Enhanced interface electric field in an all-solid-state Z-scheme Ag/AgCl/GCNT heterojunction for facilitating photocatalytic CO2 reduction performance

Jintao Dong a, Yi Zhang ab, Lu Liu c, Xuemin Zhang a, Lina Li a, Gaopeng Liu d, Huaming Li a, Pengcheng Yan *a and Jiexiang Xia *a
aSchool of Chemistry and Chemical Engineering, Jiangsu University, Zhenjiang 212013, China. E-mail: yanpengcheng@ujs.edu.cn; xjx@ujs.edu.cn
bDepartment of Applied Physics, The Hong Kong Polytechnic University, Kowloon, Hong Kong 999077, P. R. China
cFaculty of materials Science and Chemistry, China University of Geoscience, Wuhan 430074, China
dSchool of Chemistry and Chemical Engineering of Hainan Normal University, Key Laboratory of Electrochemical Energy Storage and Energy Conversion of Hainan Province, Haikou 571158, China

Received 18th December 2024 , Accepted 31st March 2025

First published on 31st March 2025


Abstract

composites of g-C3N4 nanotubes with anchored Ag/AgCl nanoparticles (AC/GCNT) were prepared using supramolecular self-assembly and an inert-atmosphere calcination method. The AC/GCNT-2 composites exhibits remarkably enhanced photocatalytic CO generation performance (25.10 μmol g−1 h−1) without cocatalysts, hole scavengers, or an organic auxiliary agent, reaching a value 4.41 times that of GCNT materials (5.68 μmol g−1 h−1).


The continuous increase of the atmospheric CO2 concentration can cause global warming, which can affect green-plant growth, ocean circulation directions, and the global distribution of water resources.1,2 Simultaneously, CO2 can be considered as a significant C1 resource for further resource utilization and energy development.3,4 The strategy of CO2 resource utilization can answer a double purpose: CO2 emission reduction and clean energy generation.5 The photocatalytic CO2 reduction process can realize efficient conversion of solar energy and CO2 into easily-stored and transportable chemical energy without being driven by other external energy, which is conducive to CO2 resource conversion and utilization, and large-scale storage of clean energy.6,7 Nevertheless, the conversion efficiency of the photocatalytic CO2 reduction process is primarily affected by the high structural stability of the linear CO2 molecule and the delayed dynamics of photogenerated-carrier migration.8 Significantly, the construction of efficient photocatalysts is deemed the decisive factor for the photocatalytic CO2 conversion process, which relies on enhancing the solar-energy conversion efficiency.

Being a non-toxic and inexpensive raw materials, with a large active surface and controllable band structure, g-C3N4 has attracted widespread attention and systematic research in the field of photocatalytic CO2 reduction.9 Nevertheless, attributed to their π-conjugated structure and non-metallic properties, the internal electric field (IEF) strength and CO2 activation site numbers of g-C3N4 materials should be further optimized via various modification strategies.10,11 The construction of a heterogeneous interface on the surface of g-C3N4 nanotube materials has gradually become a common strategy for enhancement of photocatalytic performance by forming efficient electron migration pathways and promoting the directional transport of photogenerated carriers.12,13 The ability of g-C3N4 nanotube materials to separate photogenerated electrons can be effectively enhanced through constructing heterogeneous interfaces on their surfaces via coupling with other photo-active materials, which realizes efficient photocatalytic conversion of CO2.

The morphologies of the GCNT materials, AgCl nanoparticles and AC/GCNT-2 composites were analysed using SEM and TEM measurements. As demonstrated in Fig. S1 (ESI) and Fig. 1a and b, the GCNT materials exhibits a porous nanotube structure with a diameter of about 200 nm. Furthermore, the size of the AgCl materials obtained via a hydrothermal method is from 20 nm to 100 nm (Fig. 1c). As shown in Fig. S2 (ESI) and Fig. 1d, the AC/GCNT-2 composites still maintains a porous nanotube morphology. Significantly, multitudinous nanoparticles with a diameter of 20 nm are uniformly dispersed on the surface of the AC/GCNT-2 composites. The selected area electron diffraction (SAED) pattern (Fig. 1f) of the AC/GCNT-2 composites indicates the presence of lattice diffraction fringes with spacings of 0.235 and 0.196 nm, corresponding to the Ag (1 1 1) and AgCl (2 2 0) crystalline surfaces, respectively, which demonstrates that Ag/AgCl nanoparticle-loaded GCNT materials were successfully prepared via hydrothermal and calcination methods.14,15 As indicated in Fig. 1g–j, the four elements C, N, Ag and Cl uniformly appear on the surface of the AC/GCNT-2 composites, further demonstrating the uniform distribution of Ag/AgCl nanoparticles on the GCNT materials.


image file: d4cc06531j-f1.tif
Fig. 1 TEM images of (a) and (b) GCNT, (c) AgCl, (d) and (e) AC/GCNT-2 composites; (f) SAED image and (g)–(j) mapping images of AC/GCNT-2 composites.

