孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性

庄太凤, 韩建, 刘丽玉, 华江环. 孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性[J]. 环境化学, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902
引用本文: 庄太凤, 韩建, 刘丽玉, 华江环. 孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性[J]. 环境化学, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902
ZHUANG Taifeng, HAN Jian, LIU Liyu, HUA Jianghuan. Reproductive toxicity caused by co-exposure of zebrafish to progestin megestrol acetate and estrogen 17α-ethinylestradiol[J]. Environmental Chemistry, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902
Citation: ZHUANG Taifeng, HAN Jian, LIU Liyu, HUA Jianghuan. Reproductive toxicity caused by co-exposure of zebrafish to progestin megestrol acetate and estrogen 17α-ethinylestradiol[J]. Environmental Chemistry, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902

孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性

  • 基金项目:

    山东省自然科学基金三院联合基金(ZR2015YL013)资助.

Reproductive toxicity caused by co-exposure of zebrafish to progestin megestrol acetate and estrogen 17α-ethinylestradiol

  • Fund Project: Supported by the Natural Science Foundation of Shandong Province (ZR2015YL013).
  • 摘要: 水生生物往往暴露于多种环境激素(如孕激素、雌激素)的混合物中,然而关于多种环境激素对鱼类的联合作用效应的研究较少.孕激素醋酸甲地孕酮(MTA)和雌激素乙炔雌二醇(EE2)是应用广泛的高活性药物,普遍存在于水环境中,二者均能引起鱼类的生殖毒性效应.本文研究了环境相关浓度的MTA和EE2复合暴露对斑马鱼的生殖毒性效应.将斑马鱼成鱼暴露于MTA(33,100 ng·L-1)、EE2(5,15 ng·L-1)以及二者的混合物(MTA + EE2:33 + 5 ng·L-1,100 + 15 ng·L-1)21 d,结果显示,EE2(15 ng·L-1)单独及与MTA(100 ng·L-1)复合暴露显著降低斑马鱼的产卵量;MTA、EE2单独及复合暴露均显著降低雌鱼血浆中雌二醇(E2)、睾酮(T)及雄鱼血浆中11-酮基睾酮(11-KT)的含量;EE2单独及与MTA复合暴露导致斑马鱼卵巢的组织学变化(抑制卵子发生,诱导卵泡闭锁),但对精巢影响较小.此外,复合暴露组中斑马鱼的产卵量、血浆性激素含量、性腺组织学变化与EE2单独暴露组相比均无显著差异.本研究表明,MTA和EE2复合暴露可引起斑马鱼的生殖毒性,其中EE2发挥主要毒性作用.本研究结果对于水环境中多种激素复合暴露的风险评估具有重要意义.
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  • [1] 赵砚彬,胡建英.环境孕激素和糖皮质激素的生态毒理效应:进展与展望 [J].生态毒理学报,2016,11(2):6-17.

    ZHAO Y B, HU J Y. Ecotoxicology of environmental progestogens and glucocorticoids: A short review [J]. Asian Journal of Ecotoxicology, 2016, 11(2): 6-17 (in Chinese).

