The p–n heterojunction with porous BiVO4 framework and well-distributed Co3O4 as a super visible-light-driven photocatalyst

Xueming Dang, Xiufang Zhang*, Xiaoli Dong, Wenqi Ruan, Hongchao Ma and Mang Xue
School of Light Industry and Chemical Engineering, Dalian Polytechnic University, Dalian, China 116034. E-mail: zhangxf@dlpu.edu.cn; Fax: +86 411 86323736; Tel: +86 411 86323508

Received 29th September 2014 , Accepted 6th October 2014

First published on 7th October 2014


Abstract

The p–n heterojunction with mesoporous BiVO4 framework well-distributed Co3O4 is fabricated. The mesoporous structure is prepared by nanocasting technique using KIT-6 as template, while the incorporation of Co3O4 particles is completed by the impregnation technique. Transmission electron microscopy (TEM) image shows that Co3O4 particles have been successfully loaded in the framework of the mesoporous BiVO4. Energy dispersive spectrum (EDS) mapping reveals that Co3O4 particles distribute uniformly in the sample, which is the result of the template effect of the mesoporous structure. The photocatalytic removal rate of RhB with BiVO4 is enhanced by the construction of the p–n heterojunction of Co3O4/mesoporous BiVO4. This increase can be attributed to the enhanced separation efficiency of the photogenerated charge carriers produced by the p–n heterojunction. Mesoporous BiVO4 enables the guest material of Co3O4 to be well distributed in the matrix of the mesoporous BiVO4, thereby providing a large contact area of Co3O4 and BiVO4. This promotes the charge transferring across the interface, thereby increasing the separation of electron–hole pairs, and leading to the enhancement of photocatalytic ability. Furthermore, the mesoporous structure itself contributes to the enhanced photocatalytic performance.


1. Introduction

Semiconductor photocatalysis has attracted considerable attention because of its promising performance in environmental pollution control.1–3 TiO2 has been proved to be an excellent photocatalyst due to its powerful photocatalytic activity and outstanding stability.4–6 However, the wide band gap (3.2 eV) of TiO2 limits the utilization of visible light, which accounts for a large part of the solar energy. Recently, BiVO4, with a narrow band gap of 2.4 eV, has been the focus of the field of photocatalysis. It satisfies the basic requirements as a photocatalyst for pollution control, including being responsive to visible light,7 and possessing good stability.8,9 However, the low light absorption efficiency and fast recombination of photogenerated electron–hole pairs still limit the photocatalytic activity of BiVO4. Therefore, a few attempts have been devoted for improving the photocatalytic performance of BiVO4, such as porous structure construction,10,11 noble metal modification,12,13 and heterojunction composite fabrication.14,15

Coupling BiVO4 with another semiconductor to form a heterojunction (especially a p–n heterojunction) can restrain the recombination of the photogenerated electron–hole pairs, and then enhance the photocatalytic activity of BiVO4. The large contact area of the two semiconductors can promote the charge transfer across the interface, thereby increasing the separation of electron–hole pairs, leading to the enhancement of photocatalytic ability. Thus, it is an ideal method to increase the contact area of semiconductors in the heterojunction to bring about enhanced photocatalytic ability.16

Mesoporous structure construction can also enhance the photocatalytic performance.17,18 The construction of mesoporous structures in the bulk BiVO4 can elevate the surface area of the photocatalyst to offer a large number of reactive sites.19,20 It can also enhance the light absorption efficiency because of more photons being distributed onto the surface of the photocatalyst, using the pores as light transfer paths. In addition, mesoporous materials themselves can be used as a support of guest materials.21 Mesopores in the structure enable the guest materials to get highly distributed and restrain them to be small particles.22,23 High distribution and the small particle nature of the guest materials in the framework of the host can enhance their contact area. Inspired by this idea, Co3O4 was chosen as the guest material to be loaded in the mesoporous BiVO4 to form the p–n heterojunction. It is a p-type semiconductor and a visible-light-driven photocatalyst with a band gap of 2.07 eV.24 The conduction band level (ECB) of Co3O4 is +0.37 eV vs. NHE, which is more positive compared to that of BiVO4 (ECB = 0 eV vs. NHE) and the valence band (EVB) level of Co3O4 is +2.44 eV vs. NHE, which is also more positive than that of BiVO4 (EVB = 2.40 eV vs. NHE). The matching of band levels and the types between Co3O4 and BiVO4 makes Co3O4 a suitable material for constructing a p–n heterojunction with BiVO4.

