State Environmental Protection Key Laboratory of Wetland Ecology and Vegetation Restoration, School of Environment, Northeast Normal University, Changchun 130117, China.
Key Laboratory of Industrial Ecology and Environmental Engineering, School of Environmental Science and Technology, Dalian University of Technology, Dalian 116024, China.
Aquat Toxicol. 2020 Mar;220:105417. doi: 10.1016/j.aquatox.2020.105417. Epub 2020 Jan 15.
Pyraclostrobin is a fungicide used widely across the world. However, its photolysis pathway and toxic mechanism is unclear. In this study, photolysis and photo-induced toxicity of pyraclostrobin to Vibrio fischeri were determined. The results showed that direct photolysis dominated the degradation of pyraclostrobin. Gas Chromatography-Mass spectrometry and quantum chemical calculation revealed that the pyraclostrobin was firstly photo-degraded into Methyl N-phenyl-carbamate and 1-(4-chlorophenyl)-3-hydroxy-1H-pyrzole, synthetic intermediates of pyraclostrobin, then into aniline, benzoquinone and acids. Toxicity assay showed that bioluminescent inhibition rate to V. fischeri fluctuated with radiation/illumination time and the toxicity curve can be classified into three phases (Phase I: 0-10 min, incline; Phase II: 10-60 min, decline; Phase III: 60-120 min, incline). The up-and-down curve indicates the change of parent compound during the photolysis. Simulation of molecular docking showed that the CDOCKER interaction energy of pyraclostrobin (-44.71) lower than other intermediate products (>-30.00), indicating that the parent compound is more toxic than its intermediates. An increased toxicity observed in the toxicity curve was attributed to the generation of benzoquinone with log1/EC of 6.73, which can greatly change structure of target luciferase in Vibrio fischeri. In addition, the addition of radical scavengers can inhibit the bioluminescence of the tested solutions, indicating the involvement of radicals in the transformation of intermediates. This paper reveals that one of photochemical transformation products of pyraclostrobin can cause more toxic than its parent compound to bacteria. Environmental risk assessment should consider not only the parent compound, but also its metabolites.
唑菌酯是一种在全球范围内广泛使用的杀菌剂。然而,其光解途径和毒性机制尚不清楚。本研究测定了唑菌酯对发光菌的光解和光诱导毒性。结果表明,直接光解主导唑菌酯的降解。气相色谱-质谱联用和量子化学计算揭示,唑菌酯首先光降解为甲基 N-苯基氨基甲酸酯和 1-(4-氯苯基)-3-羟基-1H-吡唑,唑菌酯的合成中间体,然后生成苯胺、苯醌和酸。毒性试验表明,发光菌的生物发光抑制率随辐照/光照时间而波动,毒性曲线可分为三个阶段(阶段 I:0-10 分钟,上升;阶段 II:10-60 分钟,下降;阶段 III:60-120 分钟,上升)。上下曲线表明光解过程中母体化合物的变化。分子对接模拟表明,唑菌酯的 CDOCKER 相互作用能(-44.71)低于其他中间产物(>-30.00),表明母体化合物比其中间产物更具毒性。毒性曲线上观察到的毒性增加归因于生成具有 log1/EC 值为 6.73 的苯醌,它可以极大地改变发光菌中目标荧光素酶的结构。此外,自由基清除剂的添加可以抑制测试溶液的生物发光,表明自由基参与了中间产物的转化。本文揭示了唑菌酯的一种光化学转化产物可能比其母体化合物对细菌产生更大的毒性。环境风险评估不仅应考虑母体化合物,还应考虑其代谢物。