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铈(Ⅲ)激活过一硫酸盐用于取代多环芳烃的降解。

Ce(Ⅲ) activates peroxymonosulfate for the degradation of substituted PAHs.

机构信息

Institute of Organic Contaminant Control and Soil Remediation, College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.

Institute of Organic Contaminant Control and Soil Remediation, College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.

出版信息

Chemosphere. 2022 Nov;306:135525. doi: 10.1016/j.chemosphere.2022.135525. Epub 2022 Jun 29.

Abstract

Substituted polycyclic aromatic hydrocarbons (SPAHs) are being intensively investigated, considering their high toxicity. Additionally, the mechanism of the effect of substituents on the removal of SPAHs and the activation of Ce(III) ions on peroxymonosulfate (PMS) have not been explored. Here we evaluated the removal efficiency of SPAHs in the oxidation system constructed by Ce(Ⅲ) ions and PMS, with emphasized the effect of substituents on SPAHs degradation. Ce(Ⅲ) has high catalytic performance for PMS, and the degradation percentage of all pollutants was higher than 92%. The significantly negative correlation between the reaction rate constants of SPAHs and the highest occupied molecular orbital-the lowest unoccupied molecular orbital gap, confirms that substituents lead to the differences in the degradation of SPAHs. The generation of reactive oxygen species (SO, OH, and O) is based on the electron transfer between Ce(Ⅲ) and PMS, and the contribution of ROS to substituted naphthalene varies due to the role of substituents. The Ce(Ⅳ)/Ce(Ⅲ) cycle accelerates the activation of PMS. Based on the transformation products and condensed Fukui function, the possible degradation pathways are inferred. In addition, inorganic anions and organic matter have little effect on the Ce(Ⅲ)/PMS system, which is a prerequisite for applying this system to real-world waste-water for SPAHs removal. This work demonstrates a new model of the degradation mechanism of SPAHs in the Ce(Ⅲ)/PMS system.

摘要

取代多环芳烃(SPAHs)因其高毒性而受到广泛研究。此外,取代基对 SPAHs 去除和过一硫酸盐(PMS)中 Ce(III)离子活化的影响机制尚未得到探索。在这里,我们评估了 Ce(Ⅲ)离子和 PMS 构建的氧化体系中 SPAHs 的去除效率,重点研究了取代基对 SPAHs 降解的影响。Ce(Ⅲ)对 PMS 具有很高的催化性能,所有污染物的降解率均高于 92%。SPAHs 的反应速率常数与最高占据分子轨道-最低未占据分子轨道能隙之间存在显著的负相关性,证实了取代基导致 SPAHs 降解的差异。活性氧物种(SO、OH 和 O)的生成基于 Ce(Ⅲ)和 PMS 之间的电子转移,而取代萘的 ROS 贡献因取代基的作用而有所不同。Ce(Ⅳ)/Ce(Ⅲ)循环加速了 PMS 的活化。基于转化产物和凝聚 Fukui 函数,推断出可能的降解途径。此外,无机阴离子和有机物对 Ce(Ⅲ)/PMS 体系的影响很小,这是将该体系应用于实际废水中去除 SPAHs 的前提条件。这项工作展示了 Ce(Ⅲ)/PMS 体系中 SPAHs 降解机制的新模型。

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