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CHINESE JOURNAL OF CHEMICAL PHYSICS VOLUME 30, NUMBER 2 APRIL 27, 2017 ARTICLE TiO 2 /BiVO 4 , 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 College of Chemistry and Chemical Engineering, Xianyang Normal University, Xianyang 712000, China (Dated: Received on September 6, 2016; Accepted on November 17, 2016) Novel TiO 2 /BiVO 4 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 TiO 2 /BiVO 4 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 TiO 2 . The TiO 2 /BiVO 4 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 TiO 2 and BiVO 4 , which not only narrowed the band gap of BiVO 4 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 TiO 2 /BiVO 4 microfibrous photocatalyst was proposed. Key words: TiO 2 /BiVO 4 , 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 BiVO 4 , 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 photocat- alytic activity of pure BiVO 4 need to be further im- proved owing to the rapid recombination rate of photo- generated carriers [4]. Therefore, it was necessary to develop effective solution to improve the charge separa- tion efficiency and enhance visible-light photoactivity. Forming a heterojunction between BiVO 4 and another semiconductor such as V 2 O 5 [5], Bi 2 O 3 [6], Cu 2 O [7, 8], and InVO 4 [9], was an effective way to address the above two issues [10, 11]. As is known, TiO 2 , as a wide band-gap semiconduc- tor, has been applied widely because of its high sta- bility, low cost, nontoxity and efficient photocatalytic activities under UV light irradiation [12]. Although it could not be excited under visible light, it had suit- able energy band that could effectively transfer the * Author to whom correspondence should be addressed. E-mail: [email protected], Tel.: +86-29-33720704 photo-generated charges from BiVO 4 [13, 14]. Hu et al. [15] reported that heterojunctions exhibited higher photocatalytic activity than the individual components, which confirmed that the combination of BiVO 4 and TiO 2 was an effective way to enhance the photocatalytic activity of BiVO 4 under visible light irradiation. Zhang et al. [14] prepared TiO 2 /BiVO 4 spherical composite photocatalysts by the one-step microwave hydrothermal method. They investigated the photocatalytic degrada- tion of RhB under UV light and Xe lamp irradiation, re- sults 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 mate- rials had a significant impact on functional diversifica- tion and potential applications [16, 17], it was expected that the TiO 2 /BiVO 4 composite with a special mor- phological diversity would have a good photocatalytic activity under visible light irradiation. Microfibers possessed high specific surface area and small thickness. These characteristics assured mi- crofibers potential to be exposed to more light and con- tact 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 photocat- alysts [18], which further accelerate the chemical reac- tions and result in the excellent photocatalytic activity. DOI:10.1063/1674-0068/30/cjcp1609175 153 c 2017 Chinese Physical Society

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Page 1: College of Chemistry and Chemical Engineering, Xianyang ... · BiVO4, one kind of visible light photocatalyst with the energy band gap of 2.4 eV, also attracted a great deal of attention

CHINESE JOURNAL OF CHEMICAL PHYSICS VOLUME 30, NUMBER 2 APRIL 27, 2017

ARTICLE

TiO2/BiVO4, a Heterojuncted Microfiber with Enhanced PhotocatalyticPerformance for Methylene Blue under Visible Light Irradiation

Zhan-ying Ma∗, Xiao-bo Li, Cai-hua Zhou, Ling-juan Deng, Guang Fan

College of Chemistry and Chemical Engineering, Xianyang Normal University, Xianyang 712000, China

(Dated: Received on September 6, 2016; Accepted on November 17, 2016)

Novel TiO2/BiVO4 microfiber heterojunctions were constructed using cotton as biomorphictemplates. The as-synthesized samples were characterized by scanning electron microscope,X-ray diffraction, X-ray photoelectron spectroscopy, UV-Vis diffuse reflectance spectra andphotocatalytic experiment. The morphology of the as-synthesized TiO2/BiVO4 compositeswas 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 ratioof 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 samplesunder visible light, and 88.58%MB could be degraded within 150 min. The enhancementof photocatalytic activity was mainly attributed to the formation of n-n heterojunction atthe 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 chargecarriers across interface. A possible photodegradation mechanism of MB in the presence ofTiO2/BiVO4 microfibrous photocatalyst was proposed.

