Ag2S sensitized mesoporous Bi2WO6 architectures with enhanced visible light photocatalytic activity and recycling properties

Owais Mehraja, Bilal M. Pirzadaa, Niyaz A. Mirb, Saima Sultanaa and Suhail Sabir*a
aDepartment of Chemistry, Aligarh Muslim University, Aligarh-202002, India. E-mail: sabirsuhail09@gmail.com; drsuhailsabir@gmail.com; Tel: +91-571-2700920 ext. 3366
bSolid State and Structural Chemistry Unit, Indian Institute of Science, Bangalore-560012, India

Received 23rd March 2015 , Accepted 5th May 2015

First published on 5th May 2015


Abstract

To harvest solar energy more efficiently, novel Ag2S/Bi2WO6 heterojunctions were synthesized by a hydrothermal route. This novel photocatalyst was synthesized by impregnating Ag2S into a Bi2WO6 semiconductor by a hydrothermal route without any surfactants or templates. The as prepared structures were characterized by multiple techniques such as X-ray diffraction (XRD), X-ray photoelectron spectroscopy (XPS), Brunauer–Emmet–Teller (BET) analysis, scanning electron microscopy (SEM), transmission electron microscopy (TEM), energy dispersive X-ray spectrometry (EDS), UV-vis diffuse reflection spectroscopy (DRS) and photoluminescence (PL). The characterization results suggest mesoporous hierarchical spherical structures with a high surface area and improved photo response in the visible spectrum. Compared to bare Bi2WO6, Ag2S/Bi2WO6 exhibited much higher photocatalytic activity towards the degradation of dye Rhodamine B (RhB). Although silver based catalysts are easily eroded by photogenerated holes, the Ag2S/Bi2WO6 photocatalyst was found to be highly stable in the cyclic experiments. Based on the results of BET, Pl and DRS analysis, two possible reasons have been proposed for the enhanced visible light activity and stability of this novel photocatalyst: (1) broadening of the photoabsorption range and (2) efficient separation of photoinduced charge carriers which does not allow the photoexcited electrons to accumulate on the conduction band of Ag2S and hence prevents the photocorrosion.


1. Introduction

The growing environment concerns and energy demand are the main driving forces for the sustained fundamental and applied research in the area of semiconductor photocatalysis for organic pollutant degradation and hydrogen generation from water splitting using solar light.1–3 Semiconductor photocatalysis involves the photoinduced generation of electron–hole pairs, therefore an ideal photocatalyst should have an extended spectral responsive range and low recombination rate of photogenerated charge carriers.4 Coupling of two photocatalysts to form a heterojunction may provide a chance to develop a new photocatalyst with enhanced separation of photoinduced charge carriers and an extended photoabsorption range.5,6

Bi2WO6 is one of the simple aurivillius oxide with perovskite-like slabs of WO42− and Bi2O22+.7,8 Owing to its non-toxicity and strong oxidizing power, Bi2WO6 has been used as one of the promising and excellent photocatalyst for the decomposition of organic pollutants under visible light.9–12 To improve the photocatalytic activity of bare Bi2WO6, many different morphologies of Bi2WO6 with different hierarchical architecture and surface area have been reported. These include the development of nanoplates,13 porous thin films,14 3D nest like mesoporous Bi2WO6 architectures15 and flower sphere like complex structures.16,17 However there are still two important factors which limits the photocatalytic efficiency and thus hinders the practical application of bare Bi2WO6 (1) the absorption edge of pure Bi2WO6 is ca., 450 nm18,19 which overlaps a small part of solar spectrum leading to the unsatisfactory photoresponse range and (2) the recombination rate of photoinduced charge carriers is large which leads to the low quantum efficiency because of the short lifetimes of the electron hole pairs.20,21

Recent studies have shown that coupling of Bi2WO6 with other semiconductors improves the photocatalytic performance of Bi2WO6 to a substantial extent by promoting the effective separation of photoinduced charge carriers and broadening the visible light responsive range, For e.g. α-Fe2O3/Bi2WO6,22 Bi2S3/Bi2WO6,4 Bi2O3 decorated Bi2WO6 and TiO2 modified flower like Bi2WO6,23 Bi2WO6/BiOBr,24 WO3–Bi2WO6[thin space (1/6-em)]25 and CuPc sensitized Bi2WO6.26

As an important chalcogenide Ag2S with a narrow band gap of 1.1 eV has been investigated extensively for the numerous applications such as photovoltaic device construction,27,28 photocatalytic decomposition of organic pollutants29,30 and photocatalytic H2 production.31 Moreover Ag2S has high absorption coefficient31–36 and besides Ag2S is free from toxic heavy elements like Pb and Cd and thus possess negligible toxicity compared to other narrow band gap materials.37 Owing to the high chemical stability, narrow band gap, high absorption coefficient and excellent optical limiting properties of Ag2S, we choose to couple it with Bi2WO6 to form a heterojunction with enhanced visible light photocatalytic activity and high stability.