Herein, Co3O4/mesoporous BiVO4 p–n heterojunction with a large contact area is first fabricated to get enhanced photocatalytic ability under visible light. The distribution role of mesoporous structure in Co3O4/mesoporous BiVO4 as a visible-light-driven photocatalyst is discussed. RhB, a common pollutant in industry wastewater, is chosen as a test substance to evaluate the photocatalytic performance of the as-prepared samples under visible light.

2. Experimental section

2.1. Sample preparation

2.1.1. Preparation of mesoporous silica KIT-6. The mesoporous silica KIT-6 with cubic Ia[3 with combining macron]d symmetry was prepared as follows:25 6 g of P123 was dissolved in 217 mL of distilled water to which 10 mL of concentrated HCl (35%) and 7.41 mL of butanol (99.4%) were added under stirring for 1 h at 35 °C. 13.8 mL of TEOS (98%) was added at 35 °C (TEOS–P123–HCl–H2O–BuOH = 1[thin space (1/6-em)]:[thin space (1/6-em)]0.017[thin space (1/6-em)]:[thin space (1/6-em)]1.83[thin space (1/6-em)]:[thin space (1/6-em)]195[thin space (1/6-em)]:[thin space (1/6-em)]1.31 in mole ratio). After stirring at 35 °C for 24 h, the mixture was transferred to an enclosed polypropylene bottle, for hydrothermal strategy at 100 °C for 6 h. The product was filtered and washed three times with deionized water and absolute ethanol, and dried at 100 °C for 5 h. Finally, the solids were calcined at 550 °C (2 °C min−1) for 5 h.
2.1.2. Preparation of mesoporous BiVO4. 2 mmol of Bi(NO3)3·5H2O was dissolved in 10 mL of 2 M HNO3 under ultrasound, and a transparent colorless solution was obtained. The same molar mass of NH4VO3 was added to the solution under ultrasound for 30 min to form a bright yellow solution. Then, 0.3 g of prepared KIT-6 was added. After the complete immersion of the KIT-6, the mixture was placed into the electrothermal constant-temperature dry box at 80 °C for 12 h to completely fill the BiVO4 precursor into the void of KIT-6. Then, the dried sample was converted by calcination at 400 °C for 12 h. Finally, the mesoporous BiVO4 was obtained with a 2 M NaOH aqueous solution to eliminate KIT-6. The final product was filtered and washed with distilled water and absolute ethanol. Reference BiVO4 was prepared by the same procedure without the KIT-6.
2.1.3. Preparation of Co3O4/BiVO4 composites. The loading of Co3O4 on BiVO4 was completed by the impregnation method from an aqueous solution of Co(NO3)2. The preparation of Co3O4/mesoporous BiVO4 was carried out by the following typical procedure: mesoporous BiVO4 powder (1.0 g) was added to 10 mL solution of Co(NO3)2 containing an appropriate amount of Co(NO3)2 as 2% Co (recorded by S1), 4% Co (recorded by S2), and 6% Co (recorded by S3) to BiVO4 in a beaker. The suspension was stirred during the evaporation of water under the irradiation of an infrared light. The resulting powder was collected and calcined in air at 300 °C for 2 h. Co3O4/BiVO4 was prepared by the same procedure with mesoporous BiVO4 replaced by BiVO4, and the mass percentage of Co to BiVO4 was 4%.

