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Jeon YS, Sangiovanni J, Boulanger E, Crump D, Liu P, Ewald J, Basu N, Xia J, Hecker M, Head J. Hepatic Transcriptomic Responses to Ethinylestradiol in Embryonic Japanese Quail and Double-Crested Cormorant. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2023. [PMID: 38116984 DOI: 10.1002/etc.5811] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/30/2023] [Revised: 11/15/2023] [Accepted: 12/13/2023] [Indexed: 12/21/2023]
Abstract
Understanding species differences in sensitivity to toxicants is a critical issue in ecotoxicology. We recently established that double-crested cormorant (DCCO) embryos are more sensitive than Japanese quail (JQ) to the developmental effects of ethinylestradiol (EE2). We explored how this difference in sensitivity between species is reflected at a transcriptomic level. The EE2 was dissolved in dimethyl sulfoxide and injected into the air cell of eggs prior to incubation at nominal concentrations of 0, 3.33, and 33.3 µg/g egg weight. At midincubation (JQ 9 days; DCCO 16 days), livers were collected from five embryos/treatment group for RNA sequencing. Data were processed and analyzed using EcoOmicsAnalyst and ExpressAnalyst. The EE2 exposure dysregulated 238 and 1,987 genes in JQ and DCCO, respectively, with 78 genes in common between the two species. These included classic biomarkers of estrogen exposure such as vitellogenin and apovitellenin. We also report DCCO-specific dysregulation of Phase I/II enzyme-coding genes and species-specific transcriptional ontogeny of vitellogenin-2. Twelve Kyoto Encyclopedia of Genes and Genomes pathways and two EcoToxModules were dysregulated in common in both species including the peroxisome proliferator-activated receptor (PPAR) signaling pathway and fatty acid metabolism. Similar to previously reported differences at the organismal level, DCCO were more responsive to EE2 exposure than JQ at the gene expression level. Our description of differences in transcriptional responses to EE2 in early life stage birds may contribute to a better understanding of the molecular basis for species differences. Environ Toxicol Chem 2024;00:1-12. © 2023 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals LLC on behalf of SETAC.
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Affiliation(s)
- Yeon-Seon Jeon
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Jonathan Sangiovanni
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Emily Boulanger
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Doug Crump
- Ecotoxicology and Wildlife Health Division, National Wildlife Research Centre, Environment and Climate Change Canada, Ottawa, Ontario, Canada
| | - Peng Liu
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Jessica Ewald
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Niladri Basu
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Jianguo Xia
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
| | - Markus Hecker
- School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
| | - Jessica Head
- Department of Natural Resource Sciences, Faculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada
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2
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Identifying multiscale translational safety biomarkers using a network-based systems approach. iScience 2023; 26:106094. [PMID: 36895646 PMCID: PMC9988559 DOI: 10.1016/j.isci.2023.106094] [Citation(s) in RCA: 2] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 08/11/2022] [Revised: 11/30/2022] [Accepted: 01/26/2023] [Indexed: 02/03/2023] Open
Abstract
Animal testing is the current standard for drug and chemicals safety assessment, but hazards translation to human is uncertain. Human in vitro models can address the species translation but might not replicate in vivo complexity. Herein, we propose a network-based method addressing these translational multiscale problems that derives in vivo liver injury biomarkers applicable to in vitro human early safety screening. We applied weighted correlation network analysis (WGCNA) to a large rat liver transcriptomic dataset to obtain co-regulated gene clusters (modules). We identified modules statistically associated with liver pathologies, including a module enriched for ATF4-regulated genes as associated with the occurrence of hepatocellular single-cell necrosis, and as preserved in human liver in vitro models. Within the module, we identified TRIB3 and MTHFD2 as a novel candidate stress biomarkers, and developed and used BAC-eGFPHepG2 reporters in a compound screening, identifying compounds showing ATF4-dependent stress response and potential early safety signals.
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3
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Pognan F, Steger-Hartmann T, Díaz C, Blomberg N, Bringezu F, Briggs K, Callegaro G, Capella-Gutierrez S, Centeno E, Corvi J, Drew P, Drewe WC, Fernández JM, Furlong LI, Guney E, Kors JA, Mayer MA, Pastor M, Piñero J, Ramírez-Anguita JM, Ronzano F, Rowell P, Saüch-Pitarch J, Valencia A, van de Water B, van der Lei J, van Mulligen E, Sanz F. The eTRANSAFE Project on Translational Safety Assessment through Integrative Knowledge Management: Achievements and Perspectives. Pharmaceuticals (Basel) 2021; 14:ph14030237. [PMID: 33800393 PMCID: PMC7999019 DOI: 10.3390/ph14030237] [Citation(s) in RCA: 7] [Impact Index Per Article: 2.3] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 01/27/2021] [Revised: 02/25/2021] [Accepted: 02/27/2021] [Indexed: 12/19/2022] Open
Abstract
eTRANSAFE is a research project funded within the Innovative Medicines Initiative (IMI), which aims at developing integrated databases and computational tools (the eTRANSAFE ToxHub) that support the translational safety assessment of new drugs by using legacy data provided by the pharmaceutical companies that participate in the project. The project objectives include the development of databases containing preclinical and clinical data, computational systems for translational analysis including tools for data query, analysis and visualization, as well as computational models to explain and predict drug safety events.
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Affiliation(s)
- François Pognan
- Preclinical Safety/Translational Medicine, Novartis, 4057 Basel, Switzerland;
| | | | - Carlos Díaz
- Synapse Research Managers SL, 28006 Madrid, Spain;
| | | | - Frank Bringezu
- Chemical & Preclinical Safety, Merck Healthcare KGaA, 64293 Darmstadt, Germany;
| | | | - Giulia Callegaro
- Leiden Academic Centre for Drug Research (LACDR), Leiden University, 2300 RA Leiden, The Netherlands; (G.C.); (B.v.d.W.)
| | | | - Emilio Centeno
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Javier Corvi
- Barcelona Supercomputing Center (BSC), 08034 Barcelona, Spain; (S.C.-G.); (J.C.); (J.M.F.); (A.V.)
| | | | | | - José M. Fernández
- Barcelona Supercomputing Center (BSC), 08034 Barcelona, Spain; (S.C.-G.); (J.C.); (J.M.F.); (A.V.)
| | - Laura I. Furlong
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
- MedBioinformatics Solutions SL, 08018 Barcelona, Spain
| | - Emre Guney
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Jan A. Kors
- Department of Medical Informatics, Erasmus University Medical Center, 3015 GD Rotterdam, The Netherlands; (J.A.K.); (J.v.d.L.); (E.v.M.)
| | - Miguel Angel Mayer
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Manuel Pastor
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Janet Piñero
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Juan Manuel Ramírez-Anguita
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Francesco Ronzano
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Philip Rowell
- Lhasa Limited, Leeds LS11 5PS, UK; (K.B.); (W.C.D.); (P.R.)
| | - Josep Saüch-Pitarch
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
| | - Alfonso Valencia
- Barcelona Supercomputing Center (BSC), 08034 Barcelona, Spain; (S.C.-G.); (J.C.); (J.M.F.); (A.V.)
- Catalan Institution for Research and Advanced Studies (ICREA), 08010 Barcelona, Spain
| | - Bob van de Water
- Leiden Academic Centre for Drug Research (LACDR), Leiden University, 2300 RA Leiden, The Netherlands; (G.C.); (B.v.d.W.)
| | - Johan van der Lei
- Department of Medical Informatics, Erasmus University Medical Center, 3015 GD Rotterdam, The Netherlands; (J.A.K.); (J.v.d.L.); (E.v.M.)
| | - Erik van Mulligen
- Department of Medical Informatics, Erasmus University Medical Center, 3015 GD Rotterdam, The Netherlands; (J.A.K.); (J.v.d.L.); (E.v.M.)
| | - Ferran Sanz
- GRIB, Hospital del Mar Institute of Medical Research (IMIM), DCEXS, Pompeu Fabra University (UPF), 08003 Barcelona, Spain; (E.C.); (L.I.F.); (E.G.); (M.A.M.); (M.P.); (J.P.); (J.M.R.-A.); (F.R.); (J.S.-P.)
- Correspondence:
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Faheem M, Bhandari RK. Detrimental Effects of Bisphenol Compounds on Physiology and Reproduction in Fish: A Literature Review. ENVIRONMENTAL TOXICOLOGY AND PHARMACOLOGY 2021; 81:103497. [PMID: 32950715 DOI: 10.1016/j.etap.2020.103497] [Citation(s) in RCA: 35] [Impact Index Per Article: 11.7] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/01/2020] [Revised: 08/24/2020] [Accepted: 09/11/2020] [Indexed: 06/11/2023]
Abstract
Bisphenol-A is one of the most studied endocrine-chemicals, which is widely used all over the world in plastic manufacture. Because of its extensive use, it has become one of the most abundant chemical environmental pollutants, especially in aquatic environments. BPA is known to affect fish reproduction via estrogen receptors but many studies advocate that BPA affects almost all aspects of fish physiology. The possible modes of action include genomic, as well as and non-genomic mechanisms, estrogen, androgen, and thyroid receptor-mediated effects. Due to the high detrimental effects of BPA, various analogs of BPA are being used as alternatives. Recent evidence suggests that the analogs of BPA have similar modes of action, with accompanying effects on fish physiology and reproduction. In this review, a detailed comparison of effects produced by BPA and analogs and their mode of action is discussed.
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5
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Bhagat J, Singh N, Nishimura N, Shimada Y. A comprehensive review on environmental toxicity of azole compounds to fish. CHEMOSPHERE 2021; 262:128335. [PMID: 33182121 DOI: 10.1016/j.chemosphere.2020.128335] [Citation(s) in RCA: 36] [Impact Index Per Article: 12.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/04/2020] [Revised: 09/04/2020] [Accepted: 09/11/2020] [Indexed: 06/11/2023]
Abstract
BACKGROUND Azoles are considered as one of the most efficient fungicides for the treatment of humans, animals, and plant fungal pathogens. They are of significant clinical importance as antifungal drugs and are widely used in personal care products, ultraviolet stabilizers, and in aircraft for its anti-corrosive properties. The prevalence of azole compounds in the natural environment and its accumulation in fish raises questions about its impact on aquatic organisms. OBJECTIVES The objective of this paper is to review the scientific studies on the effects of azole compounds in fish and to discuss future opportunities for the risk evaluation. METHODS A systematic literature search was conducted on Web of Science, PubMed, and ScienceDirect to locate peer-reviewed scientific articles on occurrence, environmental fate, and toxicological impact of azole fungicides on fish. RESULTS Studies included in this review provide ample evidence that azole compounds are not only commonly detected in the natural environment but also cause several detrimental effects on fish. Future studies with environmentally relevant concentrations of azole alone or in combination with other commonly occurring contaminants in a multigenerational study could provide a better understanding. CONCLUSION Based on current knowledge and studies reporting adverse biological effects of azole on fish, considerable attention is required for better management and effective ecological risk assessment of these emerging contaminants.
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Affiliation(s)
- Jacky Bhagat
- Graduate School of Regional Innovation Studies, Mie University, Tsu, Mie, 514-8507, Japan; Mie University Zebrafish Drug Screening Center, Tsu, Mie, 514-8507, Japan.
| | - Nisha Singh
- Environment Nanoscience Laboratory, Department of Earth Science, Indian Institute of Science Education and Research, Kolkata, 741246, India.
| | - Norihiro Nishimura
- Graduate School of Regional Innovation Studies, Mie University, Tsu, Mie, 514-8507, Japan; Mie University Zebrafish Drug Screening Center, Tsu, Mie, 514-8507, Japan.
| | - Yasuhito Shimada
- Mie University Zebrafish Drug Screening Center, Tsu, Mie, 514-8507, Japan; Department of Integrative Pharmacology, Mie University Graduate School of Medicine, Tsu, Mie, 514-8507, Japan; Department of Bioinformatics, Mie University Advanced Science Research Promotion Center, Tsu, Mie, 514-8507, Japan.