As shown in Fig. 2a, a conspicuous diffraction peak situated at 27.1° has been observed in the X-ray powder diffraction (XRD) patterns of the GCNT materials, corresponding to the (0 0 2) crystalline plane of the g-C3N4 materials. Furthermore, the numerous diffraction peaks located in the XRD patterns of the AgCl materials match with those of cubic AgCl (PDF#85-1355). The diffraction peaks situated at 38.1°, 44.3°, 64.5°, and 77.4° in the XRD patterns of the AC/GCNT-x composites correspond to the PDF#87-0717 standard card, indicating the presence of elemental Ag in the AC/GCNT-x composites. Furthermore, the weak diffraction peaks corresponding to the AgCl materials are only observed in the AC/GCNT-3 composites, which indicates that further characterization should be carried out to verify the presence of AgCl in the other AC/GCNT-x composites. As indicated in Fig. 2b, the characteristic vibrational peaks in the FT-IR spectra of GCNT and the AC/GCNT-x composites, located at 808 cm−1, 1200–1700 cm−1, and 2200 cm−1, can be attributed to triazine rings, conjugated C–N heterocyclic structures and –C[triple bond, length as m-dash]N groups in the GCNT materials.16–18 A band in the region of 1200 to 1700 cm−1 for GCNT and the AC/GCNT-2 composites has been observed (Fig. S3, ESI), which corresponds to disordered graphitic carbon–nitrogen vibrations.


image file: d4cc06531j-f2.tif
Fig. 2 (a) XRD patterns of GCNT, AgCl and AC/GCNT-x composites, and (b) FT-IR spectra of GCNT and AC/GCNT-x composites; XPS spectra of GCNT and the AC/GCNT-2 composites: (c) C 1s, (d) N 1s, (e) Ag 3d and (f) Cl 2p.

X-ray photoelectron spectroscopy (XPS) measurements were employed to investigate the chemical composition and elemental valence states of the GCNT and AC/GCNT-2 composites. As demonstrated in the C 1s high-resolution spectra of GCNT and the AC/GCNT-2 composites (Fig. 2c), three characteristic peaks are located at the binding energies of 284.8 eV, 286.7 eV, and 288.0 eV, which corresponds to C–C/C[double bond, length as m-dash]C, C[triple bond, length as m-dash]N, and N–C[double bond, length as m-dash]N bonds, indicating that the Ag/AgCl nanoparticles loading has not caused an obvious impact on the basic structure of the GCNT materials.19 The N 1s XPS spectra of GCNT and the AC/GCNT-2 composites (Fig. 2d) are Gaussian fitted to three characteristic peaks located at binding energies of 398.6 eV, 400.1 eV, and 401.1 eV, corresponding to the C–N[double bond, length as m-dash]C bond in C–N heterocycles, and N–(C)3 and C–N–H bonds.20,21 Furthermore, the high-resolution Ag 3d spectrum of the AC/GCNT-2 composites has been divided into two peaks located at binding energies of 367.4 eV and 373.6 eV, corresponding to the Ag+ of the AgCl materials. Furthermore, two peaks appear at binding energies of 368.1 eV and 374.1 eV, related to the Ag0 valence state, suggesting that Ag/AgCl nanoparticles are anchored in the structure of the AC/GCNT-2 composites.22,23 As indicated in Fig. 2f, an obvious characteristic peak corresponding to Cl in the high-resolution Cl 2p spectra has not been observed in the GCNT materials, indicating that the Cl in NH2OH·HCl has not been introduced into the GCNT materials. Moreover, the characteristic peaks in the AC/GCNT-2 composites are located at the binding energies of 197.9 eV and 199.5 eV, and are related to the Cl 2p3/2 and Cl 2p1/2 orbitals of the AgCl materials.24,25 The XPS analysis results further indicate that the Ag/AgCl nanoparticles were successfully loaded on the GCNT materials.

