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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2021, Vol. 15 Issue (4) : 52    https://doi.org/10.1007/s11783-020-1344-8
RESEARCH ARTICLE
Fabrication of highly efficient Bi2WO6/CuS composite for visible-light photocatalytic removal of organic pollutants and Cr(VI) from wastewater
Wei Mao1,2, Lixun Zhang1,2, Tianye Wang3,4, Yichen Bai3,4, Yuntao Guan1,2()
1. Guangdong Provincial Engineering Technology Research Center for Urban Water Cycle and Water Environment Safety, Tsinghua Shenzhen International Graduate School, Tsinghua University, Shenzhen 518055, China
2. State Environmental Protection Key Laboratory of Microorganism Application and Risk Control, School of Environment, Tsinghua University, Beijing 100084, China
3. College of Resources and Environment, Jilin Agricultural University, Changchun 130000, China
4. Key Laboratory of Soil Resource Sustainable Utilization for Jilin Province Commodity Grain Bases, Changchun 130118, China
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Abstract

• A novel Bi2WO6/CuS composite was fabricated by a facile solvothermal method.

• This composite efficiently removed organic pollutants and Cr(VI) by photocatalysis.

• The DOM could promoted synchronous removal of organic pollutants and Cr(VI).

• This composite could be applied at a wide pH range in photocatalytic reactions.

• Possible photocatalytic mechanisms of organic pollutants and Cr(VI) were proposed.

A visible-light-driven Bi2WO6/CuS p-n heterojunction was fabricated using an easy solvothermal method. The Bi2WO6/CuS exhibited high photocatalytic activity in a mixed system containing rhodamine B (RhB), tetracycline hydrochloride (TCH), and Cr (VI) under natural conditions. Approximately 98.8% of the RhB (10 mg/L), 87.6% of the TCH (10 mg/L) and 95.1% of the Cr(VI) (15 mg/L) were simultaneously removed from a mixed solution within 105 min. The removal efficiencies of TCH and Cr(VI) increased by 12.9% and 20.4%, respectively, in the mixed solution, compared with the single solutions. This is mainly ascribed to the simultaneous consumption electrons and holes, which increases the amount of excited electrons/holes and enhances the separation efficiency of photogenerated electrons and holes. Bi2WO6/CuS can be applied over a wide pH range (2–6) with strong photocatalytic activity for RhB, TCH and Cr(VI). Coexisiting dissolved organic matter in the solution significantly promoted the removal of TCH (from 74.7% to 87.2%) and Cr(VI) (from 75.7% to 99.9%) because it accelerated the separation of electrons and holes by consuming holes as an electron acceptor. Removal mechanisms of RhB, TCH, and Cr(VI) were proposed, Bi2WO6/CuS was formed into a p-n heterojunction to efficiently separate and transfer photoelectrons and holes so as to drive photocatalytic reactions. Specifically, when reducing pollutants (e.g., TCH) and oxidizing pollutants (e.g., Cr(VI)) coexist in wastewater, the p-n heterojunction in Bi2WO6/CuS acts as a “bridge” to shorten the electron transport and thus simultaneously increase the removal efficiencies of both types of pollutants.

Keywords Photocatalysis      Bi2WO6/CuS      Organic pollutants      Cr(VI)      Synergistic effect     
Corresponding Author(s): Yuntao Guan   
Issue Date: 10 October 2020
 Cite this article:   
Wei Mao,Lixun Zhang,Tianye Wang, et al. Fabrication of highly efficient Bi2WO6/CuS composite for visible-light photocatalytic removal of organic pollutants and Cr(VI) from wastewater[J]. Front. Environ. Sci. Eng., 2021, 15(4): 52.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-020-1344-8
https://academic.hep.com.cn/fese/EN/Y2021/V15/I4/52
Fig.1  (a) XRD patterns and (b) FT-IR spectra of photocatalysts.
Fig.2  SEM images of (a) Bi2WO6, (b) CuS, and (c) Bi2WO6/CuS-3; (d) –(e) TEM (SAED) and HRTEM images of Bi2WO6/CuS-3, and (f) EDS spectra of Bi2WO6/CuS-3.
Fig.3  XPS spectra of Bi2WO6/CuS-3: (a) survey spectra, (b)W 4f, (c) Bi 4f, and (d) Cu 2p.
Fig.4  Results of (a) UV-vis DRS, (b) band gaps, (c) EIS Nyquist, and (d) PL spectra of photocatalysts.
Fig.5  (a) Photodegradation kinetics of RhB, (b) first-order kinetic model stimulation, (c) UV-visible spectra of RhB with Bi2WO6/CuS-3, and (d) photographs schematic. (Experimental conditions: 0.1 g photocatalyst, 100 mL solution, 10 mg/L RhB).
Fig.6  (a) Photodegradation kinetics of TCH at different initial concentrations, (b) first-order kinetic model stimulation, and (c) photographs schematic. (Experimental conditions: 0.1 g photocatalyst, 100 mL solution, 2–50 mg/L TCH).
Fig.7  (a) Photoreduction kinetics of Cr(VI) at different initial concentrations, (b) first-order kinetic model stimulation, and (c) Photographs schematic. (Experimental conditions: 0.1 g photocatalyst, 100 mL solution, 5–35 mg/L Cr(VI)).
Fig.8  (a) Results of simultaneous photocatalytic removal of RhB, TCH, and Cr(VI) in mixed systems and (b) comparison of photocatalytic removal efficiencies of RhB, TCH, and Cr(VI) in single and mixed systems. (Experimental conditions: 0.1 g Bi2WO6/CuS-3, 100 mL solution, 10 mg/L RhB, 10 mg/L TCH, and/or 15 mg/L Cr(VI)).
Fig.9  Illustration of photocatalytic removal mechanisms of pure (a) RhB, (b) TCH, and (c) Cr(VI), and (d) mixed RhB, TCH, and Cr(VI) from wastewater by Bi2WO6/CuS-3 under visible-light irradiation.
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