Fundación Progreso y Salud, Seville, Spain.
National Institute of Toxicology and Forensic Sciences, Seville, Spain.
Ecotoxicol Environ Saf. 2019 Jul 30;176:309-320. doi: 10.1016/j.ecoenv.2019.03.101. Epub 2019 Apr 2.
The pollution by industrial and municipal effluents are major sources of concerns. Fish cell cultures were applied in different strategies of the evaluation of effluents, particularly whole toxicity, toxicity identification evaluation and mode of action studies based in adverse outcome pathways. Whole effluent toxicity was evaluated using a battery of five model systems from four trophic levels: Daphnia magna was the most sensitive system, followed by the hepatoma fish cell line PLHC-1, the bacterium Allivibrio fischeri, the fibroblastic fish cell line RTG-2 and the algae Chlorella vulgaris, detecting a risk of eutrofization. The uptake of neutral red was more sensitive than the content of protein assay. The main morphological alterations observed were cell loss, hydropic degeneration, and a general loss of lysosomes and of their perinuclear distribution. The toxicity was characterized in PLHC-1 cells through toxicity identification evaluation, in which a partial reduction with graduation at pH 11, filtration, aeration and addition of thiosulfate or EDTA was shown; on the other hand, a low sorption in solid phase extraction suggested that the main responsible were not organic compounds. Consequently, it was not necessary to apply an effect directed analysis HPLC fractionation. In the chemical identification phase, Zn, Cd, As, Cu and Pb were quantified in decreasing concentrations. In the toxicity confirmation phase, a reconstituted sample and individual solutions, presented decreasing toxicity: Zn > Pb > As > Cd > Cu > As, the global toxicity being explained by response addition. In the last step, the mode of action was investigated using five specific biomarkers. While metallothionein and succinate dehydrogenase activity were increased, no changes occurred for lysosomal function, acetylcholinesterase and EROD activities, the responsibility of the toxicity for the elements found being confirmed.
工业和城市污水的污染是主要关注点。鱼类细胞培养被应用于不同策略的污水评估,特别是整体毒性、毒性识别评估和基于不良结局途径的作用模式研究。使用来自四个营养级的五个模型系统评估全污水毒性:水蚤是最敏感的系统,其次是肝癌鱼类细胞系 PLHC-1、细菌 Allivibrio fischeri、成纤维细胞鱼类细胞系 RTG-2 和藻类 Chlorella vulgaris,检测到富营养化的风险。中性红的摄取比蛋白质含量测定更敏感。观察到的主要形态变化是细胞丢失、水肿变性以及溶酶体及其核周分布的普遍丧失。通过毒性识别评估对 PLHC-1 细胞中的毒性进行了表征,其中在 pH 11 下进行部分还原、过滤、曝气和添加硫代硫酸盐或 EDTA 显示出梯度;另一方面,固相萃取中的低吸附表明主要责任不是有机化合物。因此,没有必要应用定向分析 HPLC 馏分法。在化学鉴定阶段,定量测定了 Zn、Cd、As、Cu 和 Pb 的浓度,浓度依次降低。在毒性确认阶段,再构成样品和个别溶液的毒性降低:Zn>Pb>As>Cd>Cu>As,全球毒性通过反应加和解释。在最后一步,使用五个特定的生物标志物研究作用模式。虽然金属硫蛋白和琥珀酸脱氢酶活性增加,但溶酶体功能、乙酰胆碱酯酶和 EROD 活性没有变化,证实了发现的元素对毒性的责任。