Herein for the first time we report novel Ag2S/Bi2WO6 heterojunction photocatalyst to overcome the drawbacks of low photocatalytic efficiency of Bi2WO6 brought by narrow photoresponsive range and high rate of recombination of photoinduced charge carriers. The photocatalytic activity of the as prepared photocatalysts was evaluated by decomposing the dye Rhodamine B. The effect of Ag/Bi weight ratio on the photocatalytic activity was also studied. The stability of the catalyst which is a major concern for catalysts containing silver was also investigated.

2. Experimental

2.1 Synthesis of Ag2S/Bi2WO6 photocatalyst

All the reagents were of analytical purity, purchased from Sigma-Aldrich India and used without further purification. The hierarchical structures of Ag2S/Bi2WO6 were synthesized by a two-step process. In the first step the mesoporous Bi2WO6 microspheres were fabricated by a simple hydrothermal process via following procedure: 1 mmol of Na2WO4·2H2O was dissolved in 15 ml of ethylene glycol under constant stirring. Then 2 mmol of Bi(NO3)3·5H2O was added into the solution and the mixture was stirred for 20 min. Thereafter absolute ethanol (25 ml) was added into the solution and the suspension was transferred into a 50 ml Teflon-lined stainless steel autoclave and heated at 180 °C for 24 h. The autoclave was subsequently cooled to room temperature and the products were collected by filtration. The as obtained products were washed with de-ionized water and absolute ethanol for several times and then dried at 80 °C for 12 h.

In the second step, impregnation of Bi2WO6 surface with Ag2S was carried out by in situ growth of Ag2S on Bi2WO6 substrate at room temperature. In a typical experimental procedure, 0.6 g of Bi2WO6 microspheres and different amounts of AgNO3 were dispersed in 50 ml of absolute ethanol and ultrasonicated for 30 min. After ultrasonication, appropriate amount of Na2S was added to the suspension with continuous stirring. The obtained suspension was vigorously stirred for 8 h. The precipitates were collected and washed with de-ionized water and absolute ethanol for several times and then dried at 80 °C for 12 h. The different weight ratios of Ag2S to Bi2WO6 samples were prepared and noted as 3% Ag2S/Bi2WO6, 5% Ag2S/Bi2WO6, 7% Ag2S/Bi2WO6 and 9% Ag2S/Bi2WO6. For comparison pure Ag2S was also synthesized in absence of Bi2WO6.

2.2 Characterization

To examine the phase purity and crystal structure of as prepared samples, XRD analysis was carried out using PANalytical, XPert PRO powder X-ray diffractometer with CuKα radiation (λ = 1.5418 Å) having a tube voltage of 40 kV and current of 30 mA at room temperature with the scan range 2θ = 15 to 80° and step size 0.02666°. X-ray photoelectron spectroscopy (XPS) was used to analyse the surface properties of samples using MK II photoelectron spectrometer having Al-K(alpha) (1486.6 eV) as the X-ray source. The particle morphology and microstructure of the samples was investigated by FESEM using Carl-Zeiss field-emission scanning electron microscope (FESEM) equipped with EDS attachment and transmission electron microscopy (TEM) using JEOL, JEM 2100F instrument. UV-vis DRS spectra of samples in the region of 300–800 nm was recorded by UV-vis NIR spectrometer (Perkin Elmer) equipped with an integrating sphere assembly. The surface area and pore size distribution of the as prepared samples was characterized by N2 adsorption–desorption isotherm using Quantachrome Instruments Autosorb 1C. Adsorption of samples was done at 77 K and the samples were degased at 150 °C for 3 h before analysis. PL spectra was recorded on fluorospectrometer.

