生物炭负载硫化纳米零价铁活化过硫酸盐降解水溶液中环丙沙星:工艺优化及降解途径。

Activation of persulfate by biochar-supported sulfidized nanoscale zero-valent iron for degradation of ciprofloxacin in aqueous solution: process optimization and degradation pathway.

机构信息

College of Environmental Science and Engineering, Yangzhou University, Yangzhou, 225009, People's Republic of China.

School of Hydraulic and Environmental Engineering, Changsha University of Science & Technology, Changsha, 410114, People's Republic of China.

出版信息

Environ Sci Pollut Res Int. 2024 Feb;31(7):10950-10966. doi: 10.1007/s11356-024-31931-z. Epub 2024 Jan 12.

Abstract

The pollution of antibiotics, specifically ciprofloxacin (CIP), has emerged as a significant issue in the aquatic environment. Advanced oxidation processes (AOPs) are capable of achieving stable and efficient removal of antibiotics from wastewater. In this work, biochar-supported sulfidized nanoscale zero-valent iron (S-nZVI/BC) was adopted to activate persulfate (PS) for the degradation of CIP. The impacts of different influencing factors such as S/Fe molar ratios, BC/S-nZVI mass ratios, PS concentration, S-nZVI/BC dosage, CIP concentration, initial pH, coexisting anions, and humic acid on CIP degradation efficiency were explored by batch experiments. The results demonstrated that the highest degradation ability of S-nZVI/BC was achieved when the S/Fe molar ratio was 0.07 and the BC/S-nZVI mass ratio was 1:1. Under the experimental conditions with 0.6 g/L S-nZVI/BC, 2 mmol/L PS, and 10 mg/L CIP, the degradation rate reached 97.45% after 90 min. The S-nZVI/BC + PS system showed significant degradation in the pH range from 3 to 9. The coexisting anions affected the CIP degradation efficiency in the following order: CO > NO > SO > Cl. The radical quenching experiments and electron paramagnetic resonance (EPR) revealed that oxidative species, including SO, HO, O, and O, all contribute to the degradation of CIP, in which O plays a particularly prominent role. Furthermore, the probable degradation pathway of CIP was explored according to the 12 degradation intermediates identified by LC-MS. This study provides a new idea for the activation method of PS and presents a new approach for the treatment of aqueous antibiotics with highly catalytic active nanomaterials.

摘要

抗生素,特别是环丙沙星(CIP)的污染已经成为水环境中的一个重要问题。高级氧化工艺(AOPs)能够稳定有效地去除废水中的抗生素。在这项工作中,采用生物炭负载硫化纳米零价铁(S-nZVI/BC)来激活过硫酸盐(PS)以降解 CIP。通过批实验探讨了不同影响因素,如 S/Fe 摩尔比、BC/S-nZVI 质量比、PS 浓度、S-nZVI/BC 用量、CIP 浓度、初始 pH 值、共存阴离子和腐殖酸对 CIP 降解效率的影响。结果表明,当 S/Fe 摩尔比为 0.07 且 BC/S-nZVI 质量比为 1:1 时,S-nZVI/BC 的降解能力最高。在 0.6 g/L S-nZVI/BC、2 mmol/L PS 和 10 mg/L CIP 的实验条件下,90 min 后降解率达到 97.45%。S-nZVI/BC + PS 体系在 pH 3-9 范围内表现出显著的降解能力。共存阴离子对 CIP 降解效率的影响顺序为:CO > NO > SO > Cl。自由基猝灭实验和电子顺磁共振(EPR)表明,包括 SO、HO、O 和 O 在内的氧化物种都有助于 CIP 的降解,其中 O 发挥了特别突出的作用。此外,根据通过 LC-MS 鉴定的 12 种降解中间产物,探讨了 CIP 的可能降解途径。这项研究为 PS 的激活方法提供了新的思路,并为使用具有高催化活性的纳米材料处理水相抗生素提供了新的方法。

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