2.2. Sample characterization

X-ray diffraction (XRD) spectra were recorded by Rigaku D/MAX-2400 with Cu Kα radiation, accelerating voltage of 40 kV, current of 30 mA. The scanning rate was 8° (2θ) min−1, and the scanning range was 10°–80°. The light absorption intensities were measured using a UV-vis spectrophotometer (Shimadzu, UV-2450) with a wavelength range of 200–800 nm. The micro-morphologies of the samples were obtained using a transmission electron microscopy (TEM; JEM-2100(UHR) JEOL). Energy dispersive spectrum (EDS) measurements were performed using a scanning electron microscope (SEM, JSM-6460LV) with an energy spectrometer (X-Max50). X-ray Photoelectron Spectroscopy (XPS) of the samples was obtained by X-ray photoelectron spectrometer (AMICUS). Fluorescence (FL) spectra were recorded by FL spectrometer (LS-55, PE). Tristar 3000 was used to examine the N2 adsorption and desorption properties of the as-prepared samples at 77 K. The surface photovoltage spectra (SPS) were recorded by surface photovoltage measurement system, which consists of a monochromator (model Omni-λ3005) and a lock-in amplifier (model SR830-DSP) with an optical chopper (model SR540) running at a frequency of 20 Hz.

2.3. Measurement of photocatalytic activity

The photocatalytic activities of the as-obtained samples were monitored through the photodegradation of RhB under visible light irradiation. Photocatalytic reactions were conducted in a 100 mL cubic quartz reactor. A 300 W Xe lamp was employed as the visible light source. The light was passed through a filter, which shielded all wavelengths below 420 nm. In all the experiments, photocatalysts (0.10 g) were added to 100 mL RhB aqueous solution (5 mg L−1). During each photocatalytic experiment, 5 mL of the suspension was collected at predetermined time intervals. The suspension was centrifuged at 9500 rpm for 10 min, and the concentration of RhB in the supernatant was determined by measuring the absorbance at λ = 553 nm with a Shimadzu UV2000 spectrophotometer. The adsorption ability of photocatalysts was measured under the same condition without the light illumination.

3. Results and discussion

3.1. Crystal structure

The XRD patterns of BiVO4, Co3O4/BiVO4, mesoporous BiVO4, S1, S2, and S3 are shown in Fig. 1(a). Clear characteristic peaks with 2θ at 18.8°, 28.6°, 30.5°, 35.2°, 39.7° and 53.1° are observed. This indicates that BiVO4 in the samples are monoclinic scheelite structure, which could be indexed to the standard cards (JCPDS no. 14-0688). It is clear that the processes of constructing the mesoporous structure and loading Co3O4 do not influence the crystal form of BiVO4. No diffraction peaks of Co species are observed over the composite samples, which is because of the small crystallite size or low concentration of Co species. To determine the existence and species of Co, XPS was recorded and that of S2 is shown in Fig. 2(b). The peaks ascribed to Bi, V, O and Co are found, certifying the existence of Co species. The high-resolution spectrum for Co2p (Fig. 3(b)) shows two major peaks with binding energies at 779.3 and 195.2 eV, corresponding to Co 2p2/3 and 2p1/3, respectively, which is the characteristic of a Co3O4.26
image file: c4ra11417e-f1.tif
Fig. 1 (a) XRD patterns of BiVO4, Co3O4/BiVO4, mesoporous BiVO4, S1, S2 and S3 and XPS spectra of (b) S2 and (c) Co2p (high resolution).

image file: c4ra11417e-f2.tif
Fig. 2 TEM images of (a) BiVO4, (b) mesoporous BiVO4, (c) S2 and (d) the rectangular area of (c), inset is the HRTEM image of the rectangular area of (d).

image file: c4ra11417e-f3.tif
Fig. 3 EDS mapping of Co element of Co3O4/BiVO4 (a) and S2 (b).