2.3 Photocatalytic activity

To evaluate the photocatalytic activity of the samples, RhB and phenol aqueous solution was degraded under visible light irradiation. A 500 W, tungsten halogen lamp was used as the light source. Immersion well photoreactor made of pyrex glass was used to perform the experiments. Refrigerated circulating liquid bath was used to keep the temperature of the reaction constant at 20 ± 0.3 °C. The experiments were performed as follows. 0.18 g of the as prepared catalyst was added into 180 ml RhB aqueous solution. Prior to the illumination, the suspension was magnetically stirred for at least 30 min in the dark to attain adsorption–desorption equilibrium between dye and catalyst. 5 ml suspensions were sampled at 5 min time intervals and centrifuged to remove the catalyst particles. The concentration of catalyst free dye solution was analysed at λmax (554 nm) using Shimadzu UV-vis 1601, UV-vis spectrophotometer.

To determine the effect of scavengers on photocatalytic activity, appropriate quantity of scavenger species were introduced in the reaction system in a manner similar to photocatalytic experiment.

Photoluminescence (PL) technique with terephthalic acid (TA) as a probe molecule was used for the detection of ˙OH radicals. The experimental procedure was referred to previous studies.5

3. Results and discussions

3.1 XRD analysis

XRD analysis was used to determine the purity, phase structure and crystallinity of the as prepared samples. Fig. 1 presents the XRD pattern of pristine Bi2WO6 and Ag2S loaded Bi2WO6. As can be seen from the Fig. 1a, the diffraction peaks can be categorised into a set of 2θ at 28.3°, 32.8°, 47.1° and 55.9° corresponding to the indices (131), (200), (202) and (331) which indicates a perfectly orthorhombic structure for pure Bi2WO6.38 Compared with diffraction pattern of bare Bi2WO6, no significant diffraction peaks of any other phase or impurity was observed on Ag2S/Bi2WO6 composites indicating that the characteristic peaks associated with Ag2S are not obviously detected (Fig. 1b–e). This may be due to the limited amount of Ag2S (3–9%) used, small size of Ag2S nanoparticles and high dispersion of Ag2S on the surface of Bi2WO6 spherical architectures. More importantly the absence of individual Ag2S aggregates in SEM images of as prepared samples indicate high dispersion of Ag2S in composites. Fig. 1f displays the characteristic XRD pattern of pure Ag2S sample. All peaks of pure Ag2S can be assigned to monoclinic Ag2S crystal structure.39 The average crystallite size of the samples was calculated by using Scherer formula given below5 and results are listed in Table 1.
 
image file: c5ra05117g-t1.tif(1)
where D is taken as crystallite size, k is a constant, λ is X-ray wavelength, β is the full width at half maximum (FWHM) measured in radians on the 2θ scale, θ is the Bragg angle for diffraction peaks. From the results of crystallite size displayed in Table 1, it is clear that there is negligible change in the crystallite size of pure Bi2WO6 and Ag2S loaded Bi2WO6 samples.

image file: c5ra05117g-f1.tif
Fig. 1 XRD patterns of (a) the pure Bi2WO6, (b) the 3% Ag2S/Bi2WO6 catalyst, (c) the 5% Ag2S/Bi2WO6 catalyst, (d) the 7% Ag2S/Bi2WO6 catalyst, (e) the 9% Ag2S/Bi2WO6 catalyst, and (f) the pure Ag2S.
Table 1 Pseudo-first-order rate constants (Kapp) calculated from the plots of ln(C0/Ct) versus irradiation time for decolorization of RhB over different catalysts, %decolorization of RhB and average crystallite size of pure Bi2WO6 and Ag2S/Bi2WO6 catalysts with different Ag2S contents
Sample Kapp (min−1) % Decolorization Average crystallite size (nm)
Bi2WO6 0.0160 56.42994 11.12
3% Ag2S/Bi2WO6 0.0185 61.11649 11.28
5% Ag2S/Bi2WO6 0.0243 71.10206 10.56
7% Ag2S/Bi2WO6 0.0373 84.96666 10.66
9% Ag2S/Bi2WO6 0.0300 78.2553 11.42


