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Heterojunction architecture of Nb2O5/g-C3N4 for enhancing photocatalytic activity to degrade organic pollutants and deactivate bacteria in water
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Xudong Yanga, Jun Duanb, Xian Zhanga, Hongyu Zhanga, Xinlei Liua, Yueqi Fenga, Maosheng Zhenga, *
Chinese Chemical Letters | 2022, 33(8) : 3792 - 3796
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Chinese Chemical Letters | 2022, 33(8): 3792-3796
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Heterojunction architecture of Nb2O5/g-C3N4 for enhancing photocatalytic activity to degrade organic pollutants and deactivate bacteria in water
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Xudong Yanga, Jun Duanb, Xian Zhanga, Hongyu Zhanga, Xinlei Liua, Yueqi Fenga, Maosheng Zhenga, *
Affiliations
  • a The Key Laboratory of Resources and Environmental System Optimization, Ministry of Education, College of Environmental Science and Engineering, North China Electric Power University, Beijing 102206, China
  • b The Key Laboratory of Water and Sediment Science, Ministry of Education, College of Environment Science and Engineering, Peking University, Beijing 100871, China
Published: 2022-08-15 doi: 10.1016/j.cclet.2021.11.031
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Water pollution has become a serious problem owing to the development of society. Photocatalysis is a promising approach to remove various pollutants in water, such as organic pollutants and antibiotic resistance bacteria. Meanwhile, the design of heterojunction between two semiconductors is an effective path to improve photocatalytic properties due to its potential in improving separation and transfer of photoinduced carriers. In this study, Nb2O5/g-C3N4 (NO/CN) composite materials were prepared through a one-step heating method. Characterizations confirmed successful preparation of NO/CN heterojunction structure and better optical properties than pure g-C3N4 and Nb2O5. NO/CN composite materials showed excellent photocatalytic efficiency for Escherichia coli (E. coli) inactivation (95%) compared with the pure Nb2O5 (10%) and g-C3N4 (77%). Meanwhile, NO/CN exhibited better organic pollutants removal (RhB for 94%, methyl orange (MO) for 15% and methylene blue (MB) for 87%) under visible light, which is likely owing to the heterojunction structure between g-C3N4 and Nb2O5 that leads to the good separation of photogenerated electron-hole pair. Free radical scavenging and electron spin resonance (ESR) experiments demonstrated that superoxide radicals (•O2−) and holes (h+) were the dominant radicals. Therefore, the NO/CN was proposed to be a promising material for effective disinfection and removal of organic contaminants in water treatment.

Graphitic carbon nitride  /  Niobium pentoxide  /  Photocatalysis  /  Escherichia coli disinfection  /  Dyes removal
Xudong Yang, Jun Duan, Xian Zhang, Hongyu Zhang, Xinlei Liu, Yueqi Feng, Maosheng Zheng. Heterojunction architecture of Nb2O5/g-C3N4 for enhancing photocatalytic activity to degrade organic pollutants and deactivate bacteria in water[J]. Chinese Chemical Letters, 2022 , 33 (8) : 3792 -3796 . DOI: 10.1016/j.cclet.2021.11.031
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The rapid development of economy and industries of modern society have caused serious water pollution, which impacts the human health and economy growth [1]. World Health Organization (WHO) reported millions of people death due to the pathogens related disease in uncleaned drinking water, i.e., Escherichia coli (E. coli) [2]. Such pathogens have become increasingly resistant to the conventional disinfection chemicals and methods, so the disinfection efficiencies have been largely weakened [3-5], and the inadequate disinfection of drinking water may cause more health issue of human or even death [6]. Moreover, a large number of persistent and toxic chemicals are produced and used worldwide every year, such as dyes and pharmaceuticals, which also show low treatment efficiencies by conventional wastewater treatment plants (WWTPs) [7-9]. Thus, it is quite urgent to find more advanced approaches to conquer these water pollution problems.
As an environmentally friendly and energy-saving technology, photocatalysis has attracted great interests of researchers for the advanced disinfection and removal of organic chemicals, owing to the usage of clean and renewable solar energy and the formation of reactive oxygen species (ROSs) [10-12]. Under light, the generated of photoinduced electrons (e−) and holes (h+) can interact with dissolved O2 and H2O to form ROSs such as superoxide radicals (•O2−) and hydroxyl radicals (•OH) [13]. Subsequently, these ROSs will attack the bacteria and organic pollutant molecules and show improved removal efficiencies [14].
