State Key Laboratory of Water Environment Simulation, School of Environment, Beijing Normal University, Beijing 100875, China.
State Key Laboratory of Water Environment Simulation, School of Environment, Beijing Normal University, Beijing 100875, China.
J Hazard Mater. 2022 Aug 15;436:129078. doi: 10.1016/j.jhazmat.2022.129078. Epub 2022 May 5.
Lindane is a persistent organic pollutant that has attracted worldwide attention because of its threat to human health and environmental security. A horizontal planetary mechanochemical method was developed for rapid and efficient degradation of lindane in soil in an alkaline environment. Under the condition of a very low reagent-to-soil ratio (R = 2%), ball-to-powder ratio (C = 6:1), rotation speed (r = 300 rpm) and high soil single treatment capacity (S = 60 g), the lindane in four typical soils (~ 100 mg/kg) can be degraded up to 96.30% in 10 min. This method can also remediate high-concentration lindane-contaminated soil (833 ± 26 mg/kg). The experimental results and theoretical calculations proved that the stepwise dechlorination and final carbonization of lindane in soil are mainly attributed to the combined action of mechanical energy and alkalinity. The bimolecular elimination (E2) reaction was the first step of lindane destruction. Subsequently, the unimolecular elimination (E1) reaction tended to occur with the weakening of alkalinity. Then, benzene was obtained through stepwise hydrogenolysis reaction. The last was the generation of carbon substances by fragmentation or condensation of benzene rings. This work proposes a practical remediation technology for organic contaminated soil and improves the understanding of the degradation pathways of lindane in soil in alkali-assisted mechanochemical system.
林丹是一种持久性有机污染物,因其对人类健康和环境安全的威胁而引起了全世界的关注。本研究开发了一种在碱性环境中快速高效降解土壤中林丹的水平行星机械化学方法。在极低的试剂-土壤比(R=2%)、球-粉比(C=6:1)、转速(r=300rpm)和高土壤单次处理能力(S=60g)条件下,四种典型土壤(~100mg/kg)中的林丹在 10min 内可降解 96.30%以上。该方法还可修复高浓度林丹污染土壤(833±26mg/kg)。实验结果和理论计算证明,土壤中林丹的逐步脱氯和最终碳化主要归因于机械能和碱度的共同作用。双分子消除(E2)反应是林丹破坏的第一步。随后,随着碱度的减弱,单分子消除(E1)反应趋于发生。然后,通过逐步氢解反应得到苯。最后是通过苯环的碎片或缩合生成碳物质。这项工作为有机污染土壤的实际修复技术提供了一种可能,并提高了对林丹在碱性辅助机械化学体系中降解途径的认识。