21August2019

Nano-Micro Letters

Enhanced Photocatalytic Activity of Nanoparticle-Aggregated Ag-AgX(X=Cl, Br)@TiO2 Microspheres Under Visible Light

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Cuiling Zhang1,2,*, Hao Hua2, Jianlin Liu2, Xiangyu Han2, Qipeng Liu2, Zidong Wei2, Chengbin Shao1, Chenguo Hu2,*

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Nano-Micro Lett. (2017) 9: 49

First Online: 25 June 2017 (Article)

DOI:10.1007/s40820-017-0150-8

*Corresponding author. E-mail: zhangcl@ctbu.edu.cn, hucg@cqu.edu.cn

 

Abstract

 


Fig. 8 The band structures and degradation mechanisms of a Ag-AgCl@TiO2 NPAS and b Ag-AgBr@TiO2 NPAS under visible-light

Ag-AgX(X=Cl, Br)@TiO2 nanoparticle aggregated spheres (NPAS) with different mass ratio of R=TiO2/Ag(X) from 35:1 to 5:1 were synthesized by a facile sol-gel technique with post photoreduction. The photocatalytic activities of both Ag-AgCl@TiO2 and Ag-AgBr@TiO2 under visible light are effectively improved by ~3 times relative to TiO2 NPAS under the simulated sunlight for the decomposition of methyl orange (MO). Ag-AgBr@TiO2 showed 30% improvement and less stable in photocatalytic activity than that of AgCl@TiO2. The role of Ag and AgX nanoparticles on the surface of Ag-AgX(X=Cl, Br)@TiO2 was discussed. Ag on these samples not only can efficiently harvest visible light especially for AgCl, but also efficiently separate excited electrons and holes via the fast electron transfer from AgX(X=Cl, Br) to metal Ag nanoparticles and then to TiO2 aggregated spheres on the surface of heterostructure. On the basis of their efficient and stable photocatalytic activities under visible light irradiation, these photocatalysts could be widely used for degradation of organic pollutants in aqueous solution.


 

Keywords

Ag-AgX(X=Cl, Br)@TiO2; Nanoparticle-aggregated spheres; Methyl orange; Visible light; Photocatalysis

 

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1 Introduction

   As an important photocatalyst, titanium dioxide (TiO2) has been widely used in decomposition of toxic and hazardous organic pollutants, and in water-splitting for hydrogen production [1-3]. However, the rapid recombination of photoinduced electrons and holes and its wide band gap greatly lower the TiO2 quantum efficiency. Therefore, it is of great importance to improve the visible light harvesting and the separation of photoinduced electron-hole pairs in TiO2 for its further applications. TiO2-based heterostructures or composites formed by semiconductors with narrower band gap (e.g. Ag2O/TiO2, BiVO4/TiO2/BiVO4, BiOI/TiO2, Cu2O/TiO2, and Bi2O3/TiO2) have been intensively investigated to develop high activities [4-8]. In addition, noble metal-TiO2 is used to improve the generation and separation of photoinduced carriers due to the surface plasmon resonance (SPR) of noble metal nanoparticles such as Ag and Pd [9-12]. The photoinduced electrons in noble metal transfer onto the surface of semiconductor, which results in visible-light photocatalytic activity, such as Ag@TiO2 or Ag nanoparticles and graphene co-loaded TiO2. Therefore, noble metal-semiconductor junction has potential application for the visible light response in environmental purification. Specifically, because noble metal has a strong electron storage property and large work function, the excited electrons transfer from TiO2 to a noble metal nanoparticle is an ultrafast process [9]. This phenomenon improves photocatalytic activity by effective charge separation. However, there are two opposite electron transfers in the metal-semiconductor structure which is from noble metal to semiconductor and from semiconductor to noble metal respectively under an irradiation. Thus, it is important to steer the transfer of the photoinduced carriers.
   In recent years, AgX [13-22] and Ag/AgX(X=Cl, Br) have been paid much interest in the design of photosensitive composite materials because of their strong absorption of visible light by their surface plasmon resonance (SPR) and self-sensitization. It provides new opportunity for developing visible light driven photocatalyst. For example, it has been demonstrated that Ag/AgCl-BiOX (X=Cl, Br) [16], AgI/AgCl/TiO2 [17] and 3D AgX/Graphene Aerogels (X = Br, Cl) [18], AgClxBr1-x nanocrystals [19], AgBr supported on g-C3N4-decorated nitrogen-doped graphene ternary nanocomposites [20] and Ag-AgBr/TiO2 composite [21] showed enhanced photocatalytic activities. In addition, the morphology of photocatalyst is important for the photocatalytic activity [23-28]. The pristine TiO2 nanoparticles aggregated spheres (NPAS), Ag2O/TiO2 NPAS, and Pt/TiO2 NPAS showed excellent photocatalytic activity due to their large surface area and high adsorption of dyes [8, 24]. Meanwhile, because of its different band structure, AgX(X=Cl, Br) shows different photoresponsive behavior under visible light and the degradation mechanism of AgX(X=Cl, Br)/TiO2 on methyl orange (MO) might be different.

