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Nuclear receptor targets for endocrine disrupting effects – mechanisms of action for emerging pollutants? Anders Goksøyr Prosjekt 181888 - Program Norsk miljøforskning mot 2015 onsdag 19. november 2008 1 AIMS To study the mechanisms of action of selected environmental pollutants in a comparative manner, and to elucidate evolutionary differences in chemico-biological interactions of the nuclear receptors. This knowledge may lead to new and more sensitive technologies for biological effect monitoring of environmental contaminants. onsdag 19. november 2008 2 NR Responserelevance model Based on Adams (1991) onsdag 19. november 2008 3 Fifteen Years after ʻʻWingspreadʼʼ—Environmental Endocrine Disrupters and Human and Wildlife Health: Where We are Today and Where We Need to Go Hotchkiss et al. Tox Sci 2008 onsdag 19. november 2008 4 Vitellogenin induction downstream sewage treatment works Vitellogenin (mg/ml(mg/ml) plasma) Plasma vitellogenin 0,4 0,3 0,2 0,1 0,0 upstream downstream downstream 1 km downstream 2 km Vitellogenin (mean ± SEM; mg/ml) in plasma from rainbow trout caged immediately upstream or downstream and one and two km downstream from a sewage treatment works. From Parkkonen et al., 2000. onsdag 19. november 2008 5 OH HO Estradiol-17β or estrogen mimic Hepatocyte Hsp 90 ER Hsp 90 ER ER Vtg and Zr protein ERE Vtg and Zrp genes Secretion of Vtg and Zr protein Compounds shown to act via ER Vtg and Zrp mRNA Transport to ovary and incorporation into oocytes equol ß-sitosterol Daidzein genistein biochanin A formononetin coumestrol zearalenone zearalenol o,p'-DDT o,p'-DDE ß-HCH, g-HCH 1-hydroxychlordene 4-tert-butylphenol 4-tert-octylphenol 4-tert-pentylphenol 4-nonylphenol 4-nonylphenol-diethoxylate 4-nonylphenoxy-carboxylic acid 3-trifluoromethyl-4-nitrophenol di-n-butylphthalate butylbenzylphthalate toxaphene methoxychlor ethinylestradiol diethylstilbestrol bisphenol A tert-butyl-hydroxyanisole from Goksøyr et al. (2003) onsdag 19. november 2008 6 Masculinization of mosquitofish due to pulp and paper mill effluents Masculinized mosquitofish (G. holbrooki) captured in Fenholloway River, FL. Masculinized least killifish (H. formosa). From Davis & Bortone (1992), in Colborn & Clement, eds. (1992). onsdag 19. november 2008 7 Nature 18 Sep 2008 onsdag 19. november 2008 8 Nuclear receptors members of a large superfamily of ligand-modulated transcription factors target genes involved in important and diverse biological processes such as metabolism, development and reproduction, incl. phase I (CYP genes), phase II (various transferases) and III (ABC transporters) mediate transcriptional response to sex steroids (progestins, estrogens, androgens), adrenal steroids (glucocorticoids and mineralocorticoids), vitamin D3, thyroid and retinoid hormones, and a variety of metabolic ligands loss of control of nuclear receptor signaling contributes to endocrinerelated diseases. e.g. breast cancer, prostate cancer, ovarian cancer, diabetes and obesity onsdag 19. november 2008 9 Nuclear Receptors - A Large Family of Ligand Modulated Transcription Factors Bind to specific DNA targets - Hormone Response Elements Most are activators Some constitutive Few inactivate Ligands are small lipophilic molecules that freely enter cells Diffuse from source & penetrate to a target Respond to low levels of hormone Parts per billion levels Regulation of levels is important Can be disrupted by environmental contaminants onsdag 19. november 2008 10 EDCs and nuclear receptors X PXR CAR PPAR TR VDR ER AR GR PR NR3 onsdag 19. november 2008 NR1 11 Nuclear receptors as targets for endocrine disrupting compounds ER alkylphenols, bisphenol A, lindane, DDT AR p,p’-DDT, sitosterol PXR alkylphenols, bisphenol A, chlordane, lindane CAR methoxychlor, dieldrin, DDE PPAR phtalates RXR methoprene AhR dioxins, PAHs + cross-talk Goksøyr & Male (2006) DNVA onsdag 19. november 2008 12 Is there a connection? Goksøyr (2006) JTEH *a Hepatic ERα B 2000 6 b *b *bc 3 **bc mRNA levels (% of control) 6β-OHase (pmol/min/mg protein) 9 1800 ** ** NP50 NP125 1600 1400 1200 1000 800 600 * 400 200 0 C NP10 0 Control 1 5 25 125 E2 Dose (mg 4-nonylphenol/kg fish) Steroid metabolism onsdag 19. november 2008 Estrogen receptor α 13 300 (i) E2-mimic 250 Project rationale 200 150 100 50 0 200 (ii) Hormone metabolism The focus in endocrine disruption research on steroid receptors is based on an oversimplified model. % of control 150 100 The nature of the effect of some EDCs is determined by dose-dependent routing and cross-talk between different classes of nuclear receptor 50 0 1600 (iii) Receptor levels 1200 800 400 0 0 25 50 75 100 125 Important species variation in response to different compounds makes it difficult to propose general mechanisms for