Bi₂O₃ and g-C₃N₄ quantum dot modified anatase TiO₂ heterojunction system for degradation of dyes under sunlight irradiation

Abstract

A facile and feasible method was successfully utilized to incorporate Bi₂O₃ and g-C₃N₄ quantum dots on TiO₂ surface to synthesize a novel composite g-C₃N₄/TiO₂/Bi₂O₃. The photocatalytic activity of the composite g-C₃N₄/TiO₂/Bi₂O₃ for degradation of dyes under sunlight and UV light irradiation was evaluated. It possessed the higher photocatalytic performance than that of pristine TiO₂ or g-C₃N₄ under the same conditions. Under sunlight irradiation, the reaction rate constants of the g-C₃N₄/TiO₂/Bi₂O₃ was about 4.2 times and 3.3 times higher than that of TiO₂ and g-C₃N₄, respectively. The promising photocatalytic performance was attributed to the broader light absorption range and efficient separation of photoinduced carriers. Moreover, based on the TEM, XPS, XRD, UV-vis spectrum, radicals scavenging test and Mott–Schottky analysis systematic mechanism for photodegradation process was proposed. This work provides a promising strategy for the modification of TiO₂-based semiconductors by incorporating different quantum dots and promoting the efficiency of the photocatalysts in practical application.

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1 Introduction

At present, environmental contamination and energy shortage are the most serious problems on our planet. Hence, there is an urgent need for the development of an environmental, sustainable, economical and energy-saving technology for contamination control. Semiconductor photocatalysis provides an optimal solution for the problems with the potential that the clean solar energy can be harnessed for decomposition of pollutants.¹ To date, TiO₂ as the photocatalyst has drawn significant attention and been widely studied because of its desirable properties including high reactivity, chemical stability, nontoxicity, and cheap price.^2–7 Nevertheless, the application of TiO₂-based photocatalysts is hindered due to its inefficient utilization of solar energy, poor charge separation, and low adsorption of organic contaminants on the surface. Besides these intrinsic drawbacks, the complicated process of synthesis is another key factor to impede its practical application.⁸

To avoid the above limitation, various modification strategies have been carried out, such as dye-sensitization, metal or non-metal doping, and transition metal doping, etc. Particularly, compositing TiO₂ with different semiconductor into heterojunction is an efficient method to enhance the photocatalytic activity.⁸ Since the heterojunction structure would decrease the recombination of electron/hole by separating the charge carriers to different semiconductors surface due to the different potential barriers. These heterojunctions-based semiconductors exhibit advanced efficiency for degrading pollutants.

Presently, considerable attention has been paid to graphitic carbon nitride (g-C₃N₄), which is a stable kind of polymers with a layered structure like graphene. Particularly, it possesses the strong ability to harvest solar energy due to its narrow band gap (E_g = 2.7 eV). Nevertheless, the quantum efficiency of pure g-C₃N₄ is low because of the high recombination ratio of photogenerated electron/hole pair.⁹ Combining the TiO₂ with g-C₃N₄ in heterojunction is considered as an efficient method which can improve the absorption of visible light and the separation of photogenerated pairs. Yu et al.¹⁰ synthesized g-C₃N₄–TiO₂ composites by calcination process using P25 and urea, achieving the high photoactivity for the degradation of HCHO. Lei et al.¹¹ reported the synthesis of g-C₃N₄/TiO₂ photocatalyst via simple calcination using cyanamide and anatase TiO₂ as precursor. The g-C₃N₄/TiO₂ photocatalyst exhibits a promising progress in degradation of the dye Acid Orange 7 under both visible and UV light. The g-C₃N₄–TiO₂ composites with prominent photoactivity for the degradation of phenol under UV light was synthesized by Colo'n et al.¹² by impregnation. Zhang et al.¹³ found that well-dispersed TiO₂ nanocrystals with (001) facets prepared in situ on g-C₃N₄ through a solvothermal method exhibit higher efficiency for photocatalytic degradation of phenol as compared to pure g-C₃N₄ and TiO₂. Wu et al.¹⁴ prepared nanosheets TiO₂/g-C₃N₄ composite by solvothermal method, which exhibits a significant improvement in photodegradation towards methylene blue under visible light irradiation than pristine g-C₃N₄ and TiO₂.