Key words: TiO2/BiVO4, Microfiber, Visible-light-response, Photocatalysis

I. INTRODUCTION

Numerous efforts had been made to develop highlyeffective photocatalysts for the photodecomposition ofenvironmental contaminants like pesticides, dyes andheavy metal in water [1]. Monoclinic scheelite-typeBiVO4, one kind of visible light photocatalyst with theenergy band gap of 2.4 eV, also attracted a great dealof attention or pollutant elimination under visible lightirradiation [2, 3]. However, unavoidably, the photocat-alytic activity of pure BiVO4 need to be further im-proved owing to the rapid recombination rate of photo-generated carriers [4]. Therefore, it was necessary todevelop effective solution to improve the charge separa-tion efficiency and enhance visible-light photoactivity.Forming a heterojunction between BiVO4 and anothersemiconductor such as V2O5 [5], Bi2O3 [6], Cu2O [7, 8],and InVO4 [9], was an effective way to address the abovetwo issues [10, 11].

As is known, TiO2, as a wide band-gap semiconduc-tor, has been applied widely because of its high sta-bility, low cost, nontoxity and efficient photocatalyticactivities under UV light irradiation [12]. Although itcould not be excited under visible light, it had suit-able energy band that could effectively transfer the

∗Author to whom correspondence should be addressed. E-mail:[email protected], Tel.: +86-29-33720704

photo-generated charges from BiVO4 [13, 14]. Hu etal. [15] reported that heterojunctions exhibited higherphotocatalytic activity than the individual components,which confirmed that the combination of BiVO4 andTiO2 was an effective way to enhance the photocatalyticactivity of BiVO4 under visible light irradiation. Zhanget al. [14] prepared TiO2/BiVO4 spherical compositephotocatalysts by the one-step microwave hydrothermalmethod. They investigated the photocatalytic degrada-tion of RhB under UV light and Xe lamp irradiation, re-sults indicated that the degradation efficiency can reachover 94% after 330 min UV irradiation, but only about83% after 360 min Xe lamp irradiation. Considering thefact that the morphological diversity of inorganic mate-rials had a significant impact on functional diversifica-tion and potential applications [16, 17], it was expectedthat the TiO2/BiVO4 composite with a special mor-phological diversity would have a good photocatalyticactivity under visible light irradiation.

Microfibers possessed high specific surface area andsmall thickness. These characteristics assured mi-crofibers potential to be exposed to more light and con-tact with more dye molecules; meanwhile, its separationand migration efficiency of photogenerated electron-hole pairs was effectively improved. In addition, themicro-pores could serve as transport paths for smallmolecules, benefiting the reactant molecules to get tothe reactive sites on the framework walls of photocat-alysts [18], which further accelerate the chemical reac-tions and result in the excellent photocatalytic activity.

DOI:10.1063/1674-0068/30/cjcp1609175 153 c⃝2017 Chinese Physical Society

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154 Chin. J. Chem. Phys., Vol. 30, No. 2 Zhan-ying Ma et al.

Therefore, instead of the corresponding nanoparticles,microfibers being an important subclass of microstruc-tural materials are deemed as potential good candidatesfor practical applications [19].

Template procedures were an ideal way to control ma-terial structure including the outer morphology and sizeand the inner pore size and distribution [20]. In recentyears, biomorphic mineralization has been noteworthyas a new fabrication technique for functional materials,which is a technique that produces materials with mor-phologies and structures resembling those of nature liv-ing things [21]. Biomorphic mineralization was of low-cost, environmentally benign, and easily removed withheating procedures. Natural cotton had been selectedas templates to produce various advanced biomorphicmaterials, such as MgO [22], NiO [23] and In2O3 [24].

In the present work, we synthesized pure BiVO4

and a series of biomorphic TiO2/BiVO4 microfibersby using cotton fibers as biomorphic templates, anddemonstrated their physical properties. The photocat-alytic properties of the as-synthesized TiO2/BiVO4 het-erojunctions were tested by the photodegradation ofmethylene blue (MB) aqueous solution under visiblelight irradiation. The mechanism of enhanced photo-catalytic activity of TiO2/BiVO4 heterojunction pho-tocatalysts was also discussed.

II. EXPERIMENTS

A. Materials and Reagents

Bi(NO3)3·5H2O, NH4VO3, citric acid, nitric acid,ammonia, n-tetrabutyltitanate (C16H36O4Ti), methy-lene blue (MB), and other chemicals were obtained fromShanghai Chemical Reagents Company (China). Allchemicals were of analytical reagent grade and used asreceived without further purification. Ultrapure deion-ized water was used throughout the experiments.