    [2] SUMPTER J P, JOHNSON A C. Lessons from endocrine disruption and their application to other issues concerning trace organics in the aquatic environment [J]. Environmental Science & Technology, 39(12): 4321-4332.
    [3] ZHAO Y, CASTIGLIONI S, FENT K. Synthetic progestins medroxyprogesterone acetate and dydrogesterone and their binary mixtures adversely affect reproduction and lead to histological and transcriptional alterations in zebrafish (Danio rerio) [J]. Environmental Science & Technology, 2015, 49(7): 4636-4645.
    [4] ARIS A Z, SHAMSUDDIN A S, PRAVEENA S M. Occurrence of 17α-ethynylestradiol (EE2) in the environment and effect on exposed biota: A review [J]. Environment International, 2014, 69: 104-119.
    [5] MILLA S, DEPIEREUX S, KESTEMONT P. The effects of estrogenic and androgenic endocrine disruptors on the immune system of fish: A review [J]. Ecotoxicology, 2011, 20(2): 305-309.
    [6] RUNNALLS T J, BERESFORD N, LOSTY E, et al. Several synthetic progestins with different potencies adversely affect reproduction of fish [J]. Environmental Science & Technology, 2013, 47(4): 2077-2084.
    [7] FENT K. Progestins as endocrine disrupters in aquatic ecosystems: Concentrations, effects and risk assessment [J]. Environment International, 2015, 84: 115-130.
    [8] ROSSIER N M, CHEW G, ZHANG K, et al. Activity of binary mixtures of drospirenone with progesterone and 17α-ethinylestradiol in vitro and in vivo[J]. Aquatic Toxicology, 2016, 174: 109-122.
    [9] SIEGENTHALER P F, BAIN P, RIVA F, et al. Effects of antiandrogenic progestins, chlormadinone and cyproterone acetate, and the estrogen 17α-ethinylestradiol (EE2), and their mixtures: Transactivation with human and rainbowfish hormone receptors and transcriptional effects in zebrafish (Danio rerio) eleuthero-embryos [J]. Aquatic Toxicology, 2017a, 182: 142-162.
    [10] HAN J, WANG Q, WANG X, et al. The synthetic progestin megestrol acetate adversely affects zebrafish reproduction [J]. Aquatic Toxicology, 2014, 150: 66-72.
    [11] HUA J, HAN J, WANG X, et al. The binary mixtures of megestrol acetate and 17α-ethynylestradiol adversely affect zebrafish reproduction [J]. Aquatic Toxicology, 2016, 213: 776-784.
    [12] CHANG H, WAN Y, HU J. Determination and source apportionment of five classes of steroid hormones in urban rivers [J]. Environmental Science & Technology, 2009, 43(20): 7691-7698.
    [13] ZHANG K, ZHAO Y, FENT K. Occurrence and ecotoxicological effects of free, conjugated, and halogenated steroids including 17α-hydroxypregnanolone and pregnanediol in Swiss wastewater and surface water [J]. Environmental Science & Technology, 2017, 51(11): 6498-6506.
    [14] ZUCCHI S, MIRBAHAI L, CASTIGLIONI S, et al. Transcriptional and physiological responses induced by binary mixtures of drospirenone and progesterone in zebrafish (Danio rerio) at environmental concentrations [J]. Environmental Science & Technology, 2014, 48(6): 3523-3531.
    [15] RUNNALLS T J, BERESFORD N, KUGATHAS S, et al. From single chemicals to mixtures-reproductive effects of levonorgestrel and ethinylestradiol on the fathead minnow [J]. Aquatic Toxicology, 2015, 169: 152-167.
    [16] LIANG Y Q, HUANG G Y, ZHAO J L, et al. Transcriptional alterations induced by binary mixtures of ethinylestradiol and norgestrel during the early development of zebrafish (Danio rerio) [J]. Comparative Biochemistry and Physiology, Part C: Toxicology & Pharmacology, 2017, 195: 60-67.
    [17] ARGILÉS J M, ANGUERA A, STEMMLER B. A new look at an old drug for the treatment of cancer cachexia: Megestrol acetate [J]. Clinical Nutrition, 2013, 32(3): 319-324.
    [18] KAORE S N, LANGADE D K, YADAV V K, et al. Novel actions of progesterone: what we know today and what will be the scenario in the future? [J]. Journal of Pharmacy and Pharmacology, 2012, 64(8): 1040-1062.
    [19] HERREJÓN A, PALOP J, INCHAURRAGA I, et al. Low doses of megestrol acetate increase weight and improve nutrition status in patients with severe chronic obstructive pulmonary disease and weight loss [J]. Medicina Clinica, 2011, 137(5): 193-198.
    [20] LOPRINZI C L, JOHNSON P A, JENSEN M. Megestrol acetate for anorexia and cachexia [J]. Oncology, 1992, 49(Suppl 2): 46-49.
    [21] CHANG H, WAN Y, WU S, et al. Occurrence of androgens and progestogens in wastewater treatment plants and receiving river waters: comparison to estrogens [J]. Water Research, 2011, 45(2): 732-740.
    [22] FAN Z, WU S, CHANG H, et al. Behaviors of glucocorticoids, androgens and progestogens in a municipal sewage treatment plant: Comparison to estrogens [J]. Environmental Science & Technology, 2011, 45(7): 2725-2733.