   Herein, we developed a facile low temperature method to prepare Ag-AgX(X=Cl, Br)@TiO2 NPAS heterojunction photocatalysts and the influence of weight rate R (R = TiO2:AgX) and band structures of heterojunctions on the photocatalytic activity were systematically studied. Ag-AgX(X=Cl, Br)@TiO2 double heterostructures exhibited much higher photocatalytic activity for the degradation of MO under visible-light irradiation (λ>400 nm). The possible mechanism and the key role of metallic Ag on the photocatalytic activity of the Ag-AgX(X=Cl, Br)@TiO2 double heterostructures were proposed.

2 Experimental Details

2.1 Preparation of Samples

   All chemical reagents used in this experiment are of analytical purity, and without further purification.
2.1.1 P reparation of Ag-AgCl@TiO2 NPAS
   TiO2 NPAS were prepared by diglycol mediated process with minor modification, which was reported elsewhere [24]. For Ag-AgCl@TiO2 NPAS preparation, 0.23 g of TiO2 NPAS was dispersed in 20 mL deionized water with vigorous stirring for 1 h, while 0.15 g cetyltrimethyl ammonium chloride (CTAC) was added dropwise to the suspension and stirred for 1 h. Then, 800 µL 0.1 mol L-1 AgNO3 aqueous solution was added and continually stirred for 1 h and then irradiated for 30 min under the simulated sunlight. The precipitation was collected by a washing and centrifugation process and then the obtained sample was dried at 60 °C in a drying oven for 12 h. Finally, the precursors were completely crystallized and converted into Ag-AgCl@TiO2 NPAS by heating at 300 °C for 8 h in nitrogen. Ag-AgCl@TiO2 with weight ratio (R=TiO2: AgCl) of 1:0, 30:1, 25:1; 20:1; 15:1; 10:1; 5:1 denoted as sample S1- S7 was prepared by changing the amount of TiO2 NPAS as shown in Table 1.

Table1 Experimental condition for the preparation of different Ag-AgCl@TiO2 NPAS samples

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2.1.2 P reparation of Ag-AgBr@TiO2 NPAS
   The preparation of Ag-AgBr@TiO2 NPAS is similar to that of Ag-AgCl@TiO2, with cetyltrimethyl ammonium bromide (CTAB) added rather than CTAC. The Ag-AgCl@TiO2 with weight ratio (R=TiO2: AgBr) of 35:1, 30:1, 25:1, 20:1, 15:1, 10:1, 5:1 is denoted as sample S8- S14 as shown in Table 2.

Table 2 Experimental condition for the preparation of different Ag-AgBr@TiO2 NPAS samples

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2.2 Characterization

   X-ray photoelectron spectroscopy (XPS) patterns of Ag-AgX@TiO2 NPAS were determined by photoelectron spectrometer (ESCALAB 250Xi). The morphological features of the samples were characterized by a scanning electron microscope (SEM, TESCAN VEGA 3 SBH SEM), a field emission scanning electron microscopy (FESEM, Nova 400 Nano SEM) and a high resolution transmission electron microscopy (HRTEM, JEOL-4000EX). The elemental composition of the samples was recorded by energy dispersive X-ray spectroscopy (EDS, OXFORD). UV-Vis absorption spectrum was measured by the UV-Vis spectrophotometer (UV-3600, Shimadzu) with an integrating sphere attachment. Photoluminescence (PL) measurement was obtained by an Edinburgh FLS920 Fluorescence Spectrometer with the excitation source of steady-state Xe900 450W xenon lamp. All the measurement was taken at room temperature.
2.3 Photocatalytic Degradation
   Twenty mg of samples was added into 50 mL aqueous suspension of MO (14 mg L-1) in a 100 mL beaker. The suspension was magnetically stirred in dark for 30 min to establish adsorption/desorption equilibrium before illumination. An simulated sunlight instrument (CHF-XM-500W) with a power of 100 m W cm-2 was used as an illumination source and the 420 nm cutoff filter was placed on the end of light transmission tube to ensure the irradiation only in visible-light wavelength. The catalysis after degradation were collected by a washing and centrifugation process and then dried at 60 °C. In order to keep the mass of catalysis constant, some catalyst (about 2 mg) were added.