B. Preparation of TiO2/BiVO4 heterojunction microfibers

In a typical procedure, 0.485 g of Bi(NO3)3·5H2Oand the same molar of citric acid were dissolved in30 mL of 2 mol/L nitric acid aqueous solution, ad-justing the pH value to 7.0 by dropwisely titration of1 mol/L ammonia solution under stirring, and trans-parent solution A was formed. Meanwhile, 0.117 g ofNH4VO3 was dissolved in deionized water at 70 ◦C andthe same molar of citric acid was added to obtain darkgreen solution B. After mixing of solution A and B,uniform dark green solution C was obtained. Differ-ent dosage of n-tetrabutyltitanate (C16H36O4Ti) wasdissolved in ethanol at room temperature, thus pale-yellow solution D was formed. The dried and loose cot-ton fibers were immersed into the mixture of solutionC and D. After immersing for 24 h, the cotton fibers

were taken out, dried at 50 ◦C for 12 h, which werethen placed in an alundum crucible and calcined in airat 500 ◦C for 1 h. Finally, pale-yellow TiO2/BiVO4

heterojunction were obtained. The weight ratio ofC16H36O4Ti/(C16H36O4Ti+Bi(NO3)3·5H2O) was con-trolled 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 synthe-sized under the same conditions without adding n-C16H36O4Ti.

C. Characterization

The phase identification of the as-prepared pow-ders were obtained on a Riggaku D/max-3C X-raypowder X-ray diffractometry using Cu Kα radiation(λ=1.5405 nm, 40 kV, 40 mA). Scanning electron mi-croscopy (SEM) images were observed by Hitachi S-4800 scanning electron microscopy. UV-visible dif-fuse reflectance spectra (UV-Vis DRS) of the sampleswere recorded on Lambd 950 spectrophotometer usingBaSO4 as reference.

D. Measurement of photocatalytic activity

The photocatalytic activity of TiO2/BiVO4 hetero-junctions was evaluated by measuring the degradationof MB under visible light at room temperature. In atypical process, 100 mg of TiO2/BiVO4 samples wereadded to 100 mL of 10 mg/L MB solution and thenstirred in the dark for 30 min, which allowed it to reachadsorption equilibrium and uniform dispersity. The so-lution was then exposed to visible light irradiation froma 500 W Xe lamp at room temperature. UV radiationwas cut off by using a 400-nm filter, prior to irradia-tion of the sample. During the irradiation, 5 mL of thesuspension was sequentially taken from the reactor ev-ery 30 min, and filtered immediately through 0.22 µmmembrane filters for UV-Vis analysis. The decoloriza-tion efficiency was monitored by determining the ab-sorbance around 664 nm in the UV-Vis spectra.

III. RESULTS AND DISCUSSION

A. SEM analysis

Figure 1 shows SEM images of pure BiVO4 andTiO2/BiVO4 heterojunctions via cotton biomorphictemplate. From Fig.1, it is clearly shown that allthese samples are consisted of a large quantity of mi-crofibers with diameter from 2.5 µm to 5 µm, indicatingthe formation of biomorphic TiO2/BiVO4 via cottontemplate. These microfibers may present as straightor twisted shapes, which are well consistent with the

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Chin. J. Chem. Phys., Vol. 30, No. 2 TiO2/BiVO4 for Methylene Blue under Visible Light Irradiation 155

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.

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

straight or twisted shapes of cotton template. Com-pared with pure BiVO4 microfibers (Fig.1(a)), the sur-faces of TiO2/BiVO4 heterojunctions (Fig.1 (b), (c),(d), and (e)) are coarse and have many microstructureson them. In addition, the framework of TiO2/BiVO4

becomes more compact with the increase of weight ratioof TiO2. Therefore, the amount of n-tetrabutyltitanatein the impregnation step has an important influence onthe microstructure of TiO2/BiVO4 surface.