Among strategies of constructing heterojunction, synthesis of p–n junction is considered as an effective method to facilitate the photoactivity by inducing the separation of photogenerated carries due to the existence of an internal electric field. Bismuth oxide (Bi₂O₃), as a p-type semiconductor, has been extensively studied due to its suitable band gap (E_g = 2.8 eV) and visible light driven catalytic activity. Among the six different polymorphic phases of Bi₂O₃, β-Bi₂O₃ has prominent advantages for degradation of pollutants. Since TiO₂ is a n-type semiconductor, it is feasible to combine TiO₂ with β-Bi₂O₃, by which catalytic efficiency can be notably enhanced.^15–18 Recently, much efforts have been made to synthesize TiO₂/Bi₂O₃ heterojunction. Various methods have been employed such as: pulse electro-deposition,¹⁹ hydrothermal, sol–gel, and coprecipitation.^20–26 However, the complexity of these methods limits the application of photocatalysis.

Instead of above strategies, researchers have succeeded in sensitizing TiO₂ by modifying quantum dots (QDs) of low-band gap materials such as g-C₃N₄, CdS, CdSe, CdTe, and Bi-based materials, which can absorb light in the visible region. QDs can match the solar spectrum better due to the particle size effect. Additionally, QDs are recently reported to generate multiple excitons, which can improve the photocatalysis efficiency.^27–30 Jiao et al.³¹ firstly prepared Bi₂O₃ quantum dots decorated TiO₂ with exposed {001} facets on graphene sheets. Size-controllable were in situ synthesized on TiO₂ nanotube arrays and high activity in synergetic H₂ evolution and organics degradation.³²

In this study, we firstly use a simple ball-milling/calcination method to synthesize a g-C₃N₄/TiO₂/Bi₂O₃ heterojunction system which distinctly exhibit a promising synergetic improvement effect. The different properties of the catalyst are evaluated by the degradation of simulated dyeing wastewater under UV light and direct sunlight irradiation. While the different properties are confirmed by TEM, XPS, XRD and UV-vis diffuse reflection spectra. A tentative mechanism for photocatalytic degradation of RhB by the composite g-C₃N₄/TiO₂/Bi₂O₃ is proposed.

2 Materials and methods

2.1 Catalysts synthesis

2.1.1. Chemicals and reagents. Double distilled water was used throughout the experiment. The catalyst precursor used in this experiment including titanium dioxide (TiO₂, anatase, 99.8%; Shanghai Aladdin Biochemical Technology Co., Ltd), melamine (98%; Shanghai Aladdin Biochemical Technology Co., Ltd), bismuth(III) nitrate-pentahydrate (Bi(NO₃)₃·5H₂O, 98%; Shanghai Aladdin Biochemical Technology Co., Ltd). All the reagents utilized were of analytical grade and without further purification.

