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Electron transfer-based peroxydisulfate activation by waste herb residue biochar: Adsorption versus surface oxidation
被引:39
作者:
Chen, Xuantong
[1
]
Guo, Zhen
[1
]
Liu, Juemiao
[1
]
Wu, Fei
[1
]
Cheng, Cheng
[1
]
Lin, Heng
[1
,2
]
Ren, Wei
[3
]
Zhang, Hui
[1
]
机构:
[1] Wuhan Univ, Sch Resource & Environm Sci, Dept Environm Sci & Engn, Hubei Key Lab Biomass Resource Chem & Environm Bio, Wuhan 430079, Peoples R China
[2] Wuhan Univ, Dept Cardiothorac Surg, ZhongNan Hosp, Wuhan 430060, Peoples R China
[3] Nanchang Hangkong Univ, Key Lab Jiangxi Prov Persistent Pollutants Control, Nanchang 330063, Peoples R China
基金:
中国国家自然科学基金;
关键词:
Adsorption;
Biochar;
Electron transfer;
Mass transfer;
Peroxydisulfate;
Surface oxidation;
PERSISTENT FREE-RADICALS;
NONRADICAL ACTIVATION;
PERSULFATE ACTIVATION;
ORGANIC-COMPOUNDS;
CARBON NANOTUBES;
DEGRADATION;
PEROXYMONOSULFATE;
INSIGHTS;
ACID;
TRANSFORMATION;
D O I:
10.1016/j.cej.2022.138560
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
Waste herb residue biochar (WBC) was synthesized to activate peroxydisulfate (PDS) for the removal of different micropollutants. WBC prepared at 700 C (WBC700) exhibits discrepant adsorption and PDS catalytic perfor-mance to three pharmaceuticals and four phenolic compounds. At 60 min reaction time, the adsorptive removal by 0.5 g/L WBC700 varied from 31.3% (clofibric acid) to 97.6% (4-chlorophenol), while the apparent removal ranged from 36.1% (clofibric acid) to 99.5% (4-chlorophenol) when 0.5 g/L WBC700 and 1.0 mM PDS were applied. The oxidation of the micropollutants involves electron transfer mechanism via the surface-confined metastable reactive complexes (WBC-PDS*), which was verified by electrochemical tests, quenching experiments, electron paramagnetic resonance, Fourier transform infrared and in-situ Raman spectroscopy. The observed pseudo first-order kinetic constant (k(obs)) of organic removal did not exhibit a good correlation with its electrochemical redox descriptor (half-wave potential, phi(1/2), for example) as reported in the previous studies. Instead, the surface oxidation rate constant (k(oxid)), determined from a dynamic model considering liquid-solid mass transfer of micropollutant and the sequent surface oxidation by WBC-PDS* complexes, was highly related to phi(1/2). In parallel, the liquid-solid mass transfer coefficient (K(L)a) of micropollutant was obtained from a similar model excluding the surface oxidation, and k(obs) showed a more significant association with K(L)a than with adsorption capacity (Q(e)). This study provides a promising approach to understand the role of adsorption and surface oxidation in an electron transfer-dominated persulfate activation process.
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