3.2 XPX analysis

To further investigate the composition and oxidation states of as prepared samples, XPS analysis of 7% Ag2S/Bi2WO6 heterostructure (Fig. 2) was carried out. Fig. 2a displays the overall XPX spectra for the 7% Ag2S/Bi2WO6 in which peaks for Bi, W, O, Ag and S could be detected. The high resolution XPS spectra of Bi4f, W4f, O2s, S2p and Ag3d is shown in Fig. 2b–f. The Bi4f peaks (Fig. 2b) at 157.8 and 163.10 eV are attributed to the binding energies of Bi4f7/2 and Bi4f5/2 respectively which corresponds to previous results.40 The W4f peaks at 34.00 and 36.1 eV are ascribed to binding energies of 4f7/2 and 4f5/2 (Fig. 2c). The splitting energy of 2.1 eV for 4f doublet of W indicates the +6 oxidation state of W in composite catalyst.41 The O1s peak (Fig. 2d) at 528.8 eV is in good agreement with previous results.40 The high resolution Ag3d XPS spectrum is displayed in Fig. 2e. The two peaks corresponding to Ag+ at approximately 366.50 and 372.60 eV are attributed to the Ag3d5/2 and Ag3d3/2 respectively.42 Since in previous results the peaks at 368.3 and 374.2 eV are attributed to metallic Ag whereas the peaks at 367.8 and 373.8 eV are attributed to Ag+,43,44 it implies that peaks obtained in our XPS results can be ascribed to Ag+ only suggesting that no metallic Ag0 is formed. Fig. 2f displays the S2p XPS spectrum. The peak at around 163 eV can be attributed to S2p1/2 indicating the presence of S2− which further suggests the formation of Ag2S.45 From these results it can be confirmed that Ag2S/Bi2WO6 composites have been successfully synthesized.
image file: c5ra05117g-f2.tif
Fig. 2 XPS spectra of 7% Ag2S/Bi2WO6. (a) Full survey spectra, and the high resolution XPS spectra of the sample: (b) Bi4f, (c) W4f, (d) O1s, (e) Ag3d, and (f) S2p.

3.3 SEM, EDS and TEM analysis

To investigate the surface morphology of as prepared samples SEM characterization was used. Fig. 3 presents the FESEM images of pure Bi2WO6 and 7% Ag2S/Bi2WO6 composite. As clear from the Fig. 3a, the FESEM image of bare Bi2WO6 consist of abundant hierarchically structured architectures of Bi2WO6 microspheres. The higher magnification (Fig. 3b) reveals that Bi2WO6 architectures are built from numerous nanoplates aligned to the spherical surface forming a microsphere. Compared with bare Bi2WO6 the Ag2S loading affects the surface morphology of Bi2WO6 in composite (Fig. 3c) to some extent. As can be seen clearly from the higher magnification FESEM image of 7% Ag2S/Bi2WO6 composite (Fig. 3d), it is somewhat different from spherical structure showing that Ag2S has combined well with Bi2WO6 to form a heterostructure. EDX spectrum of Bi2WO6 and 7% Ag2S/Bi2WO6 was collected to confirm the presence of Ag2S in hybrids. The EDS spectrum in Fig. 3e shows clearly that bare Bi2WO6 is composed of Bi, W and O elements while as Ag2S/Bi2WO6 (Fig. 3f) composite is composed of Bi, W, O, Ag and S elements indicating the formation of Ag2S/Bi2WO6 composite. To further confirm the high dispersion of Ag2S in composite, EDX elemental mapping of 7% Ag2S/Bi2WO6 composite was performed as shown in Fig. 4. It can be seen from the Fig. 4, that Ag (Fig. 4b) and S (Fig. 4e) are highly dispersed in 7% Ag2S/Bi2WO6 hybrid.
image file: c5ra05117g-f3.tif
Fig. 3 FE-SEM images of samples. (a) Pure-Bi2WO6, (b) the high magnification SEM image of pure-Bi2WO6, (c) 7% Ag2S/Bi2WO6, (d) the high magnification SEM image of 7% Ag2S/Bi2WO6, (e) EDS spectrum of pure-Bi2WO6 sample, and (f) EDS spectrum of 7% Ag2S/Bi2WO6 sample.

image file: c5ra05117g-f4.tif
Fig. 4 EDS elemental mapping of 7% Ag2S/Bi2WO6.

TEM analysis was further used to investigate the detailed structure as shown in Fig. 5. It can be seen that Bi2WO6 structures are composed of nanoplates with a thickness around 10–20 nm (Fig. 5a). Fig. 5b shows that Bi2WO6 microspheres are mesoporous in nature which helps Ag2S particles to bind in this composite system. The TEM image for 7% Ag2S/Bi2WO6 (Fig. 5e and f) shows subtle particles of Ag2S grown on the surface of Bi2WO6 microsphere. The presence of lattice fringes (Fig. 5c) confirms the crystalline nature of Bi2WO6. Furthermore the spacing of lattice fringes was found to be 0.313 nm which corresponds to the 131 planes of orthorhombic Bi2WO6.38 The SAED (Selected Area Diffraction Pattern) demonstrates the presence of clear diffraction spots (Fig. 5d) which further confirms the crystalline structure of Bi2WO6. All these above results are in good agreement with the results of XRD and XPS analyses and strongly demonstrate the formation of Ag2S/Bi2WO6 heterojunction.


image file: c5ra05117g-f5.tif
Fig. 5 TEM images of samples. (a and b) Pure Bi2WO6, (c and d) SAED pattern of pure Bi2WO6, and (e and f) 7% Ag2S/Bi2WO6.

