Chinese Journal of Chemical Physics  2017, Vol. 30 Issue (2): 153-160

The article information

Zhan-ying Ma, Xiao-bo Li, Cai-hua Zhou, Ling-juan Deng, Guang Fan
马占营, 李小博, 周彩华, 邓玲娟, 范广
TiO2/BiVO4, a Heterojuncted Microfiber with Enhanced Photocatalytic Performance for Methylene Blue under Visible Light Irradiation
纤维状TiO2/BiVO4异质结的高可见光光催化性能
Chinese Journal of Chemical Physics, 2017, 30(2): 153-160
化学物理学报, 2017, 30(2): 153-160
http://dx.doi.org/10.1063/1674-0068/30/cjcp1609175

Article history

Received on: September 6, 2016
Accepted on: November 17, 2016
TiO2/BiVO4, a Heterojuncted Microfiber with Enhanced Photocatalytic Performance for Methylene Blue under Visible Light Irradiation
Zhan-ying Ma, Xiao-bo Li, Cai-hua Zhou, Ling-juan Deng, Guang Fan     
Dated: Received on September 6, 2016; Accepted on November 17, 2016
College of Chemistry and Chemical Engineering, Xianyang Normal University, Xianyang 712000, China
*Author to whom correspondence should be addressed. Zhan-ying Ma, E-mail:mazhanying@163.com, Tel.:+86-29-33720704
Abstract: Novel TiO2/BiVO4 microfiber heterojunctions were constructed using cotton as biomorphic templates. The as-synthesized samples were characterized by scanning electron microscope, X-ray diffraction, X-ray photoelectron spectroscopy, UV-Vis diffuse reflectance spectra and photocatalytic experiment. The morphology of the as-synthesized TiO2/BiVO4 composites was consisted of a large quantity of microfiber structures with diameter from 2.5 μm to 5 μm, and the surface of samples became more coarse and compact with the increase of weight ratio of TiO2. The TiO2/BiVO4 samples with proper content (10.00wt%) showed the highest pho-tocatalytic degradation activity for methylene blue (MB) degradation among all the samples under visible light, and 88.58%MB could be degraded within 150 min. The enhancement of photocatalytic activity was mainly attributed to the formation of n-n heterojunction at the contact interface of TiO2 and BiVO4, which not only narrowed the band gap of BiVO4 for extending the absorption range of visible light, but also promoted the transfer of charge carriers across interface. A possible photodegradation mechanism of MB in the presence of TiO2/BiVO4 microfibrous photocatalyst was proposed.
Key words: TiO2/BiVO4    Microfiber    Visible-light-response    Photocatalysis    
Ⅰ. INTRODUCTION

Numerous efforts had been made to develop highly effective photocatalysts for the photodecomposition of environmental contaminants like pesticides, dyes and heavy metal in water [1]. Monoclinic scheelite-type BiVO4, one kind of visible light photocatalyst with the energy band gap of 2.4 eV, also attracted a great deal of attention or pollutant elimination under visible light irradiation [2, 3]. However, unavoidably, the photocatalytic activity of pure BiVO4 need to be further improved owing to the rapid recombination rate of photo-generated carriers [4]. Therefore, it was necessary to develop effective solution to improve the charge separation efficiency and enhance visible-light photoactivity. Forming a heterojunction between BiVO4 and another semiconductor such as V2O5 [5], Bi2O3 [6], Cu2O [7, 8], and InVO4 [9], was an effective way to address the above two issues [10, 11].

As is known, TiO2, as a wide band-gap semiconductor, has been applied widely because of its high stability, low cost, nontoxity and efficient photocatalytic activities under UV light irradiation [12]. Although it could not be excited under visible light, it had suitable energy band that could effectively transfer the photo-generated charges from BiVO4 [13, 14]. Hu et al. [15] reported that heterojunctions exhibited higher photocatalytic activity than the individual components, which confirmed that the combination of BiVO4 and TiO2 was an effective way to enhance the photocatalytic activity of BiVO4 under visible light irradiation. Zhang et al. [14] prepared TiO2/BiVO4 spherical composite photocatalysts by the one-step microwave hydrothermal method. They investigated the photocatalytic degradation of RhB under UV light and Xe lamp irradiation, results indicated that the degradation efficiency can reach over 94% after 330 min UV irradiation, but only about 83% after 360 min Xe lamp irradiation. Considering the fact that the morphological diversity of inorganic materials had a significant impact on functional diversification and potential applications [16, 17], it was expected that the TiO2/BiVO4 composite with a special morphological diversity would have a good photocatalytic activity under visible light irradiation.