Graphitic carbon nitride (g-C3N4) has been proved to be a promising photocatalyst for water treatment with a moderate band gap (2.7 eV) and favorable light absorption (wavelength < 460 nm) [15]. The existence of strong C-N bond in the structure makes the g-C3N4 chemically stable and easy to synthesis [16]. However, the application of bare g-C3N4 in pollutant degradation is full of limitation because of the rapid recombination of e− and h+ pairs, which will cause low quantum efficiency [17, 18]. Thus, it is necessary to seek for other ways to solve these questions. Constructing photocatalyst heterojunction is a positive method to enhance the photocatalytic activity owing to the effective separation of photoinduced e− and h+ [19]. Niobium pentoxide (Nb2O5) is a good n-type transition metal oxide semiconductor and has been coupled with various photocatalysts to enhance the photocatalytic performance [20]. For instance, titanium oxide (TiO2) was coupled with Nb2O5 to form heterojunctions, which intensively enhanced photocatalytic activity for α-phenethyl alcohol and the observed rate constant (kobs) was increased by 3 or 8 folds compared to that of rutile TiO2 and Nb2O5, separately [21]. Moreover, the charge band edge (ECB) and valence band edge (EVB) of Nb2O5 (ECB = −0.9 eV, EVB = 2.5 eV) could enable it to match with g-C3N4 (ECB = −1.13 eV, EVB = 1.57 eV) to establish the heterojunction structure [22], which can dramatically facilitate the charge carrier separation and enhance overall photocatalytic performance [23].
Herein, a novel Nb2O5/g-C3N4 (NO/CN) heterojunction photocatalysts were synthesized and a series of characterizations were conducted to investigate its various properties. Besides, the photocatalytic ability of the NO/CN materials is investigated by using E. coli, and certain contaminants such as rhodamine B (RhB), methylene blue (MB), methyl orange (MO). Besides, free radical capture and electron spin resonance (ESR) experiments have shown that •O2− and h+ are the key free radicals. Finally, the possible reaction mechanism was proposed. In summary, this study has theoretical and practical significance in the disinfection process and water treatment, and the elucidation of photocatalytic mechanism. Additionally, experimental details are exhibited in Texts S1-5 in Supplementary information.
The morphologies of original g-C3N4 and NO/CN materials were considered via Transmission electron microscopy (TEM) and high-resolution TEM (HRTEM), which are illustrated in Fig. 1. g-C3N4 displays the sheet structure, which can both reduce the diffused distance of photoinduced charge carriers [24] and offer abundant surface sites to support the Nb2O5 nanoparticles (Figs. 1a and b). As can be seen in Fig. 1c, on the surface of g-C3N4, nanoscale Nb2O5 particles were dispersed with a chain-like structure. The lattice fringe space of Nb2O5 was measured to be 0.309 nm in Fig. 1d, corresponding to the (200) plane of Nb2O5 [25]. It is pretty clear to observe the border of g-C3N4 and Nb2O5, suggesting that Nb2O5 has been successfully patched on g-C3N4. In addition, the energy dispersive X-ray spectroscopy (EDS) and elemental mapping results of NO/CN proved the evenly distributed C, N, O, and Nb elements in the composite materials (Figs. S1 and S2 in Supporting information).
Powder X-ray diffraction (XRD) characterizations were utilized to measure the phase structure and crystallinity of NO/CN material. As shown in Fig. 2a, pure g-C3N4 holds two characteristic peaks at 13.1° and 27.4°, which are attributed to the periodic stacking of tri-s-triazine rings in plane (100) and graphitic layers (002), respectively [26]. Besides, the peaks of Nb2O5 are matched with orthorhombic phase of Nb2O5 (JCPDS No. 19-0862). The NO/CN composite materials barely revealed the characteristic peaks of Nb2O5, which may be attributed to the low content of Nb2O5 and excellent dispersion of Nb2O5 on the g-C3N4 [24]. Additionally, the peaks of g-C3N4 became weak and there is no impurity peak in the NO/CN material, which illustrate that NO/CN has been combined successfully.
X-ray photoelectron spectroscopy (XPS) was recorded to verify the elemental component and valent state of composite material. The NO/CN consists of element C, N, Nb, and O according to the survey spectra (Fig. 2b), which suggests the heterojunction formed between g-C3N4 and Nb2O5. In Fig. 2c, two significant peaks of C 1s were located at 288.0 eV and 284.8 eV, which can be associated with C–C single bond and the double bond between carbon atoms and nitrogen atoms [27]. The high-resolution N 1s spectra (Fig. 2d) exhibits three obvious peaks centered at 398.5 eV, 400.0 eV and 404.3 eV, which can be assigned to sp2-hybridized N (C=N-C), pyrrolic N and π-excitation, respectively [28, 29]. In the high-resolution Nb 3d spectra (Fig. 2e), two apparent peaks located at 206.9 eV and 209.6 eV were attributed to the Nb 3d3/2 and Nb 3d5/2 levels, which was consistent with previous researches of Nb2O5 [30]. Finally, based on Fig. 2f, the high-resolution spectra of O 1s at 532.9 eV are attributed to the lattice oxygen of Nb2O5.