3.4 N2 adsorption–desorption

Fig. 6 shows the nitrogen adsorption isotherm and pore size distribution of pure Bi2WO6 (Fig. 6a) and 7% Ag2S/Bi2WO6 (Fig. 6b). As can be seen from the figure, the shape of both the isotherms seem to be nearly of type IV isotherm with hysteresis loop at higher relative pressure which is usually associated with capillary condensation in mesopores.46,47 The type H3 hysteresis loop at higher relative pressure according to IUPAC classification reflect the presence of slit like pores indicating the presence of mesopores in the region of 2–10 nm which is further confirmed by the BJH pore size distribution diagram in the inset of Fig. 6. The BET surface area of bare Bi2WO6 and 7% Ag2S/Bi2WO6 are 77.6 m2 g−1 and 66 m2 g−1 respectively indicating that the loading of Ag2S leads to the decrease in surface area to some extent which is probably because Ag2S particles are embedded in the pores of Bi2WO6.48 The presence of mesoporous structure with large surface area provides more active sites and transport paths for the decomposition of contaminants in photocatalytic reaction.
image file: c5ra05117g-f6.tif
Fig. 6 N2 adsorption–desorption isotherm of the samples. (a) Pure Bi2WO6, and (b) 7% Ag2S/Bi2WO6. The inserts are the pore size distribution of the respective catalysts.

3.5 Optical properties

Fig. 7 displays the UV-vis diffuse reflectance (DRS) spectra of bare Bi2WO6 and Ag2S/Bi2WO6 heterostructures. As shown in Fig. 7a the bare Bi2WO6 has an absorption edge around 450 nm, where as weak and broadened peaks of Ag2S (Fig. 7b) are similar to the reported UV-vis spectra of pure Ag2S.48,49 With increase in Ag2S loading the absorption edge of heterostructure samples is shifted to longer wavelengths from 450–490 nm.
image file: c5ra05117g-f7.tif
Fig. 7 UV-vis diffuse reflectance spectra of (a) the pure Bi2WO6, and Ag2S/Bi2WO6 composites (b) the pure Ag2S catalyst. The insets in the (a) and (b) are band gap energies of the pure Bi2WO6, and pure Ag2S respectively.

The optical band gaps (insets of Fig. 7a and b) of Bi2WO6 and Ag2S were calculated using the equation reported by Butler.50

 
× α = (AhνEg)n/2 (2)

Since α is proportional to Kubelka–Munk function F(R), the equation becomes

 
× F(R) = (AhνEg)n/2 (3)
where, h is the planks constant, ν is the frequency, A is the proportionality constant and Eg is the band gap energy. The value of n is determined by the type of transition (n = 1 for direct and n = 4 for indirect transition). The n for Bi2WO6 has been reported by some researchers as 1 (direct transition),51,52 and by some other researchers as 4 (indirect transition).53,54 In our case we plotted (F(R) × )1/2 versus hν for Bi2WO6 (inset of Fig. 7a) and (F(R) × )2 versus hν for Ag2S (inset of Fig. 7b). The band gaps for Bi2WO6 and Ag2S were estimated as 2.74 eV and 1.1 eV respectively.