3 Results and Discussion

3.1 Crystal Structure, Morphology, and Formation Mechanism of Ag-AgX(X=Cl, Br)@TiO2 NPAS

   Figure 1a shows the XRD patterns of the Ag-AgCl@TiO2 samples S1-S7. The sample S1 with R=1:0 exhibits pure anatase phase TiO2 (JCPSD No. 21-1272), while the rest of the sample S2-S7 show the diffraction peaks of pure cubic AgCl (JCPDS No. 31-1238) besides TiO2. Both phases of AgCl and TiO2 are consistent with that of the standard card. The XRD patterns of AgCl become strong from S2 to S7 with an increase of AgCl in AgCl@TiO2. However, obvious Ag peaks are not found in the XRD patterns in all the samples. The 2-theta at 38.3º corresponding to the (111) of cubic phase Ag (Fm-3m(225), JCPDS No. 87-0719) appears to overlap with (004) (2-theta at 37.8º) and (112) (2-theta at 38.6º) of anatase phase TiO2, and the small pimple of 2-theta at 77.7º may correspond to the (311) of cubic metallic Ag. Both of them don’t demonstrably show the existence of Ag for XRD patter, which demonstrates the Ag distributed on the AgCl@TiO2 in a very small percentage. It is because there is a little elemental Ag reduced from AgCl under illumination for 30 min [29].

Fig. 1 XRD patterns of a the Ag-AgCl@TiO2 NPAS samples and b Ag-AgBr@TiO2 NPAS samples

Fig. 1 XRD patterns of a the Ag-AgCl@TiO2 NPAS samples and b Ag-AgBr@TiO2 NPAS samples

   Figure 1b shows the XRD patterns of the Ag-AgBr@TiO2 samples S8-S14. Similar to Ag-AgCl@TiO2, the samples show two phase mixture of cubic AgBr (Fm-3m (225)JCPDS No. 06-0438) and anatase phase TiO2 and they are all consistent with those of the standard cards. The relative intensity of AgBr to TiO2 increases with the decrease of R in Ag-AgBr@TiO2. We do not have clear evidence of Ag existence from XRD and another measurement to confirm the Ag metal should be carried out.

Fig. 2 FE-SEM images of Ag-AgCl@TiO2 NPAS: a S1, b S2, c S3, d S4, e S5, f S6, g-h S7 and i-l TEM and HRTEM images of sample S4

Fig. 2 FE-SEM images of Ag-AgCl@TiO2 NPAS: a S1, b S2, c S3, d S4, e S5, f S6, g-h S7 and i-l TEM and HRTEM images of sample S4

   To further obtain the structure and morphology information of Ag-AgX(X=Cl, Br)@TiO2 samples, FE-SEM, TEM, and HRTEM characterizations have been conducted as shown in Figs. 2 and 3. Figure 2a shows the FE-SEM and enlarged image in the inset of pristine TiO2 (S1) which indicates nanoparticles aggregated spheres with the diameter of 370-450 nm. The Ag-AgCl@TiO2 with R from 30:1 to 5:1 (S2-S7) are shown in Fig. 2b-g, from which we can see that the diameter is about 500-600 nm with Ag-AgCl nanoparticles coated on the surface. The morphology of Ag-AgCl@TiO2 is similar to that of the TiO2 aggregated spheres, which indicates that the precipitation of Ag-AgCl on the surface of TiO2 does not affect the structure of TiO2 aggregated spheres and TiO2 aggregated spheres present very good sites to adsorb Ag-AgCl. With the increase of Ag-AgCl in Ag-AgCl@TiO2, there are more and more small particles on the surface of samples. When R=5:1, much larger particles of Ag-AgCl appear pinned on the spheres as shown in Fig. 2g and enlarged image in Fig. 2h. No individual particles of Ag-AgCl are found, which is similar to the Ag2O-@TiO2 NPAS [24]. The TEM and HRTEM of Ag-AgCl@TiO2 with R=20:1 named S4 are presented in Fig. 2i-l. The Ag-AgCl particles with a diameter of 5-15 nm are uniformly coated on the surface of the sample. These particles connect each other and the grain boundary can be seen. The perfect combination results from the lattice-match of TiO2 and AgCl. For example, the lattice spacing of (211) (d=0.167 nm) and (215) (d=0.126 nm) for TiO2 are close to that of (311) (d=0.167 nm) and (331) (d=0.127 nm) of AgCl provided by the XRD patterns in Fig. 1. The lattice fringe of AgCl is observed clearly in Fig. 2l, and the resolved interplanar distance is ca. 0.27 nm, corresponding to the (200) plane e of AgCl. The EDS analysis and elemental mapping images (EMIs) of O, Ti, Ag, and Cl of Ag-AgCl@TiO2 are presented in Figs. S1b and S1c-f, respectively. The rusults reveal the uniform distributions of O, Ti, Ag, and Cl. Consequently, the Ag and AgCl nanoparticles are well distributed on the surface of TiO2 nanoparticles aggregated spheres.

