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雄性鱼类中的雄激素信号:具有生殖障碍的抗雄激素化学物质的实例。

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

机构信息

Iranian Fisheries Science Research Institute, Agricultural Research, Education and Extension Organization, P. O. Box: 133-15745, Tehran, Iran.

School of Biology, College of Science, University of Tehran, P. O. Box: 14155-6455, Tehran, Iran.

出版信息

Theriogenology. 2019 Nov;139:58-71. doi: 10.1016/j.theriogenology.2019.07.020. Epub 2019 Jul 19.

Abstract

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 position. Compared to T, 11-KT is a nonaromatizable steroid, and does not convert to 17β-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 Arα and Arβ 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.

摘要

类似于其他脊椎动物,雄激素在鱼类中调节精子发生。在硬骨鱼中,主要的雄激素是 11-酮睾酮(11-KT),它在 C 位氧化睾酮(T)。与 T 相比,11-KT 是一种不可芳香化的类固醇,不会转化为 17β-雌二醇。然而,T 和 11-KT 的循环水平都随着睾丸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,鱼类中已经鉴定出核 Ar 和膜 Ar。在本研究中,我们综述了鱼类中的雄激素生物合成,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对鱼类生殖雄激素信号通路的干扰机制。在后一种情况下,比较了 vinclozolin(VZ)和双(2-乙基己基)邻苯二甲酸酯(DEHP)的不良影响。VZ 和 DEHP 都能降低雄性鱼类的精子质量。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 水平以及循环黄体生成素(Lh)水平的增加有关。相比之下,DEHP 抑制 11-KT 的产生,与循环 Lh 水平降低有关。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 改变了 ar mRNA 水平,而 DEHP 则没有影响。这表明 VZ 和 DEHP 以不同的方式作用于雄性鱼类,导致雄激素依赖性生殖障碍。对核 AR 的分子分析表明,哺乳动物和鱼类模型中的 DNA 和配体结合域(分别为 DBD 和 LBD)高度保守。AR 的系统发育树显示出哺乳动物和鱼类之间的明显聚类。在鱼类中,Arα和 Arβ的亚型也在不同的聚类中分开。因此,需要进一步研究以产生 ar 敲除鱼类模型,以更好地阐明 AR 通过鱼类繁殖的雄激素调节作用。

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