Lange Anke, Sebire Marion, Rostkowski Pawel, Mizutani Takeshi, Miyagawa Shinichi, Iguchi Taisen, Hill Elizabeth M, Tyler Charles R
University of Exeter, Biosciences, College of Life & Environmental Sciences, Exeter EX4 4QD, United Kingdom.
University of Exeter, Biosciences, College of Life & Environmental Sciences, Exeter EX4 4QD, United Kingdom; Cefas Weymouth Laboratory, Barrack Road, The Nothe, Weymouth, Dorset DT4 8UB, United Kingdom.
Aquat Toxicol. 2015 Nov;168:48-59. doi: 10.1016/j.aquatox.2015.09.014. Epub 2015 Sep 26.
Sexual disruption is reported in wild fish populations living in freshwaters receiving discharges of wastewater treatment works (WwTW) effluents and is associated primarily with the feminisation of males by exposure to oestrogenic chemicals. Antiandrogens could also contribute to the feminisation of male fish, but there are far less data supporting this hypothesis and almost nothing is known for the effects of oestrogens in combination with antiandrogens in fish. We conducted a series of in vivo exposures in two fish species to investigate the potency on reproductive-relevant endpoints of the antiandrogenic antimicrobials triclosan (TCS), chlorophene (CP) and dichlorophene (DCP) and the resin, abietic acid (AbA), all found widely in WwTW effluents. We also undertook exposures with a mixture of antiandrogens and a mixture of antiandrogens in combination with the oestrogen 17α-ethinyloestradiol (EE2). In stickleback (Gasterosteus aculeatus), DCP showed a tendency to reduce spiggin induction in females androgenised by dihydrotestosterone (DHT), but these findings were not conclusive. In roach (Rutilus rutilus), exposures to DCP (178 days), or a mixture of TCS, CP and AbA (185 days), or to the model antiandrogen flutamide (FL, 178 days) had no effect on gonadal sex ratio or on the development of the reproductive ducts. Exposure to EE2 (1.5ng/L, 185 days) induced feminisation of the ducts in 17% of the males and in the mixture of antiandrogens (TCS, CP, AbA) in combination with EE2, almost all (96%) of the males had a feminised reproductive ducts. In stickleback androgen receptor (ARα and ARβ) transactivation assays, the model antiandrogens, FL and procymidone inhibited 11-ketotestosterone (11-KT) induced receptor activation, but none of the human antiandrogens, TCS, CP, DCP and AbA had an effect. These data indicate that antimicrobial antiandrogens in combination can contribute to the feminisation process in exposed males, but they do not appear to act through the androgen receptor in fish.
据报道,生活在接纳污水处理厂(WwTW)废水排放的淡水环境中的野生鱼类种群出现了性发育紊乱,这主要与雄性鱼类因接触雌激素类化学物质而雌性化有关。抗雄激素也可能导致雄性鱼类雌性化,但支持这一假设的数据要少得多,而且对于雌激素与抗雄激素联合作用对鱼类的影响几乎一无所知。我们对两种鱼类进行了一系列体内暴露实验,以研究抗雄激素抗菌剂三氯生(TCS)、氯苯吩嗪(CP)和二氯苯醚(DCP)以及树脂松香酸(AbA)(这些物质在WwTW废水中广泛存在)对生殖相关终点指标的影响。我们还进行了抗雄激素混合物以及抗雄激素与雌激素17α-乙炔雌二醇(EE2)混合物的暴露实验。在棘鱼(Gasterosteus aculeatus)中,DCP显示出降低经二氢睾酮(DHT)雄激素化的雌性棘鱼中spiggin诱导的趋势,但这些结果并不确凿。在拟鲤(Rutilus rutilus)中,暴露于DCP(178天)、或TCS、CP和AbA的混合物(185天)、或模型抗雄激素氟他胺(FL,178天)对性腺性别比例或生殖管道发育均无影响。暴露于EE2(1.5ng/L,185天)使17%的雄性拟鲤的生殖管道出现雌性化,而在抗雄激素(TCS、CP、AbA)与EE2的混合物暴露实验中,几乎所有(96%)的雄性拟鲤都出现了生殖管道雌性化。在棘鱼雄激素受体(ARα和ARβ)反式激活实验中,模型抗雄激素氟他胺和腐霉利抑制了11-酮睾酮(11-KT)诱导的受体激活,但人类抗雄激素TCS、CP、DCP和AbA均无此作用。这些数据表明,抗菌抗雄激素联合作用可导致暴露的雄性鱼类雌性化,但它们似乎并非通过鱼类的雄激素受体发挥作用。