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6
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McArdle ME, Freeman EL, Staveley JP, Ortego LS, Coady KK, Weltje L, Weyers A, Wheeler JR, Bone AJ. Critical Review of Read-Across Potential in Testing for Endocrine-Related Effects in Vertebrate Ecological Receptors. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2020; 39:739-753. [PMID: 32030793 PMCID: PMC7154679 DOI: 10.1002/etc.4682] [Citation(s) in RCA: 22] [Impact Index Per Article: 5.5] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 10/19/2019] [Revised: 12/01/2019] [Accepted: 02/03/2020] [Indexed: 05/21/2023]
Abstract
Recent regulatory testing programs have been designed to evaluate whether a chemical has the potential to interact with the endocrine system and could cause adverse effects. Some endocrine pathways are highly conserved among vertebrates, providing a potential to extrapolate data generated for one vertebrate taxonomic group to others (i.e., biological read-across). To assess the potential for biological read-across, we reviewed tools and approaches that support species extrapolation for fish, amphibians, birds, and reptiles. For each of the estrogen, androgen, thyroid, and steroidogenesis (EATS) pathways, we considered the pathway conservation across species and the responses of endocrine-sensitive endpoints. The available data show a high degree of confidence in the conservation of the hypothalamus-pituitary-gonadal axis between fish and mammals and the hypothalamus-pituitary-thyroid axis between amphibians and mammals. Comparatively, there is less empirical evidence for the conservation of other EATS pathways between other taxonomic groups, but this may be due to limited data. Although more information on sensitive pathways and endpoints would be useful, current developments in the use of molecular target sequencing similarity tools and thoughtful application of the adverse outcome pathway concept show promise for further advancement of read-across approaches for testing EATS pathways in vertebrate ecological receptors. Environ Toxicol Chem 2020;39:739-753. © 2020 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals, Inc. on behalf of SETAC.
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Affiliation(s)
| | | | | | - Lisa S. Ortego
- Environmental Safety, Bayer CropScienceChesterfieldMissouriUSA
| | - Katherine K. Coady
- Toxicology and Environmental Research and Consulting, Dow ChemicalMidlandMichiganUSA
| | - Lennart Weltje
- BASF SE, Agricultural Solutions‐EcotoxicologyLimburgerhofGermany
| | - Arnd Weyers
- Crop Science DivisionBayerMonheim am RheinGermany
| | | | - Audrey J. Bone
- Environmental Safety, Bayer CropScienceChesterfieldMissouriUSA
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7
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Gonçalves ÍFS, Souza TM, Vieira LR, Marchi FC, Nascimento AP, Farias DF. Toxicity testing of pesticides in zebrafish-a systematic review on chemicals and associated toxicological endpoints. ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH INTERNATIONAL 2020; 27:10185-10204. [PMID: 32062774 DOI: 10.1007/s11356-020-07902-5] [Citation(s) in RCA: 47] [Impact Index Per Article: 11.8] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/02/2019] [Accepted: 01/27/2020] [Indexed: 06/10/2023]
Abstract
The use of zebrafish (Danio rerio) has arisen as a promising biological platform for toxicity testing of pesticides such as herbicides, insecticides, and fungicides. Therefore, it is relevant to assess the use of zebrafish in models of exposure to investigate the diversity of pesticide-associated toxicity endpoints which have been reported. Thus, this review aimed to assess the recent literature on the use of zebrafish in pesticide toxicity studies to capture data on the types of pesticide used, classes of pesticides, and zebrafish life stages associated with toxicity endpoints and phenotypic observations. A total of 352 articles published between September 2012 and May 2019 were curated. The results show an increased trend in the use of zebrafish for testing the toxicity of pesticides, with a great diversity of pesticides (203) and chemical classes (58) with different applications (41) being used. Furthermore, experimental outcomes could be clustered in 13 toxicity endpoints, mainly developmental toxicity, oxidative stress, and neurotoxicity. Organophosphorus, pyrethroid, azole, and triazine were the most studied classes of pesticides and associated with various toxicity endpoints. Studies frequently opted for early life stages (embryos and larvae). Although there is an evident lack of standardization of nomenclatures and phenotypic alterations, the information gathered here highlights associations between (classes of) pesticides and endpoints, which can be used to relate mechanisms of action specific to certain classes of chemicals.
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Affiliation(s)
- Íris Flávia Sousa Gonçalves
- Laboratory of Risk Assessment for Novel Technologies, Department of Molecular Biology, Federal University of Paraiba, Campus I, CEP, João Pessoa, 58051-900, Brazil
- Post-Graduation Program in Biochemistry, Federal University of Ceara, Campus Pici, CEP, Fortaleza, 60440-900, Brazil
| | - Terezinha Maria Souza
- Department of Toxicogenomics, GROW School for Oncology and Developmental Biology, Maastricht University, Maastricht, 6229 ER, The Netherlands.
| | - Leonardo Rogério Vieira
- Post-Graduation Program in Biochemistry, Federal University of Ceara, Campus Pici, CEP, Fortaleza, 60440-900, Brazil
| | - Filipi Calbaizer Marchi
- Laboratory of Risk Assessment for Novel Technologies, Department of Molecular Biology, Federal University of Paraiba, Campus I, CEP, João Pessoa, 58051-900, Brazil
| | - Adailton Pascoal Nascimento
- Laboratory of Risk Assessment for Novel Technologies, Department of Molecular Biology, Federal University of Paraiba, Campus I, CEP, João Pessoa, 58051-900, Brazil
| | - Davi Felipe Farias
- Laboratory of Risk Assessment for Novel Technologies, Department of Molecular Biology, Federal University of Paraiba, Campus I, CEP, João Pessoa, 58051-900, Brazil.
- Post-Graduation Program in Biochemistry, Federal University of Ceara, Campus Pici, CEP, Fortaleza, 60440-900, Brazil.
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8
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Martyniuk CJ, Feswick A, Munkittrick KR, Dreier DA, Denslow ND. Twenty years of transcriptomics, 17alpha-ethinylestradiol, and fish. Gen Comp Endocrinol 2020; 286:113325. [PMID: 31733209 PMCID: PMC6961817 DOI: 10.1016/j.ygcen.2019.113325] [Citation(s) in RCA: 23] [Impact Index Per Article: 5.8] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Submit a Manuscript] [Subscribe] [Scholar Register] [Received: 08/20/2019] [Revised: 10/14/2019] [Accepted: 11/12/2019] [Indexed: 02/06/2023]
Abstract
In aquatic toxicology, perhaps no pharmaceutical has been investigated more intensely than 17alpha-ethinylestradiol (EE2), the active ingredient of the birth control pill. At the turn of the century, the fields of comparative endocrinology and endocrine disruption research witnessed the emergence of omics technologies, which were rapidly adapted to characterize potential hazards associated with exposures to environmental estrogens, such as EE2. Since then, significant advances have been made by the scientific community, and as a result, much has been learned about estrogen receptor signaling in fish from environmental xenoestrogens. Vitellogenin, the egg yolk precursor protein, was identified as a major estrogen-responsive gene, establishing itself as the premier biomarker for estrogenic exposures. Omics studies have identified a plethora of estrogen responsive genes, contributing to a wealth of knowledge on estrogen-mediated regulatory networks in teleosts. There have been ~40 studies that report on transcriptome responses to EE2 in a variety of fish species (e.g., zebrafish, fathead minnows, rainbow trout, pipefish, mummichog, stickleback, cod, and others). Data on the liver and testis transcriptomes dominate in the literature and have been the subject of many EE2 studies, yet there remain knowledge gaps for other tissues, such as the spleen, kidney, and pituitary. Inter-laboratory genomics studies have revealed transcriptional networks altered by EE2 treatment in the liver; networks related to amino acid activation and protein folding are increased by EE2 while those related to xenobiotic metabolism, immune system, circulation, and triglyceride storage are suppressed. EE2-responsive networks in other tissues are not as comprehensively defined which is a knowledge gap as regulated networks are expected to be tissue-specific. On the horizon, omics studies for estrogen-mediated effects in fish include: (1) Establishing conceptual frameworks for incorporating estrogen-responsive networks into environmental monitoring programs; (2) Leveraging in vitro and computational toxicology approaches to identify chemicals associated with estrogen receptor-mediated effects in fish (e.g., male vitellogenin production); (3) Discovering new tissue-specific estrogen receptor signaling pathways in fish; and (4) Developing quantitative adverse outcome pathway predictive models for estrogen signaling. As we look ahead, research into EE2 over the past several decades can serve as a template for the array of hormones and endocrine active substances yet to be fully characterized or discovered.
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Affiliation(s)
- Christopher J Martyniuk
- Department of Biology, University of New Brunswick, Saint John, New Brunswick, Canada; Center for Environmental & Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, University of Florida, Gainesville, FL, USA; University of Florida Genetics Institute, USA; Canadian Rivers Institute, Canada.
| | - April Feswick
- Department of Biology, University of New Brunswick, Saint John, New Brunswick, Canada; Canadian Rivers Institute, Canada
| | - Kelly R Munkittrick
- Department of Biology, University of New Brunswick, Saint John, New Brunswick, Canada; Department of Biology, Wilfrid Laurier University, Waterloo, ON, Canada; Canadian Rivers Institute, Canada
| | - David A Dreier
- Center for Environmental & Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, University of Florida, Gainesville, FL, USA; Syngenta Crop Protection, LLC, Greensboro, NC, USA
| | - Nancy D Denslow
- Center for Environmental & Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, University of Florida, Gainesville, FL, USA; University of Florida Genetics Institute, USA
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9
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Control performance of fish short term reproduction assays with fathead minnow (Pimephales promelas). Regul Toxicol Pharmacol 2019; 108:104424. [DOI: 10.1016/j.yrtph.2019.104424] [Citation(s) in RCA: 5] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 04/05/2019] [Revised: 06/19/2019] [Accepted: 07/15/2019] [Indexed: 11/17/2022]
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10
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Doering JA, Villeneuve DL, Poole ST, Blackwell BR, Jensen KM, Kahl MD, Kittelson AR, Feifarek DJ, Tilton CB, LaLone CA, Ankley GT. Quantitative Response-Response Relationships Linking Aromatase Inhibition to Decreased Fecundity are Conserved Across Three Fishes with Asynchronous Oocyte Development. ENVIRONMENTAL SCIENCE & TECHNOLOGY 2019; 53:10470-10478. [PMID: 31386814 DOI: 10.1021/acs.est.9b02606] [Citation(s) in RCA: 10] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/10/2023]
Abstract
Quantitative adverse outcome pathways (qAOPs) describe quantitative response-response relationships that can predict the probability or severity of an adverse outcome for a given magnitude of chemical interaction with a molecular initiating event. However, the taxonomic domain of applicability for these predictions is largely untested. The present study began defining this applicability for a previously described qAOP for aromatase inhibition leading to decreased fecundity developed using data from fathead minnow (Pimephales promelas). This qAOP includes quantitative response-response relationships describing plasma 17β-estradiol (E2) as a function of plasma fadrozole, plasma vitellogenin (VTG) as a function of plasma E2, and fecundity as a function of plasma VTG. These quantitative response-response relationships simulated plasma E2, plasma VTG, and fecundity measured in female zebrafish (Danio rerio) exposed to fadrozole for 21 days but not these responses measured in female Japanese medaka (Oryzias latipes). However, Japanese medaka had different basal levels of plasma E2, plasma VTG, and fecundity. Normalizing basal levels of each measurement to equal those of female fathead minnow enabled the relationships to accurately simulate plasma E2, plasma VTG, and fecundity measured in female Japanese medaka. This suggests that these quantitative response-response relationships are conserved across these three fishes when considering relative change rather than absolute measurements. The present study represents an early step toward defining the appropriate taxonomic domain of applicability and extending the regulatory applications of this qAOP.
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Affiliation(s)
- Jon A Doering
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
- National Research Council , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Daniel L Villeneuve
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Shane T Poole
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Brett R Blackwell
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Kathleen M Jensen
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Michael D Kahl
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Ashley R Kittelson
- Oak Ridge Institute of Science Education , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - David J Feifarek
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Charlene B Tilton
- Oak Ridge Institute of Science Education , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Carlie A LaLone
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
| | - Gerald T Ankley
- Mid-Continent Ecology Division , U.S. Environmental Protection Agency , Duluth , Minnesota 55804 United States
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11
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Lagadic L, Bender K, Burden N, Salinas ER, Weltje L. Recommendations for Reducing the USE of Fish and Amphibians in Endocrine-Disruption Testing of Biocides and Plant Protection Products in Europe. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2019; 15:659-662. [PMID: 31349386 PMCID: PMC6852156 DOI: 10.1002/ieam.4156] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/03/2023]
Affiliation(s)
- Laurent Lagadic
- Bayer AG, Crop Science Division, Environmental Safety, Ecotoxicology, Monheim am Rhein, Germany
| | - Katrin Bender
- Bayer AG, Crop Science Division, Environmental Safety, Ecotoxicology, Monheim am Rhein, Germany
| | | | - Edward R Salinas
- BASF SE, Agricultural Solutions - Ecotoxicology, Limburgerhof, Germany
| | - Lennart Weltje
- BASF SE, Agricultural Solutions - Ecotoxicology, Limburgerhof, Germany
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12
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Fabian E, Gomes C, Birk B, Williford T, Hernandez TR, Haase C, Zbranek R, van Ravenzwaay B, Landsiedel R. In vitro-to-in vivo extrapolation (IVIVE) by PBTK modeling for animal-free risk assessment approaches of potential endocrine-disrupting compounds. Arch Toxicol 2018; 93:401-416. [DOI: 10.1007/s00204-018-2372-z] [Citation(s) in RCA: 39] [Impact Index Per Article: 6.5] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 08/24/2018] [Accepted: 12/04/2018] [Indexed: 11/30/2022]
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13
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Browne P, Kleinstreuer NC, Ceger P, Deisenroth C, Baker N, Markey K, Thomas RS, Judson RJ, Casey W. Development of a curated Hershberger database. Reprod Toxicol 2018; 81:259-271. [PMID: 30205136 PMCID: PMC6711601 DOI: 10.1016/j.reprotox.2018.08.016] [Citation(s) in RCA: 21] [Impact Index Per Article: 3.5] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/25/2018] [Revised: 07/20/2018] [Accepted: 08/23/2018] [Indexed: 01/17/2023]
Abstract
A systematic literature review was conducted to identify Hershberger bioassays for ∼3200 chemicals including those used to validate the OECD/US EPA guideline assay, US EPA's chemicals screened for endocrine activity, and the library of chemicals run in US EPA 's ToxCast in vitro assays. For 134 chemicals that met pre-defined criteria, experimental results were extracted into a database used to characterize uncertainty in results and evaluate the concordance of the Hershberger assay with other in vivo rodent studies that measure androgen-responsive endpoints. Of 25 chemicals tested in >1 Hershberger study, 28% had disagreements between studies (i.e. ≥1 positive and ≥1 negative study), and of the 65 chemicals tested in Hershberger studies and other in vivo studies with androgen-responsive endpoints, 43% indicated disagreements, though in some cases these may be explained by differences in study designs or physiology of the animal model. Ultimately, 49 chemicals were identified with reproducible androgen pathway responses confirmed in ≥2 in vivo rodent studies that could be considered reference chemicals useful for validating alternative methods.