    [23] ZHANG H C, YU X J, YANG W C, et al. MCX based solid phase extraction combined with liquid chromatography tandem mass spectrometry for the simultaneous determination of 31 endocrine-disrupting compounds in surface water of Shanghai [J]. Journal of Chromatography B, 2011, 879(28): 2998-3004.
    [24] CHANG H, WU S, HU J, et al. Trace analysis of androgens and progestogens in environmental waters by ultra-performance liquid chromatography-electrospray tandem mass spectrometry [J]. Journal of Chromatography A, 2008, 1195(1-2): 44-51.
    [25] AMMANN A A, MACIKOVA P, GROH K J, et al. LC-MS/MS determination of potential endocrine disruptors of cortico signalling in rivers and wastewaters [J]. Analytical and Bioanalytical Chemistry, 2014, 406(29): 7653-7665.
    [26] GÓMEZ-CANELA C, VENTURA F, CAIXACH J, et al. Occurrence of cytostatic compounds in hospital effluents and wastewaters, determined by liquid chromatography coupled to high-resolution mass spectrometry [J]. Analytical and Bioanalytical Chemistry, 2014, 406(16): 3801-3814.
    [27] PESSOA G P, DE SOUZA N C, VIDAL C B, et al. Occurrence and removal of estrogens in Brazilian wastewater treatment plants [J]. Science of the Total Environment, 2014, 490: 288-295.
    [28] YING G G, KOOKANA R S, KUMAR A, et al. Occurrence and implications of estrogens and xenoestrogens in sewage effluents and receiving waters from South East Queensland [J]. Science of the Total Environment, 2009, 407(18): 5147-5155.
    [29] SUN L, YONG W, CHU X, et al. Simultaneous determination of 15 steroidal oral contraceptives in water using solid-phase disk extraction followed by high performance liquid chromatography-tandem mass spectrometry [J]. Journal of Chromatography A, 2009, 1216(28): 5416-5123.
    [30] COLMAN J R, BALDWIN D, JOHNSON L L, et al. Effects of the synthetic estrogen, 17α-ethinylestradiol, on aggression and courtship behavior in male zebrafish (Danio rerio) [J]. Aquatic Toxicology, 2009, 91(4): 346-354.
    [31] HILL RL JR, JANZ D M. Developmental estrogenic exposure in zebrafish (Danio rerio): Effects on sex ratio and breeding success [J]. Aquatic Toxicology, 2003, 63(4): 417-429.
    [32] SANTOS E M, PAULL G C, VAN LOOK K J W, et al. Gonadal transcriptome responses and physiological consequences of exposure to oestrogen in breeding zebrafish (Danio rerio) [J]. Aquatic Toxicology, 2007, 83(2): 134-142.
    [33] WEBER L P, HILL RJ JR, JANZ D M. Developmental estrogenic exposure in zebrafish (Danio rerio): Ⅱ. Histological evaluation of gametogenesis and organ toxicity [J]. Aquatic Toxicology, 2003, 63(4): 431-446.
    [34] NASH J P, KIME D E, VAN DER VEN L T, et al. Long-term exposure to environmental concentrations of the pharmaceutical ethynylestradiol causes failure in fish [J]. Environmental Health Perspectives, 2004, 112(17): 1725-1733.
    [35] VAN DEN BELT K, VERHEYEN R, WITTERS H. Reproductive effects of ethynylestradiol and 4t-octylphenol on the zebrafish (Danio rerio) [J]. Archives of Environmental Contamination and Toxicology, 2001, 41(4): 458-467.
    [36] COE T S, HAMILTON P B, HODGSON D, et al. An environmental estrogen alters reproductive hierarchies, disrupting sexual selection in group-spawning fish [J]. Environmental Science & Technology, 2008, 42(13): 5020-5025.
    [37] VAN DEN BELT K, WESTER P W, VAN DER VEN L T, et al. Effects of ethynylestradiol on the reproductive physiology in zebrafish (Danio rerio): time dependency and reversibility [J]. Environmental Toxicology and Chemistry, 2002, 21(4): 767-775.
    [38] ANKLEY G T, JENSEN K M, KAHL M D, et al. Description and evaluation of a short-term reproduction test with the fathead minnow (Pimephales promelas) [J]. Environmental Toxicology and Chemistry, 2001, 20(6): 1276-1290.
    [39] WANG Q, LAM J C, HAN J, et al. Developmental exposure to the organophosphorus flame retardant tris(1,3-dichloro-2-propyl) phosphate: Estrogenic activity, endocrine disruption and reproductive effects on zebrafish [J]. Aquatic Toxicology, 2015, 160: 163-171.
    [40] ZEILINGER J, STEGER-HARTMANN T, MASER E, et al. Effects of synthetic gestagens on fish reproduction [J]. Environmental Toxicology and Chemistry, 2009, 28(12): 2663-2670.
    [41] VERSONNEN B J, ARIJS K, VERSLYCKE T, et al. In vitro and in vivo estrogenicity and toxicity of o-, m-, and p-dichlorobenzene [J]. Environmental Toxicology and Chemistry, 2003, 22(2): 329-335.
    [42] FLORES-VALVERDE A M, HORWOOD J, HILL E M. Disruption of the steroid metabolome in fish caused by exposure to the environmental estrogen 17α-ethinylestradiol [J]. Environmental Science & Technology, 2010, 44(9): 3552-3558.
