%) or TCDD (10 nM) for 24 or 72 hr. Zebrafish were dechorionated and examined by fluorescence microscopy. We observed no GFP expression in DMSO-exposed injected fish, whereas approximately 43% of injected embryos exposed to TCDD exhibited GFP expression. We observed GFP expression most consistently in the eye and nose and along the vertebrae of TCDD-exposed developing zebrafish (24 and 48 hr after fertilization; Figure 4).


GFP expression pattern correlates with sites of TCDD-induced toxicity. Numerous reports (31-35) have demonstrated that TCDD exposure causes gross morphologic abnormalities during development. Although the mechanisms underlying TCDD-induced toxicity are not understood, evidence derived from AhR knockout mice has confirmed that toxicity is mediated via AhR (6-8). We were interested to determine whether patterns of AhR-dependent GFP expression in transgenic zebrafish correlated with sites of toxicity in developing zebrafish. We exposed wild-type zebrafish to DMSO (0.01%) or TCDD (10 nM) for 5 days after fertilization and examined them for gross morphologic differences. We observed diverse toxicity, including a lack of eyes and a range of vertebral abnormalities (Figure 5). These data suggest that AhR-regulated GFP expression accurately predicts sites of TCDD-induced toxicity and may provide a novel method for examining the physiologic function of AhR. A recent study (36) has demonstrated that AhR plays an important role in regulating development of vascular structures in murine embryos through transcriptional regulation of as yet unidentified genes by the AhR. The AhR regulated GFP expression system described here could be a useful tool to elaborate the molecular mechanism by which AhR regulates important developmental genes in vascular tissues.



In this report, we used zebrafish as a model to investigate the spatio-temporal expression pattern of AhR during development. AhR mRNA was detected by RT-PCR in unfertilized eggs and in embryos at 1 and 2 hr after fertilization, suggesting the presence of maternal transcript. AhR mRNA levels increased dramatically at 4 hr after fertilization and appeared to be regulated throughout development, suggesting that this gene has an important and specific functions during development. We used the 5' regulatory region of the human CYP1A1 gene, an AhR-regulated gene, to construct two reporter plasmids, p1A1Luc and p1A1GFP, that express luciferase and GFP, respectively. By transiently transfecting the luciferase construct into zebrafish liver cells, we showed that this regulatory region was functional in the zebrafish system and was induced in response to TCDD, a potent AhR ligand. Microinjection of plA1GFP into single-cell zebrafish embryos produced GFP expression after exposure to TCDD but not the vehicle control (DMSO). We observed GFP expression up to at least 48 hr, after which the onset of pigmentation limited observation of GFP expression. We detected GFP expression in the eye, nose, and vertebrae, suggesting that AhR may play an important physiologic role in the development of these structures. These data are in agreement with those of other laboratories (36), which showed a role for AhR as a regulator of vascular structures in mice. Activation of AhR indicated that TCDD-induced toxicity targeted morphologic development of the vertebrae and cranio-facial structures including the eye. AhR-regulated GFP expression, therefore, appears to be an accurate predictor of TCDD-induced toxicity and may provide important information about the normal physiologic function of this receptor. Expression of AhR-regulated reported groups could be used as an assay system to elucidate functions of potential natural ligands for AhR and may be a powerful tool to elaborate physiologic as well as toxicologic functions of AhR during development. Further, it is possible that specific receptor-regulated GFP expression systems could be useful transgenic biosensor systems to detect xenobiotic toxicants in the environment.


(1.) Whitlock JP Jr. Induction of cytochrome P4501A1. Annu Rev Pharmacol Toxicol 39:103-125 (1999).

(2.) Ricci MS, Toscano DG, Mattingly CJ, Toscano WA Jr. Reversible modulation of Ah receptor action by 17 [beta]-estradiol in cultured human endometrial cells. J Biol Chem 274:3430-3438 (1999).

(3.) Choi EJ, Toscano DC, Ryan JA, Riedel N, Toscano WA Jr. Dioxin induces transforming growth factor-[alpha] in human keratinocytes. J Biol Chem 266:9591-9597 (1991).

(4.) Gaido KW, Maness SC, Leonard LS, Greenlee WF. 2,3,7,8-Tetrachlorodibenzo-p-dioxin-dependent regulation of transforming growth factors-ct and [beta] 2 expression in a keratinocyte cell line involves both transcriptional and post-transcriptional control. J Biol Chem 267:24591-24595 (1992).

(5.) Lorick K, Toscano DG, Toscano WA Jr. 2,3,7,8-Tetrachlorodibenzo-p-dioxin alters retinoic acid receptor function in human keratinocytes. Biochem Biophys Res Commun 243:749-752 (1998).

(6.) Fernandez-Salguero P, Pineau T, Hilbert DM, McPhail T, Lee SST, Kimura S, Nebert DW, Rudikoff S, Ward JM, Gonzalez FJ. Immune system impairment and hepatic fibrosis in mice lacking the dioxin-binding Ah receptor. Science 268:722-726 (1995).