Fig. 3 FE-SEM images of Ag-AgBr@TiO2 NPAS: a S8, b S9, c S10, d S12, e S13, f S14 and g-i TEM and HRTEM images of sample S11

Fig. 3 FE-SEM images of Ag-AgBr@TiO2 NPAS: a S8, b S9, c S10, d S12, e S13, f S14 and g-i TEM and HRTEM images of sample S11

   Figure 3a-f show FE-SEM images of Ag-AgBr@TiO2 samples S8-S10 and S12-S14, respectively, from which we can see that Ag-AgBr nanoparticles are coated on the surface of TiO2 aggregated spheres with the diameter of 500-600 nm. The morphology of Ag-AgBr@TiO2 is similar to that of the TiO2 aggregated spheres, which indicates that the precipitation of Ag-AgBr on the surface of TiO2 does not affect the structure of TiO2 NPAS and TiO2 NPAS present very good sites to adsorb Ag-AgBr. With the increase of Ag-AgBr in Ag-AgBr@TiO2, there are more and more small particles on the surface of samples. The TEM and HRTEM images of sample S11 are presented in Fig. 3g-i. The Ag-AgBr particles about 10 nm are uniformly coated on the surface of the samples and connect each other. The corresponding EDS analysis and EMIs of Ag-AgBr@TiO2 are presented in Figs. S2b and S2c-f, which reveal the uniform distributions of O, Ti, Ag, and Br. Consequently, the Ag and Br are well distributed on the surface of TiO2 nanoparticles aggregated spheres.

Fig. 4 XPS patterns of sample S4. Wide survey scan for a Ag-AgCl@TiO2 and b Ag-AgBr@TiO2, c Ti 2p, d Cl 2p, e Br 3p, f Ag 3d and g Ag 3d of sample S11, h Ag 3d in S4 and i Br 3p in S11 after 5 cycles of photocatalytic degradation. The inset EDS patterns of samples 4 and 11 are in the inset in (a-b)

Fig. 4 XPS patterns of sample S4. Wide survey scan for a Ag-AgCl@TiO2 and b Ag-AgBr@TiO2, c Ti 2p, d Cl 2p, e Br 3p, f Ag 3d and g Ag 3d of sample S11, h Ag 3d in S4 and i Br 3p in S11 after 5 cycles of photocatalytic degradation. The inset EDS patterns of samples 4 and 11 are in the inset in (a-b)

   The surface chemical states of the Ag-AgX(X=Cl, Br)@TiO2 with further investigation by XPS are shown in Fig. 4. The peak positions in all the XPS spectra were calibrated with C 1s at 286.4 eV. The XPS spectrum of the Ag-AgX(X=Cl, Br)@TiO2 indicates that the product consists of Ag, Ti, O, and X (X=Cl, Br) elements (Fig. 4). The peak of N 1s results from the surface adsorption of nitrogen during preparation of Ag-AgX(X=Cl, Br)@TiO2 at 300 °C for 8 h under the protection of nitrogen. Two strong peaks at 464.3 and 458.6 eV are attributed to Ti 2p of TiO2 (Fig. 4c), which is slightly shifted towards lower binding energies compared with that of pristine TiO2 due to the direct contact between Ag nanoparticles and TiO2 [21]. The peak of Cl can be divided into two peaks Cl 2p3 and Cl 2p1 peaks (Fig. 4d) [19], which correspond to 200.5 and 197.6 eV, respectively. Br 3d5/2 and Br 3d3/2 binding energies in XPS spectra correspond to 67.8 and 68.8 eV, respectively, which could be assigned to Br- in AgBr (Fig. 4e) [18]. There are two strong peaks for Ag 3d at about 374 and 367.8 eV as shown in Fig. 4f-g. The peaks at 374 and 367.8 eV can be divided into two peaks at about 374.2 and 373.4 eV, 367.4 and 368.4 eV, respectively. Two strong peaks at 373.4 and 367.4 eV are attributed to Ag3d3/2 and Ag 3d5/2 of AgX in Ag-AgX(X=Cl, Br)@TiO2. And the peaks at 374.2 and 368.4 eV are attributed to the metallic Ag of Ag3d3/2 and Ag 3d5/2 in Ag-AgX(X=Cl, Br)@TiO2 [17]. On the basis of XPS results, it can be confirmed that the coexistence of Ag(0) and AgX on the surface of TiO2. EDS results are consistent with those of XPS, demonstrating distribution of Ag, Ti, O, and X (Cl, Br) on the samples as shown in the inset in Fig. 4a, b.

