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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front. Chem. Sci. Eng.    2023, Vol. 17 Issue (7) : 918-929    https://doi.org/10.1007/s11705-023-2305-0
RESEARCH ARTICLE
Cuprous oxide/copper oxide interpenetrated into ordered mesoporous cellulose-based carbon aerogels for efficient photocatalytic degradation of methylene blue
Rui Cui, Dongnv Jin, Gaojie Jiao, Zhendong Liu, Jiliang Ma(), Runcang Sun()
Liaoning Key Lab of Lignocellulose Chemistry and Biomaterials, Liaoning Collaborative Innovation Center for Lignocellulosic Biorefinery, College of Light Industry and Chemical Engineering, Dalian Polytechnic University, Dalian 116034, China
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Abstract

The casual discharge of dyes from industrial settings has seriously polluted global water systems. Owing to the abundance of biomass resources, preparing photocatalysts for photocatalytic degradation of dyes is significant; however, it still remains challenging. In this work, a cuprous oxide/copper oxide composite was interpenetrated onto carbon nanosheets of cellulose-based flexible carbon aerogels (Cu2O/CuO@CAx) via a simple freeze-drying-calcination method. The introduction of the carbon aerogel effectively prevents the aggregation of the cuprous oxide/copper oxide composite. In addition, Cu2O/CuO@CA0.2 has a larger specific surface area, stronger charge transfer capacity, and lower recombination rate of photogenerated carriers than copper oxide. Moreover, Cu2O/CuO@CA0.2 exhibited high photocatalytic activity in decomposing methylene blue, with a degradation rate reaching up to 99.09% in 60 min. The active oxidation species in the photocatalytic degradation process were systematically investigated by electron spin resonance characterization and poisoning experiments, among which singlet oxygen played a major role. In conclusion, this work provides an effective method for preparing photocatalysts using biomass resources in combination with different metal oxides. It also promotes the development of photocatalytic degradation of dyes.

Keywords carbon aerogel      photocatalysis      dye degradation      biomass      cuprous oxide/copper oxide     
Corresponding Author(s): Jiliang Ma,Runcang Sun   
About author:

* These authors contributed equally to this work.

Online First Date: 17 May 2023    Issue Date: 05 July 2023
 Cite this article:   
Rui Cui,Dongnv Jin,Gaojie Jiao, et al. Cuprous oxide/copper oxide interpenetrated into ordered mesoporous cellulose-based carbon aerogels for efficient photocatalytic degradation of methylene blue[J]. Front. Chem. Sci. Eng., 2023, 17(7): 918-929.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-023-2305-0
https://academic.hep.com.cn/fcse/EN/Y2023/V17/I7/918
Fig.1  (a) Schematic of Cu2O/CuO@CAx preparation. (b–e) Scanning electron microscopy images of Cu2O/CuO@CA0.2. Elemental mapping images of Cu2O/CuO@CA0.2: (f) C, (g) N, (h) O and (i) Cu. (j) Energy-dispersive X-ray spectroscopy of Cu2O/CuO@CA0.2.
Fig.2  (a) N2 adsorption?desorption isotherms and (b) Barret?Joyner?Halenda pore size distributions of copper oxide (CuO) and Cu2O/CuO@CA0.2; (c) Fourier transform infrared (FTIR) spectra of CuO and Cu2O/CuO@CA0.2 and (d) its local zoom of FTIR spectrum for Cu2O/CuO@CA0.2.
Fig.3  (a) X-ray diffraction patterns of copper oxide and Cu2O/CuO@CA0.2; X-ray photoelectron spectroscopy (XPS) spectra of Cu2O/CuO@CA0.2: (b) XPS survey spectrum, (c) C 1s, (d) N 1s, (e) O 1s and (f) Cu 2p.
Fig.4  Mott?Schottky plots of (a) copper oxide (CuO) and (b) Cu2O/CuO@CA0.2; (c, d) ultraviolet photoelectron spectroscopy of CuO and Cu2O/CuO@CA0.2; (e) periodic ON/OFF photocurrent response of CuO and Cu2O/CuO@CA0.2 in 0.1 mol·L?1 Na2SO4 electrolyte under visible light irradiation (λ > 420 nm) at 0.5 V vs. Ag/AgCl electrode; (f) electrochemical impedance spectroscopy Nyquist plots in the visible light illumination of CuO and Cu2O/CuO@CA0.2.
Fig.5  The effects of (a) pH and (b) catalyst dosage on the photocatalytic degradation of methylene blue using Cu2O/CuO@CA0.2; the effect of (c) reaction time on the photocatalytic degradation of methylene blue using Cu2O/CuO@CAx; photocatalytic degradation kinetics of methylene blue using (d, g) Cu2O/CuO@CA0.1, (e, h) Cu2O/CuO@CA0.2 and (f, i) Cu2O/CuO@CA0.3.
Fig.6  2,2,6,6-Tetramethylpiperidine-N-oxide electron spin resonance (ESR) spin labeling for (a) electrons and (b) holes, 5,5-dimethyl-1-pyrroline-N-oxide ESR spin trapping for (c) superoxide radical and (d) hydroxyl radical as well as 2,2,6,6-tetramethyl-4-piperidone-1-yloxy ESR spin labeling for (e) singlet oxygen (control: under the dark conditions or irradiation without samples); (f) the effect of different active oxidation species on methylene blue’s degradation.
Fig.7  The possible photocatalytic mechanism for degradation of methylene blue using Cu2O/CuO@CA0.2.
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