(7.) Fernandez-Salguero P, Hilbert DM, Rudikoff S, Ward JM, Gonzalez FJ. Aryl-hydrocarbon receptor-deficient mice are resistant to TCDD-induced toxicity. Toxicol Appl Pharmacol 140:173-179 (1996).

(8.) Mimura J, Yamashite K, Nakarnura K, Morita M, Takagi TN, Nakao K, Ema M, Sogawa K, Yasuda M, Katsuki M, et el. Loss of teratogenic response to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in mice lacking the Ah (dioxin) receptor. Genes Cells 2:645-654 (1997).

(9.) Schmidt JV, Su GH, Reddy JK, Simon MC, Bradfield CA. Characterization of a murine AhR null allele: involvement of the AhR in hepatic growth and development. Proc Natl Acad Sci USA 93:6731-6736 (1996).

(10.) Amsterdam A, Lin S, Hopkins N. The Aequorea victoria green fluorescent protein can be used as a reporter in live zebrafish embryos. Dev Biol 171:123-129 (1995).

(11.) Amsterdam A, Lin S, Moss LG, Hopkins N. Requirements for green fluorescent protein detection in transgenic zebrafish embryos. Gene 173:99-103 (1996).

(12). Peters JM, Narotsky MG, Elizondo G, Fernandez-Salguero PM, Gonzalez F J, Abbott BD. Amelioration of TCDD-induced teratogenesis in aryl hydrocarbon receptor (AhR)-null mice. Toxicol Sci 47:86-92 (1999).

(13). Westerfield M. The Zebrafish Book: A Guide for the Laboratory Use of Zebrafish (Danio rerio). Eugene, OR:University of Oregon Press, 1993.

(14). Wang W-D, Chen Y-M, Hu C-H. Detection of Ah receptor and Ah receptor nuclear translocator mRNAs in the oocytes and developing embryos of zebrafish (Danio rerio). Fish Physiol Biochem 18:49-57 (1998).

(15.) Hines RN, Mathis JM, Jacob CS. Identification of multiple regulatory elements on the human cytochrome P4501A1 gene. Carcinogenesis 9:1599-1805 (1988).

(16.) Kawajiri K, Watanabe J, Gotoh O, Tagashira Y, Sogawe K, Fujii-Kuriyama Y. Structure and drug inducibility of the human cytochrome P450C gene. Eur J Biochem 159:219-225 (1986).

(17.) Quattrochi LC, Pendurthi UR, Okino ST, Potenza C, Tukey RH. Human Cytochrome P450 4 mRNA and gene: part of a multigene family that contains Alu Sequences in its mRNA. Proc Natl Acad Sci USA 83:6731-6735 (1986).

(18.) Ko HP, Okino ST, Ma Q, Whitlock JP Jr. Dioxin-induced CYP1A1 transcription in vivo: the aromatic hydrocarbon receptor mediates transactivation, enhancer-promoter communication, and changes in chromatin structure. Mol Cell Biol 16:430-436 (1996).

(19.) Ko HP, Okino ST, Ma Q, Whitlock JP Jr. Transactivation domains facilitate promoter occupancy for the dioxininducible CYP1A1 gene in vivo. Mol Cell Biol 17:3497-3504 (1997).

(20.) Collodi P, Kamei Y, Ernst T, Miranda C, Buhler DR, Barnes DW. Culture of cells from zebrafish (Brachydanio rerio) embryo and adult tissues. Cell Biol Toxicol 8:43-61 (1992).

(21.) Goldman LR, Harnly M, Flattery J, Patterson DC; Jr, Needham LL Serum polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans among people eating contaminated home-produced eggs and beef. Environ Health Perspect 108:13-19 (1999).

(22.) Paterson GL. A simplification of the protein assay method of Lowry et al. which is generally more applicable. Anal Biochem 83:346-356 (1977).

(23.) Stuart GW, McMurray JV, Westerfield M. Replication, integration and stable germ-line transmission of foreign sequences injected into early zebrafish embryos. Development 103:403-412 (1988).

(24.) Culp P, Nusslein-Volhard C, Hopkins N. High-frequency germ-line transmission of plasma DNA sequences injected into fertilized zebrafish eggs. Proc Natl Acad Sci USA 88:7953-7957 (1991).

(25). Juchau MR, Chen H. Developmental enzymology: xenobiotic biotransformation. In: Handbook of Developmental Neurotoxicology (Slikker W Jr, Chang LW, ads). San Diego, CA:Academic Press, Inc., 1998;321-337.

(26.) Poellinger L. Mechanism of signal transduction by the basic helix-loop-helix dioxin receptor. In: Inducible Gene Expression, Vol 1 (Baeuerle PA, ed). Boston, MA: Birkhauser, 1995;177-205.