The photocatalytic CO2 conversion performance of the GCNT and AC/GCNT-x composite was investigated to evaluate the effect of Ag/AgCl particle introduction under conditions with pure water, no sacrificial agent, and no catalytic additive. The photocatalytic CO generation rate of the GCNT materials (Fig. 3a) reaches 5.68 μmol g−1 h−1, and AC/GCNT-x composite exhibit a significantly enhanced photocatalytic CO generation ability compared with that of the GCNT materials. The photocatalytic CO generation rates of the AC/GCNT-1, AC/GCNT-2, and AC/GCNT-3 composite reach 12.11, 25.10, and 12.77 μmol g−1 h−1 (Fig. 3b), which are 2.13, 4.41, and 2.25 times higher than that of the GCNT materials. Compared with previous reports about other C3N4-based materials for photocatalytic CO2 reduction (Table S2, ESI), AC/GCNT-2 composites possesses a high CO evolution rate and selectivity. The continuous photocatalytic CO2 reduction tests were performed on the AC/GCNT-2 composites to evaluate the reaction stability of the AC/GCNT-2 composites. As shown in Fig. 3c, the photocatalytic CO generation rate of the AC/GCNT-2 composites keeps a continuous increase in a 40 h continuous photocatalytic CO2 reduction measurement, indicating that the AC/GCNT-2 composites possesses good CO2 reduction stability. The control experiments (Fig. 3d) indicate that light, the AC/GCNT-2 composites and injecting CO2 are indispensable reaction conditions for realizing photocatalytic CO2 conversion.


image file: d4cc06531j-f3.tif
Fig. 3 (a) The photocatalytic CO evolution performance and (b) the photocatalytic CO evolution rate of the GCNT materials and AC/GCNT-x composites; (c) the stability of AC/GCNT-x composites for photocatalytic CO2 conversion; (d) the control experiments for the photocatalytic CO evolution rate of the AC/GCNT-2 composites.

The transient photocurrent response, electrochemical impedance spectroscopy (EIS) results, photoluminescence (PL) spectra and time-resolved PL (TRPL) decay curves (Fig. S4a–d, ESI) of the GCNT materials and AC/GCNT-2 composites indicate that the AC/GCNT-2 composites possesses enhanced photogenerated-electron migration efficiency.26 The distribution model for the electric field was constructed to further elaborate on the IEF enhancement mechanism of the AC/GCNT composites between the GCNT materials and Ag/AgCl nanoparticles (Fig. 4a). As indicated in Fig. 4b and d, a uniform surface electric field distribution has been observed in the GCNT materials, which demonstrates that the electronic transmission efficiency of the GCNT materials needs to be further strengthened.27 As demonstrated in Fig. 4c, a “hot spot” is significantly observed in the centre position of the Ag/AgCl nanoparticles and a remarkable enhanced electric field distribution appears in the interface of the GCNT materials and Ag/AgCl nanoparticles at 470 nm, which indicates that the introduced Ag/AgCl nanoparticles can effectively increase the IEF intensity. Furthermore, the “hot spot” appears at the periphery of the Ag/AgCl nanoparticles at 530 nm, which strengthens the IEF between the GCNT materials and Ag/AgCl nanoparticles to accelerate electron transport to CO2 reduction sites. Accordingly, the simulation of the electric field distribution shows that the introduction of Ag/AgCl nanoparticles can achieve efficient migration and utilization of electrons for participation in catalytic CO2 conversion.


image file: d4cc06531j-f4.tif
Fig. 4 (a) The schematic diagram of the AC/GCNT-2 composites; the COMSOL simulation results of the GCNT materials at (b) 470 nm and (d) 530 nm, and the AC/GCNT-2 composites with the excitation light wavelength at (c) 470 nm and (e) 530 nm; (f) the CO2 adsorption isotherm of GCNT and the AC/GCNT-2 composites; (g) in situ FT-IR spectra for the photocatalytic CO2 reduction process of the AC/GCNT-2 composites; (h) schematic illustration of the possible charge transfer mechanism in the AC/GCNT composites.

