Svensson Johan, Mustafa Arshi, Fick Jerker, Schmitz Monika, Brunström Björn
Department of Environmental Toxicology, Uppsala University, Norbyvägen 18A, SE-75 236, Uppsala, Sweden.
Department of Comparative Physiology, Uppsala University, Norbyvägen 18A, SE-75 236 Uppsala, Sweden.
Aquat Toxicol. 2016 Aug;177:316-23. doi: 10.1016/j.aquatox.2016.06.010. Epub 2016 Jun 14.
Progestins are aquatic contaminants that in low concentrations can impair fish reproduction. The mechanisms are likely multiple since different progestins interact with other steroid receptors in addition to progesterone receptors. Puberty is the process when animals first acquire the capability to reproduce and it comprises maturation of sperm and eggs. In zebrafish, puberty is initiated around 45days post fertilization (dpf) in females and around 53-55 dpf in males, and is marked by increased production of pituitary gonadotropins. We exposed juvenile zebrafish from 20 to 80 dpf to the androgenic progestin levonorgestrel at concentrations of 5.5, 79 and 834ngL(-1) and to the non-androgenic progestin progesterone at concentrations of 3.7, 77 and 1122ngL(-1), during sexual differentiation and puberty. Levonorgestrel exposure caused 100% males even at the lowest concentration tested whereas progesterone did not affect the sex ratio. Transcript levels of the gonadal genes amh, CYP11B and CYP19a1a indicated that the masculinizing effect of levonorgestrel occurred very rapidly. Transcript concentrations of gonadotropins in pituitaries were low in control fish at 44 dpf, but high at 55 dpf and onward. In fish exposed to levonorgestrel or progesterone gonadotropin transcript concentrations were high already at 44 dpf, indicating that both progestins caused precocious puberty. Gonad histology at 50 dpf confirmed a well advanced sexual maturation, but only in males. Our results show that progestins can affect sexual development in fish and that the androgenic progestin levonorgestrel induces a male phenotype at concentrations similar to those detected in aquatic environments.
孕激素是一类水生污染物,低浓度时就能损害鱼类繁殖。其作用机制可能是多方面的,因为不同的孕激素除了与孕酮受体相互作用外,还会与其他类固醇受体相互作用。青春期是动物首次获得繁殖能力的过程,包括精子和卵子的成熟。在斑马鱼中,雌性在受精后约45天(dpf)开始进入青春期,雄性则在53 - 55 dpf左右开始,其标志是垂体促性腺激素分泌增加。在性分化和青春期期间,我们将20至80 dpf的幼年斑马鱼暴露于浓度为5.5、79和834 ngL(-1)的雄激素孕激素左炔诺孕酮以及浓度为3.7、77和1122 ngL(-1)的非雄激素孕激素孕酮中。即使在测试的最低浓度下,左炔诺孕酮暴露也导致产生了100%的雄性,而孕酮对性别比例没有影响。性腺基因amh、CYP11B和CYP19a1a的转录水平表明,左炔诺孕酮的雄性化作用发生得非常迅速。在44 dpf时,对照鱼垂体中促性腺激素的转录浓度较低,但在55 dpf及之后则较高。在暴露于左炔诺孕酮或孕酮的鱼中,促性腺激素转录浓度在44 dpf时就已经很高,这表明两种孕激素都导致了青春期早熟。50 dpf时的性腺组织学检查证实性成熟程度很高,但仅在雄性中如此。我们的结果表明,孕激素可影响鱼类的性发育,并且雄激素孕激素左炔诺孕酮在与水生环境中检测到的浓度相似时就能诱导出雄性表型。