B. XRD analysis

The phases and crystallinity of the as-prepared pureBiVO4 and TiO2/BiVO4 heterojunctions were charac-terized by XRD, as shown in Fig.2. From Fig.2(a), thecrystal form of the BiVO4 can be identified to the mon-oclinic scheelite type with characteristic 2θ values of18.85◦ (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 characteristicpeaks appearing in the TiO2/BiVO4 composites weresimilar to those of pure BiVO4. However, a carefulcomparison shows a small peak at 2θ=25.4◦ in XRDpatterns of TiO2/BiVO4 heterojunctions, but not inXRD patterns of pure BiVO4 sample. This small peakwas ascribed to the characteristic peak (101) of anataseTiO2 (JCPDS card No.21-1272), indicating the exis-tence of TiO2. With increasing the contents of TiO2 inthe composites, the peak intensities of the anatase TiO2

increased. No extra peaks except for BiVO4 and TiO2

crystal phase were detected in TiO2/BiVO4 heterojunc-tions. It was also found that after the introduction ofTiO2 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

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156 Chin. J. Chem. Phys., Vol. 30, No. 2 Zhan-ying Ma et al.

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

heterojunctions.

displayed higher crystallinity than others. Furthermore,from the (011) peak, there was a slight shift to highdiffraction angel in 10.00%TiO2/BiVO4 XRD pattern,compared with pure BiVO4 (Fig.2(b)), indicating thatthe appropriate introduction of TiO2 into BiVO4 al-ter the crystalline structure of BiVO4. All these resultsconfirmed that the heterojunction structure was formedbetween TiO2 and BiVO4.

C. XPS analysis

To contrast the electronic environment and sur-face composition of 10.00%TiO2/BiVO4 heterojunc-tions with that of pure BiVO4, survey XPS andhigh-resolution XPS analysis of both pure BiVO4 and10.00%TiO2/BiVO4 were performed and the results areshown in Fig.3. From Fig.3(A), Bi, V, O and C (the car-bon contamination is often ubiquitous in the XPS mea-surements [25]) were observed in the samples of bothpure BiVO4 and 10.00%TiO2/BiVO4 where they wereexpected 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 theliterature data for TiO2 [26] in 10.00%TiO2/BiVO4

composites. From the high-resolution XPS spectra ofthe Bi4f region in Fig.3(C), it could be seen that thepeaks of Bi4f7/2 and Bi4f5/2 in pure BiVO4 were ob-

served at 158.7 and 164.1 eV, respectively, which wasin agreement with the literature data [27]. While thepeaks of Bi4f7/2 and Bi4f5/2 for 10.00%TiO2/BiVO4

shifted to 159.0 and 164.3 eV, respectively. FromFig.3(D), V2p peaks in the XPS spectra located at524.0 and 516.5 eV for pure BiVO4 shifted to 524.4 and516.9 eV for 10.00%TiO2/BiVO4. A similar shift wasalso found in the XPS spectra of O1s (529.5 eV forpure BiVO4 shifted to 529.8 eV) (Fig.3(E)). Such in-ner shift of the Bi4f, V2p, and V1s orbits originatedfrom the interaction of BiVO4 and TiO2. The analysisdistinctly revealed that the interaction between BiVO4

and TiO2 was chemical bonding rather than a simplephysical mixing.

D. UV-Vis DRS analysis

The energy band structure feature of a semicon-ductor was a key factor in determining its photocat-alytic activity. Figure 4(a) presented UV-Vis diffusereflectance analysis of the pure BiVO4, pure TiO2

and 10.00%TiO2/BiVO4 samples. It was shown thatpure TiO2 displayed no absorption of visible-light andthe spectrum of pure BiVO4 showed absorption fromUV light to 600 nm, while the 10.00%TiO2/BiVO4

showed drastic and stronger photoabsorption in the400−600 nm wavelength range due to the band gaptransition. For a crystalline semiconductor, the opti-

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Chin. J. Chem. Phys., Vol. 30, No. 2 TiO2/BiVO4 for Methylene Blue under Visible Light Irradiation 157

FIG. 4 (a) UV-Vis diffuse reflectance spectra of pureBiVO4, pure TiO2 and 10.00%TiO2/BiVO4 heterojunc-tions. (b) Plots of (αhν)2 versus the band gap energies (Eg).

cal absorption near the band edge follows Eq.(1) [28]:

(αhν)2 = A(hν − Eg)n/2 (1)

where α, ν, Eg, and A are the absorption coefficient,the light frequency, the band gap, and a constant, re-spectively. Therefore, plot (αhν)2 versus hν, and theband gap energies (Eg) can be estimated by extrapo-lating the linear region straight line to the hν axis in-tercept as shown in Fig.4(b). In this work, the bandgaps (Eg) were estimated to be 2.80, 3.20, and 2.16 eVfrom the absorption edge, corresponding to the pureBiVO4, pure TiO2 and 10.00%TiO2/BiVO4. Thus,10.00%TiO2/BiVO4 has a wider photoabsorption rangeand more suitable band gap for photocatalytic applica-tions.