Microfibers possessed high specific surface area and small thickness. These characteristics assured microfibers potential to be exposed to more light and contact with more dye molecules; meanwhile, its separation and migration efficiency of photogenerated electron-hole pairs was effectively improved. In addition, the micro-pores could serve as transport paths for small molecules, benefiting the reactant molecules to get to the reactive sites on the framework walls of photocatalysts [18], which further accelerate the chemical reactions and result in the excellent photocatalytic activity. Therefore, instead of the corresponding nanoparticles, microfibers being an important subclass of microstructural materials are deemed as potential good candidates for practical applications [19].

Template procedures were an ideal way to control material structure including the outer morphology and size and the inner pore size and distribution [20]. In recent years, biomorphic mineralization has been noteworthy as a new fabrication technique for functional materials, which is a technique that produces materials with morphologies and structures resembling those of nature living things [21]. Biomorphic mineralization was of low-cost, environmentally benign, and easily removed with heating procedures. Natural cotton had been selected as templates to produce various advanced biomorphic materials, such as MgO [22], NiO [23] and In2O3 [24].

In the present work, we synthesized pure BiVO4 and a series of biomorphic TiO2/BiVO4 microfibers by using cotton fibers as biomorphic templates, and demonstrated their physical properties. The photocatalytic properties of the as-synthesized TiO2/BiVO4 heterojunctions were tested by the photodegradation of methylene blue (MB) aqueous solution under visible light irradiation. The mechanism of enhanced photocatalytic activity of TiO2/BiVO4 heterojunction photocatalysts was also discussed.

Ⅱ. EXPERIMENTS A. Materials and Reagents

Bi (NO3)3·5H2O, NH4VO3, citric acid, nitric acid, ammonia, n-tetrabutyltitanate (C16H36O4Ti), methylene blue (MB), and other chemicals were obtained from Shanghai Chemical Reagents Company (China). All chemicals were of analytical reagent grade and used as received without further purification. Ultrapure deionized water was used throughout the experiments

B. Preparation of TiO2/BiVO4 heterojunction microfibers

In a typical procedure, 0.485 g of Bi (NO3)3·5H2O and the same molar of citric acid were dissolved in 30 mL of 2 mol/L nitric acid aqueous solution, adjusting the pH value to 7.0 by dropwisely titration of 1 mol/L ammonia solution under stirring, and transparent solution A was formed. Meanwhile, 0.117 g of NH4VO3 was dissolved in deionized water at 70 ℃ and the same molar of citric acid was added to obtain dark green solution B. After mixing of solution A and B, uniform dark green solution C was obtained. Different dosage of n-tetrabutyltitanate (C16H36O4Ti) was dissolved in ethanol at room temperature, thus pale-yellow solution D was formed. The dried and loose cotton fibers were immersed into the mixture of solution C and D. After immersing for 24 h, the cotton fibers were taken out, dried at 50 ℃ for 12 h, which were then placed in an alundum crucible and calcined in air at 500 ℃ for 1 h. Finally, pale-yellow TiO2/BiVO4 heterojunction were obtained. The weight ratio of C16H36O4Ti/(C16H36O4Ti+Bi (NO3)3·5H2O) was controlled from 12% to 48%, and the final TiO2/BiVO4 were labelled as 4.58%, 10.00%, 16.54% and 24.53%, respectively.

For reference, pure BiVO4 microfibers were synthesized under the same conditions without adding n-C16H36O4Ti.

C. Characterization

The phase identification of the as-prepared powders were obtained on a Riggaku D/max-3C X-ray powder X-ray diffractometry using Cu Kα radiation (λ=1.5405 nm, 40 kV, 40 mA). Scanning electron microscopy (SEM) images were observed by Hitachi S-4800 scanning electron microscopy. UV-visible diffuse reflectance spectra (UV-Vis DRS) of the samples were recorded on Lambd 950 spectrophotometer using BaSO4 as reference.

