Department of Environmental and Occupational Health Sciences, University of Washington, Seattle, WA 98105, USA.
Aquat Toxicol. 2010 Apr 1;97(1):42-50. doi: 10.1016/j.aquatox.2009.11.013. Epub 2009 Dec 11.
The polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental contaminants whose residues are increasing in fish, wildlife and human tissues. However, relatively little is known regarding the mechanisms of cell injury caused by PBDE congeners in fish. In the present study, we employed flow cytometry-based analyses to understand the onset and mechanisms of cell injury in rainbow trout gill cells (RTgill-W1 cells) exposed to 2,2',4,4'-tetrabromodiphenyl ether (BDE 47). Substantial optimization and validation for flow cytometry protocols were required during assay development for the trout gill cell line. Exposure to micromolar concentrations of BDE 47 elicited a significant loss in RTgill-W1 cell viability that was accompanied by a decrease in NAD(P)H autofluorescence, a marker associated with disruption of cellular redox status. This loss in NAD(P)H content was accompanied by a decrease in nonyl acridine orange fluorescence, indicating mitochondrial membrane lipid peroxidation. Furthermore, low doses of BDE 47 altered cellular forward angle light scatter (FS, a measure of cell diameter or size) and side light scatter properties (SS, a measure of cellular internal complexity), consistent with the early stages of apoptosis. These changes were more pronounced at higher BDE 47 concentrations, which led to an increase in the percentage of cells undergoing frank apoptosis as evidenced by sub-G1 DNA content. Apoptosis was also observed at a relatively low dose (3.2muM) of BDE 47 if cells were exposed for an extended period of time (24h). Collectively, the results of these studies indicate that exposure of rainbow trout gill cells to BDE47 is associated with the induction of apoptosis likely originating from disruption of cellular redox status and mitochondrial oxidative injury. The current report extends observations in other species demonstrating that oxidative stress is an important mechanism of BDE 47 mediated cellular toxicity, and supports the use of oxidative stress-associated biomarkers in assessing the sublethal effects of PBDEs and their replacements in fish. The application of flow cytometry endpoints using fish cell lines should facilitate study of the mechanisms of chemical injury in aquatic species.
多溴联苯醚(PBDEs)是普遍存在的环境污染物,其残留物在鱼类、野生动物和人类组织中不断增加。然而,对于 PBDE 同系物在鱼类中引起细胞损伤的机制,人们知之甚少。在本研究中,我们采用流式细胞术分析方法,了解暴露于 2,2',4,4'-四溴二苯醚(BDE-47)的虹鳟鱼鳃细胞(RTgill-W1 细胞)细胞损伤的发生和机制。在为该鳜鱼细胞系开发测定法的过程中,需要对流式细胞术方案进行大量的优化和验证。在微摩尔浓度的 BDE-47 暴露下,RTgill-W1 细胞活力显著下降,同时 NAD(P)H 自发荧光减少,这是与细胞氧化还原状态破坏相关的标志物。NAD(P)H 含量的减少伴随着壬基吖啶橙荧光的减少,表明线粒体膜脂质过氧化。此外,低剂量的 BDE-47 改变了细胞的前向角光散射(FS,细胞直径或大小的测量)和侧光散射特性(SS,细胞内部复杂性的测量),与细胞凋亡的早期阶段一致。在更高浓度的 BDE-47 下,这些变化更为明显,这导致了更多的细胞经历明显的凋亡,证据是亚 G1 DNA 含量的增加。在相对较低的 BDE-47 剂量(3.2μM)下,如果细胞暴露时间延长(24 小时),也观察到凋亡。总的来说,这些研究的结果表明,暴露于 BDE47 的虹鳟鱼鳃细胞与诱导凋亡有关,这可能源于细胞氧化还原状态的破坏和线粒体氧化损伤。本报告扩展了在其他物种中的观察结果,表明氧化应激是 BDE-47 介导的细胞毒性的一个重要机制,并支持在评估 PBDE 及其替代品对鱼类的亚致死效应时使用与氧化应激相关的生物标志物。使用鱼类细胞系的流式细胞术终点的应用应有助于研究水生物种的化学损伤机制。