2.1.2 Methods.
1. Synthesis of pure g-C₃N₄. 5 g of melamine were added into crucible with a cover then heated at 520 °C under air atmosphere for 2 h with a heating rate of 5 °C min⁻¹. After cooling to the room temperature naturally, the resulting yellow bulks were collected and ball-milled into powders for further evaluation.
2. Synthesis of pure Bi₂O₃. 3 g Bi(NO₃)₃·5H₂O were added into crucible with a cover then heated at 520 °C under air atmosphere for 2 h with a heating rate of 5 °C min⁻¹. After cooling to the room temperature naturally, the resulting bulks were collected and ball-milled into powders for further evaluation.
3. Synthesis of g-C₃N₄/TiO₂/Bi₂O₃. The g-C₃N₄/TiO₂/Bi₂O₃ catalysts were prepared by the processes of ball-milling and calcination. Firstly, 400 mg of anatase TiO₂ powders and 600 mg of melamine were added into the agate ball milling tank, followed by the process of ball milling for 2 h with a ball powder ratio of 10 : 1, at a speed of 400 rpm in a planetary ball mill. Then, a certain amount of Bi(NO₃)₃·5H₂O were added into the agate ball milling tank which was filled with TiO₂ and melamine. The powders mixed by ball milling for 2 h with a ball powder ratio of 10 : 1, at a speed of 400 rpm in a planetary ball mill. Subsequently, the mixed powder was placed into a crucible with a cover then heated at 520 °C under air atmosphere for 2 h with a heating rate of 5 °C min⁻¹. After cooling to the room temperature naturally, the resulting yellow bulks were collected and ball-milled into powders for further evaluation. The obtained powers was named as TCB-x, where the x refers to the weight percentage of Bi(NO₃)₃·5H₂O to the weight of TiO₂ and melamine.

2.2 Characterization

The crystal phases was characterized by X-ray diffraction (XRD, Bruker D8 ADVANCE A25X) with a Cu Kα radiation with a diffraction angle between 10–80°

Transmission electron microscopy (TEM) and high-resolution transmission electron microscopy (HRTEM) were measured by Tecnai G2 F20 S-TWIN (200 kV). The samples were dispersed in ethanol and dropped on copper grids. Chemical composition and valence band (VB) were observed by X-ray photoelectron spectroscopy (XPS, Escalab 250Xi) using a monochromatic micro-focused Al Kα (1486. 6 eV) source. UV-vis diffuse reflectance spectroscopy (UV-vis DRS) absorption spectra of the wavelength between 200 nm and 800 nm were carried out at a Shimadzu UV-3600 spectrophotometer using BaSO₄ as a reference.

The electrochemical studies were conducted on an electrochemical workstation (CHI660C, CH Instrument Corp, Shanghai), which used catalyst-deposited FTO glass as working electrode, Pt as the counter electrode and Ag/AgCl as the reference electrode. Meanwhile, 0.5 M Na₂SO₄ was served as the electrolyte solution. The working electrode was prepared as follows: 20 mg PEG-600 and 10 mg pure TiO₂ and Bi₂O₃ were dispersed in 1 mL ethanol and ultrasonically scattered for 1 h. Then, the suspension above was added onto the FTO glass (1 × 1 cm) and evaporated to dry. The Mott–Schottky measurement was performed at frequency of 1000 Hz.

2.3 Photocatalytic activity test

The aqueous Rhodamine B (RhB), methylene blue (MB) and methyl orange (MO) dyes were used as model organic contaminants to evaluate the photocatalytic activities of the synthesized catalysts. Degradation experiments were carried out under UV and direct solar light irradiation. A high-pressure 300 W mercury lamp with the radiation of 365 nm was used as the UV light source. To study the photocatalytic activity of the samples under visible light, the photoreactor were directly exposed to sunlight. And the illumination intensity was measured by solar power meter (TES-1333R). 50 mg catalyst powders were suspended in 50 mL aqueous organic dye solution and the dyes concentration was 20 mg L⁻¹. To reach adsorption–desorption equilibrium, the solution was stirred for 60 min in the dark. At given time intervals, 4 mL aliquots were taken and centrifuged at 10 000 rpm for 10 min to remove the particles. Then, the concentration of organic dyes in filtrates was analyzed using an Alpha-1506 UV-vis spectroscopy (Shanghai Lab-Spectrum Instruments Co. Ltd, China) at the wavelength of 554 nm, 664 nm, 465 nm for RhB, MB, MO, respectively. The experiments were repeated 3 times.