D. Measurement of photocatalytic activity

The photocatalytic activity of TiO2/BiVO4 heterojunctions was evaluated by measuring the degradation of MB under visible light at room temperature. In a typical process, 100 mg of TiO2/BiVO4 samples were added to 100 mL of 10 mg/L MB solution and then stirred in the dark for 30 min, which allowed it to reach adsorption equilibrium and uniform dispersity. The solution was then exposed to visible light irradiation from a 500 W Xe lamp at room temperature. UV radiation was cut off by using a 400-nm filter, prior to irradiation of the sample. During the irradiation, 5 mL of the suspension was sequentially taken from the reactor every 30 min, and filtered immediately through 0.22 μm membrane filters for UV-Vis analysis. The decolorization efficiency was monitored by determining the absorbance around 664 nm in the UV-Vis spectra.

Ⅲ. RESULTS AND DISCUSSION A. SEM analysis

Figure 1 shows SEM images of pure BiVO4 and TiO2/BiVO4 heterojunctions via cotton biomorphic template. From Fig. 1, it is clearly shown that all these samples are consisted of a large quantity of microfibers with diameter from 2.5 μm to 5 μm, indicating the formation of biomorphic TiO2/BiVO4 via cotton template. These microfibers may present as straight or twisted shapes, which are well consistent with the straight or twisted shapes of cotton template. Compared with pure BiVO4 microfibers (Fig. 1(a)), the surfaces of TiO2/BiVO4 heterojunctions (Fig. 1 (b), (c), (d), and (e)) are coarse and have many microstructures on them. In addition, the framework of TiO2/BiVO4 becomes more compact with the increase of weight ratio of TiO2. Therefore, the amount of n-tetrabutyltitanate in the impregnation step has an important influence on the microstructure of TiO2/BiVO4 surface.

FIG. 1 SEM images of (a) pure BiVO4, (b) 4.58%TiO2/BiVO4, (c) 10.00%TiO2/BiVO4, (d) 16.54%TiO2/BiVO4, and (e) 24.53%TiO2/BiVO4.
B. XRD analysis

The phases and crystallinity of the as-prepared pure BiVO4 and TiO2/BiVO4 heterojunctions were characterized by XRD, as shown in Fig. 2. From Fig. 2(a), the crystal form of the BiVO4 can be identified to the monoclinic scheelite type with characteristic 2θ values of 18.85° (110), 28.85° (011), 30.54° (121), 34.38° (040), 35.19° (200), 39.91° (002), 42.40° (141), 46.00° (211), 46.82° (150), 47.25° (132), 50.00° (240), 50.26° (222), 53.21° (161), 58.28° (123) and 59.38° (321) respectively (JCPDS card No.14-0688). The main characteristic peaks appearing in the TiO2/BiVO4 composites were similar to those of pure BiVO4. However, a careful comparison shows a small peak at 2θ=25.4° in XRD patterns of TiO2/BiVO4 heterojunctions, but not in XRD patterns of pure BiVO4 sample. This small peak was ascribed to the characteristic peak (101) of anatase TiO2 (JCPDS card No.21-1272), indicating the existence of TiO2. With increasing the contents of TiO2 in the composites, the peak intensities of the anatase TiO2 increased. No extra peaks except for BiVO4 and TiO2 crystal phase were detected in TiO2/BiVO4 heterojunctions. It was also found that after the introduction of TiO2 into BiVO4, the intensities of the diffraction peaks (011) increased, in XRD patterns of 4.58%TiO2/BiVO4 and 10.00%TiO2/BiVO4 samples, indicating that they displayed higher crystallinity than others. Furthermore, from the (011) peak, there was a slight shift to high diffraction angel in 10.00%TiO2/BiVO4 XRD pattern, compared with pure BiVO4 (Fig. 2(b)), indicating that the appropriate introduction of TiO2 into BiVO4 alter the crystalline structure of BiVO4. All these results confirmed that the heterojunction structure was formed between TiO2 and BiVO4.