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Affiliation(s)
| | | | | | | | | | | | | | | | - W Casey
- NIH/NIEHS/DNTP/NICEATM, RTP, NC, USA
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14
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Kleinstreuer NC, Browne P, Chang X, Judson R, Casey W, Ceger P, Deisenroth C, Baker N, Markey K, Thomas RS. Evaluation of androgen assay results using a curated Hershberger database. Reprod Toxicol 2018; 81:272-280. [PMID: 30205137 PMCID: PMC7171594 DOI: 10.1016/j.reprotox.2018.08.017] [Citation(s) in RCA: 23] [Impact Index Per Article: 3.8] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 05/25/2018] [Revised: 07/25/2018] [Accepted: 08/23/2018] [Indexed: 12/18/2022]
Abstract
A set of 39 reference chemicals with reproducible androgen pathway effects in vivo, identified in the companion manuscript [1], were used to interrogate the performance of the ToxCast/Tox 21 androgen receptor (AR) model based on 11 high throughput assays. Cytotoxicity data and specificity confirmation assays were used to distinguish assay loss-of-function from true antagonistic signaling suppression. Overall agreement was 66% (19/29), with ten additional inconclusive chemicals. Most discrepancies were explained using in vitro to in vivo extrapolation to estimate equivalent administered doses. The AR model had 100% positive predictive value for the in vivo response, i.e. there were no false positives, and chemicals with conclusive AR model results (agonist or antagonist) were consistently positive in vivo. Considering the lack of reproducibility of the in vivo Hershberger assay, the in vitro AR model may better predict specific AR interaction and can rapidly and cost-effectively screen thousands of chemicals without using animals.
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15
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Marty MS, Borgert C, Coady K, Green R, Levine SL, Mihaich E, Ortego L, Wheeler JR, Yi KD, Zorrilla LM. Distinguishing between endocrine disruption and non-specific effects on endocrine systems. Regul Toxicol Pharmacol 2018; 99:142-158. [PMID: 30217484 DOI: 10.1016/j.yrtph.2018.09.002] [Citation(s) in RCA: 44] [Impact Index Per Article: 7.3] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 07/13/2018] [Accepted: 09/04/2018] [Indexed: 10/28/2022]
Abstract
The endocrine system is responsible for growth, development, maintaining homeostasis and for the control of many physiological processes. Due to the integral nature of its signaling pathways, it can be difficult to distinguish endocrine-mediated adverse effects from transient fluctuations, adaptive/compensatory responses, or adverse effects on the endocrine system that are caused by mechanisms outside the endocrine system. This is particularly true in toxicological studies that require generation of effects through the use of Maximum Tolerated Doses (or Concentrations). Endocrine-mediated adverse effects are those that occur as a consequence of the interaction of a chemical with a specific molecular component of the endocrine system, for example, a hormone receptor. Non-endocrine-mediated adverse effects on the endocrine system are those that occur by other mechanisms. For example, systemic toxicity, which perturbs homeostasis and affects the general well-being of an organism, can affect endocrine signaling. Some organs/tissues can be affected by both endocrine and non-endocrine signals, which must be distinguished. This paper examines in vitro and in vivo endocrine endpoints that can be altered by non-endocrine processes. It recommends an evaluation of these issues in the assessment of effects for the determination of endocrine disrupting properties of chemicals. This underscores the importance of using a formal weight of evidence (WoE) process to evaluate potential endocrine activity.
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Affiliation(s)
- M Sue Marty
- The Dow Chemical Company, Toxicology & Environmental Research and Consulting, 1803 Building, Midland, MI, 48674, USA.
| | - Chris Borgert
- Applied Pharmacology and Toxicology, Inc., C.E.H.T. Dept. Physiological Sciences, University of FL College of Veterinary Medicine, 2250 NW 24th Avenue, Gainesville, FL, 32605, USA.
| | - Katie Coady
- The Dow Chemical Company, Toxicology & Environmental Research and Consulting, 1803 Building, Midland, MI, 48674, USA.
| | - Richard Green
- Dow AgroSciences, 3b Park Square, Milton Park, Abingdon, Oxfordshire, OX14 4RN, United Kingdom.
| | - Steven L Levine
- Monsanto Company, Global Regulatory Science, 700 Chesterfield Parkway W, Chesterfield, MO, 63017, USA.
| | - Ellen Mihaich
- Environmental and Regulatory Resources, LLC, 6807 Lipscomb Drive, Durham, NC, 27712, USA.
| | - Lisa Ortego
- Bayer CropScience, 2 TW Alexander Dr, Research Triangle Park, NC, 27709, USA.
| | - James R Wheeler
- Dow AgroSciences, 3b Park Square, Milton Park, Abingdon, Oxfordshire, OX14 4RN, United Kingdom.
| | - Kun Don Yi
- Syngenta Crop Protection, LLC, 410 S Wing Rd, Greensboro, NC, 27409, USA.
| | - Leah M Zorrilla
- Bayer CropScience, 2 TW Alexander Dr, Research Triangle Park, NC, 27709, USA.
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16
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Basili D, Zhang JL, Herbert J, Kroll K, Denslow ND, Martyniuk CJ, Falciani F, Antczak P. In Silico Computational Transcriptomics Reveals Novel Endocrine Disruptors in Largemouth Bass ( Micropterus salmoides). ENVIRONMENTAL SCIENCE & TECHNOLOGY 2018; 52:7553-7565. [PMID: 29878769 DOI: 10.1021/acs.est.8b02805] [Citation(s) in RCA: 5] [Impact Index Per Article: 0.8] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/08/2023]
Abstract
In recent years, decreases in fish populations have been attributed, in part, to the effect of environmental chemicals on ovarian development. To understand the underlying molecular events we developed a dynamic model of ovary development linking gene transcription to key physiological end points, such as gonadosomatic index (GSI), plasma levels of estradiol (E2) and vitellogenin (VTG), in largemouth bass ( Micropterus salmoides). We were able to identify specific clusters of genes, which are affected at different stages of ovarian development. A subnetwork was identified that closely linked gene expression and physiological end points and by interrogating the Comparative Toxicogenomic Database (CTD), quercetin and tretinoin (ATRA) were identified as two potential candidates that may perturb this system. Predictions were validated by investigation of reproductive associated transcripts using qPCR in ovary and in the liver of both male and female largemouth bass treated after a single injection of quercetin and tretinoin (10 and 100 μg/kg). Both compounds were found to significantly alter the expression of some of these genes. Our findings support the use of omics and online repositories for identification of novel, yet untested, compounds. This is the first study of a dynamic model that links gene expression patterns across stages of ovarian development.
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Affiliation(s)
- Danilo Basili
- Institute for Integrative Biology, University of Liverpool , L69 7ZB , Liverpool , United Kingdom
| | - Ji-Liang Zhang
- Henan Open Laboratory of Key Subjects of Environmental and Animal Products Safety, College of Animal Science and Technology , Henan University of Science and Technology , Henan 471003 , China
- Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine and UF Genetics Institute , University of Florida , Gainesville , Florida 32611 , United States
| | - John Herbert
- Institute for Integrative Biology, University of Liverpool , L69 7ZB , Liverpool , United Kingdom
| | - Kevin Kroll
- Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine and UF Genetics Institute , University of Florida , Gainesville , Florida 32611 , United States
| | - Nancy D Denslow
- Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine and UF Genetics Institute , University of Florida , Gainesville , Florida 32611 , United States
| | - Christopher J Martyniuk
- Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine and UF Genetics Institute , University of Florida , Gainesville , Florida 32611 , United States
| | - Francesco Falciani
- Institute for Integrative Biology, University of Liverpool , L69 7ZB , Liverpool , United Kingdom
| | - Philipp Antczak
- Institute for Integrative Biology, University of Liverpool , L69 7ZB , Liverpool , United Kingdom
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17
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Jackovitz AM, Koistinen KA, Lent EM, Bannon DI, Quinn MJ, Johnson MS. Neuromuscular anomalies following oral exposure to 3-nitro-1,2,4-triazol-5-one (NTO) in a one-generation study with Japanese quail (Coturnix japonica). JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH. PART A 2018; 81:718-733. [PMID: 29939830 DOI: 10.1080/15287394.2018.1485123] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.2] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/08/2023]
Abstract
Substances used as explosives in munitions by the military often result in environmental releases through manufacturing, testing, training, and combat activities. The toxicity of 3-nitro-1,2,4-triazol-5-one (nitrotriazolone or NTO) was evaluated following oral exposure in Japanese quail (Coturnix japonica) to determine if environmental releases result in unacceptable risks to avian populations. In an acute test at the limit dose (2000 mg/kg), one female was ataxic, exhibited tremors, and showed signs of neurological toxicity approximately 24 h after dosing. In a subsequent one-generation study, parental generation (F0) birds were exposed orally to 1000, 500, 100, or 20mg/kg-day NTO suspended in corn oil. After 5 consecutive days of dosing, 2-week-old birds receiving 1000 mg/kg-day displayed ataxia, convulsions, backward arching of the neck (opisthotonos), and alternated between prostrate inactivity and ataxic wing activity. Birds in the 500 mg/kg-day group exhibited neuromuscular anomalies after 17 days exposure. Ultimately, all of the 1000 mg/kg-day birds and all but one of the 500 mg/kg-day birds met euthanasia criteria and were humanely euthanized prior to behavioral and reproductive evaluation. As such, first-generation (F1) birds were exposed to 100 or 20 mg/kg-day NTO. Mild neuromuscular anomalies occurred in 10% of F1 birds from the 100 mg/kg-day group, but not in birds from 20 mg/kg-day or controls in either generation. Vacuolization of cerebellum and/or the brainstem was observed on histopathologic examination in a dose-dependent manner. Therefore, brain vacuoles and neuromuscular anomalies were identified as critical endpoints in this study. A mean Benchmark Dose (BMD) for brain vacuoles of 62 mg/kg-day was derived for male and female F0-generation quail, which corresponded to a Benchmark Dose Low (BMDL10) of 35 mg/kg-day.