3.2. Morphologies

The particle size of BiVO4 based on TEM image (Fig. 2(a)) is about 500 nm. The big particle size and nonporous structure lead to a low surface area of BiVO4 (1.54 m2). From Fig. 2(b), the replica of KIT-6 with several mesopores in BiVO4 is determined. The determined surface area of mesoporous BiVO4 is 41.2 m2 g−1, which is highly larger than that of BiVO4. This enhancement can be attributed to the mesoporous structure and the small size of the BiVO4 particles. The big surface area of mesoporous BiVO4 can provide more sites for the loading of foreign materials. Fig. 2(c) and (d) show typical TEM images of S2. Most pores in mesoporous BiVO4 are filled with Co3O4 particles. It can be measured from HRTEM image (inset of Fig. 2(d)) that d-spacings are 0.308 and 0.243 nm, which are in agreement with the (121) plane of BiVO4 and the (311) plane of Co3O4, respectively. It is apparent that the Co3O4 particles have been successfully loaded in the mesoporous BiVO4. To investigate the distribution of Co3O4 in mesoporous BiVO4, the Co element distribution of Co3O4/BiVO4 and Co3O4/mesoporous BiVO4 is studied using EDS mapping. The EDS mapping image indicates that the Co element is well dispersed in Co3O4/mesoporous BiVO4 (Fig. 3(b)). This can be attributed to the template action of the mesoporous structure of the composite, which can highly distribute the guest materials and modulate the guest materials to be small particles. The good dispersion of Co element in the framework of mesoporous BiVO4 can enhance the contact area of Co3O4 and BiVO4, and thus elevate the photocatalytic ability of Co3O4/mesoporous BiVO4. From Fig. 3(a), compared with that of Co3O4/mesoporous BiVO4, a few accumulation of Co element on BiVO4 particles is determined, suggesting that the Co element in Co3O4/BiVO4 is not well distributed. The proposed loading mechanism of Co3O4 on the surface of BiVO4 and mesoporous BiVO4 is illustrated in Scheme 1.
image file: c4ra11417e-s1.tif
Scheme 1 The proposed loading mechanism of Co3O4 on the surface of BiVO4 and mesoporous BiVO4.

3.3. Separation ability of photogenerated charge carriers

FL analysis is used to reveal the separation efficiency of the photogenerated electrons27 and holes in semiconductors, and the results are shown in Fig. 4(a). Considering that the FL emission results from the free charge carrier recombination, the lower peak indicates lower the rate of recombination of photogenerated charge carriers. As can be seen from this figure, the FL intensity of BiVO4 is the highest, suggesting that BiVO4 has the highest recombination rate of photogenerated charge carriers. The results confirm that the separation of photogenerated electrons and holes can be improved by the construction of mesoporous BiVO4 or/and the formation of p–n heterojunctions between Co3O4 and BiVO4, leading to the enhancement of photocatalytic activity. The FL intensity of Co3O4/BiVO4 is higher than those of Co3O4/mesoporous BiVO4. Moreover, the mesoporous structure, the larger contact area of Co3O4/mesoporous BiVO4 caused by the good distribution of Co3O4 in the composite contributes to the efficient separation of photogenerated of electrons and holes of Co3O4/mesoporous BiVO4. The FL intensities of S1, S2 and S3 are different, and S2 gets the lowest. The reason why the FL intensity of S1 is higher than S2 is the lower content of Co, which affects the formation of the p–n heterojunctions structure. However, upon the introduction of considerably high Co3O4 into mesoporous BiVO4, the pores and channels of samples may get crammed by Co3O4. On the basis of the low recombination rate of S2, it could be expected that S2 should have high photocatalytic ability. SPS is one of indexes evaluating the separation efficiency of the photogenerated holes and electrons.28 In general, the larger surface photovoltage the photocatalyst has, the better the separation ability of the photogenerated carriers. The SPS are recorded, and the results are shown in Fig. 4(b). The result obtained by the analyses of FL is further confirmed by SPS result.
image file: c4ra11417e-f4.tif
Fig. 4 (a) FL spectra and (b) SPS of BiVO4, Co3O4/BiVO4, mesoporous BiVO4, S1, S2 and S3.