3 Result and discussion

3.1 XRD characterization

Fig. 1 shows the XRD patterns of TCB-30%, pristine TiO₂, g-C₃N₄ and Bi₂O₃. In TCB-30% patterns, the diffraction peaks at 25.3°, 37.9°, 48.0°, 53.9° could be well indexed to the (101), (004), (200) and (105) planes of the anatase phase TiO₂.^23,33 There are four peaks at 27.9°, 31.8°, 32.8°, 46.3°, corresponding to the (211), (002), (220), and (222) plane of pristine Bi₂O₃.^26,34,35 The characteristic peaks of g-C₃N₄ at 27.5° (ref. 27 and 36) was also detected in TCB-30% patterns. The diffraction peaks with relatively low intensity indicated the small sized Bi₂O₃ and TiO₂ quantum dots, in consistent with the results of TEM. The well crystallized diffraction peaks detected in TCB-30% patterns suggested the well crystalline structure of anatase TiO₂, g-C₃N₄ and Bi₂O₃, without the generation of other crystal structure.

Fig. 1 XRD pattern of TCB-30%, TiO₂, g-C₃N₄ and Bi₂O₃.

3.2 Microstructure analysis

The morphology of the prepared catalysts was characterized by TEM and high-resolution. TEM image Fig. 2b, c and d are enlarged views of Fig. 2a. As shown in Fig. 2a, TiO₂ particles have a spherical structure with an average size between 30–60 nm, which was in well accordance with the crystallite size obtained from Scherrer equation. Bi₂O₃ and g-C₃N₄ showed a much smaller size below 10 nm, and intimately cover on the surface of TiO₂ particles, which intensively increase the specific surface area of TiO₂.

Fig. 2 (a) Selected TEM figure of TCB-30%, (b, c and d) HRTEM figures of TCB-30%, (e) SEM figure of pure g-C₃N₄, (f) SEM figure of pure Bi₂O₃.

Clear lattice fringes for the identification of crystallographic spacing could be observed in Fig. 2c, and the lattice spacing of 0.350 nm and 0.321 nm corresponded well with (101) phase of TiO₂ and (221) phase of Bi₂O₃,^15–17 respectively. In Fig. 2d, the lattice spacing of 0.318 nm matched the (002) crystal phase of g-C₃N₄.^37–39

Thus, these TEM images indicated the interaction of g-C₃N₄/TiO₂/TiO₂ heterojunction composite. The g-C₃N₄ and Bi₂O₃ located on the surface of TiO₂ as quantum dots. In Fig. 2e, the pure g-C₃N₄ showed aggregated morphologies, which were comprised of block-based flakiness. Fig. 2f displayed a spheroidal structure of Bi₂O₃. It was obvious that the process of ball-milling played a significant role in synthesizing g-C₃N₄ and Bi₂O₃ quantum dots on TiO₂ surface.

3.3 Chemical compositions

Fig. 3 showed the full survey and high-resolution spectra for the Ti 2p, O 1s, C 1s, N 1s and Bi 4f region. Fig. 3b depicts the C 1s of the prepared. The peak centered at 284.6 eV could be assigned to the adventitious carbon while the peak at 287.5 eV belongs to the N–C=N group of the g-C₃N₄.^40–42 Fig. 3d showed N 1s spectrum of catalyst. The N 1s peak was fitted into two peaks at 399.3 eV and 400.2 eV, which were the sp²-hybridized nitrogen (C=N–C) and tertiary nitrogen (N-3), respectively.^40–42 Furthermore, two fitted peaks of Ti 2p3/2 and Ti 2p1/2 at 458.9 eV and 464.4 eV suggested the presence of Ti(IV).^27,36,43 In Fig. 3a, two fitted peaks at 158.9 eV and 164.3 eV belonged to Bi 4f5/2 and Bi 4f7/2, suggesting the existence of Bi₂O₃ in the catalyst.^24,34,35 These results suggested that the composite TCB-30% consisted of g-C₃N₄, anatase TiO₂ and Bi₂O₃.

