College of Life Sciences, Wenzhou Medical University, Wenzhou 325035, China.
Key Laboratory of Watershed Sciences and Health of Zhejiang Province, Wenzhou Medical University, Wenzhou 325035, China.
Environ Toxicol Pharmacol. 2018 Jan;57:9-18. doi: 10.1016/j.etap.2017.11.006. Epub 2017 Dec 27.
Triclosan (TCS), 2,4,6-trichlorophenol (2,4,6-TCP) and 2,4-dichlorophenol (2,4-DCP) are the most prevalent chlorinated phenolic pollutants in aquatic environments. Our results showed LC and EC values of 0.51, 1.11, 2.45mg/L, and 0.36, 0.74, 1.53mg/L for TCS, 2,4,6-TCP and 2,4-DCP, respectively, to 120hpf zebrafish. The highest TCSD (the mixture of TCS, 2,4,6-TCP and 2,4-DCP) toxicity was observed at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4. LC and EC values of TCSD mixtures for 120-hpf zebrafish were 2.28 and 1.16mg/L, respectively. Two toxicity assessment methods (Toxic Unit and Mixture Toxicity Index) indicated that TCSD interactions produced partly additive toxicity. TCSD exposure decreased zebrafish hatching rate and led to a series of malformations. Following alkaline phosphatase staining, a large area of vascular ablation was observed with almost complete disappearance of vascular branches and a smaller coverage range. Prominent reddening of the yolk sac and visceral mass after oil red O staining implied that TCSD exposure severely affected fat metabolism. Following acridine orange staining, cell death occurred in eyes while high TCSD concentrations (0.84mg/L) induced cardiovascular circulation dysfunction. Alcian blue staining increased the α angle between Meckel's cartilages and β angle between two ceratobranchial. Basihyal and palatoquadrate became shorter and developmental abnormality or defects occurred in the fifth ceratobranchial. Overall, these results provide a theoretical basis for systematically evaluating the combined toxicity of the prevalent chlorinated phenolic pollutants in real-world aquatic environments.
三氯生(TCS)、2,4,6-三氯苯酚(2,4,6-TCP)和 2,4-二氯苯酚(2,4-DCP)是水生环境中最常见的含氯酚类污染物。我们的结果表明,TCS、2,4,6-TCP 和 2,4-DCP 对 120 小时pf 斑马鱼的 LC 和 EC 值分别为 0.51、1.11、2.45mg/L 和 0.36、0.74、1.53mg/L。TCSD(TCS、2,4,6-TCP 和 2,4-DCP 的混合物)的毒性最高,在 TCS:2,4,6-TCP:2,4-DCP 浓度比为 1:2:4 时观察到。120 小时pf 斑马鱼的 TCSD 混合物 LC 和 EC 值分别为 2.28 和 1.16mg/L。两种毒性评估方法(毒性单位和混合物毒性指数)表明 TCSD 相互作用产生部分相加毒性。TCSD 暴露降低了斑马鱼的孵化率,并导致一系列畸形。碱性磷酸酶染色后,观察到大面积血管消融,几乎完全消失了血管分支,覆盖范围较小。油红 O 染色后卵黄囊和内脏质量明显变红,表明 TCSD 暴露严重影响脂肪代谢。吖啶橙染色后,眼睛发生细胞死亡,而高浓度 TCSD(0.84mg/L)导致心血管循环功能障碍。阿利新蓝染色增加了 Meckel 软骨之间的α角和两个角鳃软骨之间的β角。基舌骨和腭方骨变短,第五对角鳃软骨发生发育异常或缺陷。总的来说,这些结果为系统评估实际水生环境中常见含氯酚类污染物的联合毒性提供了理论依据。