4.8 Article

Sulfate radical-based photo-Fenton reaction derived by CuBi2O4 and its composites with α-Bi2O3 under visible light irradiation: Catalyst fabrication, performance and reaction mechanism

Journal

APPLIED CATALYSIS B-ENVIRONMENTAL
Volume 235, Issue -, Pages 264-273

Publisher

ELSEVIER SCIENCE BV
DOI: 10.1016/j.apcatb.2018.04.058

Keywords

CuBi2O4; Sulfate radical photo-Fenton; Rhodamine B; Peroxymonosulfate

Funding

  1. Fundamental Research Funds for the Central Universities [2017PT01]
  2. National Natural Science Foundation of China [51578520, 51378063]
  3. Beijing Natural Science Foundation [L160006]

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Sulfate radical-based photo-Fenton (SR-photo-Fenton) reaction, assisted by visible light irradiation, was achieved by CuBi2O4 and its composites with alpha-Bi2O3 for refractory chemical degradation in aqueous solution. Herein, this catalyst was fabricated by a sol-gel method and the fabrication conditions, including calcination temperature and molar ratio of Cu/Bi, were optimized according to the crystal phase composition, catalytic activity and toxic copper ion leaching. The optimal calcination temperature was 500 degrees C and molar ratio of Bi to Cu was 2.0. The catalyst containing CuBi2O4 and alpha-Bi2O3 showed a higher density of surface-OH which might be the key surface active site than pure CuBi2O4. The influence of initial solution pH, PMS concentration, catalyst dosage and catalyst reuse on rhodamine B (RhB) degradation was investigated. Importantly, calcination at 500 degrees C reverted the catalytic activity of catalyst. Results of electron paramagnetic resonance, competitive radical experiments and surface chemical property characterization demonstrated that the reaction mechanism of this novel SR-photo-Fenton reaction is a combination of interface and solution reactions. In the interface reaction, the transfer of photogenerated electron/hole pairs drives the decomposition of PMS to produce SO4 center dot(-) and center dot OH. Furthermore, the cycling of Cu(I)/Cu(II) facilitated effective PMS activation to generate free radical that was responsible for the degradation of RhB. The second order reaction rate constant between RhB and SO4 center dot(-) was determined to be 0.595-6.436 x 10(10) M-1 S-1 based on the chemical reaction kinetics of radical, which was a first and important report for SO4 center dot(-) chemistry.

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