Fig. 3 XPS spectrum of (a) TCB-30%, (b) C 1s, (c) Ti 2P, (d) N 1s.

3.4 UV-vis DRS analyses

The UV-vis diffuse reflectance spectra of different composites were exhibited in Fig. 4. It is obvious that the composite of TCB-30% showed a significant red shift of band edge to 456.5 nm compared with the initial TiO₂, Bi₂O₃ and g-C₃N₄. There is also an intensively long tailing absorption in visible region, which can be explained by the synergistic effects of Bi₂O₃ and g-C₃N₄ quantum dots with a narrower band gap.

Fig. 4 (a) UV-vis DRS spectra and (b) optical bandgap of the TCB-30%, TiO₂, g-C₃N₄ and Bi₂O₃.

The band gap energies were determined using the equation below:

αhv = A(hv − E_g)^n/2

where A, h, v, E_g and α are the absorption coefficient, Planck's constant, frequency, band gap energy and a constant, respectively. For the composites in this study, n is 4 because of the indirect transition. Therefore, Tauc's plots of (αhν)^1/2 versus photon energy (hν) are obtained. As shown in Fig. 4b, the band gap energies of TiO₂, TCB-30%, Bi₂O₃ and g-C₃N₄ are 3.20 eV, 2.24 eV, 2.80 eV and 2.7 eV, respectively. The TCB-30% has a lower band gap energy compared to TiO_2, which may be due to the heterojunction structure of the composite.

In order to further explain the photocatalytic activity of the ternary composite, the band structure of Bi₂O₃ was explored according to the following empirical equation.

E_CB = X − E^e − 0.5E_g

E_CB = E_VB − E_g

where E_VB is the valence band edge potentials, E_CB is the conduction band energy, X is the electronegativity of semiconductor, E^e is the energy value of free electrons on the hydrogen scale, E_g is gap energy of semiconductor. The value of X for Bi₂O₃ is ca. 5.99 eV. The calculated conduction band and valence band of Bi₂O₃ are 0.33 eV and 3.13 eV, respectively. The band structure of TiO₂ and g-C₃N₄ was calculated in above-mentioned method as well. And the results were showed in Table 1.

Table 1 Band structure of Bi₂O₃, TiO₂ and g-C₃N₄

Catalyst	Band gap (eV)	Valence band (VB)	Conduction band (CB)
TiO2	3.2	2.7	−0.5
g-C3N4	2.7	1.4	−1.3
TCB-30%	2.2
Bi2O3	2.8	3.13	0.33

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3.5 Photocatalytic activity

Fig. 5 displays the change of RhB concentration versus irradiation time with the pure TiO₂, g-C₃N₄ or TCB-x under UV irradiation and sunlight irradiation. From Fig. 5a, pure TiO₂ and pure g-C₃N₄ exhibited limited degradation rate of RhB under the UV light, which were only 66.9% and 62.1% after 50 min irradiation respectively. With the incorporation of Bi₂O₃ and construction of heterojunction, the photocatalytic activity substantially enhanced. In particular, the TCB-30% displayed the highest degradation rate of 96.5%. Moreover, TCB-30% showed the best photodegradation ability on RhB (completely degraded within 120 min) under sunlight irradiation (about 640 W m⁻²).

Fig. 5 Photocatalytic activity of TCB-30%, TiO₂ and g-C₃N₄ for degradation of RhB under (a) UV light irradiation (b) sunlight irradiation.

The degradation of RhB followed the first-order kinetics, which can be expressed by the equation: ln(C₀/C_t) = k_a⁻¹t, where C₀ and C_t is RhB concentration at time 0 and time t, and k_a⁻¹ represents the first-order reaction rate constant. As shown in Fig. 6, TCB-30% displayed a maximum value of rate constant under UV, which was about 2.2 times as high as that of TiO₂ and 2.6 times as that of g-C₃N₄. When under the solar irradiation (640 W m⁻²), the k_a⁻¹ of TCB-30% was 4.2 times and 3.3 times higher than that of TiO₂ and g-C₃N₄ respectively. Therefore, the improvement of photocatalytic activity under solar irradiation is more remarkable than that in the condition of UV light.

