Xu Youxin, Zhang Chenxi, Zou Haobing, Chen Guangrong, Sun Xiaomin, Wang Shuguang, Tian Huifang
Institute of Environmental Biotechnology and Functional Materials, School of Environmental Science and Engineering, Shandong University, Qingdao 266237, China.
Shandong Engineering Laboratory for Clean Utilization of Chemical Resources, Weifang University of Science and Technology, Weifang 262700, China.
Toxics. 2024 Mar 9;12(3):207. doi: 10.3390/toxics12030207.
Persulfate-based advanced oxidation process has been proven to be a promising method for the toxic pesticide chlorpyrifos (CPY) degradation in wastewater treatment. However, due to the limitation for the short-lived intermediates detection, a comprehensive understanding for the degradation pathway remains unclear. To address this issue, density functional theory was used to analyze the degradation mechanism of CPY at the M06-2X/6-311++G(3df,3pd)//M06-2X/6-31+G(d,p) level, and computational toxicology methods were employed to explore the toxicity of CPY and its degradation products. Results show that hydroxyl radicals (·OH) and sulfate radicals (SO) initiate the degradation reactions by adding to the P=S bond and abstracting the H atom on the ethyl group, rather than undergoing α-elimination of the pyridine ring in the persulfate oxidation process. Moreover, the addition products were attracted and degraded by breaking the P-O bond, while the abstraction products were degraded through dealkylation reactions. The transformation products, including 3,5,6-trichloro-2-pyridynol, O,O-diethyl phosphorothioate, chlorpyrifos oxon, and acetaldehyde, obtained through theoretical calculations have been detected in previous experimental studies. The reaction rate constants of CPY with ·OH and SO were 6.32 × 10 and 9.14 × 10 M·s at room temperature, respectively, which was consistent with the experimental values of 4.42 × 10 and 4.5 × 10 M s. Toxicity evaluation results indicated that the acute and chronic toxicity to aquatic organisms gradually decreased during the degradation process. However, some products still possess toxic or highly toxic levels, which may pose risks to human health. These research findings contribute to understanding the transformation behavior and risk assessment of CPY in practical wastewater treatment.
基于过硫酸盐的高级氧化工艺已被证明是一种在废水处理中降解有毒农药毒死蜱(CPY)的有前景的方法。然而,由于短寿命中间体检测的局限性,对降解途径的全面理解仍不清楚。为了解决这个问题,采用密度泛函理论在M06 - 2X/6 - 311++G(3df,3pd)//M06 - 2X/6 - 31+G(d,p)水平分析CPY的降解机理,并运用计算毒理学方法探究CPY及其降解产物的毒性。结果表明,在过硫酸盐氧化过程中,羟基自由基(·OH)和硫酸根自由基(SO)通过加成到P = S键和夺取乙基上的H原子引发降解反应,而不是通过吡啶环的α - 消除反应。此外,加成产物通过断裂P - O键被吸引并降解,而夺取产物则通过脱烷基反应降解。通过理论计算得到的转化产物,包括3,5,6 - 三氯 - 2 - 吡啶醇、O,O - 二乙基硫代磷酸酯、毒死蜱氧磷和乙醛,已在先前的实验研究中被检测到。CPY与·OH和SO在室温下的反应速率常数分别为6.32×10和9.14×10 M·s,这与实验值4.42×10和4.5×10 M s一致。毒性评估结果表明,在降解过程中对水生生物的急性和慢性毒性逐渐降低。然而,一些产物仍具有毒性或高毒水平,这可能对人类健康构成风险。这些研究结果有助于理解CPY在实际废水处理中的转化行为和风险评估。