Research Center Jülich, Department of Analytics (ZEA-3), Jülich 52425, Germany; RWTH -Aachen University, Aachen Biology and Biotechnology - ABBt, Institute for Environmental Research, Department of Ecosystem Analysis, Aachen 52074, Germany.
RWTH -Aachen University, Aachen Biology and Biotechnology - ABBt, Institute for Environmental Research, Department of Ecosystem Analysis, Aachen 52074, Germany.
Sci Total Environ. 2018 May 1;622-623:1193-1201. doi: 10.1016/j.scitotenv.2017.11.317. Epub 2017 Dec 13.
Tricolsan (TCS), an antimicrobial agent, is considered as emerging pollutant due to its wide dispersive use in personal care products and high aquatic toxicity. In the present study, phase I metabolism of triclosan was investigated through laboratory electrochemical simulation studies. The products formed in the electrochemical (EC) cell were identified by online and offline coupling with QTRAP and high-resolution FTICR mass spectrometers, respectively. The sequential formation and disappearance of each product, with the continuous increase of voltage from 0 to 3500 mV, was observed to reveal the transformation pathways of TCS. The toxic potential of TCS and the identified products was estimated using Quantitative structure-activity relationship (QSAR) modeling on 16 target proteins. The toxicity change of TCS during simulated metabolism and toxicological effects of reaction mixture were assessed by Fish embryo toxicity (FET) test (Danio rerio) and quantitative real-time polymerase chain reaction (qPCR). Eight metabolites formed during the simulated metabolism of TCS mainly via the mechanisms of hydroxylation, ether-bond cleavage and cyclization. In FET test, the reaction mixture (LC=1.28 mg/L) after electrochemical reactions showed high acute toxicity on zebrafish embryos, which was comparable to that of triclosan (LC=1.34 mg/L). According to the modeling data, less toxic products formed only via ether-bond cleavage of TCS while the products formed through other mechanisms showed high toxicity. AhR-mediated dioxin-like effects on zebrafish embryos, such as developmental retardation in skeleyton and malformations in cardiovascular system, were also observed after exposure to the TCS reaction mixture in FET test. Activation of the AhR by the reaction mixture in zebrafish embryos was further proved in cyp1a gene expression analysis.
三氯生(TCS)作为一种抗菌剂,由于其在个人护理产品中的广泛应用和高水生毒性,被认为是一种新兴的污染物。本研究通过实验室电化学模拟研究,考察了三氯生的 I 相代谢。通过在线和离线耦合与 QTRAP 和高分辨率 FTICR 质谱仪,分别鉴定了在电化学(EC)电池中形成的产物。随着电压从 0 连续增加到 3500 mV,观察到每个产物的连续形成和消失,揭示了 TCS 的转化途径。利用定量构效关系(QSAR)模型对 16 种靶蛋白进行预测,评估了 TCS 的毒性和鉴定产物的毒性。通过鱼类胚胎毒性(FET)试验(斑马鱼)和实时定量聚合酶链反应(qPCR)评估 TCS 在模拟代谢过程中的毒性变化和反应混合物的毒理学效应。在 TCS 的模拟代谢过程中形成了 8 种代谢物,主要通过羟化、醚键断裂和环化等机制。在 FET 试验中,电化学反应后的反应混合物(LC=1.28mg/L)对斑马鱼胚胎表现出高急性毒性,与三氯生(LC=1.34mg/L)相当。根据建模数据,仅通过 TCS 的醚键断裂形成的毒性较小的产物,而通过其他机制形成的产物则表现出高毒性。FET 试验中,还观察到暴露于 TCS 反应混合物后,AhR 介导的二恶英样效应,如骨骼发育迟缓和心血管系统畸形。在 FET 试验中,cyp1a 基因表达分析进一步证明了反应混合物在斑马鱼胚胎中激活 AhR。