Therefore, based on these characterization results,it can be deduced that the photoabsorption perfor-mance of BiVO4 was greatly improved by coupling theappropriate amount of TiO2, and 10.00%TiO2/BiVO4

composite will be a potential candidate as visible-lightdriven photocatalyst.

E. Photocatalytic properties

The photocatalytic activity of the TiO2/BiVO4 het-erojunctions was evaluated for degradation of dye MBin aqueous solution under visible light, and com-pared with pure BiVO4 under the same condition.

FIG. 5 Photodecomposition of MB under visible lightirradiation in the presence of pure BiVO4 (a), andTiO2/BiVO4 heterojunctions (b) 4.58%TiO2/BiVO4,(c) 10.00%TiO2/BiVO4, (d) 16.54%TiO2/BiVO4, (e)24.53%TiO2/BiVO4.

Figure 5 shows the photodegradation efficiency of MBunder visible light in the presence of pure BiVO4 andTiO2/BiVO4 heterojunctions. It was observed thatthe pure BiVO4 degraded about 33.22% of MB in150 min while 4.58%TiO2/BiVO4, 10.00%TiO2/BiVO4,16.54%TiO2/BiVO4, and 24.53%TiO2/BiVO4 de-graded about 64%, 88.58%, 71.07%, and 74.28%, re-spectively. It was clear that the coupling of TiO2 withBiVO4 increased the photodegradation efficiency of MBunder the visible light. It also showed that the photo-catalytic activity of TiO2/BiVO4 was strongly depen-dent on the coupling amount of TiO2. Optimum TiO2

coupling amount in this study was 10.00%. This waspossibly due to the enhanced light absorption inten-sity of the TiO2/BiVO4 heterojunction as emphasizedby UV-Vis DRS spectra in Fig.4. An excess of TiO2

amount (16.54% and 24.53%) might block the incidentvisible light irradiation on BiVO4, due to the fact thatTiO2 displays no absorption of visible-light.

Regular 10.00%TiO2/BiVO4 particles (10.00%TiO2/BiVO4-R) were synthesized by a similar procedure tothat of 10.00%TiO2/BiVO4 microfiber, except thatno cotton template was used. Figure 6 shows thephotocatalytic performance of 10.00%TiO2/BiVO4-R and 10.00%TiO2/BiVO4 for the degradationof MB. The inset described SEM images of10.00%TiO2/BiVO4-R and 10.00%TiO2/BiVO4.As shown, 10.00%TiO2/BiVO4-R showed the lowestactivity of 54.11% after 150 min irradiation, whilemicrofiber 10.00%TiO2/BiVO4 showed a significantactivity as high as 88.58%. Such dramatic activityenhancement should be due to the large surface area[29]. With a larger surface area, the number of activesurface sites increases and so does the surface chargecarrier transfer rate in photocatalysis, which cancontribute to the higher photocatalytic activity [30].Furthermore, the microfiber structure can facilitatemass transfer and increase the accessibility of activesites on 10.00%TiO2/BiVO4 surface to methylene blue

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158 Chin. J. Chem. Phys., Vol. 30, No. 2 Zhan-ying Ma et al.

FIG. 6 Photodecomposition of MB under visible lightirradiation in the presence of 10%TiO2/BiVO4-R and10%TiO2/BiVO4 microfiber heterojunctions.

molecules. The result was in agreement with the ideathat photocatalytic activity is structure dependent[16, 17].

Figure 7 shows the time-dependent UV-Vis ab-sorption spectra of MB during photoirradiation withpure BiVO4 and 10.00%TiO2/BiVO4 heterojunction.As shown, the characteristic absorption band around664 nm could be attributed to a chromophore con-taining a long conjugated π system, while the absorp-tion peaks at 245 and 292 nm were related to aro-matic rings [31]. From Fig.7, it could be seen that the10.00%TiO2/BiVO4 (Fig.7(b)) decolorized MB fasterthan pure BiVO4 (Fig.7(a)), and the characteristic ab-sorption peaks at 292 and 664 nm diminished gradu-ally with no detection of any new peak. According toFig.7(b), the decrease of the 664 nm absorption bandsuggested the conjugated π bond of the molecule struc-ture of MB was broken [31]. The decrease of the ab-sorption bands around 245 and 292 nm in the UV re-gion was due to the breaking of the aromatic ringsin the MB molecules which confirms the destructionof degradation intermediates including aminobenzoth-iazole and aniline [31, 32]. These results indicated thatthe MB molecules were photocatalytically decomposedby 10.00%TiO2/BiVO4 under visible light irradiation.The exact intermediate and the final products were cur-rently unclear, and will be elucidated in future work.