3.6 Photocatalytic properties

To assess the photocatalytic activity of as prepared samples, RhB was selected as a probe molecule. The characteristic absorption band of RhB at 554 nm was employed to determine the process of degradation. Fig. 8 displays the photocatalytic performances of all Ag2S/Bi2WO6 heterojunctions with different Ag2S contents over degradation of RhB (Ct/C0) under visible light irradiation. As shown in Fig. 8b, the blank experiment (without photocatalyst) shows that the concentration of RhB remains unchanged even after 50 min of visible light irradiation indicating the significance of photocatalyst. The adsorption of RhB dye by 7% Ag2S/Bi2WO6 was also checked for 50 min and it was found that the adsorption in dark is insignificant. As is shown the pure mesoporous Bi2WO6 exhibit photocatalytic efficiency of 56.5% in 50 min. The better performance of pure mesoporous Bi2WO6 photocatalyst was attributed to the high surface area and mesoporous structure of Bi2WO6. The high surface area and mesoporous structure not only provide more active sites and transport paths in photocatalytic reaction but also improves the contact of photocatalyst with organic pollutants. When Ag2S and Bi2WO6 are combined to construct a heterostructure, the photocatalytic activity of the composites is dramatically enhanced even though the Ag2S content is very low. The photocatalytic activity of all Ag2S/Bi2WO6 heterostructures with Ag2S weight percentage of 3%, 5%, 7% and 9% is higher than the bare Bi2WO6 and are listed in Table 1. The best photocatalytic performance was obtained for 7% Ag2S/Bi2WO6 for which almost 85% of RhB was degraded in 50 min. The reason for enhanced visible light activity is the formation of heterojunction which results into the generation of natural energy bias at heterojunction with subsequent transfer of photoinduced charge carriers and thereby impeding the electron hole recombination, which is the main factor responsible for low visible light activity of Bi2WO6. With further increase in Ag2S content to 9%, the photocatalytic activity decreases but is still higher than bare Bi2WO6. Therefore the optimal content of Ag2S in Ag2S/Bi2WO6 composite is 7%. The optimum content of AgBr in the heterojunction can be related to two factors. (1) For efficient electron–hole separation the space charge region potential must be certain.38 When Ag2S content was above 7% (optimal value) the space charge region might become narrow and lead to the recombination of photoinduced charge carriers. (2) The loading of Ag2S leads to decrease in surface area as discussed in section 3.4. When Ag2S content was above optimal value the surface area might decrease substantially leading to decrease in photocatalytic activity. Fig. 8a displays the absorption spectral changes of the photocatalytic degradation of RhB aqueous solution over 7% Ag2S/Bi2WO6. As can be seen from the Fig. 8a, the absorbance of RhB at 554 nm decreases significantly with increase in reaction time accompanied by a slight shift of absorption band towards blue region which is attributed to the step wise de-ethylation process of RhB into intermediates as reported in previous works.55,56 The apparent pseudo first order kinetics model given by the eqn (4) was applied in experiments to understand the reaction mechanism.57
 
ln(C0/Ct) = Kappt (4)

image file: c5ra05117g-f8.tif
Fig. 8 (a) UV-vis spectral changes of the degradation of RhB by the 7% Ag2S/Bi2WO6 catalyst, (b) the degradation efficiency (Ct/C0) of RhB in presence of pure Bi2WO6 and Ag2S/Bi2WO6 composites with different Ag2S contents and (c) Rhodamine B decolourization curves of ln(C0/Ct) versus irradiation time for different catalysts.

Kapp is apparent pseudo-first order reaction constant and its value for bare Bi2WO6 and all heterojunctions was calculated via the first order linear fit data (Fig. 8c) and are displayed in Table 1. From Table 1, it is clear that photocatalytic activity of 7% Ag2S/Bi2WO6 is 2.4 times higher than the bare Bi2WO6 suggesting that Ag2S/Bi2WO6 is an excellent photocatalyst under visible light.

3.7 Proposed mechanism

The trapping experiments of active species formed during photocatalytic oxidation process were carried out to investigate the possible mechanism involved in RhB degradation over 7% Ag2S/Bi2WO6 heterojunction. Benzoquinone (BQ)58,59 isopropyl alcohol (IPA)58,60 and ammonium oxalate (AO)61 were used as superoxide (˙O2), hydroxyl (˙OH) and hole (h+) scavengers respectively. Fig. 9a displays the effect of different scavengers and it can be seen from the figure that the rate of RhB degradation decreases substantially in presence of AO. However addition of IPA had no obvious effect on rate of RhB degradation whereas addition of BQ slightly decreases the photocatalytic performance of 7% Ag2S/Bi2WO6 compared with no scavenger under same conditions. These results indicate that h+ are the main active species rather than ˙O2 and ˙OH in the RhB degradation over 7% Ag2S/Bi2WO6 system under visible light irradiation.
image file: c5ra05117g-f9.tif
Fig. 9 (a) Effect of different scavengers on the degradation of RhB over 7% Ag2S/Bi2WO6 catalyst; BQ = benzoquinone, IA = isopropyl alcohol, AO = ammonium oxalate. (b) The degradation efficiency (Ct/C0) of phenol in presence of pure Bi2WO6 and 7% Ag2S/Bi2WO6 composite.

