Department of Environmental Health Sciences, Arnold School of Public Health, University of South Carolina, Columbia, South Carolina 29208, USA.
Toxicol Sci. 2012 Jan;125(1):262-73. doi: 10.1093/toxsci/kfr269. Epub 2011 Oct 9.
G protein-coupled estrogen receptor 1 (GPER) is a G protein-coupled receptor (GPCR) unrelated to nuclear estrogen receptors but strongly activated by 17β-estradiol in both mammals and fish. To date, the distribution and functional characterization of GPER within reproductive and nonreproductive vertebrate organs have been restricted to juvenile and adult animals. In contrast, virtually nothing is known about the spatiotemporal distribution and function of GPER during vertebrate embryogenesis. Using zebrafish as an animal model, we investigated the potential functional role and expression of GPER during embryogenesis. Based on real-time PCR and whole-mount in situ hybridization, gper was expressed as early as 1 h postfertilization (hpf) and exhibited strong stage-dependent expression patterns during embryogenesis. At 26 and 38 hpf, gper mRNA was broadly distributed throughout the body, whereas from 50 to 98 hpf, gper expression was increasingly localized to the heart, brain, neuromasts, craniofacial region, and somite boundaries of developing zebrafish. Continuous exposure to a selective GPER agonist (G-1)-but not continuous exposure to a selective GPER antagonist (G-15)-from 5 to 96 hpf, or within three developmental windows ranging from 10 to 72 hpf, resulted in adverse concentration-dependent effects on survival, gross morphology, and somite formation within the trunk of developing zebrafish embryos. Importantly, based on co-exposure studies, G-15 blocked severe G-1-induced developmental toxicity, suggesting that G-1 toxicity is mediated via aberrant activation of GPER. Overall, our findings suggest that xenobiotic-induced GPER activation represents a potentially novel and understudied mechanism of toxicity for environmentally relevant chemicals that affect vertebrate embryogenesis.
G 蛋白偶联雌激素受体 1(GPER)是一种与核雌激素受体无关的 G 蛋白偶联受体(GPCR),但在哺乳动物和鱼类中均被 17β-雌二醇强烈激活。迄今为止,GPER 在生殖和非生殖脊椎动物器官中的分布和功能特征仅限于幼体和成年动物。相比之下,几乎没有关于 GPER 在脊椎动物胚胎发生过程中的时空分布和功能的信息。我们使用斑马鱼作为动物模型,研究了 GPER 在胚胎发生过程中的潜在功能作用和表达。基于实时 PCR 和全胚胎原位杂交,gper 在受精后 1 小时(hpf)即可表达,并在胚胎发生过程中表现出强烈的阶段依赖性表达模式。在 26 和 38 hpf 时,gper mRNA 广泛分布于全身,而从 50 到 98 hpf,gper 表达逐渐局限于心脏、大脑、神经丘、颅面部区域和发育中斑马鱼的体节边界。从 5 到 96 hpf 连续暴露于选择性 GPER 激动剂(G-1)而不是连续暴露于选择性 GPER 拮抗剂(G-15),或在 10 到 72 hpf 的三个发育窗口内,会导致对发育中斑马鱼胚胎存活率、总体形态和体节形成产生不利的浓度依赖性影响。重要的是,基于共暴露研究,G-15 阻断了 G-1 引起的严重发育毒性,表明 G-1 毒性是通过 GPER 的异常激活介导的。总的来说,我们的研究结果表明,外源性物质诱导的 GPER 激活代表了一种潜在的新的和未被充分研究的毒性机制,可能涉及影响脊椎动物胚胎发生的环境相关化学物质。