    [43] PAWLOWSKI S, VAN AERLE R, TYLER C R, et al. Effects of 17a-ethinylestradiol in a fathead minnow (Pimephales promelas) gonadal recrudescence assay [J]. Ecotoxicology and Environmental Safety, 2004, 57(3): 330-345.
    [44] DEQUATTRO Z A, PEISSIG E J, ANTKIEWICZ D S, et al. Effects of progesterone on reproduction and embryonic development in the fathead minnow (Pimephales promelas) [J]. Environmental Toxicology and Chemistry, 2012, 31(4): 851-856.
    [45] FRANKEL T E, MEYER M T, KOLPIN D W, et al. Exposure to the contraceptive progestin, gestodene, alters reproductive behavior, arrests egg deposition, and masculinizes development in the fathead minnow (Pimephales promelas) [J]. Environmental Science & Technology, 2016, 50(11): 5991-5999.
    [46] PAULOS P, RUNNALLS T J, NALLANI G, et al. Reproductive responses in fathead minnow and Japanese medaka following exposure to a synthetic progestin, Norethindrone [J]. Aquatic Toxicology, 2010, 99(2): 256-262.
    [47] SIEGENTHALER P F, ZHAO Y, ZHANG K, et al. Reproductive and transcriptional effects of the antiandrogenic progestin chlormadinone acetate in zebrafish (Danio rerio) [J]. Environmental Pollution, 2017b, 223: 346-356.
    [48] ZHAO Y, CASTIGLIONI S, FENT K. Environmental progestins progesterone and drospirenone alter the circadian rhythm network in zebrafish (Danio rerio) [J]. Environmental Science & Technology, 2015b, 49(16): 10155-10164.
    [49] SCHINDLER A E, CAMPAGNOLI C, DRUCKMANN R, et al. Reprint of classification and pharmacology of progestins [J]. Maturitas, 2008, 61: 171-180.
    [50] ANKLEY G T, BENCIC D C, BREEN M S, et al. Endocrine disrupting chemicals in fish: Developing exposure indicators and predictive models of effects based on mechanism of action [J]. Aquatic Toxicology, 2009, 92(3): 168-178.
    [51] JI K, HONG S, KHO Y, et al. Effects of bisphenol S exposure on endocrine functions and reproduction of zebrafish [J]. Environmental Toxicology and Chemistry, 2013, 47(15): 8793-8800.
    [52] ZHOU B S. Adverse outcome pathway: Framework, application, and challenges in chemical risk assessment [J]. Journal of Environmental Sciences, 2015, 35: 191-193.
    [53] KROUPOVA H K, TRUBIROHA A, LORENZ C, et al. The progestin levonorgestrel disrupts gonadotropin expression and sex steroid levels in pubertal roach (Rutilus rutilus) [J]. Aquatic Toxicology, 2014, 154: 154-162.
    [54] ATTEKE C, VETILLARD A, FOSTIER A, et al. Effects of progesterone and estradiol on the reproductive axis in immature diploid and triploid rainbow trout [J]. Comparative Biochemistry and Physiology Part A: Molecular & Integrative Physiology, 2003, 134(4): 693-705.
    [55] SCHULTZ I R, SKILLMAN A, NICOLAS J M, et al. Short-term exposure to 17α-ethynylestradiol decreases the fertility of sexually maturing male rainbow trout (Oncorhynchus mykiss) [J]. Environmental Toxicology and Chemistry, 2003, 22: 1272-1280.
    [56] PETERS R E M, COURTENAY S C, CAGAMPAN S, et al. Effects on reproductive potential and endocrine status in the mummichog (Fundulus heteroclitus) after exposure to 17 alpha-ethynylestradiol in a short-term reproductive bioassay [J]. Aquatic Toxicology, 2007, 85: 154-166.
    [57] BLVTHGEN N, CASTIGLIONI S, SUMPTER J P, et al. Effects of low concentrations of the antiprogestin mifepristone (RU486) in adults and embryos of zebrafish (Danio rerio): 1. Reproductive and early developmental effects [J]. Aquatic Toxicology, 2013, 144: 83-95.
    [58] TYLER C R, SUMPTER J P. Oocyte growth and development in teleosts [J]. Reviews in Fish Biology and Fisheries, 1996, 6: 287-318.
    [59] PAPOULIAS D M, NOLTIE D B, TILLITT D E. An in vivo model fish system to test chemical effects on sexual differentiation and development: Exposure to ethinylestradiol [J]. Aquatic Toxicology, 1999, 48: 37-50.
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  • 收稿日期:  2017-06-29
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庄太凤, 韩建, 刘丽玉, 华江环. 孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性[J]. 环境化学, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902
引用本文: 庄太凤, 韩建, 刘丽玉, 华江环. 孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性[J]. 环境化学, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902
ZHUANG Taifeng, HAN Jian, LIU Liyu, HUA Jianghuan. Reproductive toxicity caused by co-exposure of zebrafish to progestin megestrol acetate and estrogen 17α-ethinylestradiol[J]. Environmental Chemistry, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902
Citation: ZHUANG Taifeng, HAN Jian, LIU Liyu, HUA Jianghuan. Reproductive toxicity caused by co-exposure of zebrafish to progestin megestrol acetate and estrogen 17α-ethinylestradiol[J]. Environmental Chemistry, 2017, 36(7): 1440-1450. doi: 10.7524/j.issn.0254-6108.2017.07.2017062902

