Research Institute of Poyang Lake, Jiangxi Academy of Sciences, Nanchang 330012, China.
College of Biotechnology and Bioengineering, Zhejiang University of Technology, Hangzhou 310032, China.
Ecotoxicol Environ Saf. 2019 Apr 30;171:460-466. doi: 10.1016/j.ecoenv.2019.01.010. Epub 2019 Jan 9.
6:2 chlorinated polyfluorinated ether sulfonate (F-53B), a Chinese PFOS alternative, has recently been identified in river water, sewage sludge, wildlife and humans, causing great concerns about its potential toxic effects. Here, we report the first investigation of the toxicokinetics and oxidative stress of F-53B in adult zebrafish. Adult male and female zebrafish were exposed to 10 and 100 μg/L of F-53B for 7 days followed by a 5-d depuration period to examine bioaccumulation, distribution, and depuration of F-53B in fish. The results showed that F-53B was readily accumulated in fish tissues with log BCF values of 2.36-3.65, but was eliminated slowly (t = 152.4-358.5 h). F-53B accumulation was greater in males than in females and the concentration in tissues decreased in the following order: gonad ≈ liver ≫ gill ≫ brain in females and liver ≈ gill ≫ gonad ≫ brain in males, showing sex- and tissue- specific accumulation of F-53B in fish. After chronic exposure to F-53B for 28 days, a significant dose-dependent increase in histopathological changes in the liver were mainly manifested by vacuolation. Furthermore, F-53B also significantly reduced the enzyme activity (or content) of most of the measured oxidative stress-related markers (e.g., SOD, CAT and MDA) except for an increase in GSH-Px activity, indicating that oxidative stress was induced in zebrafish after treatment with F-53B. The results of this study provide important information on the toxicokinetics and toxic effects of F-53B, which will contribute to the ecological risk assessments of F-53B released into surface waters.
6:2 氯化聚全氟醚砜(F-53B)是一种中国的 PFOS 替代品,最近在河水、污水污泥、野生动物和人类中被发现,这引起了人们对其潜在毒性影响的极大关注。在这里,我们首次报道了 F-53B 在成年斑马鱼体内的毒代动力学和氧化应激情况。雄性和雌性成年斑马鱼分别暴露于 10 和 100μg/L 的 F-53B 中 7 天,随后进行 5 天的净化期,以检测 F-53B 在鱼体内的生物积累、分布和净化情况。结果表明,F-53B 很容易在鱼组织中积累,其 log BCF 值为 2.36-3.65,但消除速度较慢(t = 152.4-358.5 h)。F-53B 在雄性体内的积累量大于雌性,且组织中浓度的降低顺序为:雌性性腺≈肝脏>鳃>脑,雄性肝脏>鳃>性腺>脑,表明 F-53B 在鱼体内具有性别和组织特异性的积累。在慢性暴露于 F-53B 28 天后,肝脏的组织病理学变化明显增加,主要表现为空泡化。此外,F-53B 还显著降低了大多数测量的氧化应激相关标志物的酶活性(如 SOD、CAT 和 MDA)的含量(或活性),除了 GSH-Px 活性增加外,表明 F-53B 处理后斑马鱼发生了氧化应激。本研究的结果提供了关于 F-53B 毒代动力学和毒性效应的重要信息,这将有助于对释放到地表水中的 F-53B 进行生态风险评估。