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Affiliation(s)
| | | | - Emily M Lent
- a Toxicology Directorate, Army Public Health Center , MD , USA
| | | | - Michael J Quinn
- a Toxicology Directorate, Army Public Health Center , MD , USA
| | - Mark S Johnson
- a Toxicology Directorate, Army Public Health Center , MD , USA
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18
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Lavelle C, Smith LC, Bisesi JH, Yu F, Silva-Sanchez C, Moraga-Amador D, Buerger AN, Garcia-Reyero N, Sabo-Attwood T, Denslow ND. Tissue-Based Mapping of the Fathead Minnow ( Pimephales promelas) Transcriptome and Proteome. Front Endocrinol (Lausanne) 2018; 9:611. [PMID: 30459712 PMCID: PMC6232228 DOI: 10.3389/fendo.2018.00611] [Citation(s) in RCA: 5] [Impact Index Per Article: 0.8] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Submit a Manuscript] [Subscribe] [Scholar Register] [Received: 07/05/2018] [Accepted: 09/26/2018] [Indexed: 12/11/2022] Open
Abstract
Omics approaches are broadly used to explore endocrine and toxicity-related pathways and functions. Nevertheless, there is still a significant gap in knowledge in terms of understanding the endocrine system and its numerous connections and intricate feedback loops, especially in non-model organisms. The fathead minnow (Pimephales promelas) is a widely used small fish model for aquatic toxicology and regulatory testing, particularly in North America. A draft genome has been published, but the amount of available genomic or transcriptomic information is still far behind that of other more broadly studied species, such as the zebrafish. Here, we used a proteogenomics approach to survey the tissue-specific proteome and transcriptome profiles in adult male fathead minnow. To do so, we generated a draft transcriptome using short and long sequencing reads from liver, testis, brain, heart, gill, head kidney, trunk kidney, and gastrointestinal tract. We identified 30,378 different putative transcripts overall, with the assembled contigs ranging in size from 264 to over 9,720 nts. Over 17,000 transcripts were >1,000 nts, suggesting a robust transcriptome that can be used to interpret RNA sequencing data in the future. We also performed RNA sequencing and proteomics analysis on four tissues, including the telencephalon, hypothalamus, liver, and gastrointestinal tract of male fish. Transcripts ranged from 0 to 600,000 copies per gene and a large portion were expressed in a tissue-specific manner. Specifically, the telencephalon and hypothalamus shared the most expressed genes, while the gastrointestinal tract and the liver were quite distinct. Using protein profiling techniques, we identified a total of 4,045 proteins in the four tissues investigated, and their tissue-specific expression pattern correlated with the transcripts at the pathway level. Similarly to the findings with the transcriptomic data, the hypothalamus and telencephalon had the highest degree of similarity in the proteins detected. The main purpose of this analysis was to generate tissue-specific omics data in order to support future aquatic ecotoxicogenomic and endocrine-related studies as well as to improve our understanding of the fathead minnow as an ecological model.
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Affiliation(s)
- Candice Lavelle
- Department of Environmental and Global Health, University of Florida, Gainesville, FL, United States
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
| | - Ley Cody Smith
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
- Department of Physiological Sciences, University of Florida, Gainesville, FL, United States
| | - Joseph H. Bisesi
- Department of Environmental and Global Health, University of Florida, Gainesville, FL, United States
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
| | - Fahong Yu
- Interdisciplinary Center for Biotechnology Research, University of Florida, Gainesville, FL, United States
| | - Cecilia Silva-Sanchez
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
- Interdisciplinary Center for Biotechnology Research, University of Florida, Gainesville, FL, United States
| | - David Moraga-Amador
- Interdisciplinary Center for Biotechnology Research, University of Florida, Gainesville, FL, United States
| | - Amanda N. Buerger
- Department of Environmental and Global Health, University of Florida, Gainesville, FL, United States
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
| | - Natàlia Garcia-Reyero
- Environmental Laboratory, US Army Engineer Research & Development Center, Vicksburg, MS, United States
| | - Tara Sabo-Attwood
- Department of Environmental and Global Health, University of Florida, Gainesville, FL, United States
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
| | - Nancy D. Denslow
- Center for Environmental and Human Toxicology, University of Florida, Gainesville, FL, United States
- Department of Physiological Sciences, University of Florida, Gainesville, FL, United States
- *Correspondence: Nancy D. Denslow
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19
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Gray LE. Twenty-five years after "Wingspread"- Environmental endocrine disruptors (EDCs) and human health. CURRENT OPINION IN TOXICOLOGY 2017; 3:40-47. [PMID: 29806043 DOI: 10.1016/j.cotox.2017.04.004] [Citation(s) in RCA: 6] [Impact Index Per Article: 0.9] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/19/2022]
Abstract
The aim of this paper is to provide the reader with a view of the Endocrine Disruptor Chemical (EDC) research field and its relevance to human health. My perspective is from working on the effects of EDCs that act via the androgen (A) or estrogen (E) signaling pathways in a regulatory agency for the last four decades with the objective of producing data that risk assessors could use to reduce the uncertainty in risk assessment. In vitro and in vivo data from our studies has contributed to regulatory agencies decision-making since the 1990s (https://www3.epa.gov/pesticides/chem_search/cleared_reviews/csr_PC-113201_7-Apr-98_238.pdf). From the start, we were evaluating the utility of in vitro and short-term in vivo effects to predict the adverse effects in developing animals [1; 2]. This approach has expanded greatly to include what is now known as Adverse Outcome Pathways (AOP) and networks (AOPn) [3; 4]. The AOP framework for the effects of chemicals that disrupt androgen signaling during sexual differentiation of the fetal male rat provides biological context for extrapolating mechanistic information from in vitro and in vivo assays in rodents to other species including humans. Such an approach has biological validity because the E and A pathways are highly conserved in vertebrates, including humans and laboratory animals.
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Affiliation(s)
- Leon Earl Gray
- US ENVIRONMENTAL PROTECTION AGENCY, 109 TW Alexander Drive, Durham, North Carolina 27705, United States
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20
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Mihaich EM, Schäfers C, Dreier DA, Hecker M, Ortego L, Kawashima Y, Dang ZC, Solomon K. Challenges in assigning endocrine-specific modes of action: Recommendations for researchers and regulators. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2017; 13:280-292. [PMID: 27976826 DOI: 10.1002/ieam.1883] [Citation(s) in RCA: 30] [Impact Index Per Article: 4.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/05/2016] [Revised: 09/22/2016] [Accepted: 12/01/2016] [Indexed: 06/06/2023]
Abstract
As regulatory programs evaluate substances for their endocrine-disrupting properties, careful study design and data interpretation are needed to distinguish between responses that are truly endocrine specific and those that are not. This is particularly important in regulatory environments where criteria are under development to identify endocrine-disrupting properties to enable hazard-based regulation. Irrespective of these processes, most jurisdictions use the World Health Organization/International Programme on Chemical Safety definition of an endocrine disruptor, requiring that a substance is demonstrated to cause a change in endocrine function that consequently leads to an adverse effect in an intact organism. Such a definition is broad, and at its most cautious might capture many general mechanisms that would not specifically denote an endocrine disruptor. In addition, endocrine responses may be adaptive in nature, designed to maintain homeostasis rather than induce an irreversible adverse effect. The likelihood of indirect effects is increased in (eco)toxicological studies that require the use of maximum tolerated concentrations or doses, which must produce some adverse effect. The misidentification of indirect effects as truly endocrine mediated has serious consequences for prompting animal- and resource-intensive testing and regulatory consequences. To minimize the risk for misidentification, an objective and transparent weight-of-evidence procedure based on biological plausibility, essentiality, and empirical evidence of key events in an adverse outcome pathway is recommended to describe the modes of action that may be involved in toxic responses in nontarget organisms. Confounding factors such as systemic toxicity, general stress, and infection can add complexity to such an evaluation and should be considered in the weight of evidence. A recommended set of questions is proffered to help guide researchers and regulators in discerning endocrine and nonendocrine responses. Although many examples provided in this study are based on ecotoxicology, the majority of the concepts and processes are applicable to both environmental and human health assessments. Integr Environ Assess Manag 2017;13:280-292. © 2016 SETAC.
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Affiliation(s)
- Ellen M Mihaich
- Environmental and Regulatory Resources, Durham, North Carolina, USA
| | | | - David A Dreier
- Center for Environmental & Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, University of Florida, Gainesville, Florida, USA
| | - Markus Hecker
- School of the Environment & Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
| | - Lisa Ortego
- Bayer CropScience, Research Triangle Park, North Carolina, USA
| | | | | | - Keith Solomon
- Centre for Toxicology, School of Environmental Sciences, University of Guelph, Guelph, Ontario, Canada
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21
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Coady KK, Biever RC, Denslow ND, Gross M, Guiney PD, Holbech H, Karouna-Renier NK, Katsiadaki I, Krueger H, Levine SL, Maack G, Williams M, Wolf JC, Ankley GT. Current limitations and recommendations to improve testing for the environmental assessment of endocrine active substances. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2017; 13:302-316. [PMID: 27791330 PMCID: PMC6059567 DOI: 10.1002/ieam.1862] [Citation(s) in RCA: 25] [Impact Index Per Article: 3.6] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/03/2016] [Revised: 09/22/2016] [Accepted: 10/20/2016] [Indexed: 05/18/2023]
Abstract
In the present study, existing regulatory frameworks and test systems for assessing potential endocrine active chemicals are described, and associated challenges are discussed, along with proposed approaches to address these challenges. Regulatory frameworks vary somewhat across geographies, but all basically evaluate whether a chemical possesses endocrine activity and whether this activity can result in adverse outcomes either to humans or to the environment. Current test systems include in silico, in vitro, and in vivo techniques focused on detecting potential endocrine activity, and in vivo tests that collect apical data to detect possible adverse effects. These test systems are currently designed to robustly assess endocrine activity and/or adverse effects in the estrogen, androgen, and thyroid hormone signaling pathways; however, there are some limitations of current test systems for evaluating endocrine hazard and risk. These limitations include a lack of certainty regarding: 1) adequately sensitive species and life stages; 2) mechanistic endpoints that are diagnostic for endocrine pathways of concern; and 3) the linkage between mechanistic responses and apical, adverse outcomes. Furthermore, some existing test methods are resource intensive with regard to time, cost, and use of animals. However, based on recent experiences, there are opportunities to improve approaches to and guidance for existing test methods and to reduce uncertainty. For example, in vitro high-throughput screening could be used to prioritize chemicals for testing and provide insights as to the most appropriate assays for characterizing hazard and risk. Other recommendations include adding endpoints for elucidating connections between mechanistic effects and adverse outcomes, identifying potentially sensitive taxa for which test methods currently do not exist, and addressing key endocrine pathways of possible concern in addition to those associated with estrogen, androgen, and thyroid signaling. Integr Environ Assess Manag 2017;13:302-316. © 2016 The Authors. Integrated Environmental Assessment and Management published by Wiley Periodicals, Inc. on behalf of Society of Environmental Toxicology & Chemistry (SETAC).
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Affiliation(s)
- Katherine K Coady
- The Dow Chemical Company, Toxicology and Environmental Research and Consulting, Midland, Michigan, USA
- Address correspondence to
| | | | - Nancy D Denslow
- Department of Physiological Sciences and Center for Environmental and Human Toxicology, University of Florida, Gainesville, Florida, USA
| | | | - Patrick D Guiney
- Molecular and Environmental Toxicology Center, University of Wisconsin, Madison, Madison, Wisconsin, USA
| | - Henrik Holbech
- Department of Biology, University of Southern Denmark, Odense M, Denmark
| | | | - Ioanna Katsiadaki
- Centre for Environment Fisheries and Aquaculture Science, Dorset, United Kingdom
| | - Hank Krueger
- Wildlife International, Division of EAG Laboratories, Easton, Maryland, USA
| | - Steven L Levine
- Global Regulatory Sciences, Monsanto Company, St Louis, Missouri, USA
| | - Gerd Maack
- German Environment Agency, Dessau-Roßlau, Germany
| | | | - Jeffrey C Wolf
- Experimental Pathology Laboratories, Sterling, Virginia, USA
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22
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Matthiessen P, Ankley GT, Biever RC, Bjerregaard P, Borgert C, Brugger K, Blankinship A, Chambers J, Coady KK, Constantine L, Dang Z, Denslow ND, Dreier DA, Dungey S, Gray LE, Gross M, Guiney PD, Hecker M, Holbech H, Iguchi T, Kadlec S, Karouna-Renier NK, Katsiadaki I, Kawashima Y, Kloas W, Krueger H, Kumar A, Lagadic L, Leopold A, Levine SL, Maack G, Marty S, Meado J, Mihaich E, Odum J, Ortego L, Parrott J, Pickford D, Roberts M, Schaefers C, Schwarz T, Solomon K, Verslycke T, Weltje L, Wheeler JR, Williams M, Wolf JC, Yamazaki K. Recommended approaches to the scientific evaluation of ecotoxicological hazards and risks of endocrine-active substances. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2017; 13:267-279. [PMID: 28127947 PMCID: PMC6069525 DOI: 10.1002/ieam.1885] [Citation(s) in RCA: 4] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/05/2016] [Revised: 09/12/2016] [Accepted: 11/28/2016] [Indexed: 05/02/2023]
Abstract
A SETAC Pellston Workshop® "Environmental Hazard and Risk Assessment Approaches for Endocrine-Active Substances (EHRA)" was held in February 2016 in Pensacola, Florida, USA. The primary objective of the workshop was to provide advice, based on current scientific understanding, to regulators and policy makers; the aim being to make considered, informed decisions on whether to select an ecotoxicological hazard- or a risk-based approach for regulating a given endocrine-disrupting substance (EDS) under review. The workshop additionally considered recent developments in the identification of EDS. Case studies were undertaken on 6 endocrine-active substances (EAS-not necessarily proven EDS, but substances known to interact directly with the endocrine system) that are representative of a range of perturbations of the endocrine system and considered to be data rich in relevant information at multiple biological levels of organization for 1 or more ecologically relevant taxa. The substances selected were 17α-ethinylestradiol, perchlorate, propiconazole, 17β-trenbolone, tributyltin, and vinclozolin. The 6 case studies were not comprehensive safety evaluations but provided foundations for clarifying key issues and procedures that should be considered when assessing the ecotoxicological hazards and risks of EAS and EDS. The workshop also highlighted areas of scientific uncertainty, and made specific recommendations for research and methods-development to resolve some of the identified issues. The present paper provides broad guidance for scientists in regulatory authorities, industry, and academia on issues likely to arise during the ecotoxicological hazard and risk assessment of EAS and EDS. The primary conclusion of this paper, and of the SETAC Pellston Workshop on which it is based, is that if data on environmental exposure, effects on sensitive species and life-stages, delayed effects, and effects at low concentrations are robust, initiating environmental risk assessment of EDS is scientifically sound and sufficiently reliable and protective of the environment. In the absence of such data, assessment on the basis of hazard is scientifically justified until such time as relevant new information is available. Integr Environ Assess Manag 2017;13:267-279. © 2017 The Authors. Integrated Environmental Assessment and Management published by Wiley Periodicals, Inc. on behalf of Society of Environmental Toxicology & Chemistry (SETAC).