FIG. 2 XRD patterns of pure BiVO4 and TiO2/BiVO4 heterojunctions.
C. XPS analysis

To contrast the electronic environment and surface composition of 10.00%TiO2/BiVO4 heterojunctions with that of pure BiVO4, survey XPS and high-resolution XPS analysis of both pure BiVO4 and 10.00%TiO2/BiVO4 were performed and the results are shown in Fig. 3. From Fig. 3(A), Bi, V, O and C (the carbon contamination is often ubiquitous in the XPS measurements [25]) were observed in the samples of both pure BiVO4 and 10.00%TiO2/BiVO4 where they were expected to be. In the 10.00%TiO2/BiVO4 sample, two peaks with binding energies of 464.1 and 458.2 eV, corresponding to Ti2p1/2 and Ti2p3/2 were detected (Fig. 3(B)), which was in excellent agreement with the literature data for TiO2 [26] in 10.00%TiO2/BiVO4 composites. From the high-resolution XPS spectra of the Bi4f region in Fig. 3(C), it could be seen that the peaks of Bi4f7/2 and Bi4f5/2 in pure BiVO4 were observed at 158.7 and 164.1 eV, respectively, which was in agreement with the literature data [27]. While the peaks of Bi4f7/2 and Bi4f5/2 for 10.00%TiO2/BiVO4 shifted to 159.0 and 164.3 eV, respectively. From Fig. 3(D), V2p peaks in the XPS spectra located at 524.0 and 516.5 eV for pure BiVO4 shifted to 524.4 and 516.9 eV for 10.00%TiO2/BiVO4. A similar shift was also found in the XPS spectra of O1s (529.5 eV for pure BiVO4 shifted to 529.8 eV) (Fig. 3(E)). Such inner shift of the Bi4f, V2p, and V1s orbits originated from the interaction of BiVO4 and TiO2. The analysis distinctly revealed that the interaction between BiVO4 and TiO2 was chemical bonding rather than a simple physical mixing.

FIG. 3 XPS survey spectra (A) and high-resolution XPS spectra of Bi4f (C), V2p (D), O1s (E) and C1s (F) for the surface of pure BiVO4 (a) and 10.00%TiO2/BiVO4 heterojunctions (b), (B) high-resolution XPS spectra of Ti2p in 10.00%TiO2/BiVO4 heterojunctions.
D. UV-Vis DRS analysis

The energy band structure feature of a semiconductor was a key factor in determining its photocatalytic activity. Figure 4(a) presented UV-Vis diffuse reflectance analysis of the pure BiVO4, pure TiO2 and 10.00%TiO2/BiVO4 samples. It was shown that pure TiO2 displayed no absorption of visible-light and the spectrum of pure BiVO4 showed absorption from UV light to 600 nm, while the 10.00%TiO2/BiVO4 showed drastic and stronger photoabsorption in the 400-600 nm wavelength range due to the band gap transition. For a crystalline semiconductor, the optical absorption near the band edge follows Eq.(1) [28]:

(1)

where α, υ, Eg, and A are the absorption coefficient, the light frequency, the band gap, and a constant, respectively. Therefore, plot (αhυ)2 versus , and the band gap energies (Eg) can be estimated by extrapolating the linear region straight line to the axis intercept as shown in Fig. 4(b). In this work, the band gaps (Eg) were estimated to be 2.80, 3.20, and 2.16 eV from the absorption edge, corresponding to the pure BiVO4, pure TiO2 and 10.00%TiO2/BiVO4. Thus, 10.00%TiO2/BiVO4 has a wider photoabsorption range and more suitable band gap for photocatalytic applications.

FIG. 4 (a) UV-Vis diffuse reflectance spectra of pure BiVO4, pure TiO2 and 10.00%TiO2/BiVO4 heterojunctions. (b) Plots of (αhν)2 versus the band gap energies (Eg).

Therefore, based on these characterization results, it can be deduced that the photoabsorption performance of BiVO4 was greatly improved by coupling the appropriate amount of TiO2, and 10.00%TiO2/BiVO4 composite will be a potential candidate as visible-light driven photocatalyst.

E. Photocatalytic properties

The photocatalytic activity of the TiO2/BiVO4 heterojunctions was evaluated for degradation of dye MB in aqueous solution under visible light, and compared with pure BiVO4 under the same condition. Figure 5 shows the photodegradation efficiency of MB under visible light in the presence of pure BiVO4 and TiO2/BiVO4 heterojunctions. It was observed that the pure BiVO4 degraded about 33.22% of MB in 150 min while 4.58%TiO2/BiVO4, 10.00%TiO2/BiVO4, 16.54%TiO2/BiVO4, and 24.53%TiO2/BiVO4 degraded about 64%, 88.58%, 71.07%, and 74.28%, respectively. It was clear that the coupling of TiO2 with BiVO4 increased the photodegradation efficiency of MB under the visible light. It also showed that the photocatalytic activity of TiO2/BiVO4 was strongly dependent on the coupling amount of TiO2. Optimum TiO2 coupling amount in this study was 10.00%. This was possibly due to the enhanced light absorption intensity of the TiO2/BiVO4 heterojunction as emphasized by UV-Vis DRS spectra in Fig. 4. An excess of TiO2 amount (16.54% and 24.53%) might block the incident visible light irradiation on BiVO4, due to the fact that TiO2 displays no absorption of visible-light.