biological consequences of exposure to different EDCs acting through NRs Dose of 4-nonylphenol (mg/kg) Figure 1. Dose dependent effects of NP (i) as E2mimic, (ii) modulating hormone metabolism, and (iii) modulating receptor levels (data from Atlantic salmon, from Goksøyr, 2006) onsdag 19. november 2008 14 PXR/SXR • PXR/SXR has an unusually large ligand specificity • activated by many xenobiotics, incl. PCBs • but some PCBs are PXR antagonists • the most potent antagonists are non-planar, highly chlorinated (≥6 Cl) species • large species differences exist • PXR is poorly conserved between species onsdag 19. november 2008 15 PBDEs activate hPXR (SXR) hPXR hAhR Pacyniak et al. (2007) Tox Sci onsdag 19. november 2008 16 Species specific activation of PXR - luciferase reporter assay principle Alkylphenols, NDL-PCBs, BPA, BFRs, PCN, Ketoconazole, Pharmaceuticals Cotransfect CaPO4 onsdag 19. november 2008 Cos-7 17 Species differences in NR activation (example: SXR/PXR) human dog mouse rat chicken Xenopus fathead minnow zebrafish medaka octylphenol bisphenol A chlordane p,p-DDE ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✘ ✓ ✓ ✘ ✘ ✘ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✘ ✓ ✓ ✓ ✓ ✓ ✓ ✘ ✘ ✘ toxaphene 2,4-DCP ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✘ ✘ ✘ ✘ ✘ ✘ ✘ ✘ ✘ ✓ endosulfan dybutylphthalate ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✘ ✘ ✓ ✓ ✓ ✓ ✓ ✘ ✓ ✘ ✘ ? ? ? ✓>4-fold ✘<4-fold based on Milnes et al., Environ Health Persp (2008) onsdag 19. november 2008 18 Nuclear receptors - comparative aspects X X X X X X X comparative protein-protein interacions comparative ligand specificities Shulman & Mangelsdorf (2005) NEJM ChIP-PCR onsdag 19. november 2008 ChIP-chip comparative transcriptomics ChIP-seq 19 Experimental outline of ChIP assay Target protein T DNA 5. Add protein A/G Protein A/G 1. Add 1 % formaldehyde A/G Formaldehyde crosslinked cells ab T 6. Elute DNA-protein complex 2. Cell lysis Cell lysate with crosslinked protein-DNA complexes A/G ab 3.Sonication 7.Reverse crosslinks A/G 4. Add antibody Antibody onsdag 19. november 2008 ab 8. Amplify target gene ab 20 Biphasic dose-response curves from Calabrese & Baldwin (2003) onsdag 19. november 2008 21 Biomarker discovery in Atlantic cod fry liver after continuous exposure to produced water pI control low dose PW high dose PW Mw * * medium dose PW E2 Kjersem (2007), PhD thesis onsdag 19. november 2008 22 The dose-response concept revisited 100 75 50 25 0 log [dose] The nature of the effect of some EDCs is determined by dosedependent routing and cross-talk between different modes of toxicological action - Goksøyr (2006) J Toxicol Environ Health A vol 69 onsdag 19. november 2008 23 Summary The focus in endocrine disruption research on steroid receptors is based on an oversimplified model. Nuclear receptors represent an expanded range of mediators of endocrine disrupting effects compared to previous research focus Grün and Blumberg (2006): “The link that has been forged between organotins and adipocyte differentiation opens an important new area of research into environmental influences on human health with respect to obesity and related metabolic disorders such as type 2 diabetes and cardiovascular disease” The nature of the effect of some EDCs is determined by dose-dependent routing and cross-talk between different classes of nuclear receptor Important species variation in response to different compounds makes it difficult to propose general mechanisms for biological consequences of exposure to different EDCs acting through NRs onsdag 19. november 2008 24 Project members • Anders Goksøyr, project leader • Rune Male, co-PI • Marte Rusten, post doc (at Blumberg lab, UCI, 2008-2009) • Roger Lille-Langøy, PhD student • Marianne Brattås, PhD student • Astrid Mork, Master student • Hilde Førde, Master student onsdag 19. november 2008 25 Collaborating partners •Jonathan Verreault, Canada •Ian Mayer, Dept of Biology, UoB, NO •Sonnic Meier, IMR Bergen NO •Geir Wing Gabrielsen, Norwegian Polar Institute, Tromsø NO •Lisa Bjørnsdatter Helgason, Norwegian Polar Institute, Tromsø NO •Lionel Camus, Akvaplan-niva AS, Tromsø, NO •Robert Letcher, Canada •Heli Routti, Norwegian Polar Institute, Tromsø, NO •Audun Nerland, Dept of Molecular Biology, UoB •Ole Jakob Nøstbakken, NIFES • • • • • • • • • • Anders Goksøyr & Rune Male, Department of Molecular Biology, University of Bergen, NO Marit Bakke, Department of Biomedicine, UoB, NO Gunnar Mellgren, Dept of Medicine, UoB, NO Augustine Arukwe, Dept of Biology, NTNU, Trondheim, NO Malin Celander, Dept of Zoophysiology, GU, SE Joakim Larsson, Sahlgrenska, GU, SE Helen Håkansson, KI, SE Bruce Blumberg, UC Irvine, CA, USA Eric F. Johnson, Scripps, La Jolla, CA, USA Inge Jonassen, CBU, UoB, NO onsdag 19. november 2008 26