Chinese Journal of Catalysis ›› 2024, Vol. 66: 181-194.DOI: 10.1016/S1872-2067(24)60132-4
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Lu Zhanga,b,1, Hourui Zhanga,b,1, Dongyang Zhuc, Zihan Fua,b, Shuangshi Donga,b, Cong Lyua,b,*()
Received:
2024-06-19
Accepted:
2024-09-04
Online:
2024-11-18
Published:
2024-11-10
Contact:
*E-mail: About author:
1Contributed equally to this work.
Supported by:
Lu Zhang, Hourui Zhang, Dongyang Zhu, Zihan Fu, Shuangshi Dong, Cong Lyu. Construction of multivariate donor-acceptor heterojunction in covalent organic frameworks for enhanced photocatalytic oxidation: Regulating electron transfer and superoxide radical generation[J]. Chinese Journal of Catalysis, 2024, 66: 181-194.
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URL: https://www.cjcatal.com/EN/10.1016/S1872-2067(24)60132-4
Fig. 2. The chemical identity of COFs. PXRD patterns (a1-a4), FTIR patterns (b1-b4), 13C CP-MAS solid-state NMR spectra (c1-c4), and SEM images (d1-d4) of COF-H and COF-Br@R (R = OCH3, OC3H7, and OC8H17).
Fig. 3. Optoelectronic characteristics of COFs. The UV-vis diffuse reflectance spectra (DRS) spectra and Tauc plot analysis (illustration of (a)) (a), band alignment (b), Photocurrents (c), LSV plot (d), EIS Nyquist plot (e), Tafel curve (f), photoluminescence spectra (g), EPR spectra (h) for detecting electron, and quantum yield (QY) (i) of COF-H, COF-Br, and COF-Br@R (R = OCH3, OC3H7, and OC8H17).
Fig. 4. Evaluation of the photocatalytic performance of COFs. The photocatalytic degradation of TC over COF-H and COF-Br@R (R = OCH3, OC3H7, and OC8H17) (a) and its reaction rate constant (b). (c) Photocatalytic degradation of TC over COF-Br@OCH3 with different Br/OCH3 ratio. (d) Photocatalytic degradation of TC over COF-Cl and COF-Cl@R (R = OCH3, OC3H7, and OC8H17). (e) Ratio to the values of COF-Br@R. (f) Comparison of the kinetic rate constants of degradation previously reported in the degradation system of TC with this work. Conditions: [TC] = 20 mg L-1, [COFs] = 0.3 g L-1.
Fig. 5. Identification of reactive species in photocatalytic degradation of TC by COFs. Photocatalytic degradation of TC over COF-H (a), COF-Br@CH3 (b), COF-Br@OC3H7 (c), and COF-Br@OC8H17 (d) with different scavengers. (e) Degradation efficiency under different scavengers in COF-H and COF-Br@R (R = OCH3, OC3H7, and OC8H17) system. (f) Photocatalytic degradation of NBT over COF-H and COF-Br@R and concentration of generated ?O2-. ESR spectrum for detecting h+ (g), ?O2- (h), and ?OH (i) in COFs photocatalytic systems. Conditions: [TC] = 20 mg L-1, [COFs] = 0.3 g L-1, [p-BQ] = [EDTA-2Na] = [tBA] = 100 mmol L-1, [NBT] = 0.05 mmol L-1.
Fig. 6. The DFT calculations. Hole (blue) and electron (green) distribution (a1-a4) and electrostatic potential calculations (b1-b4) of COF-H, COF-Br, COF-Br@OCH3, and COF-Br@OC3H7. (c) In-situ ATR-FTIR spectra of COF-Br@OCH3. The energy barrier of H2O oxidation to *OH (d) and O2 reduction to *OOH (e) on the ortho-carbon atom of the benzene ring, and O2 reduction to *O2 and *OOH (f) on the carbon atom on the imine bond in COF-H and COF-Br@OCH3.
Fig. 7. Mechanism of photocatalytic degradation of TC over traditional D-A COFs (COF-H) and multivariate D-A COFs (COF-Br@R, R = OCH3, OC3H7, and OC8H17) under visible light irradiation.
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