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Affiliation(s)
- Peter Matthiessen
- independent Consultant, Dolfan Barn, Beulah, Llanwrtyd Wells, Powys, United Kingdom
| | | | | | - Poul Bjerregaard
- Department of Biology, University of Southern Denmark, Odense M, Denmark
| | - Christopher Borgert
- Applied Pharmacology and Toxicology, Gainesville, Florida, USA; Dept Physiol Sciences, CEHT, Univ of Florida College of Veterinary Medicine, Gainesville, Florida, USA
| | - Kristin Brugger
- DuPont Crop Protection, Stine-Haskell Research Center, Newark, New Jersey, USA
| | - Amy Blankinship
- Office of Pesticide Programs, United States Environmental Protection Agency, Washington DC
| | - Janice Chambers
- College of Veterinary Medicine, Mississippi State University, Mississippi, USA
| | - Katherine K Coady
- The Dow Chemical Company, Toxicology and Environmental Research and Consulting, Midland, Michigan, USA
| | | | | | - Nancy D Denslow
- Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, University of Florida, Gainesville, Florida, USA
| | - David A Dreier
- Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, University of Florida, Gainesville, Florida, USA
| | - Steve Dungey
- Environment Agency, Wallingford, Oxfordshire, United Kingdom
| | - L Earl Gray
- US Environmental Agency, Reproductive Toxicology Branch, Research Triangle Park, North Carolina
| | | | - Patrick D Guiney
- Molecular & Environmental Toxicology Center, University of Wisconsin, Madison, Wisconsin, USA
| | - Markus Hecker
- Toxicology Centre and School of the Environment & Sustainability, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
| | - Henrik Holbech
- Department of Biology, University of Southern Denmark, Odense M, Denmark
| | - Taisen Iguchi
- National Institute for Basic Biology, Myodaiji, Okazaki, Japan
| | - Sarah Kadlec
- University of Minnesota, Integrated Biosciences Graduate Program, Duluth, Minnesota, USA
| | | | - Ioanna Katsiadaki
- Centre for Environment Fisheries and Aquaculture Science (Cefas), Weymouth, Dorset, United Kingdom
| | | | - Werner Kloas
- Leibniz Institute of Freshwater Ecology and Inland Fisheries, Berlin, Germany
| | | | - Anu Kumar
- CSIRO, Glen Osmond, South Australia, Australia
| | - Laurent Lagadic
- Bayer AG, Crop Science Division, Environmental Safety, Ecotoxicology, Monheim am Rhein, Germany
| | | | - Steven L Levine
- Global Regulatory Sciences, Monsanto Company, St Louis, Missouri, USA
| | - Gerd Maack
- German Environment Agency (UBA), Dessau-Roßlau, Germany
| | - Sue Marty
- Dow Chemical Company, Midland, Michigan, USA
| | - James Meado
- Ecotoxicology and Environmental Fish Health Program, Northwest Fisheries Science Center, NOAA, Seattle, Washington, USA
| | - Ellen Mihaich
- Environmental and Regulatory Resources, Durham, North Carolina, USA
| | - Jenny Odum
- Regulatory Science Associates, Binley Business Park, Coventry, United Kingdom
| | - Lisa Ortego
- Bayer CropScience, Research Triangle Park, North Carolina, USA
| | - Joanne Parrott
- Environment and Climate Change Canada, Water Science and Technology Directorate, Burlington, Ontario, Canada
| | - Daniel Pickford
- Syngenta, Jealotts Hill International Research Centre, Bracknell, United Kingdom
| | - Mike Roberts
- Independent Consultant, Burnham-on-Crouch, Essex, United Kingdom
| | | | - Tamar Schwarz
- Centre for Environment Fisheries and Aquaculture Science (Cefas), Weymouth, Dorset, United Kingdom
| | - Keith Solomon
- Centre for Toxicology, School of Environmental Sciences, University of Guelph, Ontario, Canada
| | | | | | | | | | - Jeffrey C Wolf
- Experimental Pathology Laboratories, Sterling, Virginia, USA
| | - Kunihiko Yamazaki
- Department of Environmental Health, Ministry of the Environment, Tokyo, Japan
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23
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Manibusan MK, Touart LW. A comprehensive review of regulatory test methods for endocrine adverse health effects. Crit Rev Toxicol 2017; 47:433-481. [PMID: 28617201 DOI: 10.1080/10408444.2016.1272095] [Citation(s) in RCA: 19] [Impact Index Per Article: 2.7] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 01/22/2023]
Abstract
Development of new endocrine disruption-relevant test methods has been the subject of intensive research efforts for the past several decades, prompted in part by mandates in the 1996 Food Quality Protection Act (FQPA). While scientific understanding and test methods have advanced, questions remain on whether current scientific methods are capable of adequately addressing the complexities of the endocrine system for regulatory health and ecological risk assessments. The specific objective of this article is to perform a comprehensive, detailed evaluation of the adequacy of current test methods to inform regulatory risk assessments of whether a substance has the potential to perturb endocrine-related pathways resulting in human adverse effects. To that end, approximately 42 existing test guidelines (TGs) were considered in the evaluation of coverage for endocrine-related adverse effects. In addition to evaluations of whether test methods are adequate to capture endocrine-related effects, considerations of further enhancements to current test methods, along with the need to develop novel test methods to address existing test method gaps are described. From this specific evaluation, up to 35 test methods are capable of informing whether a chemical substance perturbs known endocrine related biological pathways. Based on these findings, it can be concluded that current validated test methods are adequate to discern substances that may perturb the endocrine system, resulting in an adverse health effect. Together, these test methods predominantly form the core data requirements of a typical food-use pesticide registration submission. It is recognized, however, that the current state of science is rapidly advancing and there is a need to update current test methods to include added enhancements to ensure continued coverage and public health and environmental protection.
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Affiliation(s)
| | - L W Touart
- b Equiparent Consulting , Woodbridge , VA , USA
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24
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Ankley GT, LaLone CA, Gray LE, Villeneuve DL, Hornung MW. Evaluation of the scientific underpinnings for identifying estrogenic chemicals in nonmammalian taxa using mammalian test systems. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2016; 35:2806-2816. [PMID: 27074246 DOI: 10.1002/etc.3456] [Citation(s) in RCA: 30] [Impact Index Per Article: 3.8] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/25/2016] [Revised: 04/03/2016] [Accepted: 04/08/2016] [Indexed: 05/02/2023]
Abstract
The US Environmental Protection Agency has responsibility for assessing endocrine activity of more than 10 000 chemicals, a task that cannot reasonably be achieved solely through use of available mammalian and nonmammalian in vivo screening assays. Hence, it has been proposed that chemicals be prioritized for in vivo testing using data from in vitro high-throughput assays for specific endocrine system targets. Recent efforts focused on potential estrogenic chemicals-specifically those that activate estrogen receptor-alpha (ERα)-have broadly demonstrated feasibility of the approach. However, a major uncertainty is whether prioritization based on mammalian (primarily human) high-throughput assays accurately reflects potential chemical-ERα interactions in nonmammalian species. The authors conducted a comprehensive analysis of cross-species comparability of chemical-ERα interactions based on information concerning structural attributes of estrogen receptors, in vitro binding and transactivation data for ERα, and the effects of a range of chemicals on estrogen-signaling pathways in vivo. Overall, this integrated analysis suggests that chemicals with moderate to high estrogenic potency in mammalian systems also should be priority chemicals in nonmammalian vertebrates. However, the degree to which the prioritization approach might be applicable to invertebrates is uncertain because of a lack of knowledge of the biological role(s) of possible ERα orthologs found in phyla such as annelids. Further, comparative analysis of in vitro data for fish and reptiles suggests that mammalian-based assays may not effectively capture ERα interactions for low-affinity chemicals in all vertebrate classes. Environ Toxicol Chem 2016;35:2806-2816. Published 2016 Wiley Periodicals Inc. on behalf of SETAC. This article is a US Government work and, as such, is in the public domain in the United States of America.
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Affiliation(s)
- Gerald T Ankley
- Mid-Continent Ecology Division, US Environmental Protection Agency, Duluth, Minnesota.
| | - Carlie A LaLone
- Mid-Continent Ecology Division, US Environmental Protection Agency, Duluth, Minnesota
| | - L Earl Gray
- Toxicity Assessment Division, US Environmental Protection Agency, Research Triangle Park, North Carolina
| | - Daniel L Villeneuve
- Mid-Continent Ecology Division, US Environmental Protection Agency, Duluth, Minnesota
| | - Michael W Hornung
- Mid-Continent Ecology Division, US Environmental Protection Agency, Duluth, Minnesota
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25
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Cote I, Andersen ME, Ankley GT, Barone S, Birnbaum LS, Boekelheide K, Bois FY, Burgoon LD, Chiu WA, Crawford-Brown D, Crofton KM, DeVito M, Devlin RB, Edwards SW, Guyton KZ, Hattis D, Judson RS, Knight D, Krewski D, Lambert J, Maull EA, Mendrick D, Paoli GM, Patel CJ, Perkins EJ, Poje G, Portier CJ, Rusyn I, Schulte PA, Simeonov A, Smith MT, Thayer KA, Thomas RS, Thomas R, Tice RR, Vandenberg JJ, Villeneuve DL, Wesselkamper S, Whelan M, Whittaker C, White R, Xia M, Yauk C, Zeise L, Zhao J, DeWoskin RS. The Next Generation of Risk Assessment Multi-Year Study-Highlights of Findings, Applications to Risk Assessment, and Future Directions. ENVIRONMENTAL HEALTH PERSPECTIVES 2016; 124:1671-1682. [PMID: 27091369 PMCID: PMC5089888 DOI: 10.1289/ehp233] [Citation(s) in RCA: 62] [Impact Index Per Article: 7.8] [Reference Citation Analysis] [Abstract] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/12/2015] [Revised: 10/30/2015] [Accepted: 03/29/2016] [Indexed: 05/19/2023]
Abstract
BACKGROUND The Next Generation (NexGen) of Risk Assessment effort is a multi-year collaboration among several organizations evaluating new, potentially more efficient molecular, computational, and systems biology approaches to risk assessment. This article summarizes our findings, suggests applications to risk assessment, and identifies strategic research directions. OBJECTIVE Our specific objectives were to test whether advanced biological data and methods could better inform our understanding of public health risks posed by environmental exposures. METHODS New data and methods were applied and evaluated for use in hazard identification and dose-response assessment. Biomarkers of exposure and effect, and risk characterization were also examined. Consideration was given to various decision contexts with increasing regulatory and public health impacts. Data types included transcriptomics, genomics, and proteomics. Methods included molecular epidemiology and clinical studies, bioinformatic knowledge mining, pathway and network analyses, short-duration in vivo and in vitro bioassays, and quantitative structure activity relationship modeling. DISCUSSION NexGen has advanced our ability to apply new science by more rapidly identifying chemicals and exposures of potential concern, helping characterize mechanisms of action that influence conclusions about causality, exposure-response relationships, susceptibility and cumulative risk, and by elucidating new biomarkers of exposure and effects. Additionally, NexGen has fostered extensive discussion among risk scientists and managers and improved confidence in interpreting and applying new data streams. CONCLUSIONS While considerable uncertainties remain, thoughtful application of new knowledge to risk assessment appears reasonable for augmenting major scope assessments, forming the basis for or augmenting limited scope assessments, and for prioritization and screening of very data limited chemicals. Citation: Cote I, Andersen ME, Ankley GT, Barone S, Birnbaum LS, Boekelheide K, Bois FY, Burgoon LD, Chiu WA, Crawford-Brown D, Crofton KM, DeVito M, Devlin RB, Edwards SW, Guyton KZ, Hattis D, Judson RS, Knight D, Krewski D, Lambert J, Maull EA, Mendrick D, Paoli GM, Patel CJ, Perkins EJ, Poje G, Portier CJ, Rusyn I, Schulte PA, Simeonov A, Smith MT, Thayer KA, Thomas RS, Thomas R, Tice RR, Vandenberg JJ, Villeneuve DL, Wesselkamper S, Whelan M, Whittaker C, White R, Xia M, Yauk C, Zeise L, Zhao J, DeWoskin RS. 2016. The Next Generation of Risk Assessment multiyear study-highlights of findings, applications to risk assessment, and future directions. Environ Health Perspect 124:1671-1682; http://dx.doi.org/10.1289/EHP233.