The optical properties of the NO/CN are studied via employing the UV-vis diffused reflectance spectra (UV-DRS). In Fig. 3a, g-C3N4 and Nb2O5 possess the light absorption edge of roughly 440 and 395 nm, respectively, corresponding to the band gap of 2.82 eV and 3.14 eV based on Fig. 3b [31]. The light absorption edge of NO/CN composite exhibited a slight red shift from 440 nm to 449 nm, which indicates that the band gap of NO/CN composite is narrowed (2.76 eV) and can efficiently utilize visible light. Additionally, the band structures of g-C3N4, Nb2O5 and NO/CN are further analyzed by using valence band XPS in Fig. 3c, which were 1.73, 2.67 and 1.94 eV, respectively. According to the results of UV-DRS and VB-XPS, the diagrammatic sketch of band structure of g-C3N4, and NO/CN were depicted in Fig. 3d. Compared with g-C3N4, the VB and CB position of NO/CN were altered after loading Nb2O5, which indicates that the obtained heterojunction structure would benefit the photocatalytic activity.
Then, the photocatalytic experiments were performed to examine the disinfection ability of the as-prepared photocatalysts. As observed in Fig. 4a, the amount of viable cells remain nearly unchanged under visible light irritation within 240 min and only 0.7 log CFU/mL of cells were inactivated with the addition of pure Nb2O5, indicating visible light and pure Nb2O5 have limited impact on E. coli inactivation. In the presence of pure g-C3N4, 5.4 log CFU/mL of cells were disinfected within 240 min, showing the good visible light responses of g-C3N4. The disinfection efficiency was further enhanced in the presence of NO/CN composite material, with 6.67 log CFU/mL of cells disinfected within 240 min. The different disinfection ability of various materials could also be clearly observed in the final bacterial colony counts (Fig. S3 in Supporting information). Apparently, the NO/CN heterojunction photocatalyst has improved photocatalytic sterilization activity than pristine Nb2O5 and g-C3N4, which can be caused by the construction of heterojunction structure and better separation of charge carriers that promotes the generation of ROSs. Meanwhile, potassium ion (K+) was a crucial intracellular ion that can regulate protein synthesis and the decrease of K+ will cause the deactivation of cells [32]. Therefore, the release of K+ was also studied to reflect the damage of cytomembrane. As can be seen in Fig. 4b, the concentration of K+ increased from 0 mg/L to 1.19 mg/L in 60 min, which further verified the death of E. coli cells.
Then, the as-prepared materials were further tested to degrade RhB, MO, and MB dyes as depicted in Figs. 4c and d. An environmentally relevant concentration of 10 mg/L was used as the initial concentration for dyes [33]. The concentration of RhB kept unchanged in the blank experiment within 60 min, indicating RhB could not be degraded under the existence of visible light. The degradation efficiency was increased to 10%, 45% and 94% in the occurrence of pure Nb2O5, g-C3N4, and NO/CN, respectively. The kinetic data was well fitted with the first-order kinetic model (ln (C/C0) = kt) in Fig. S4 (Supporting information) [34], and the rate constant value (k1) of NO/CN (k1 = 0.05 min−1) was 5 and 50 times of Nb2O5 (k1 = 1 × 10−3 min−1) and g-C3N4 (k1 = 1 × 10−2 min−1), respectively. The enhanced RhB removal efficiency suggests the construction of heterojunction structure plays an essential effect in enhancing the photocatalytic capacities of materials [32]. Additionally, degradation of MO and MB was also tested to verify the photocatalytic activity (Fig. 4d). Compared to g-C3N4, the degradation efficiency increased from 0% to 15% for MO, and from 35% to 87% for MB, respectively, in the presence of NO/CN, further proving the superior photocatalytic performance of NO/CN towards various contaminants.
