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介质阻挡放电等离子体联合P25/NH-MIL-125(Ti)对土壤中芴的协同降解

Synergistic degradation of fluorene in soil by dielectric barrier discharge plasma combined with P25/NH-MIL-125(Ti).

作者信息

Lu Hongyu, Deng Chengxun, Yu Zhimin, Zhang Dianya, Li Weiping, Huang Jun, Bao Teng, Liu Xiaowei

机构信息

School of Biology, Food, and Environment, Hefei University, Hefei, 230601, China; International (Sino-German) Joint Research Center for Biomass of Anhui Province, Hefei, 230601, China.

Heifei Engineering Research Center for Soil and Groundwater Remediation, Hefei, 230088, China.

出版信息

Chemosphere. 2022 Jun;296:133950. doi: 10.1016/j.chemosphere.2022.133950. Epub 2022 Feb 14.

DOI:10.1016/j.chemosphere.2022.133950
PMID:35176305
Abstract

Plasma techniques to degrade pollutants are generally more efficient than conventional methods, but exist some problems such as high energy consumption, incomplete degradation of pollutants, and secondary pollution caused by highly toxic intermediates. In this study, the dielectric barrier discharge plasma (DBDP) combined with the Ti-based metal organic frameworks (MOFs) catalysts (P25/NH-MIL-125(Ti)) was used to degrade fluorene in the soil. The synergistic treatment technique used in soil remediation can realize a green and promising treatment efficiency with relatively low energy consumption. Compared with DBDP system alone, the synergetic treatment system of DBDP and P25/NH-MIL-125(Ti) considerably increased the degradation efficiency of fluorene in the soil to above 90% at 10 min, even with a relatively low discharge voltage (5 kV). The synergistic treatment system achieved 88.8% of fluorene mineralization at 60 min. Optical emission spectroscopy and electron paramagnetic resonance spectroscopy both showed that •OH and •O played an important role in the synergetic treatment system. Nine main intermediates were identified using gas chromatography-mass spectrometry and Fourier transform infrared analysis. The main degradation of fluorine in soil was caused by the electronic transition of the catalytic material excited by DBDP, and finally mineralized into CO and HO. The fluorene and its toxic intermediates were effectively removed. This study provides an insight for achieving high efficiency and environmentally friendly application perspective in soil remediation.

摘要

等离子体降解污染物的技术通常比传统方法更有效,但存在一些问题,如高能耗、污染物降解不完全以及由高毒性中间体引起的二次污染。在本研究中,采用介质阻挡放电等离子体(DBDP)与钛基金属有机框架(MOFs)催化剂(P25/NH-MIL-125(Ti))相结合的方法降解土壤中的芴。土壤修复中使用的协同处理技术能够以相对较低的能耗实现绿色且有前景的处理效率。与单独的DBDP系统相比,DBDP与P25/NH-MIL-125(Ti)的协同处理系统在10分钟时将土壤中芴的降解效率显著提高到90%以上,即使在相对较低的放电电压(5 kV)下也是如此。协同处理系统在60分钟时实现了88.8%的芴矿化。发射光谱和电子顺磁共振光谱均表明,•OH和•O在协同处理系统中起重要作用。利用气相色谱 - 质谱联用和傅里叶变换红外分析鉴定出九种主要中间体。土壤中芴的主要降解是由DBDP激发的催化材料的电子跃迁引起的,最终矿化为CO和HO。芴及其有毒中间体被有效去除。本研究为在土壤修复中实现高效且环保的应用前景提供了思路。

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