FIG. 5 Photodecomposition of MB under visible light irradiation in the presence of pure BiVO4 (a), and TiO2/BiVO4 heterojunctions (b) 4.58%TiO2/BiVO4, (c) 10.00%TiO2/BiVO4, (d) 16.54%TiO2/BiVO4, (e) 24.53%TiO2/BiVO4.

Regular 10.00%TiO2/BiVO4 particles (10.00%TiO2/ BiVO4-R) were synthesized by a similar procedure to that of 10.00%TiO2/BiVO4 microfiber, except that no cotton template was used. Figure 6 shows the photocatalytic performance of 10.00%TiO2/BiVO4-R and 10.00%TiO2/BiVO4 for the degradation of MB. The inset described SEM images of 10.00%TiO2/BiVO4-R and 10.00%TiO2/BiVO4. As shown, 10.00%TiO2/BiVO4-R showed the lowest activity of 54.11% after 150 min irradiation, while microfiber 10.00%TiO2/BiVO4 showed a significant activity as high as 88.58%. Such dramatic activity enhancement should be due to the large surface area [29]. With a larger surface area, the number of active surface sites increases and so does the surface charge carrier transfer rate in photocatalysis, which can contribute to the higher photocatalytic activity [30]. Furthermore, the microfiber structure can facilitate mass transfer and increase the accessibility of active sites on 10.00%TiO2/BiVO4 surface to methylene blue molecules. The result was in agreement with the idea that photocatalytic activity is structure dependent [16, 17].

FIG. 6 Photodecomposition of MB under visible light irradiation in the presence of 10%TiO2/BiVO4-R and 10%TiO2/BiVO4 microfiber heterojunctions.

Figure 7 shows the time-dependent UV-Vis absorption spectra of MB during photoirradiation with pure BiVO4 and 10.00%TiO2/BiVO4 heterojunction. As shown, the characteristic absorption band around 664 nm could be attributed to a chromophore containing a long conjugated π system, while the absorption peaks at 245 and 292 nm were related to aromatic rings [31]. From Fig. 7, it could be seen that the 10.00%TiO2/BiVO4 (Fig. 7(b)) decolorized MB faster than pure BiVO4 (Fig. 7(a)), and the characteristic absorption peaks at 292 and 664 nm diminished gradually with no detection of any new peak. According to Fig. 7(b), the decrease of the 664 nm absorption band suggested the conjugated π bond of the molecule structure of MB was broken [31]. The decrease of the absorption bands around 245 and 292 nm in the UV region was due to the breaking of the aromatic rings in the MB molecules which confirms the destruction of degradation intermediates including aminobenzothiazole and aniline [31, 32]. These results indicated that the MB molecules were photocatalytically decomposed by 10.00%TiO2/BiVO4 under visible light irradiation. The exact intermediate and the final products were currently unclear, and will be elucidated in future work.

FIG. 7 UV-Vis absorption spectra of MB during the photodegradation process in the presence of (a) pure BiVO4 and (b) 10.00%TiO2/BiVO4.

In order to investigate the mechanism of the enhanced photocatalytic activity of heterojunction, the band edge positions of conduction band (CB) and valence band (VB) of the two semiconductors at the point of zero charge should be confirmed according to the empirical equation [33, 34]:

(2)