3.4. Optical absorption

The color of the Co3O4/mesoporous BiVO4 composite powder is dark green and becomes darker and darker with increasing Co content. The UV-vis diffuse reflectance spectra of the BiVO4, Co3O4/BiVO4, mesoporous BiVO4, S1, S2 and S3 are shown in Fig. 5(a). All the samples with mesoporous structure (mesoporous BiVO4, S1, S2 and S3) show enhanced absorption intensity over BiVO4, indicating the benefits of the mesoporous structure for the absorption of the photons. This result has also been obtained in other published work.29 Moreover, obvious red shifts of the band gap edge are observed in the spectra of Co3O4/BiVO4, S1, S2 and S3. The calculated band gaps of Co3O4/BiVO4, S1, S2 and S3 are 2.34, 2.20, 2.09 and 2.31 eV (shown in Fig. 5(b)), which are smaller than that of BiVO4 (2.43 eV). This should be attributed to the small band gap of Co3O4 (2.07 eV). Among Co3O4/mesoporous BiVO4 composites, S2 has the strongest absorption intensity and the narrowest band gap. Thus, under the same light intensity, S2 can absorb more photons, and the enhanced photocatalytic ability can be anticipated.
image file: c4ra11417e-f5.tif
Fig. 5 (a) UV-vis absorption spectra of BiVO4, Co3O4/BiVO4, mesoporous BiVO4, S1, S2 and S3 and (b) calculation of the band gap by Kubelka–Munk function of BiVO4, Co3O4/BiVO4, S1, S2 and S3.

3.5. Adsorption ability

Adsorption ability of the target substance is very important for the photocatalytic reaction. After 70 min, the removal rate of MB in the solution with mesoporous BiVO4 is 20.0%, whereas that with BiVO4 is 4.15% (Fig. 6). It is obvious that the adsorption ability of BiVO4 is enhanced by the mesoporous structure, which can be attributed to the increase of the surface area. The adsorption ability of mesoporous BiVO4 slightly decreases when Co3O4 is loaded on it. The decreased surface area of S2 (29.3 m2 g−1) results in this decline.
image file: c4ra11417e-f6.tif
Fig. 6 RhB concentration Ct/C0 vs. time for RhB adsorption.

3.6. Photocatalytic activity and stability

In this experiment, RhB was adopted as a typical pollutant to evaluate the photocatalytic activity of photocatalysts under visible light irradiation. The variation of RhB concentration (Ct/C0) vs. irradiation time with photocatalysts is shown in Fig. 7(a). In 70 min, only 15.7% of RhB is removed with BiVO4, while the RhB removal rate with mesoporous BiVO4 is 53.8%, indicating that the mesoporous structure dramatically enhances the photocatalytic ability of BiVO4. The kinetic analysis shows that the photocatalytic reaction with BiVO4 can be considered as a first order reaction (see Fig. 7(b)), and calculated k value of mesoporous BiVO4 is 0.0106 min−1, which is higher than that of BiVO4 (0.00228 min−1). The enhanced light absorption ability, adsorption ability and separation efficiency of the photogenerated charge carriers are responsible for this increase. In 70 min, the RhB removal rate with S2 is 90.3%. The k value of the S2 (0.0323 min−1) is nearly three times as high as that of mesoporous BiVO4. The loading of Co3O4 on the mesoporous BiVO4 to form the p–n heterojunction can enhance the photocatalytic performance of mesoporous BiVO4. To confirm the heterojunction effect, the same amounts of mesoporous BiVO4 (95 mg) and Co3O4 (5 mg) to those of S2 are used as the photocatalyst to degrade RhB. Under the same condition, the RhB removal rate is largely lower than S2 (Fig. 7(c)), confirming that the enhanced photocatalytic ability of S2 is attributed to the heterojunction effect. This enhancement can be attributed to the increased light absorption ability and separation efficiency of photogenerated holes and electrons. The loading quantity of Co3O4 affects the photocatalytic degradation ability of Co3O4/mesoporous BiVO4. Among the Co3O4/mesoporous BiVO4 composites, the removal rate of S2 is the highest one. However, the determined RhB removal rate of S3 is even lower compared to that of mesoporous BiVO4, indicating that considerably high Co3O4 loaded on the surface of mesoporous BiVO4 can decrease its photocatalytic ability. This result is beyond the explanation based on the light absorption ability and the separation efficiency of photogenerated charge carriers. Thus, it can be reasonably speculated that there are other factors that affect the photocatalytic ability of Co3O4/mesoporous BiVO4. It is reported that the pores in the photocatalysts can accelerate the diffusion of the reactants, and then promote the surface reaction of the photocatalysis.30 The determined pore volumes of mesoporous BiVO4 and S3 are 0.0820 and 0.0615 cm3 g−1, respectively, indicating that the loading of Co3O4 can decrease the pore volume and that some of pores of photocatalysts may be crammed. Thus, the surface reaction should be restrained, and the photocatalytic ability will decrease. To further analyze the role of mesoporous structure, the photocatalytic ability of Co3O4/BiVO4 is compared with that of S2. On one hand, the enhanced photocatalytic ability of S2 can be attributed to the increase in the light absorption ability, separation efficiency of photogenerated charge carriers and adsorption ability caused by the construction of the mesoporous structure. On the other hand, Co3O4/mesoporous BiVO4 has a large contact area of Co3O4 and BiVO4, which can promote the charge transfer across the interface, thereby increasing the separation of electron–hole pairs, and leading to the enhancement of photocatalytic ability.
image file: c4ra11417e-f7.tif
Fig. 7 RhB concentration Ct/C0 (a) and ln(C0/Ct) (b) vs. time for the photocatalytic degradation of RhB with BiVO4, Co3O4/BiVO4, mesoporous BiVO4, S1, S2 and S3, RhB concentration Ct/C0 vs. time for photocatalytic degradation of RhB with S2 and the mixture of mesoporous BiVO4 and Co3O4 (c), UV-vis absorbance spectra of RhB solution after photocatalytic degradation with S2 (d) and cycling runs in the photocatalytic degradation of RhB with S2 (e) under visible light irradiation.