To further confirm that ˙OH did not play any role, we carried out the terephthalic acid photoluminescence studies. The PL spectral changes observed during irradiation of Ag2S/Bi2WO6 in a basic terephthalic acid solution (315 excitation wavelength) are displayed in Fig. 10. As clear from the figure no Pl signals were observed at 425 nm throughout the photocatalytic oxidation process, indicating that no ˙OH is formed on the surface of catalyst.


image file: c5ra05117g-f10.tif
Fig. 10 ˙OH trapping PL spectral changes over 7% Ag2S/Bi2WO6 catalyst in a basic terephthalic acid solution (excitation at 315 nm) with irradiation time.

To ensure that the reactive species originate from the photocatalytic process of catalysts and not form the sensitization of dye, we selected a colourless molecule phenol as a probe. Fig. 9b displays the photocatalytic performances of pure Bi2WO6 and 7% Ag2S/Bi2WO6 heterojunctions over degradation of phenol (Ct/C0) under visible light irradiation. As can be seen from the Fig. 9b the concentration of phenol decreases with increasing reaction time in presence of both pure Bi2WO6 and 7% Ag2S/Bi2WO6. The concentration (Ct/C0) decreases sharply in presence of 7% Ag2S/Bi2WO6 under visible light irradiation while as in case of pure Bi2WO6 the decrease in the concentration (Ct/C0) of phenol is lower than 7% Ag2S/Bi2WO6. Since phenol cannot absorb visible light, it follows directly that reactive spies originate from the photocatalytic process of samples under visible light ruling out the possibility of sensitization of dye. The results obtained are in accordance with the results obtained for the degradation of RhB.

The BET surface area of bare Bi2WO6 was calculated to be 77.6 m2 g−1. The high surface area and mesoporous structure of Bi2WO6 makes it an excellent visible light photocatalyst but the surface area of 7% Ag2S/Bi2WO6 was calculated to be only 66 m2 g−1 which is obviously less than the bare Bi2WO6. The Ag2S loading on the surface of Bi2WO6 enhances the visible light photocatalytic activity of Bi2WO6 substantially although the surface area is decreased. Therefore it can be assumed that large surface area may be responsible for the high photocatalytic activity of bare Bi2WO6 but it is not the influence factor for the enhancement of visible light activity of Ag2S/Bi2WO6 composites up to 7% loading. Therefore to analyse the mechanism of improved photocatalytic activity of Ag2S/Bi2WO6 composites the relative positions of the conduction band and valence band edges of Ag2S and Bi2WO6 were investigated for the flow chart of photoinduced charge carriers in a heterojunction. The relative position of valence band (VB) of Ag2S and Bi2WO6 was evaluated by the empirical formula in eqn (5).62

 
EVB = XEc + 0.5Eg (5)
where X is the electronegativity of semiconductor expressed as geometric mean of absolute electronegativity of constituent atoms, Ec is the energy of free electrons on hydrogen scale (4.5 eV) and Eg is the band gap energy. The EVB for Ag2S and Bi2WO6 were calculated to be 1.1 eV and 3.23 eV respectively. The relative position of conduction band (CB) of Ag2S and Bi2WO6 were estimated from eqn (6).
 
ECB = EVBEg (6)

The ECB for Ag2S and Bi2WO6 were calculated to be 0 eV and 0.49 eV respectively.

Based on the results of BET analysis, DRS, trapping experiments and TA PL spectra we presented a schematic diagram (Fig. 11) to illustrate the photocatalytic reaction mechanism and charge transfer of Ag2S/Bi2WO6 system. We propose that under visible light irradiation both Ag2S and Bi2WO6 are excited and generate electron hole pairs. Since the CB energy level of Ag2S and Bi2WO6 is 0 and 0.49 eV (vs. SHE), the single electron reduction of O2 to ˙O2(−0.046 vs. SHE)63,64 is not possible. When two semiconductors are in contact, the electrons from less positive conduction band of Ag2S (0 eV) are injected with high efficiency into more positive conduction band of Bi2WO6 (0.49 eV). On the other hand holes from more positive valence band of Bi2WO6 (3.23 eV) are transferred to the less positive VB of Ag2S (1.1 eV). The photoinduced charge carriers are thus effectively separated at the interface of Ag2S/Bi2WO6. The holes (h+) on the valence band of Ag2S could not react with OH/H2O to form ˙OH because VB of Ag2S is more negative (1.1 eV) than that of ˙OH/H2O (2.30 eV vs. SHE).38 Hence holes from valence band of Ag2S migrate to the surface of a photocatalyst where they take part in photocatalytic reaction to mineralize the organic pollutants and thereby enhancing the photocatalytic activity.


image file: c5ra05117g-f11.tif
Fig. 11 Schematic diagram showing the band structure and separation of photoinduced electron hole pairs at interface of 7% Ag2S/Bi2WO6 catalyst under visible light irradiation.