The CO2 adsorption performance of a photocatalyst is perceived as a considerable evaluation factor for determining the promotion mechanism of the photocatalytic CO generation rate. As indicated in Fig. 4f, the maximum value of CO2 quantity adsorbed for the GCNT materials is 4.86 cm3 per g STP, which reaches 3.23-fold that of the AC/GCNT-2 composites (1.50 cm3 per g STP), further demonstrating that the determining factor is the strengthening of the IEF by heterojunction construction rather than CO2 adsorption performance. The investigation of intermediate generation in the photocatalytic CO2 reduction process using in situ spectroscopy possesses high research significance and scientific value for analysing the photocatalytic CO2 reduction process. As observed in Fig. 4g, in the in situ FT-IR spectra, the intensity of the vibrational peaks corresponding to m-CO32− (1347 cm−1), HCO3 (1455 cm−1), COOH* (1517 cm−1), CO2 (1713 cm−1), and HCOOH (1735 cm−1) intermediates gradually increases with temporal evolution, indicating that the photogenerated electrons continuously interact with CO2 adsorbed on the AC/GCNT-2 composites to generate reaction intermediates.28 The energy band structure of the AgCl and GCNT materials has been analysed using (αhv)2vs. hv curves29 (Fig. S5a and b, ESI) and Mott–Schottky plots (Fig. S5c and d, ESI). Based on electron spin resonance (ESR) spectra (Fig. S6a and b, ESI) and work-function calculations (Fig. S7a–c, ESI), an all-solid-state Z-scheme charge transfer mechanism formed by the Ag, AgCl and GCTN materials has been proposed, as shown in Fig. 4h. The TEMPO quenching (Fig. S8a and b, ESI) and Kelvin probe force microscopy (KPFM) images (Fig. S9a–d, ESI) further indicate that the AC/GCNT-2 composites possesses high oxidation–reduction ability and spatial distribution of photogenerated carriers.

In summary, composites of g-C3N4 nanotubes with anchored Ag/AgCl nanoparticles (AC/GCNT) were successfully constructed. The high-performance directional migration of photogenerated electrons endows the AC/GCNT composites with a high photocatalytic CO2 reduction rate (25.10 μmol g−1 h−1), which is 4.41 times that of the GCNT materials (5.68 μmol g−1 h−1). The photogenerated carrier migration path in the all-solid-state Z-scheme AC/GCNT heterojunction formed by the Ag/AgCl nanoparticles and GCNT materials has been revealed by ESR spectra and energy band structure analysis. The simulation of the electric field distribution using COMSOL software and the CO2 adsorption isotherms of GCNT and the AC/GCNT-2 composites indicate that an intensified IEF strength has a crucial function, rather than CO2 absorption performance. This manuscript inspires the construction of all-solid-state Z-scheme heterojunctions and contributes a research reference for g-C3N4-based composites for photocatalytic CO2 conversion processes.

This work was financially supported by the National Natural Science Foundation of China (no. 22378172, 22202086).

Data availability

The data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of interest

There are no conflicts to declare.