It is well-reported that the RhB photodegradation occurs via two competitive processes: N-deethylation and the destruction of the conjugated structure.31–33 The intermediates produced in RhB degradation process include DER, EER, DR and ER, which result from losing one and/or two ethyl groups from the xanthene ring in the parent RhB structure. If RhB is degraded by N-deethylation, these intermediates would be generated and the color of the oxidized RhB would gradually change from pink to green. On the other hand, if RhB is decomposed by the destruction of the conjugated structure (cleavage of the chromophore structure), the maximum absorption wavelength of the solution during degradation will not obviously change. With the photocatalysis of S2, the absorption maximum of the solution does not obviously shift (Fig. 7(d)), indicating RhB is decomposed by the destruction of the conjugated structure.

The stability of the Co3O4/mesoporous BiVO4 composite (S2) was also evaluated and the result is shown in Fig. 7(e). After recycling five times for the photocatalytic degradation of RhB, no obvious loss in activity is observed, indicating that Co3O4/mesoporous BiVO4 composite is very stable and recyclable.

4. Conclusions

Co3O4/mesoporous BiVO4 with mesoporous BiVO4 networks containing well-dispersed Co3O4 particles is successfully fabricated. The construction of p–n heterojunction with mesoporous structure as the framework can enhance the photocatalytic ability of BiVO4. Mesoporous BiVO4 provides well-distributed space to host Co3O4 particles. The high distribution of Co3O4 particles in the matrix of the mesoporous BiVO4 provides a large contact area of Co3O4 and BiVO4, which promotes the charge transfer across the interface, thereby increasing the separation of photogenerated electron–hole pairs, and leading to the enhancement of photocatalytic ability. Furthermore, mesoporous structure in BiVO4 can enhance the photo absorption ability, adsorption ability and separation ability of photogenerated charge carriers, which contributes to the enhanced photocatalytic ability. On the basis of the results obtained here, it is confirmed that using mesoporous structure as the network to construct p–n heterojunction is an efficient way to enhance the photocatalytic ability.

Acknowledgements

This work was supported by the National Science Fund China (project no. 21107007) and Cultivation Program for Excellent Talents of Science and Technology Department of Liaoning Province (no. 2014026009).

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