Department of Biological Sciences, Simon Fraser University, 8888 University Drive, Burnaby, British Columbia V5A 1S6, Canada.
Department of Physiological Sciences and Center for Environmental and Human Toxicology, UF Genetics Institute, College of Veterinary Medicine, University of Florida, Gainesville, USA.
Aquat Toxicol. 2020 May;222:105446. doi: 10.1016/j.aquatox.2020.105446. Epub 2020 Feb 12.
The objective of this study was to examine the acute toxicity and sub-lethal effects of the commercial formulation of diquat dibromide, Reward® Landscape and Aquatic Herbicide, on multiple life stages of rainbow trout. The continuous exposure 96 h LC derived for juvenile feeding fry aged 85 d post-hatch was 9.8 mg/L. Rainbow trout eyed embryos and juvenile feeding fry were also exposed to concentrations of Reward® ranging from 0.12 to 10 mg/L during two 24 h pulse exposures separated by 14 d of rearing in fresh water to mimic the manufacturers instructions for direct applications to water bodies. Decreased survival and body morphometrics were evident at 9.3 mg/L during the embryo/alevin exposures, but not in feeding juveniles, indicating a higher sensitivity of the early life stage fish. Quantitative proteomics and subnetwork enrichment analyses were conducted in the livers for both life stages to evaluate protein profiles after exposure to 0.37 mg/L diquat via Reward® exposure. Unique protein profiles were revealed for pre-feeding swim-up fry and for feeding juvenile fish, reflecting differences between the two life stages in sub-cellular responses after diquat dibromide exposure. Hepatic proteome effects were more dramatic in the pre-feeding swim-up fry with 315 proteins differentially expressed between the control and exposed fish while in the later life stage feeding fry, only 84 proteins were different after Reward® exposure. Exposure to Reward® significantly increased RNA/mRNA processes, induced activation of Atk/mTOR and caspase activity, and altered energy homeostasis. Proteomic alterations are associated with reduced growth observed in embryo/alevin at higher exposure concentrations, offering insight into key events underlying growth impairment within the adverse outcome pathway framework. This study is the first to report the sub-cellular and whole organism level effects of diquat dibromide in a commercial formulation and demonstrates that concentrations based on aquatic application rates alter the hepatic proteome.
本研究旨在检测二溴化百草枯商品制剂 Reward®景观和水生除草剂对虹鳟多个生活阶段的急性毒性和亚致死效应。从孵化后 85 天的幼鱼摄食期幼鱼得出的 96 小时连续暴露 LC50 值为 9.8mg/L。虹鳟鱼眼斑胚胎和幼鱼摄食期幼鱼还暴露于 Reward®浓度范围为 0.12 至 10mg/L,进行两次 24 小时脉冲暴露,中间间隔 14 天在淡水养殖以模拟制造商直接向水体应用的说明。在胚胎/仔鱼暴露期间,9.3mg/L 时出现存活率和身体形态测量值降低,但在摄食幼鱼中未出现,表明早期生活阶段鱼类的敏感性更高。在暴露于 0.37mg/L 二溴化百草枯后,通过 Reward®暴露,对两个生活阶段的肝脏进行定量蛋白质组学和子网络富集分析,以评估蛋白质图谱。在预摄食游泳幼鱼和摄食幼鱼中揭示了独特的蛋白质图谱,反映了二溴化百草枯暴露后两个生活阶段亚细胞反应之间的差异。在预摄食游泳幼鱼中,肝蛋白质组的影响更为明显,暴露于百草枯的鱼与对照组鱼之间有 315 种蛋白质差异表达,而在后期生活阶段摄食幼鱼中,仅 84 种蛋白质在 Reward®暴露后有差异。暴露于 Reward®显著增加 RNA/mRNA 过程,诱导 Atk/mTOR 和半胱天冬酶活性的激活,并改变能量稳态。蛋白质组学改变与在较高暴露浓度下观察到的胚胎/仔鱼生长减少有关,为生长损害在不利结果途径框架内的关键事件提供了深入了解。本研究首次报告了商业制剂中二溴化百草枯的亚细胞和全生物体水平效应,并表明基于水生应用率的浓度改变了肝蛋白质组。