References

  1. H. S. Baker, R. J. Millar, D. J. Karoly, U. Beyerle, B. P. Guillod, D. Mitchell, H. Shiogama, S. Sparrow, T. Woollings and R. A. Myles, Nat. Clim. Change, 2018, 8, 604–608 CrossRef CAS.
  2. R. G. Hilton and J. A. West, Nat. Rev. Earth Environ., 2020, 1, 284–299 CrossRef CAS.
  3. E. Orsi, P. I. Nikel, L. K. Nielsen and S. Donati, Nat. Commun., 2023, 14, 6673 CrossRef CAS.
  4. X. L. Zhu, H. B. Zong, C. J. V. Pérez, H. H. Miao, W. Sun, Z. M. Yuan, S. H. Wang, G. X. Zeng, H. Xu, Z. Y. Jiang and G. A. Ozin, Angew. Chem., Int. Ed., 2023, 62, e202218694 CrossRef CAS.
  5. J. T. Dong, S. N. Ji, Y. Zhang, M. X. Ji, B. Wang, Y. J. Li, Z. G. Chen, J. X. Xia and H. M. Li, Acta Phys. -Chim. Sin., 2023, 39, 2212011 Search PubMed.
  6. B. Wang, H. L. Chen, W. Zhang, H. Y. Liu, Z. K. Zheng, F. C. Huang, J. Y. Liu, G. P. Liu, X. W. Yan, Y.-X. Weng, H. M. Li, Y. B. She, P. K. Chu and J. X. Xia, Adv. Mater., 2024, 36, 2312676 CrossRef CAS PubMed.
  7. L. N. Li, G. P. Liu, S. Q. Cao, J. T. Dong, B. Wang, Y. B. She, J. X. Xia and H. M. Li, Appl. Catal., B, 2024, 124904 Search PubMed.
  8. J. T. Dong, J. Z. Zhao, X. W. Yan, L. N. Li, G. P. Liu, M. X. Ji, B. Wang, Y. B. She, H. M. Li and J. X. Xia, Appl. Catal., B, 2024, 351, 123993 CrossRef CAS.
  9. Q. Q. Lu, K. Eid, W. P. Li, A. M. Abdullah, G. B. Xu and R. S. Varma, Green Chem., 2021, 23, 5394–5428 RSC.
  10. X. X. Lv, X. M. You, J. Y. Pang, H. Zhou, Z. J. Huang, Y. F. Yao and X. L. Wang, Chem. Commun., 2024, 60, 4652–4655 RSC.
  11. S. Hu, P. Z. Qiao, X. L. Yi, Y. M. Lei, H. M. Hu, J. H. Ye and D. F. Wang, Angew. Chem., Int. Ed., 2022, 61, e202206579 CrossRef PubMed.
  12. L. Chen, H. Y. Li, H. M. Li, W. S. Qi, Q. Zhang, J. Zhu, P. Zhao and S. D. Yang, Appl. Catal., B, 2021, 318, 121863 CrossRef.
  13. W. H. Liu, S. Q. Hu, Y. Wang, B. B. Zhang, R. Y. Jin and G. S. Hu, Nanoscale Res. Lett., 2019, 14, 108 CrossRef PubMed.
  14. S. Bera, S. Ghosh and R. N. Basu, J. Alloys Compd., 2020, 830, 154527 CrossRef CAS.
  15. F. Wang, Z. Li, H. H. Wang, M. Chen, C. B. Zhang, P. Ning and H. He, Nano Res., 2022, 15, 452–456 CrossRef CAS.
  16. D. B. Nimbalkar, P. V. R. K. Ramacharyulu, S. R. Sahoo, J. R. Chen, C. M. Chang, A. N. Maity and S. C. Ke, Appl. Catal., B, 2020, 273, 119036 CrossRef CAS.
  17. Z. J. Liu, L. Wang, P. F. Liu, K. R. Zhao, S. Y. Ye and G. X. Liang, Food Chem., 2021, 357, 129753 CrossRef CAS PubMed.
  18. L. X. Ma, Y. P. Gao, B. Q. Wei, L. Huang, N. Zhang, Q. Weng, L. Zhang, S. Z. Liu and R. B. Jiang, ACS Catal., 2024, 14, 2775–2786 CrossRef CAS.
  19. W. Luo, Y. L. Li, J. S. Wang, J. C. Liu, N. Zhang, M. D. Zhao, J. S. Wu, W. Y. Zhou and L. Z. Wang, Nano Energy, 2021, 87, 106168 CrossRef CAS.
  20. Y. Dai, W. R. Peng, Y. Ji, J. Wei, J. H. Che, Y. Q. Huang, W. H. Huang, W. M. Yang and W. Z. Xu, J. Food Sci., 2024, 89, 8022–8035 CrossRef CAS PubMed.
  21. Q. Li, Y. Q. Jiao, Y. Q. Tang, J. Zhou, B. G. Wu, B. J. Jiang and H. G. Fu, J. Am. Chem. Soc., 2023, 145, 20837–20848 CrossRef CAS PubMed.
  22. D. Sun, Y. Zhang, Y. F. Liu, Z. G. Wang, X. C. Chen, Z. Y. Meng, S. F. Kang, Y. Y. Zheng, L. F. Cui, M. L. Chen, M. D. Dong and B. Hu, Chem. Eng. J., 2020, 384, 123259 CrossRef CAS.
  23. R. Qiao, M. M. Mao, Y. J. Zhong, J. Q. Ning and Y. Hu, Inorg. Chem., 2015, 54, 9033–9039 CrossRef CAS PubMed.
  24. Y. T. Yu, Z. J. Zhu, F. Chen, T. Y. Ma and H. W. Huang, Adv. Mater., 2024, 36, 2413835 CrossRef CAS PubMed.
  25. F. R. Guo, C. L. Mao, C. Liang, P. Xing, L. H. Yu, Y. Shi, S. B. Cao, F. Y. Wang, X. Liu, Z. H. Ai and L. Z. Zhang, Angew. Chem., Int. Ed., 2023, 62, e202314243 CrossRef CAS PubMed.
  26. S. Bera, S. Ghosh, T. Maiyalagan and R. N. Basu, ACS Appl. Energy Mater., 2022, 5, 3821–3833 CrossRef CAS.
  27. D. Sun, J. Mao, H. L. Wei, Q. Zhang, L. Cheng, Z. L. Yang and P. W. Li, ACS Appl. Mater. Interfaces, 2022, 14, 28021–28032 CrossRef CAS PubMed.
  28. J. Xie, Z. L. Lu, Y. Feng, J. G. Huang, J. D. Hu, A. Z. Hao and Y. L. Cao, Nano Res., 2024, 17, 297–306 CrossRef CAS.
  29. J. J. Lai, L. J. Ding, Y. Liu, C. H. Fan, F. H. You, J. Wei, J. Qian and K. Wang, Food Chem., 2023, 423, 136285 CrossRef CAS PubMed.

Footnotes

Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4cc06531j
These authors contributed equally.

This journal is © The Royal Society of Chemistry 2025
Click here to see how this site uses Cookies. View our privacy policy here.