(27.) Kimmel CB, Ballard WW, Kimmel SR, Ullman B, Schilling TF. Stages of embryonic development of the zebrafish. Dev Dyn 203:253-310 (1995).

(28) Zamir E, Kam Z, Yarden A. Transcription-dependent induction of G1 phase during the zebrafish midblastula transition. Mol Cell Biol 17:529-536 (1997).

(29.) Nebert DW, Gonzalez FJ. P450 genes: structure, evolution, and regulation. Annu Rev Biochem 56:945-993 (1987).

(30.) Nebert DW, Nelson DR, Feyereisen R. Evolution of the cytochrome P450 genes. Xenobiotica 19:1149-1160 (1989).

(31.) Gray LE, Ostby JS. In utero 2,3,7,8-tetrachlorodibenzo-pdioxin (TCDD) alters reproductive morphology and function in female rat offspring. Toxicol Appl Pharmacol 133:285-294 (1995).

(32). Gray LE Jr, Kelce WR, Monosson E, Ostby JS, Birnbaum LS. Exposure to TCDD during development permanently alters reproductive function in male Long Evans rats and hamsters: reduced ejaculated and epididymal sperm numbers and sex accessory gland weights in offspring with normal androgenic status. Toxicol Appl Pharmacol 131:108-118 (1995).

(33.) Henry TR, Spitsbergen JM, Hornung MW, Abnet CC, Peterson RE. Early life stage toxicity of 2,3,7,8-TCDD in zebra fish (Danio rerio). Toxicol Appl Pharmacol 142:56-68 (1997).

(34.) Spitsbergen JM, Walker MK, 01son JR, Peterson RE. Pathologic alterations in early life stages of Lake Trout, Salvelinus namaycush, exposed to TCDD as fertilized eggs. Aquat Toxicol 19:41-72 (1991).

(35.) Walker MK, Pollenz RS, Smith SM. Expression of aryl hydrocarbon receptor (AhR) and AhR nuclear translocator during chick cardiogenesis is consistent with 2,3,7,8tetrachlorodibenzo-p-dioxin-induced heart defects. Toxicol Appl Pharmacol 143:407-419 (1997).

(36.) Lahvis GP, Lindell SL, Thomas RS, McCuskey RS, Murphy C, Glover E, Bentz M, Southard J, Bradfield CA. Portosystemic shunting and persistent fetal vascular structures in aryl hydrocarbon receptor-deficient mice. Proc Natl Acad Sci USA 97:10442-10447 (2000).

Carolyn J. Mattingly, (1) * John A. McLachlan, (1) and William A. Toscano, Jr. (1,2)

(1) Interdisciplinary Program in Molecular Cellular Toxicology, Tulane University, Center for Bioenvironmental Research, New Orleans, Louisiana, USA; (2)Division of Environmental and Occupational Health, School of Public Health, University of Minnesota, Minneapolis, Minnesota, USA

Address correspondence to W.A. Toscano, Jr., School of Public Health, EOH, MMC 807 Mayo Building, Suite 1260, 420 Delaware St, SE, Minneapolis, MN 55455 USA. Telephone: (612) 624-2967. Fax: (612) 626-4837. E-mail: tosca001@

* Current address: Health Science Communications, New York, NY.

This work was supported by grants from the Department of Defense/DoD: DSWA01-96-1-0004.

Received 21 November 2000; accepted 26 February 2001.
COPYRIGHT 2001 National Institute of Environmental Health Sciences
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2001, Gale Group. All rights reserved. Gale Group is a Thomson Corporation Company.

Article Details
Printer friendly Cite/link Email Feedback
Author:Toscano, William A., Jr.
Publication:Environmental Health Perspectives
Date:Aug 1, 2001
Previous Article:Neuropsychologic effects of long-term exposure to pesticides: results from the French phytoner study. (Articles).
Next Article:An exploratory analysis of the effect of pesticide exposure on the risk of spontaneous abortion in an Ontario farm population. (Children's Health...

Related Articles
The shape of more colors to come.
It came from Earth: green-blooded fish.
Monkey See, Monkey Glow.
Use of reporter genes and vertebrate DNA motifs in transgenic zebrafish as sentinels for assessing aquatic pollution. (Correspondence).
Developmental toxicology of cadmium in living embryos of a stable transgenic zebrafish line. (Articles).
Biomedical/biotechnology section. (Senior Division 2002).
Flavonoids as aryl hydrocarbon receptor agonists/antagonists: effects of structure and cell context.
Unraveling gene-gene interactions regulated by ligands of the aryl hydrocarbon receptor *.
Synergistic embryotoxicity of polycyclic aromatic hydrocarbon aryl hydrocarbon receptor agonists with cytochrome p4501a inhibitors in fundulus...
Aryl hydrocarbon receptor-independent toxicity of weathered crude oil during fish development.

Terms of use | Privacy policy | Copyright © 2019 Farlex, Inc. | Feedback | For webmasters