孕激素醋酸甲地孕酮和雌激素乙炔雌二醇复合暴露对斑马鱼的生殖毒性

  • 1.  首都医科大学附属北京妇产医院, 北京, 100026;
  • 2.  山东省科学院生物研究所, 济南, 250014;
  • 3.  北京理工大学材料学院, 北京, 100081;
  • 4.  湖北中医药大学基础医学院, 武汉, 430065;
  • 5.  中国科学院水生生物研究所, 淡水生态与生物技术国家重点实验室, 武汉, 430072
基金项目:

山东省自然科学基金三院联合基金(ZR2015YL013)资助.

摘要: 水生生物往往暴露于多种环境激素(如孕激素、雌激素)的混合物中,然而关于多种环境激素对鱼类的联合作用效应的研究较少.孕激素醋酸甲地孕酮(MTA)和雌激素乙炔雌二醇(EE2)是应用广泛的高活性药物,普遍存在于水环境中,二者均能引起鱼类的生殖毒性效应.本文研究了环境相关浓度的MTA和EE2复合暴露对斑马鱼的生殖毒性效应.将斑马鱼成鱼暴露于MTA(33,100 ng·L-1)、EE2(5,15 ng·L-1)以及二者的混合物(MTA + EE2:33 + 5 ng·L-1,100 + 15 ng·L-1)21 d,结果显示,EE2(15 ng·L-1)单独及与MTA(100 ng·L-1)复合暴露显著降低斑马鱼的产卵量;MTA、EE2单独及复合暴露均显著降低雌鱼血浆中雌二醇(E2)、睾酮(T)及雄鱼血浆中11-酮基睾酮(11-KT)的含量;EE2单独及与MTA复合暴露导致斑马鱼卵巢的组织学变化(抑制卵子发生,诱导卵泡闭锁),但对精巢影响较小.此外,复合暴露组中斑马鱼的产卵量、血浆性激素含量、性腺组织学变化与EE2单独暴露组相比均无显著差异.本研究表明,MTA和EE2复合暴露可引起斑马鱼的生殖毒性,其中EE2发挥主要毒性作用.本研究结果对于水环境中多种激素复合暴露的风险评估具有重要意义.

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