Photoluminescence spectra of hierarchically structured bare Bi2WO6 and 7% Ag2S/Bi2WO6 was carried out to further demonstrate the enhancement of separation of charge carriers. The lower intensity of PL peak represents the lower probability of electron–hole recombination. Fig. 12 presents the PL spectra of bare Bi2WO6 and 7% Ag2S/Bi2WO6 with an excitation wavelength of 380 nm. From the Fig. 12 it is clear that the intensity of PL spectra decreases significantly in 7% Ag2S/Bi2WO6 compared to the bare Bi2WO6 indicating that the loading of Ag2S on Bi2WO6 has greatly restrained the recombination of photoinduced charge carriers between Bi6s and O2p to the empty W4d orbitals.22


image file: c5ra05117g-f12.tif
Fig. 12 PL spectra of samples. (a) Pure-Bi2WO6 and (b) 7% Ag2S/Bi2WO6 (Ex = 380 nm).

3.8 Stability of the catalyst and cycling runs

The stability of silver based compounds has always been a matter of concern,65 particularly the metal chalcogenides get easily eroded by the photogenerated holes.66 Therefore cyclic experiments with 7% Ag2S/Bi2WO6 sample were carried out to determine the stability of a photocatalyst. Fig. 13 displays the results of RhB degradation by 7% Ag2S/Bi2WO6 after 4 repeated cycles. It can be seen from the Fig. 13 that the degradation of RhB by 7% Ag2S/Bi2WO6 is maintained at 81.3% even after 4 repeated cycles indicating the high stability of photocatalyst. Fig. 14 presents the Ag3d XPS spectrum and XRD analysis of used 7% Ag2S/Bi2WO6 catalyst after 4 repeated cycles. It is clear from the Fig. 14a that the Ag3d XPS spectrum of used catalyst is similar to that of fresh catalyst (Fig. 2e) with no peak detected for metallic Ag in used catalyst after 4 repeated cycles. The XRD analysis of used catalyst (Fig. 14b) after 4 repeated cycles also confirms that the structure and phase of the used catalyst remains intact with no additional peak detected for Ag metal. From these results it is clear that the Ag2S/Bi2WO6 is a stable photocatalyst under visible light irradiation and the main reason for the enhanced stability is the transfer of CB electrons from Ag2S to Bi2WO6 which reduces the chances of erosion of catalyst.
image file: c5ra05117g-f13.tif
Fig. 13 The repeated experiments of photocatalytic degradation of RhB over 7% Ag2S/Bi2WO6 catalyst.

image file: c5ra05117g-f14.tif
Fig. 14 (a) Ag3d XPS spectra of used 7% Ag2S/Bi2WO6 catalyst after 4 recycling runs, and (b) XRD pattern of used 7% Ag2S/Bi2WO6 catalyst after 4 recycling runs.

4. Conclusion

Mesoporous Bi2WO6 was modified with Ag2S by hydrothermal method without any surfactant or template. The introduction of Ag2S extended the photoabsorption range of Bi2WO6 and the composite showed red shift compared to the pure Bi2WO6. The Ag2S/Bi2WO6 heterostructures showed enhanced photocatalytic activity in the degradation of RhB under visible light irradiation which is 2.4 times higher than the pure Bi2WO6. The Ag2S/Bi2WO6 composite even after 4 recycling runs did not show any significant decrease in photocatalytic activity except for about 4%. The enhanced photocatalytic activity and stability was attributed to the broadening of photoabsorption range and efficient separation of the photoinduced electron hole pairs as a result of natural energy bias at heterojunction. This study inspires a thought of utilizing visible spectrum efficiently and simultaneously presents a way to promote separation of photo induced electron hole pairs.

Acknowledgements

The authors are highly thankful to Department of Physics AMU Aligarh, USIF AMU Aligarh and Department of Chemistry AMU Aligarh for providing the instrumentation facility. DST and UGC is duly acknowledged for financial support in the form of FIST, PURSE and DRS II research grants. The authors are also thankful to UGC, New Delhi, India for providing financial assistance. Niyaz A. Mir thanks Department of Science & Technology, India for the award of Young Scientist grant (SERB/F/1214/2014-2015).

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