Where χ is the absolute electronegativity of the semiconductor, which is defined as the geometric mean of the absolute electronegativity of the constitute atoms. According to the equation above, the calculated CB and VB of TiO2 are -0.2 and 3.00 eV, and of BiVO4 are 0.11 and 2.27 eV, respectively. When the BiVO4 and TiO2 were closely contacted together and visible-light irradiation took place, BiVO4 was excited and the electrons (e-) in the VB were excited to the CB, leaving the holes (h+) behind. Then the excited-state electrons could be easily injected from the CB of BiVO4 into the CB of coupled TiO2 due to the joint of the electric fields between two materials. The electrons and holes transfer between the semiconductors made the Fermi level of TiO2 to move down, while that of BiVO4 move up until pseudo-equilibrium was reached. Thus, TiO2/BiVO4 n-n junction would be formed, which was favorable for the fast separation of electrons and holes due to the effect of inner electric field, analogous to BiOI/TiO2 [35], Bi2O2CO3/BiOI [36], Bi2WO6/TiO2 [37] and TiO2/Bi2O3 [38] heterojunctions. Thus, based on the above results, a possible photocatalytic mechanism of TiO2/BiVO4 heterostructure was proposed, as shown in Scheme 1.

Scheme 1 The energy band diagram of TiO2/BiVO4 heterostructure photocatalyst after the thermodynamic equlilibrium.

The photoinduced holes in VB of BiVO4 were powerful oxidative species, they were able to oxidize water (H2O) molecules and hydroxyl (OH-) groups to generate highly reactive hydroxyl (·OH) radicals. Meanwhile, the electrons injected into the CB of TiO2 would then be captured by O2 to yield ·O2-. Highly reactive ·OH and ·O2- radicals had extremely strong oxidative capability to partially or completely mineralize MB molecules. In this way, the recombination of electron-hole pairs generated on BiVO4 could be effectively reduced. The activity enhancement of BiVO4 was ascertained owing to this high efficient separation mode for TiO2/BiVO4 heterostrucutre. Furthermore, the weak photosensitization effect of dyes on TiO2/BiVO4 could be also favorable for the dyes degradation [39].

Ⅳ. CONCLUSION

In this study, TiO2/BiVO4 heterojunctions with microfiber structures were synthesized by using cotton as biotemplates. It was demonstrated that coupling of TiO2 with BiVO4 can result in a high active photocatalyst for degradation of dye MB in aqueous solution under visible light irradiation. The introduction of TiO2 led to the formation of n-n heterojunction at the contact interface of TiO2 and BiVO4, which not only narrowed the band gap of BiVO4 for extending the absorption range of visible light, but also promoted the transfer of charge carriers across interface for suppressing the recombination of photogenerated electron-hole pairs, and thus improved the photocatalytic performance of TiO2/BiVO4 heterojunctions. The results indicated that the photocatalysts with proper coupling weight ratio of TiO2 can efficiently catalyze the degradation of MB relative to pure BiVO4. 10.00%TiO2/BiVO4 photocatalyst showed the highest photocatalytic activity towards the degradation of MB, and 88.58%MB could be degraded within 150 min. This work provides a new insight for developing novel composite catalysts, as well as offering high efficient visible-light-driven photocatalysts for water purification and environmental remediation.

Ⅴ. ACKNOWLEDGMENTS

This work was supported by the Scientific Research Program Funded by Shaanxi Provincial Education Department (No.2013JK0690), Fundamental Research Funds of Xianyang Normal University (No.14XSYK011, No.12XSYK025), Shaanxi Province Natural Science Foundation (No.2015JQ5188).

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纤维状TiO2/BiVO4异质结的高可见光光催化性能
马占营, 李小博, 周彩华, 邓玲娟, 范广     
咸阳师范学院化学与化工学院, 咸阳 712000
摘要: 以棉花纤维为生物模板制备了系列纤维状TiO2/BiVO4异质结材料, 采用SEM、XRD、XPS、UV-Vis DRS及光催化实验表征了样品的微观形貌结构及光催化性能.结果表明所制备的TiO2/BiVO4样品呈纤维状, 直径约为2.5~5 μm, 且样品中TiO2含量越大, 样品表面越粗糙紧致.当TiO2含量为10.0wt%时, TiO2/BiVO4异质结材料对MB的光催化降解性能最高, 可见光照射150 min, 降解率可达到88.58%.纤维状TiO2/BiVO4光催化活性增强主要由于TiO2和BiVO4界面之间n-n异质结的形成, 不仅拓宽了TiO2/BiVO4的可见光吸收范围, 而且促进了光生电子-空穴对的有效分离, 在此基础上提出了TiO2/BiVO4异质结对MB的可见光光催化机理.
关键词: TiO2/BiVO4    纤维    可见光    光催化