Great Lakes Toxicology and Ecology Division, US Environmental Protection Agency, Duluth, Minnesota, USA.
Great Lakes Toxicology and Ecology Division, US Environmental Protection Agency, Cincinnati, Ohio, USA.
Environ Toxicol Chem. 2022 Nov;41(11):2708-2720. doi: 10.1002/etc.5450. Epub 2022 Sep 14.
Metformin, along with its biotransformation product guanylurea, is commonly observed in municipal wastewaters and subsequent surface waters. Previous studies in fish have identified metformin as a potential endocrine-active compound, but there are inconsistencies with regard to its effects. To further investigate the potential reproductive toxicity of metformin and guanylurea to fish, a series of experiments was performed with adult fathead minnows (Pimephales promelas). First, explants of fathead minnow ovary tissue were exposed to 0.001-100 µM metformin or guanylurea to investigate whether the compounds could directly perturb steroidogenesis. Second, spawning pairs of fathead minnows were exposed to metformin (0.41, 4.1, and 41 µg/L) or guanylurea (1.0, 10, and 100 µg/L) for 23 days to assess impacts on reproduction. Lastly, male fathead minnows were exposed to 41 µg/L metformin, 100 µg/L guanylurea, or a mixture of both compounds, with samples collected over a 96-h time course to investigate potential impacts to the hepatic transcriptome or metabolome. Neither metformin nor guanylurea affected steroid production by ovary tissue exposed ex vivo. In the 23 days of exposure, neither compound significantly impacted transcription of endocrine-related genes in male liver or gonad, circulating steroid concentrations in either sex, or fecundity of spawning pairs. In the 96-h time course, 100 µg guanylurea/L elicited more differentially expressed genes than 41 µg metformin/L and showed the greatest impacts at 96 h. Hepatic transcriptome and metabolome changes were chemical- and time-dependent, with the largest impact on the metabolome observed at 23 days of exposure to 100 µg guanylurea/L. Overall, metformin and guanylurea did not elicit effects consistent with reproductive toxicity in adult fathead minnows at environmentally relevant concentrations. Environ Toxicol Chem 2022;41:2708-2720. © 2022 SETAC. This article has been contributed to by U.S. Government employees and their work is in the public domain in the USA.
二甲双胍及其生物转化产物胍基脲通常存在于城市废水中,随后也存在于地表水中。先前在鱼类中的研究表明,二甲双胍是一种具有潜在内分泌活性的化合物,但关于其作用存在不一致之处。为了进一步研究二甲双胍和胍基脲对鱼类的潜在生殖毒性,用成年黑头呆鱼(Pimephales promelas)进行了一系列实验。首先,将黑头呆鱼卵巢组织的外植体暴露于 0.001-100µM 二甲双胍或胍基脲中,以研究这些化合物是否能直接干扰类固醇生成。其次,将产卵对的黑头呆鱼暴露于二甲双胍(0.41、4.1 和 41µg/L)或胍基脲(1.0、10 和 100µg/L)中 23 天,以评估对繁殖的影响。最后,雄性黑头呆鱼暴露于 41µg/L 二甲双胍、100µg/L 胍基脲或两者的混合物中,在 96 小时的时间过程中采集样本,以研究对肝转录组或代谢组的潜在影响。暴露于离体的二甲双胍或胍基脲均未影响卵巢组织的类固醇生成。在 23 天的暴露期间,这两种化合物都没有显著影响雄性肝脏或性腺中与内分泌相关的基因转录、两性循环类固醇浓度或产卵对的繁殖力。在 96 小时的时间过程中,100µg/L 胍基脲比 41µg/L 二甲双胍引起更多差异表达的基因,并且在 96 小时时表现出最大的影响。肝转录组和代谢组的变化与化学物质和时间有关,在暴露于 100µg/L 胍基脲 23 天时,对代谢组的影响最大。总体而言,在环境相关浓度下,二甲双胍和胍基脲在成年黑头呆鱼中未引起与生殖毒性一致的作用。环境毒理化学 2022;41:2708-2720。版权所有 2022 SETAC。本文已由美国政府雇员贡献,并在美国公有领域。