Fig. 6 Reaction rate constant for degradation RhB of TCB-30%, TiO₂, g-C₃N₄ and Bi₂O₃ under (a) UV light irradiation (b) sunlight irradiation.

Moreover, TCB-30% was also used to degrade different kinds of dyes with the same initial concentration under sunlight irradiation, including methylene blue (MB) and methyl orange (MO). As it shown in Fig. 7a, TCB-30% displayed a limited degradation rate for methylene blue and methyl orange compared with RhB. Fig. 8 showed the dark adsorption of three dyes over TCB-30%. It was supposed that the promising reaction rate could be contributed by the strong adsorption of the prepared heterojunction materials towards organic dyes with hydroxy groups. Thus, it is worth further research on how the surface groups of this composite affects the reaction with organic pollutants.

Fig. 7 Comparison of the photocatalytic activity towards degradation of RhB, MB and MO under (a) UV light irradiation (b) sunlight irradiation.

Fig. 8 Dark adsorption of three dyes over TCB-30%.

To figure out the contribution of photo-induced active radical in the reaction process, benzoquinone (BQ), isopropanol (IPA) and ammonium oxalate (AO) were applied as scavengers of superoxide radical (·O₂⁻), hydroxyl radical (·OH) and hole (h⁺), respectively. The comparison experiments were carried out in the presence of the same molar concentration of scavengers (BQ, IPA and AO) for visible light degradation of RhB with TCB-30%. As displayed in Fig. 9, the degradation rate without any scavengers is 99.6%. By contrast, by adding BQ and IPA, the degradation rate sharply suppressed. While with the addition of AO scavengers, there is only a slight decrease of degradation rate. Therefore, it can be concluded that superoxide radical (·O₂⁻) and hydroxyl radical (·OH) play key roles in degradation towards RhB under visible light.

Fig. 9 Radical capture test (a) and stability test of TCB-30% for degradation of RhB (b) under sunlight irradiation.

During the practical application of catalysts, the by-products tend to be adsorbed on the active sites of photocatalysts' surface, leading to the dramatic decrease of the photocatalytic activity. To evaluate the stability of the prepared TCB-30%, recycle experiments were conducted under solar irradiation. As shown in the Fig. 9, the TCB-30% still presents the excellent photocatalytic performance after three cycles.

3.6 Mechanism discussion

In order to investigate the electrochemical properties of TiO₂ and Bi₂O₃, Mott–Schottky plots were obtained. In Fig. 10a, TiO₂ exhibit a positive slope indicating that it’s n-type semiconductor. On the contrary, BiO₂ shows a negative slope, which indicts a p-type semiconductor.

Fig. 10 (a) Mott–Schottky plots of Bi₂O₃ and TiO₂ in 0.5 M Na₂SO₄ at a frequency of 1 kHz, and (b) energy band structure of p-type Bi₂O₃/n-type TiO₂.

Based on the results of XRD, XPS, TEM and UV-vis DRS analysis and Mott–Schottky, a tentative heterojunction system proposed and depicted in Scheme 1. TiO₂ is placed as a support and connector of Bi₂O₃ and g-C₃N₄ quantum dots. The promising photocatalytic performance of TCB-30% under visible light is significantly related to the extended light adsorption spectrum and enhanced electron–hole separation.

Scheme 1 Photocatalytic degradation mechanism from the generation of photoinduced electron–hole to the decomposition of dyes.