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Affiliation(s)
- Ila Cote
- National Center for Environmental Assessment, U.S. Environmental Protection Agency (EPA), Washington, District of Columbia, USA
- Address correspondence to I. Cote, U.S. Environmental Protection Agency, Region 8, Room 8152, 1595 Wynkoop St., Denver, CO 80202-1129 USA. Telephone: (202) 288-9539. E-mail:
| | | | - Gerald T. Ankley
- National Health and Environmental Effects Research Laboratory, U.S. EPA, Duluth, Minnesota, USA
| | - Stanley Barone
- Office of Chemical Safety and Pollution Prevention, U.S. EPA, Washington, District of Columbia, USA
| | - Linda S. Birnbaum
- National Institute of Environmental Health Sciences, and
- National Toxicology Program, National Institutes of Health (NIH), Department of Health and Human Services (DHHS), Research Triangle Park, North Carolina, USA
| | - Kim Boekelheide
- Department of Pathology and Laboratory Medicine, Brown University, Providence, Rhode Island, USA
| | - Frederic Y. Bois
- Unité Modèles pour l’Écotoxicologie et la Toxicologie, Institut National de l’Environnement Industriel et des Risques, Verneuil en Halatte, France
| | - Lyle D. Burgoon
- U.S. Army Engineer Research and Development Center, Research Triangle Park, North Carolina, USA
| | - Weihsueh A. Chiu
- Department of Veterinary Integrative Biosciences, College of Veterinary Medicine and Biomedical Sciences, Texas A&M University, College Station, Texas, USA
| | | | | | - Michael DeVito
- National Institute of Environmental Health Sciences, and
- National Toxicology Program, National Institutes of Health (NIH), Department of Health and Human Services (DHHS), Research Triangle Park, North Carolina, USA
| | - Robert B. Devlin
- National Health and Environmental Effects Research Laboratory, U.S. EPA, Research Triangle Park, North Carolina, USA
| | - Stephen W. Edwards
- National Health and Environmental Effects Research Laboratory, U.S. EPA, Research Triangle Park, North Carolina, USA
| | | | - Dale Hattis
- George Perkins Marsh Institute, Clark University, Worcester, Massachusetts, USA
| | | | - Derek Knight
- European Chemicals Agency, Annankatu, Helsinki, Finland
| | - Daniel Krewski
- McLaughlin Centre for Population Health Risk Assessment, University of Ottawa, Ottawa, Ontario, Canada
| | - Jason Lambert
- National Center for Environmental Assessment, U.S. EPA, Cincinnati, Ohio, USA
| | - Elizabeth Anne Maull
- National Institute of Environmental Health Sciences, and
- National Toxicology Program, National Institutes of Health (NIH), Department of Health and Human Services (DHHS), Research Triangle Park, North Carolina, USA
| | - Donna Mendrick
- National Center for Toxicological Research, Food and Drug Administration, Jefferson, Arkansas, USA
| | | | - Chirag Jagdish Patel
- Department of Biomedical Informatics, Harvard Medical School, Boston, Massachusetts, USA
| | - Edward J. Perkins
- U.S. Army Engineer Research and Development Center, Vicksburg, Mississippi, USA
| | - Gerald Poje
- Grant Consulting Group, Washington, District of Columbia, USA
| | | | - Ivan Rusyn
- Department of Veterinary Integrative Biosciences, College of Veterinary Medicine and Biomedical Sciences, Texas A&M University, College Station, Texas, USA
| | - Paul A. Schulte
- Education and Information Division, National Institute for Occupational Safety and Health, Centers for Disease Control and Prevention, Cincinnati, Ohio, USA
| | - Anton Simeonov
- National Center for Advancing Translational Sciences, NIH, DHHS, Bethesda, Maryland, USA
| | - Martyn T. Smith
- Division of Environmental Health Sciences, School of Public Health, University of California, Berkeley, Berkeley, California, USA
| | - Kristina A. Thayer
- National Institute of Environmental Health Sciences, and
- National Toxicology Program, National Institutes of Health (NIH), Department of Health and Human Services (DHHS), Research Triangle Park, North Carolina, USA
| | | | - Reuben Thomas
- Gladstone Institutes, University of California, San Francisco, San Francisco, California, USA
| | - Raymond R. Tice
- National Institute of Environmental Health Sciences, and
- National Toxicology Program, National Institutes of Health (NIH), Department of Health and Human Services (DHHS), Research Triangle Park, North Carolina, USA
| | - John J. Vandenberg
- National Center for Environmental Assessment, U.S. Environmental Protection Agency (EPA), Washington, District of Columbia, USA
| | - Daniel L. Villeneuve
- National Health and Environmental Effects Research Laboratory, U.S. EPA, Duluth, Minnesota, USA
| | - Scott Wesselkamper
- National Center for Environmental Assessment, U.S. EPA, Cincinnati, Ohio, USA
| | - Maurice Whelan
- Systems Toxicology Unit, European Commission Joint Research Centre, Ispra, Italy
| | - Christine Whittaker
- Education and Information Division, National Institute for Occupational Safety and Health, Centers for Disease Control and Prevention, Cincinnati, Ohio, USA
| | - Ronald White
- Center for Effective Government, Washington, District of Columbia, USA
| | - Menghang Xia
- National Center for Advancing Translational Sciences, NIH, DHHS, Bethesda, Maryland, USA
| | - Carole Yauk
- Environmental Health Science and Research Bureau, Health Canada, Ottawa, Ontario, Canada
| | - Lauren Zeise
- Office of Environmental Health Hazard Assessment, California EPA, Oakland, California, USA
| | - Jay Zhao
- National Center for Environmental Assessment, U.S. EPA, Cincinnati, Ohio, USA
| | - Robert S. DeWoskin
- National Center for Environmental Assessment, U.S. Environmental Protection Agency (EPA), Washington, District of Columbia, USA
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26
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Rohr JR, Salice CJ, Nisbet RM. The pros and cons of ecological risk assessment based on data from different levels of biological organization. Crit Rev Toxicol 2016; 46:756-84. [PMID: 27340745 PMCID: PMC5141515 DOI: 10.1080/10408444.2016.1190685] [Citation(s) in RCA: 52] [Impact Index Per Article: 6.5] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 01/31/2016] [Revised: 05/12/2016] [Accepted: 05/13/2016] [Indexed: 01/15/2023]
Abstract
Ecological risk assessment (ERA) is the process used to evaluate the safety of manufactured chemicals to the environment. Here we review the pros and cons of ERA across levels of biological organization, including suborganismal (e.g., biomarkers), individual, population, community, ecosystem and landscapes levels. Our review revealed that level of biological organization is often related negatively with ease at assessing cause-effect relationships, ease of high-throughput screening of large numbers of chemicals (it is especially easier for suborganismal endpoints), and uncertainty of the ERA because low levels of biological organization tend to have a large distance between their measurement (what is quantified) and assessment endpoints (what is to be protected). In contrast, level of biological organization is often related positively with sensitivity to important negative and positive feedbacks and context dependencies within biological systems, and ease at capturing recovery from adverse contaminant effects. Some endpoints did not show obvious trends across levels of biological organization, such as the use of vertebrate animals in chemical testing and ease at screening large numbers of species, and other factors lacked sufficient data across levels of biological organization, such as repeatability, variability, cost per study and cost per species of effects assessment, the latter of which might be a more defensible way to compare costs of ERAs than cost per study. To compensate for weaknesses of ERA at any particular level of biological organization, we also review mathematical modeling approaches commonly used to extrapolate effects across levels of organization. Finally, we provide recommendations for next generation ERA, submitting that if there is an ideal level of biological organization to conduct ERA, it will only emerge if ERA is approached simultaneously from the bottom of biological organization up as well as from the top down, all while employing mathematical modeling approaches where possible to enhance ERA. Because top-down ERA is unconventional, we also offer some suggestions for how it might be implemented efficaciously. We hope this review helps researchers in the field of ERA fill key information gaps and helps risk assessors identify the best levels of biological organization to conduct ERAs with differing goals.
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Affiliation(s)
| | | | - Roger M. Nisbet
- University of California at Santa Barbara, Santa Barbara, CA 93106-9620
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27
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Johnston TK, Perkins E, Ferguson DC, Cropek DM. Tissue explant coculture model of the hypothalamic-pituitary-gonadal-liver axis of the fathead minnow (Pimephales promelas) as a predictive tool for endocrine disruption. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2016; 35:2530-2541. [PMID: 26931821 DOI: 10.1002/etc.3415] [Citation(s) in RCA: 2] [Impact Index Per Article: 0.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/02/2015] [Revised: 10/19/2015] [Accepted: 02/26/2016] [Indexed: 06/05/2023]
Abstract
Endocrine-disrupting compounds (EDCs) can impact the reproductive system by interfering with the hypothalamic-pituitary-gonadal (HPG) axis. Although in vitro testing methods have been developed to screen chemicals for endocrine disruption, extrapolation of in vitro responses to in vivo action shows inconsistent accuracy. The authors describe a tissue coculture of the fathead minnow (Pimephales promelas) HPG axis and liver (HPG-L) as a tissue explant model that mimics in vivo results. Brain (hypothalamus), pituitary, gonad, and liver tissue explants from adult fish were examined for function both individually and in coculture to determine combinations and conditions that could replicate in vivo behavior. Only cocultures had the ability to respond to an EDC, trenbolone, similarly to in vivo studies, based on estradiol, testosterone, and vitellogenin production trends, where lower exposure doses suppressed hormone production but higher doses increased production, resulting in distinctive U-shaped curves. These data suggest that a coculture system with all components of the HPG-L axis can be used as a link between in vitro and in vivo studies to predict endocrine system disruption in whole organisms. This tissue-based HPG-L system acts as a flexible deconstructed version of the in vivo system for better control and examination of the minute changes in system operation and response on EDC exposure with options to isolate, interrogate, and recombine desired components. Environ Toxicol Chem 2016;35:2530-2541. Published 2016 Wiley Periodicals Inc. on behalf of SETAC. This article is a US Government work and, as such, is in the public domain in the United States of America.
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Affiliation(s)
- Theresa K Johnston
- US Army Corps of Engineers, Engineer Research and Development Center, Construction Engineering Research Laboratory, Champaign, Illinois
- Department of Comparative Biosciences, University of Illinois, Urbana, Illinois, USA
| | - Edward Perkins
- US Army Corps of Engineers, Engineer Research and Development Center, Environmental Laboratory, Vicksburg, Mississippi
| | - Duncan C Ferguson
- Department of Comparative Biosciences, University of Illinois, Urbana, Illinois, USA
| | - Donald M Cropek
- US Army Corps of Engineers, Engineer Research and Development Center, Construction Engineering Research Laboratory, Champaign, Illinois.
- Department of Comparative Biosciences, University of Illinois, Urbana, Illinois, USA.
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28
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Karmaus AL, Toole CM, Filer DL, Lewis KC, Martin MT. High-Throughput Screening of Chemical Effects on Steroidogenesis Using H295R Human Adrenocortical Carcinoma Cells. Toxicol Sci 2016; 150:323-32. [PMID: 26781511 PMCID: PMC4809454 DOI: 10.1093/toxsci/kfw002] [Citation(s) in RCA: 49] [Impact Index Per Article: 6.1] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 12/04/2022] Open
Abstract
Disruption of steroidogenesis by environmental chemicals can result in altered hormone levels causing adverse reproductive and developmental effects. A high-throughput assay using H295R human adrenocortical carcinoma cells was used to evaluate the effect of 2060 chemical samples on steroidogenesis via high-performance liquid chromatography followed by tandem mass spectrometry quantification of 10 steroid hormones, including progestagens, glucocorticoids, androgens, and estrogens. The study employed a 3 stage screening strategy. The first stage established the maximum tolerated concentration (MTC; ≥ 70% viability) per sample. The second stage quantified changes in hormone levels at the MTC whereas the third stage performed concentration-response (CR) on a subset of samples. At all stages, cells were prestimulated with 10 µM forskolin for 48 h to induce steroidogenesis followed by chemical treatment for 48 h. Of the 2060 chemical samples evaluated, 524 samples were selected for 6-point CR screening, based in part on significantly altering at least 4 hormones at the MTC. CR screening identified 232 chemical samples with concentration-dependent effects on 17β-estradiol and/or testosterone, with 411 chemical samples showing an effect on at least one hormone across the steroidogenesis pathway. Clustering of the concentration-dependent chemical-mediated steroid hormone effects grouped chemical samples into 5 distinct profiles generally representing putative mechanisms of action, including CYP17A1 and HSD3B inhibition. A distinct pattern was observed between imidazole and triazole fungicides suggesting potentially distinct mechanisms of action. From a chemical testing and prioritization perspective, this assay platform provides a robust model for high-throughput screening of chemicals for effects on steroidogenesis.