In order to investigate the mechanism of the enhancedphotocatalytic activity of heterojunction, the band edgepositions of conduction band (CB) and valence band(VB) of the two semiconductors at the point of zerocharge should be confirmed according to the empiricalequation [33, 34]:

E0CB = χ− EC − Eg (2)

Where χ is the absolute electronegativity of the semi-conductor, which is defined as the geometric mean ofthe absolute electronegativity of the constitute atoms.

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

According to the equation above, the calculated CB andVB of TiO2 are −0.2 and 3.00 eV, and of BiVO4 are0.11 and 2.27 eV, respectively. When the BiVO4 andTiO2 were closely contacted together and visible-lightirradiation took place, BiVO4 was excited and the elec-trons (e−) in the VB were excited to the CB, leavingthe holes (h+) behind. Then the excited-state electronscould be easily injected from the CB of BiVO4 intothe CB of coupled TiO2 due to the joint of the elec-tric fields between two materials. The electrons andholes transfer between the semiconductors made theFermi 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 wasfavorable for the fast separation of electrons and holesdue to the effect of inner electric field, analogous toBiOI/TiO2 [35], Bi2O2CO3/BiOI [36], Bi2WO6/TiO2

[37] and TiO2/Bi2O3 [38] heterojunctions. Thus, basedon the above results, a possible photocatalytic mecha-nism of TiO2/BiVO4 heterostructure was proposed, asshown in Scheme 1.

The photoinduced holes in VB of BiVO4 were pow-erful oxidative species, they were able to oxidize water(H2O) molecules and hydroxyl (OH−) groups to gener-

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Chin. J. Chem. Phys., Vol. 30, No. 2 TiO2/BiVO4 for Methylene Blue under Visible Light Irradiation 159

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

ate highly reactive hydroxyl (·OH) radicals. Meanwhile,the electrons injected into the CB of TiO2 would then becaptured by O2 to yield ·O2

−. Highly reactive ·OH and·O2

− radicals had extremely strong oxidative capabilityto partially or completely mineralize MB molecules. Inthis way, the recombination of electron-hole pairs gen-erated on BiVO4 could be effectively reduced. The ac-tivity enhancement of BiVO4 was ascertained owing tothis high efficient separation mode for TiO2/BiVO4 het-erostrucutre. Furthermore, the weak photosensitizationeffect of dyes on TiO2/BiVO4 could be also favorablefor the dyes degradation [39].

IV. CONCLUSION

In this study, TiO2/BiVO4 heterojunctions with mi-crofiber structures were synthesized by using cotton asbiotemplates. It was demonstrated that coupling ofTiO2 with BiVO4 can result in a high active photocata-lyst for degradation of dye MB in aqueous solution un-der visible light irradiation. The introduction of TiO2

led to the formation of n-n heterojunction at the contactinterface of TiO2 and BiVO4, which not only narrowedthe band gap of BiVO4 for extending the absorptionrange of visible light, but also promoted the transferof charge carriers across interface for suppressing therecombination of photogenerated electron-hole pairs,and thus improved the photocatalytic performance ofTiO2/BiVO4 heterojunctions. The results indicatedthat the photocatalysts with proper coupling weight ra-tio of TiO2 can efficiently catalyze the degradation ofMB relative to pure BiVO4. 10.00%TiO2/BiVO4 pho-tocatalyst showed the highest photocatalytic activitytowards the degradation of MB, and 88.58%MB couldbe degraded within 150 min. This work provides a newinsight for developing novel composite catalysts, as wellas offering high efficient visible-light-driven photocata-lysts for water purification and environmental remedia-tion.

V. ACKNOWLEDGMENTS

This work was supported by the Scientific ResearchProgram Funded by Shaanxi Provincial EducationDepartment (No.2013JK0690), Fundamental ResearchFunds of Xianyang Normal University (No.14XSYK011,No.12XSYK025), Shaanxi Province Natural ScienceFoundation (No.2015JQ5188).

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