On the one hand, the generation of g-C₃N₄ and Bi₂O₃ quantum dots with a narrow band gap facilitated the improvement of visible light harvesting ability, which motivates the generation of photoinduced carriers under visible light. On the other hand, the Fermi energy level of n-type semiconductors located nearer to the VB while the Fermi energy of p-type semiconductors located nearer to the VB.^23,27,35 Therefore, after p-type Bi₂O₃ and n-type TiO₂ were in contact, the electrons near the interface diffused from TiO₂ to Bi₂O₃ while the holes diffused from Bi₂O₃ to TiO₂. When the electrons migrated from TiO₂, leaving a positively charged donor ion, and a positive charge region was formed on the side of the n region. In the same way, a negative charge region was formed on the side of p region. Therefore, there was no electrical neutrality on both sides of the interface of the p–n junction, and a positively and negatively charged region appeared, becoming a space charge region, which can force photoinduced electrons and holes to transfer in the opposite direction (Fig. 10b). The photogenerated electrons can only transfer from the CB of Bi₂O₃ to CB of TiO₂, in contrast the holes can only transfer from the VB of TiO₂ to the VB of Bi₂O₃, leading to a notably efficient separation of photoinduced pairs between Bi₂O₃ and TiO₂. As for the heterojunction between g-C₃N₄ quantum dots and TiO₂ particles, since the g-C₃N₄ has a more positive conduction band edge potential than that of TiO₂ (−0.28 eV), the photoinduced electrons under visible irradiation tend to transfer from the CB of g-C₃N₄ to CB of TiO₂.

Based on above calculation and analysis, an energy band structure has been proposed in Scheme 1. The photogenerated electrons and holes are unable to migrate from g-C₃N₄ to Bi₂O₃ through TiO₂. Besides, the Bi₂O₃ and g-CN₄ quantum dots don't interact and they are located in different position of TiO₂ surface. Consequently, it's believed that there are just two heterojunctions (TiO₂/g-C₃N₄, TiO₂/Bi₂O₃) instead of a ternary heterojunction.

According to the previous researches, there are three types of radical degradation mechanism, including superoxide radical (·O₂⁻), hydroxyl radical (·OH) and hole (h⁺).^3,7,8,44,45 Steps of generation of the three radicals can be explained as follows:

e⁻ + O₂ → ·O₂⁻

·O₂⁻ + H⁺ → HO₂^˙

2HO₂ → O₂ + H₂O₂

H₂O₂ +·O⁻₂ → ·OH + OH⁻ + O₂

OH⁻ + h⁺ → ·OH

In this work, there was a minor change in degradation performance after eliminating the holes through the scavenging test. Thus, it was concluded that the majority dye was degraded by superoxide radical (·O₂⁻) or hydroxyl radical (·OH) induced by photo catalysis. Meanwhile, a slight number of dyes is degraded by hydroxyl radical (·OH) induced by photoinduced holes or directly oxidation by the holes.

Eventually, the systematic mechanism, including the generation and transfer of carriers, generation of radicals and reaction between radicals and dyes, was proposed in Scheme 1.

4 Conclusion

In summary, a facile ball-milling/calcination was successively utilized to prepared a Bi₂O₃ and g-C₃N₄ quantum dots modified anatase TiO₂ heterojunction system. It was found that TCB-30% exhibited the highest removal rate for degradation of dyes under UV light irradiation and sunlight irradiation. Under sunlight irradiation, there was remarkable improvement of TCB-30%, the reaction rate constant was about 4.2 times and 3.3 times higher than that of TiO₂ and g-C₃N₄ towards degradation of RhB. The notable enhancement of photocatalytic activity is mainly due to the ability of visible light harvesting and efficient separation of the carriers, which was induced by the modification of Bi₂O₃ and g-C₃N₄ quantum dots.

Conflicts of interest

There are no conflicts to declare.

Acknowledgements

This work was supported by National Key Research and Development Program (2018YFC1802605), Nature Science Foundation of Sichuan Province (2017GZ0383, 2017SZ0181), Science Foundation of China (31100374), the Key Research and Development Project of Sichuan Province (2018GZ0455), and the Sci-tech innovation seedling project from Sichuan Institute of Computer Science (18-YCG041).

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