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Affiliation(s)
- Agnes L Karmaus
- *National Center for Computational Toxicology, US EPA, Research Triangle Park, North Carolina;
| | | | - Dayne L Filer
- *National Center for Computational Toxicology, US EPA, Research Triangle Park, North Carolina
| | | | - Matthew T Martin
- *National Center for Computational Toxicology, US EPA, Research Triangle Park, North Carolina;
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29
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LaLone CA, Berninger JP, Villeneuve DL, Ankley GT. Leveraging existing data for prioritization of the ecological risks of human and veterinary pharmaceuticals to aquatic organisms. Philos Trans R Soc Lond B Biol Sci 2015; 369:rstb.2014.0022. [PMID: 25405975 DOI: 10.1098/rstb.2014.0022] [Citation(s) in RCA: 38] [Impact Index Per Article: 4.2] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 12/18/2022] Open
Abstract
Medicinal innovation has led to the discovery and use of thousands of human and veterinary drugs. With this comes the potential for unintended effects on non-target organisms exposed to pharmaceuticals inevitably entering the environment. The impracticality of generating whole-organism chronic toxicity data representative of all species in the environment has necessitated prioritization of drugs for focused empirical testing as well as field monitoring. Current prioritization strategies typically emphasize likelihood for exposure (i.e. predicted/measured environmental concentrations), while incorporating only rather limited consideration of potential effects of the drug to non-target organisms. However, substantial mammalian pharmacokinetic and mechanism/mode of action (MOA) data are produced during drug development to understand drug target specificity and efficacy for intended consumers. An integrated prioritization strategy for assessing risks of human and veterinary drugs would leverage available pharmacokinetic and toxicokinetic data for evaluation of the potential for adverse effects to non-target organisms. In this reiview, we demonstrate the utility of read-across approaches to leverage mammalian absorption, distribution, metabolism and elimination data; analyse cross-species molecular target conservation and translate therapeutic MOA to an adverse outcome pathway(s) relevant to aquatic organisms as a means to inform prioritization of drugs for focused toxicity testing and environmental monitoring.
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Affiliation(s)
- Carlie A LaLone
- Water Resources Center, College of Food, Agricultural and Natural Resource Sciences, University of Minnesota, 1985 Buford Avenue, St Paul, MN 55108, USA Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, US Environmental Protection Agency, 6201 Congdon Boulevard, Duluth, MN 55804, USA
| | - Jason P Berninger
- National Research Council, 6201 Congdon Boulevard, Duluth, MN 55804, USA
| | - Daniel L Villeneuve
- Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, US Environmental Protection Agency, 6201 Congdon Boulevard, Duluth, MN 55804, USA
| | - Gerald T Ankley
- Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, US Environmental Protection Agency, 6201 Congdon Boulevard, Duluth, MN 55804, USA
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Tokarz J, Möller G, Hrabě de Angelis M, Adamski J. Steroids in teleost fishes: A functional point of view. Steroids 2015; 103:123-44. [PMID: 26102270 DOI: 10.1016/j.steroids.2015.06.011] [Citation(s) in RCA: 127] [Impact Index Per Article: 14.1] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Journal Information] [Submit a Manuscript] [Subscribe] [Scholar Register] [Received: 04/07/2015] [Revised: 06/11/2015] [Accepted: 06/15/2015] [Indexed: 01/23/2023]
Abstract
Steroid hormones are involved in the regulation of a variety of processes like embryonic development, sex differentiation, metabolism, immune responses, circadian rhythms, stress response, and reproduction in vertebrates. Teleost fishes and humans show a remarkable conservation in many developmental and physiological aspects, including the endocrine system in general and the steroid hormone related processes in particular. This review provides an overview of the current knowledge about steroid hormone biosynthesis and the steroid hormone receptors in teleost fishes and compares the findings to the human system. The impact of the duplicated genome in teleost fishes on steroid hormone biosynthesis and perception is addressed. Additionally, important processes in fish physiology regulated by steroid hormones, which are most dissimilar to humans, are described. We also give a short overview on the influence of anthropogenic endocrine disrupting compounds on steroid hormone signaling and the resulting adverse physiological effects for teleost fishes. By this approach, we show that the steroidogenesis, hormone receptors, and function of the steroid hormones are reasonably well understood when summarizing the available data of all teleost species analyzed to date. However, on the level of a single species or a certain fish-specific aspect of physiology, further research is needed.
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Affiliation(s)
- Janina Tokarz
- Helmholtz Zentrum München, German Research Center for Environmental Health, Institute of Experimental Genetics, Genome Analysis Center, Ingolstaedter Landstrasse 1, 85764 Neuherberg, Germany
| | - Gabriele Möller
- Helmholtz Zentrum München, German Research Center for Environmental Health, Institute of Experimental Genetics, Genome Analysis Center, Ingolstaedter Landstrasse 1, 85764 Neuherberg, Germany
| | - Martin Hrabě de Angelis
- Helmholtz Zentrum München, German Research Center for Environmental Health, Institute of Experimental Genetics, Genome Analysis Center, Ingolstaedter Landstrasse 1, 85764 Neuherberg, Germany; Lehrstuhl für Experimentelle Genetik, Technische Universität München, 85350 Freising-Weihenstephan, Germany; Member of German Center for Diabetes Research (DZD), Ingolstaedter Landstrasse 1, 85764 Neuherberg, Germany
| | - Jerzy Adamski
- Helmholtz Zentrum München, German Research Center for Environmental Health, Institute of Experimental Genetics, Genome Analysis Center, Ingolstaedter Landstrasse 1, 85764 Neuherberg, Germany; Lehrstuhl für Experimentelle Genetik, Technische Universität München, 85350 Freising-Weihenstephan, Germany; Member of German Center for Diabetes Research (DZD), Ingolstaedter Landstrasse 1, 85764 Neuherberg, Germany.
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Villeneuve DL, Crump D, Garcia-Reyero N, Hecker M, Hutchinson TH, LaLone CA, Landesmann B, Lettieri T, Munn S, Nepelska M, Ottinger MA, Vergauwen L, Whelan M. Adverse outcome pathway development II: best practices. Toxicol Sci 2015; 142:321-30. [PMID: 25466379 DOI: 10.1093/toxsci/kfu200] [Citation(s) in RCA: 168] [Impact Index Per Article: 18.7] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 02/06/2023] Open
Abstract
Organization of existing and emerging toxicological knowledge into adverse outcome pathway (AOP) descriptions can facilitate greater application of mechanistic data, including those derived through high-throughput in vitro, high content omics and imaging, and biomarker approaches, in risk-based decision making. The previously ad hoc process of AOP development is being formalized through development of internationally harmonized guidance and principles. The goal of this article was to outline the information content desired for formal AOP description and some rules of thumb and best practices intended to facilitate reuse and connectivity of elements of an AOP description in a knowledgebase and network context. For example, key events (KEs) are measurements of change in biological state that are indicative of progression of a perturbation toward a specified adverse outcome. Best practices for KE description suggest that each KE should be defined as an independent measurement made at a particular level of biological organization. The concept of "functional equivalence" can help guide both decisions about how many KEs to include in an AOP and the specificity with which they are defined. Likewise, in describing both KEs and evidence that supports a causal linkage or statistical association between them (ie, a key event relationship; KER), best practice is to build from and contribute to existing KE or KER descriptions in the AOP knowledgebase rather than creating redundant descriptions. The best practices proposed address many of the challenges and uncertainties related to AOP development and help promote a consistent and reliable, yet flexible approach.
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Affiliation(s)
- Daniel L Villeneuve
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Doug Crump
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Natàlia Garcia-Reyero
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Markus Hecker
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Thomas H Hutchinson
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Carlie A LaLone
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Brigitte Landesmann
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocompu
| | - Teresa Lettieri
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocompu
| | - Sharon Munn
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocompu
| | - Malgorzata Nepelska
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocompu
| | - Mary Ann Ottinger
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocompu
| | - Lucia Vergauwen
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium
| | - Maurice Whelan
- *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocomputing and Biotechnology, Mississippi State University, Starkville, MS 39762, School of the Environment and Sustainability and Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada SK S7N 5B3, School of Biological Sciences, University of Plymouth, Plymouth, Devon, PL4 8AA, UK, Water Resources Center, University of Minnesota, St. Paul, MN 55108, European Commission, Joint Research Centre, Via E. Fermi 2749, 21027 Ispra, Italy, Department of Biology and Biochemistry, University of Houston, Houston, TX 77004, Zebrafishlab, Veterinary Physiology and Biochemistry, Department of Veterinary Sciences, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Belgium *US EPA Mid-Continent Ecology Division, 6201 Congdon Blvd, Duluth, MN 55804, Environment Canada, Ecotoxicology and Wildlife Health Division, Ottawa, Ontario, Canada K1A 0H3, Institute for Genomics, Biocompu
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Versteeg DJ, Naciff JM. In response: ecotoxicogenomics addressing future needs: an industry perspective. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2015; 34:704-706. [PMID: 25809103 DOI: 10.1002/etc.2843] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.1] [Reference Citation Analysis] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/04/2023]
Affiliation(s)
- Donald J Versteeg
- Global Product Stewardship The Procter & Gamble Company Cincinnati, OH, USA
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Ankley GT, Villeneuve DL. Temporal Changes in Biological Responses and Uncertainty in Assessing Risks of Endocrine-Disrupting Chemicals: Insights from Intensive Time-Course Studies with Fish. Toxicol Sci 2015; 144:259-75. [DOI: 10.1093/toxsci/kfu320] [Citation(s) in RCA: 45] [Impact Index Per Article: 5.0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/13/2022] Open
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Kim WK, Lee SK, Park JW, Choi K, Cargo J, Schlenk D, Jung J. Integration of multi-level biomarker responses to cadmium and benzo[k]fluoranthene in the pale chub (Zacco platypus). ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY 2014; 110:121-128. [PMID: 25217733 DOI: 10.1016/j.ecoenv.2014.08.025] [Citation(s) in RCA: 22] [Impact Index Per Article: 2.2] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/02/2014] [Revised: 08/19/2014] [Accepted: 08/19/2014] [Indexed: 06/03/2023]
Abstract
The Cd exposure for 14 days significantly increased both the molecular (DNA single-strand breaks) and biochemical (metallothionein concentrations) biomarkers in the freshwater pale chub, Zacco platypus, whereas changes in the histological and physiological biomarker responses were negligible. The BkF exposure for 14 days led to significant increases in the mRNA expression of catalase and superoxide dismutase, 7-ethoxyresorufin-O-deethylase enzymatic activity and DNA single-strand breakage at the molecular and biochemical levels. In addition, exposure to 50μg/L of BkF induced histological alteration in the liver, with significant changes to the liver somatic index and condition factor at the physiological level. The integration of multi-level biomarker responses at the molecular, biochemical and physiological levels was highly correlated with the concentrations of Cd and BkF.
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Affiliation(s)
- Woo-Keun Kim
- Future Environmental Research Center, Korea Institute of Toxicology, Jinju 660-844, Korea
| | - Sung-Kyu Lee
- Future Environmental Research Center, Korea Institute of Toxicology, Jinju 660-844, Korea
| | - June-Woo Park
- Future Environmental Research Center, Korea Institute of Toxicology, Jinju 660-844, Korea
| | - Kyungho Choi
- School of Public Health, Seoul National University, Seoul 151-742, Korea
| | - Jordan Cargo
- Department of Environmental Science, University of California, Riverside, CA 92521, USA
| | - Daniel Schlenk
- Department of Environmental Science, University of California, Riverside, CA 92521, USA
| | - Jinho Jung
- Division of Environmental Science and Ecological Engineering, Korea University, Seoul 136-713, Korea.