To explore the underlying reaction mechanism, different scavengers were added to the system to recognize the major radicals that contribute to the E. coli disinfection and dyes degradation by NO/CN composite. Accordingly, for dyes degradation, tert-butanol alcohol (TBA), triethanolamine (TEA), p-benzoquinone (BQ) were applied to quench the •OH, h+ and •O2− respectively [8, 35-37] as described in Fig. 5a. The introduction of TBA had little effect on the degradation efficiency of RhB by NO/CN, which indicates •OH plays a minor role during the photocatalytic removal of RhB. In addition, with the addition of TEA and BQ, the degradation of RhB was severely inhibited with the efficiency decreasing to 11% and 5%, respectively, illustrating that h+ and •O2− are the major ROSs for degrading pollutants. Additionally, in terms of E. coli disinfection, Na2C2O4, isopropanol, and vitamin C (VC) were used to trap h+, •OH and •O2− [38, 39] respectively, as observed in Fig. 5b. The results were similar with dyes degradation, i.e., isopropanol had sight impact on the E. coli disinfection by NO/CN material, suggesting that •OH was not the dominate free radical during the photocatalytic disinfection of E. coli. The addition of Na2C2O4 and VC inhibited extremely the disinfection of E. coli and disinfection efficiency was decreased to 1.8 and 1.2 log CFU/mL, respectively, indicating that h+ and •O2− played a significant role for inactivating E. coli. Furthermore, the ESR test was utilized to prove the formation of •O2− during the photocatalytic process (Fig. 5c) [8]. In the dark condition, no •O2− spectra were captured, while four distinct peaks of DMPO-•O2− can be detected after 5 min visible light irradiation [40, 41]. Meanwhile, the signal intensity of •O2− became stronger when irradiation time was prolonged to 10 min, suggesting the continuous generation of •O2− radicals during the photocatalytic experiment. The ESR result was consistent with the radicals quenching experiments.
Based on the aforementioned results, the detail working mechanisms of NO/CN was depicted in Fig. 5d. g-C3N4 and Nb2O5 were activated easily and generated h+ and e− on the VB and CB, respectively, in the process of visible light illumination. g-C3N4, compared with Nb2O5, possesses higher Fermi level, leading photoinduced e− of g-C3N4 (CB) readily migrate to the CB of Nb2O5, which enables e− to accumulate in the CB of Nb2O5 and facilitate the formation of active species •O2− [42]. Simultaneously, h+ generated (VB) of Nb2O5 will migrate to the g-C3N4 (VB), thus forming a type-Ⅱ heterojunction. As a consequence, the photoinduced e− and h+ were effectively separated and the recombination of e− and h+ pair were inhibited [43]. Hence, the inactivation performance and dyes removal efficiency were enhanced for composite materials under visible light. In this process, •O2− and h+ played the key role for inactivating E. coli and degrading pollutants. To be specific, the dissolved O2 can capture e− to form •O2− in the CB of Nb2O5 and react with pollutants and bacteria. Similarly, the h+ accumulated (VB) of g-C3N4 can react with pollutants and bacteria to generate the oxidized products as well. The following equations Eqs. 1–4 described the ROSs formation and the removal of contaminants process.
To sum up, a one-step heating method successfully synthesized the NO/CN composite material in this study. Characterization results confirmed the successful preparation of the heterojunction structure. Compared with pure g-C3N4, the NO/CN material exhibited excellent photocatalytic activities for E. coli activation and dyes removal under visible light irradiation. Besides, free radical quenching experiment and ESR test demonstrated that the main active substances were •O2− and h+ for removing pollutants and sterilization. The type Ⅱ heterojunction structure of NO/CN facilitated the migration of photogenerated e− and h+ and hindered the recombination of photo-induced e− and h+ pairs, thereby enhancing the generation of ROSs and photocatalytic performance. Thus, the NO/CN composite seems a potential material towards the degradation of organic pollutants and bacteria in water treatment.
Declaration of competing interest
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The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
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Financial support from the Fundamental Research Funds for the Central Universities (No. 2019MS041) and Postdoctoral Science Foundation of China (No. 2021M690208) is highly acknowledged.
Supplementary materials
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Supplementary material associated with this article can be found, in the online version, at doi:10.1016/j.cclet.2021.11.031
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Year 2022 volume 33 Issue 8
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Article Info
doi: 10.1016/j.cclet.2021.11.031
  • Receive Date：2021-08-19
  • Online Date：2025-12-19
  • Published：2022-08-15
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  • Received：2021-08-19
  • Revised：2021-09-27
  • Accepted：2021-11-07
Affiliations
    a The Key Laboratory of Resources and Environmental System Optimization, Ministry of Education, College of Environmental Science and Engineering, North China Electric Power University, Beijing 102206, China
    b The Key Laboratory of Water and Sediment Science, Ministry of Education, College of Environment Science and Engineering, Peking University, Beijing 100871, China
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表12种不同金属材料的力学参数
科
Family		 属数
Number of
genus		 种数
Number of
species		 占总种数比例
Percentage of
total species (%)		 属
Genus		 种数
Number of
species		 占总种数比例
Percentage of total
species (%)
鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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