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Androgen signaling in male fishes: Examples of anti-androgenic chemicals that cause reproductive disorders

机译:雄性鱼类中的雄激素信号:抗雄激素化学品的例子,导致生殖障碍

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Similar to other vertebrates, androgens regulate spermatogenesis in fishes. In teleosts, the main androgen is 11-Ketotestosterone (11-KT), which is oxidized testosterone (T) at the C-11 position. Compared to T, 11-KT is a nonaromatizable steroid, and does not convert to 17 beta-estradiol. However, circulatory levels of both T and 11-KT undergo seasonal variations along with testicular development. Physiological functions of androgens are mediated via androgen receptor (Ar). So far, nuclear Ar and membrane Ar have been identified in fishes. In the present study, we reviewed androgen biosynthesis in fishes, compared molecular structure of nuclear Ar in models of mammals and fishes, and investigated the mechanisms of action of environmental contaminants that differentially disrupt androgen signaling in fish reproduction. In the latter case, the adverse effects of vinclozolin (VZ) and bis(2-ethylhexyl) phthalate (DEHP) are compared. Both VZ and DEHP are capable of decreasing sperm quality in males. Vinclozolin causes an increase in 11-KT production associated with increases in kisspeptin (kiss-1) and salmon gonadotropin-releasing hormone (gnrh3) mRNA levels as well as circulatory levels of luteinizing hormone (Lh). In contrast, DEHP inhibits 11-KT production associated with a decrease in circulatory Lh levels. However, DEHP-inhibited 11-KT production is not associated with changes in kiss-1 and gnrh3 mRNA levels. Studies also show that VZ alters ar mRNA levels, while DEHP is without effect. These suggest that VZ and DEHP act differentially to cause androgen-dependent reproductive disorder in male fishes. Molecular analyses of the nuclear AR show that both DNA and ligand binding domains (DBD and LBD, respectively) are highly conserved within models of mammals and fishes. A phylogeny tree of the AR shows distinct clusters between mammals and fishes. In fishes, subtypes of Ar alpha and Ar beta are also separated in distinct clusters. Thus, further studies need to generate ar knockout fish model to better elucidate androgen regulation of reproduction in fishes via Ar. (C) 2019 Elsevier Inc. All rights reserved.
机译:与其他脊椎动物类似,雄激素调节鱼类的精子发生。硬骨鱼体内的主要雄激素是11-酮睾酮(11-KT),它是C-11位置的氧化睾酮(T)。与T相比,11-KT是一种非芳香族类固醇,不会转化为17β-雌二醇。然而,T和11-KT的循环水平随着睾丸的发育而发生季节性变化。雄激素的生理功能是通过雄激素受体(Ar)介导的。到目前为止,已经在鱼类中发现了核Ar和膜Ar。在本研究中,我们回顾了鱼类的雄激素生物合成,比较了哺乳动物和鱼类模型中核Ar的分子结构,并研究了环境污染物在鱼类繁殖中不同程度地破坏雄激素信号的作用机制。在后一种情况下,比较了vinclozolin(VZ)和邻苯二甲酸双(2-乙基己基)酯(DEHP)的不良反应。VZ和DEHP都能降低男性的精子质量。Vinclozolin导致11-KT产量增加,与kisspeptin(kiss-1)和鲑鱼促性腺激素释放激素(gnrh3)mRNA水平以及促黄体生成激素(Lh)循环水平的增加相关。相反,DEHP抑制与循环Lh水平降低相关的11-KT生成。然而,DEHP抑制的11-KT产生与kiss-1和gnrh3 mRNA水平的变化无关。研究还表明,VZ可以改变ar mRNA水平,而DEHP则不起作用。这表明VZ和DEHP在雄性鱼类中的作用不同,导致雄激素依赖性生殖障碍。核AR的分子分析表明,DNA和配体结合域(分别为DBD和LBD)在哺乳动物和鱼类模型中高度保守。AR的系统发育树显示哺乳动物和鱼类之间存在明显的集群。在鱼类中,Arα和Arβ的亚型也以不同的簇分开。因此,进一步的研究需要通过ar(C)2019 Elsevier Inc.生成ar敲除鱼类模型,以更好地阐明雄性激素对鱼类繁殖的调节。版权所有。

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