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Ankley GT, Jensen KM. A novel framework for interpretation of data from the fish short-term reproduction assay (FSTRA) for the detection of endocrine-disrupting chemicals. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2014; 33:2529-2540. [PMID: 25098918 DOI: 10.1002/etc.2708] [Citation(s) in RCA: 30] [Impact Index Per Article: 3.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/06/2014] [Revised: 07/25/2014] [Accepted: 08/01/2014] [Indexed: 06/03/2023]
Abstract
The fish short-term reproduction assay (FSTRA) is a key component of the US Environmental Protection Agency's Endocrine Disruptor Screening Program (EDSP), which uses a weight-of-evidence analysis based on data from several assays to identify the potential for chemicals to act as agonists or antagonists of the estrogen or androgen receptors (ER and AR), or inhibitors of steroidogenic enzymes. The FSTRA considers a variety of mechanistic and apical responses in 21-d exposures with the fathead minnow (Pimephales promelas), including plasma steroid and vitellogenin (VTG; egg yolk protein) concentrations, secondary sex characteristics, gonad size and histopathology, and egg production. Although the FSTRA initially was described several years ago, recent data generation associated with implementation of the EDSP highlighted the need for more formal guidance regarding evaluation of information from the assay. The authors describe a framework for interpretation of FSTRA data relative to perturbation of endocrine pathways of concern to the EDSP. The framework considers end points individually and as suites of physiologically related responses relative to pathway identification. Sometimes changes in single end points can be highly diagnostic (e.g., induction of VTG in males by ER agonists, production of male secondary sex characteristics in females by AR agonists); in other instances, however, multiple, related end points are needed to reliably assess pathway perturbation (e.g., AR antagonism, steroid synthesis inhibition). In addition to describing an interpretive framework, the authors demonstrate its practical utility using publicly available FSTRA data for a wide range of known and hypothesized endocrine-disrupting chemicals. Environ Toxicol Chem 2014;33:2529-2540. Published 2014 Wiley Periodicals Inc., on behalf of SETAC. This article is a US government work and, as such, is in the public domain in the United States of America.
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Affiliation(s)
- Gerald T Ankley
- Mid-Continent Ecology Division, Office of Research and Development, US Environmental Protection Agency, Duluth, Minnesota
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Sébillot A, Damdimopoulou P, Ogino Y, Spirhanzlova P, Miyagawa S, Du Pasquier D, Mouatassim N, Iguchi T, Lemkine GF, Demeneix BA, Tindall AJ. Rapid fluorescent detection of (anti)androgens with spiggin-gfp medaka. ENVIRONMENTAL SCIENCE & TECHNOLOGY 2014; 48:10919-10928. [PMID: 25171099 DOI: 10.1021/es5030977] [Citation(s) in RCA: 28] [Impact Index Per Article: 2.8] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/03/2023]
Abstract
Widespread environmental antiandrogen contamination has been associated with negative impacts on biodiversity and human health. In particular, many pesticides are antiandrogenic, creating a need for robust and sensitive environmental monitoring. Our aim was to develop a sensitive and specific transgenic medaka (Oryzias latipes) model bearing an androgen responsive fluorescent reporter construct for whole organism-based environmental screening of pro- and antiandrogens. We analyzed the 5' regions of the androgen responsive three-spined stickleback (Gasterosteus aculeatus) spiggin genes in silico, revealing conserved blocks of sequence harboring androgen response elements. Identified putative promoters were cloned upstream of GFP. Germinal transgenesis with spg1-gfp led to stable medaka lines. GFP induction was exclusive to the kidney, the site of spiggin protein production in sticklebacks. Significant GFP expression was induced by three or four-day androgen treatment of newly hatched fry, but not by estrogens, mineralocorticoids, glucocorticoids or progestogens. The model responded dose-dependently to androgens, with highest sensitivity to 17MT (1.5 μg/L). In addition to flutamide, the biocides fenitrothion, vinclozolin and linuron significantly inhibited 17MT-induced GFP induction, validating the model for detection of antiandrogens. The spg1-gfp medaka model provides a sensitive, specific, and physiologically pertinent biosensor system for analyzing environmental androgen activity.
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Pinto PIS, Estêvão MD, Power DM. Effects of estrogens and estrogenic disrupting compounds on fish mineralized tissues. Mar Drugs 2014; 12:4474-94. [PMID: 25196834 PMCID: PMC4145326 DOI: 10.3390/md12084474] [Citation(s) in RCA: 42] [Impact Index Per Article: 4.2] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 04/01/2014] [Revised: 07/17/2014] [Accepted: 07/30/2014] [Indexed: 02/07/2023] Open
Abstract
Estrogens play well-recognized roles in reproduction across vertebrates, but also intervene in a wide range of other physiological processes, including mineral homeostasis. Classical actions are triggered when estrogens bind and activate intracellular estrogen receptors (ERs), regulating the transcription of responsive genes, but rapid non-genomic actions initiated by binding to plasma membrane receptors were recently described. A wide range of structurally diverse compounds from natural and anthropogenic sources have been shown to interact with and disrupt the normal functions of the estrogen system, and fish are particularly vulnerable to endocrine disruption, as these compounds are frequently discharged or run-off into waterways. The effect of estrogen disruptors in fish has mainly been assessed in relation to reproductive endpoints, and relatively little attention has been given to other disruptive actions. This review will overview the actions of estrogens in fish, including ER isoforms, their expression, structure and mechanisms of action. The estrogen functions will be considered in relation to mineral homeostasis and actions on mineralized tissues. The impact of estrogenic endocrine disrupting compounds on fish mineralized tissues will be reviewed, and the potential adverse outcomes of exposure to such compounds will be discussed. Current lacunae in knowledge are highlighted along with future research priorities.
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Affiliation(s)
- Patricia I S Pinto
- CCMAR-Centre of Marine Sciences, University of Algarve, Campus de Gambelas, Faro 8005-139, Portugal.
| | - Maria D Estêvão
- CCMAR-Centre of Marine Sciences, University of Algarve, Campus de Gambelas, Faro 8005-139, Portugal.
| | - Deborah M Power
- CCMAR-Centre of Marine Sciences, University of Algarve, Campus de Gambelas, Faro 8005-139, Portugal.
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de Peyster A, Mihaich E. Hypothesis-driven weight of evidence analysis to determine potential endocrine activity of MTBE. Regul Toxicol Pharmacol 2014; 69:348-70. [DOI: 10.1016/j.yrtph.2014.04.017] [Citation(s) in RCA: 10] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 02/05/2014] [Revised: 04/10/2014] [Accepted: 04/28/2014] [Indexed: 12/16/2022]
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Kahl MD, Villeneuve DL, Stevens K, Schroeder A, Makynen EA, LaLone CA, Jensen KM, Hughes M, Holmen BA, Eid E, Durhan EJ, Cavallin JE, Berninger J, Ankley GT. An inexpensive, temporally integrated system for monitoring occurrence and biological effects of aquatic contaminants in the field. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2014; 33:1584-95. [PMID: 24668901 DOI: 10.1002/etc.2591] [Citation(s) in RCA: 4] [Impact Index Per Article: 0.4] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 01/14/2014] [Revised: 02/26/2014] [Accepted: 03/21/2014] [Indexed: 05/03/2023]
Abstract
Assessment of potential risks of complex contaminant mixtures in the environment requires integrated chemical and biological approaches. In support of the US Great Lakes Restoration Initiative, the US Environmental Protection Agency lab in Duluth, MN, is developing these types of methods for assessing possible risks of aquatic contaminants in near-shore Great Lakes (USA) sites. One component involves an exposure system for caged fathead minnow (Pimephales promelas) adults suitable for the wide range of habitat and deployment situations encountered in and around the Great Lakes. To complement the fish exposure system, the authors developed an automated device for collection of composite water samples that could be simultaneously deployed with the cages and reflect a temporally integrated exposure of the animals. The present study describes methodological details of the design, construction, and deployment of a flexible yet comparatively inexpensive (<600 USD) caged-fish/autosampler system. The utility and performance of the system were demonstrated with data collected from deployments at several Great Lakes sites. For example, over 3 field seasons, only 2 of 130 deployed cages were lost, and approximately 99% of successfully deployed adult fish were recovered after exposures of 4 d or longer. A number of molecular, biochemical, and apical endpoints were successfully measured in recovered animals, changes in which reflected known characteristics of the study sites (e.g., upregulation of hepatic genes involved in xenobiotic metabolism in fish held in the vicinity of wastewater treatment plants). The automated composite samplers proved robust with regard to successful water collection (>95% of deployed units in the latest field season), and low within- and among-unit variations were found relative to programmed collection volumes. Overall, the test system has excellent potential for integrated chemical-biological monitoring of contaminants in a variety of field settings.
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Affiliation(s)
- Michael D Kahl
- US Environmental Protection Agency, Duluth, Minnesota, USA
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40
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Relevance Weighting of Tier 1 Endocrine Screening Endpoints by Rank Order. ACTA ACUST UNITED AC 2014; 101:90-113. [DOI: 10.1002/bdrb.21096] [Citation(s) in RCA: 31] [Impact Index Per Article: 3.1] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 11/04/2013] [Accepted: 12/30/2013] [Indexed: 12/31/2022]
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41
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Phthalates in Food Packaging, Consumer Products, and Indoor Environments. MOLECULAR AND INTEGRATIVE TOXICOLOGY 2014. [DOI: 10.1007/978-1-4471-6500-2_2] [Citation(s) in RCA: 18] [Impact Index Per Article: 1.8] [Reference Citation Analysis] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 12/19/2022]
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Lalone CA, Villeneuve DL, Burgoon LD, Russom CL, Helgen HW, Berninger JP, Tietge JE, Severson MN, Cavallin JE, Ankley GT. Molecular target sequence similarity as a basis for species extrapolation to assess the ecological risk of chemicals with known modes of action. AQUATIC TOXICOLOGY (AMSTERDAM, NETHERLANDS) 2013; 144-145:141-54. [PMID: 24177217 DOI: 10.1016/j.aquatox.2013.09.004] [Citation(s) in RCA: 78] [Impact Index Per Article: 7.1] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/30/2013] [Revised: 09/03/2013] [Accepted: 09/04/2013] [Indexed: 05/20/2023]
Abstract
It is not feasible to conduct toxicity tests with all species that may be impacted by chemical exposures. Therefore, cross-species extrapolation is fundamental to environmental risk assessment. Recognition of the impracticality of generating empirical, whole organism, toxicity data for the extensive universe of chemicals in commerce has been an impetus driving the field of predictive toxicology. We describe a strategy that leverages expanding databases of molecular sequence information together with identification of specific molecular chemical targets whose perturbation can lead to adverse outcomes to support predictive species extrapolation. This approach can be used to predict which species may be more (or less) susceptible to effects following exposure to chemicals with known modes of action (e.g., pharmaceuticals, pesticides). Primary amino acid sequence alignments are combined with more detailed analyses of conserved functional domains to derive the predictions. This methodology employs bioinformatic approaches to automate, collate, and calculate quantitative metrics associated with cross-species sequence similarity of key molecular initiating events (MIEs). Case examples focused on the actions of (a) 17α-ethinyl estradiol on the human (Homo sapiens) estrogen receptor; (b) permethrin on the mosquito (Aedes aegypti) voltage-gated para-like sodium channel; and (c) 17β-trenbolone on the bovine (Bos taurus) androgen receptor are presented to demonstrate the potential predictive utility of this species extrapolation strategy. The examples compare empirical toxicity data to cross-species predictions of intrinsic susceptibility based on analyses of sequence similarity relevant to the MIEs of defined adverse outcome pathways. Through further refinement, and definition of appropriate domains of applicability, we envision practical and routine utility for the molecular target similarity-based predictive method in chemical risk assessment, particularly where testing resources are limited.
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Affiliation(s)
- Carlie A Lalone
- U.S. Environmental Protection Agency, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Mid-Continent Ecology Division, 6201 Congdon Boulevard, Duluth, MN 55804, USA.
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Kugathas S, Runnalls TJ, Sumpter JP. Metabolic and reproductive effects of relatively low concentrations of beclomethasone dipropionate, a synthetic glucocorticoid, on fathead minnows. ENVIRONMENTAL SCIENCE & TECHNOLOGY 2013; 47:9487-9495. [PMID: 23869980 DOI: 10.1021/es4019332] [Citation(s) in RCA: 30] [Impact Index Per Article: 2.7] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/02/2023]
Abstract
Pharmaceuticals present in the aquatic environment could adversely affect aquatic organisms. Synthetic glucocorticoids (GC) are used in large quantities as anti-inflammatory drugs and have been reported to be present in river water. In order to assess the impact of environmental concentrations of GCs, an in vivo experiment was conducted with adult fathead minnows. Fish were exposed to 0.1 μg/L, 1 μg/L, or 10 μg/L beclomethasone dipropionate (BCMD) via a flow-through system over a period of 21 days. Similar duplicate tanks served as control, with no chemical added. There was a concentration-related increase in plasma glucose concentration and a decrease in blood lymphocyte count. Induction of male secondary sexual characters and a decreasing trend in plasma vitellogenin (Vtg) concentrations in female fish were observed with increasing exposure concentration of BCMD. Expression profiles of selected genes (phosphoenolpyruvate carboxykinase - PEPCK, glucocorticoid receptor - GR, and Vtg) in liver also demonstrated concentration-related effects at all three tested concentrations. The results suggest that GCs could cause effects in lower micrograms per liter concentrations that could be environmentally relevant for total GCs present in the environment. Therefore, studies to determine the environmental concentrations of GCs and no effect concentrations are needed to assess if GCs pose a risk to the aquatic environment.
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Affiliation(s)
- Subramaniam Kugathas
- Institute for the Environment, Brunel University , Uxbridge, Middlesex UB8 3PH, United Kingdom.
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