Fig. 5 a UV-vis absorption spectra and b PL spectra of Ag-AgCl@TiO2, Ag-AgBr@TiO2, AgCl@TiO2 and AgBr@TiO2 structures

Fig. 5 a UV-vis absorption spectra and b PL spectra of Ag-AgCl@TiO2, Ag-AgBr@TiO2, AgCl@TiO2 and AgBr@TiO2 structures

   The element of Cl and Br come from C16H33(CH3)3NCl (CTAC) and C16H33(CH3)3NBr (CTAB) respectively. Their long molecular chain, about 2.3-2.5 nm, is favorable to connect with TiO2, but is not in tangle. On the basis of the above experimental results, a possible two-step growth mechanism for the formation of Ag-AgX(X=Cl, Br)@TiO2 NPAS is proposed. In the first step, homogenously distributed AgX(X=Cl, Br) nanoparticles on the surface of TiO2 aggregate sphere are formed via an interaction between CTAC or CTAB and AgNO3, which induces nanoparticles to assemble into the final AgX(X=Cl, Br)@TiO2 microspheres. The microspheres of Ag-AgX(X=Cl, Br)@TiO2 are formed in the second step when they are exposed to the simulated sunlight. Unbound metallic Ag (Ag0) appears due to the photo-induced reduction reaction of AgX nanoparticles. Free metallic Ag(Ag0) attaches each other on the surfaces of AgX(X=Cl, Br)@TiO2 and forms the final Ag-AgX(X=Cl, Br)@TiO2 NPAS. The reduced Ag0 atoms may also react with other silver species (Ag+ ions, Ag0 atoms, or silver clusters). The formation process is shown by the following equations [30]:

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   To understand the formation of Ag clusters and its role in photoactivity in Ag-AgX@TiO2 NPAS, we prepared the AgX@TiO2 NPAS in the same way without irradiation. Figure 5a displays the UV–vis absorption spectra of Ag-AgCl@TiO2, Ag-AgBr@TiO2, AgBr@TiO2, and AgCl@TiO2. It is well known that the band gap of anatase TiO2 is about 3.2 eV. However, the absorption edge of the four samples are around 410 nm (about 3.1 eV), which is smaller than the band gap of anatase TiO2. It might result from surface defect of nanoparticle aggregation spheres with large specific surface and imprecise measurement, which contribute to the absorption edge starting at a little larger wavelength [31]. In addition, AgCl and AgBr on the surface of TiO2 have little influence on the absorption edge of Ag-AgX@TiO2 NPAS. AgCl@TiO2 has no absorption in visible light because of the large band gap of AgCl (about 3.3 eV), while AgBr@TiO2 has weak absorption in the visible light due to its smaller band gap (about 2.6 eV). Obviously, Ag-AgCl@TiO2 has weak visible light absorption. Thus, the photoactivity of Ag-AgCl@TiO2 extends from the UV into the visible light region. The absorption of Ag-AgBr@TiO2 in the range of 400-800 nm is stronger than that of AgBr@TiO2 because of the emergence of Ag. Therefore, as the accumulated excited electrons on the surface of AgX combine with Ag+ to form Ag0 clusters under the simulated sunlight irradiation, Ag-AgX@TiO2 is formed. Silver clusters have empty energy levels below the conduction band of AgCl, which enables a new electronic transition from the valence band of AgCl to the empty Ag cluster energy levels [30]. This is the well-known self-photosensitive property of AgX semiconductor, and it extends the light absorption from the UV to the visible region because of the silver clusters adsorbed on AgCl@TiO2 surface [30]. The self-sensitization is different from the spectral sensitization effect of Ag clusters that makes an electron injection from Ag clusters into the AgCl conduction band [19]. Thus, the absorption in the visible light comes from the combined action of the surface plasmon resonance of metallic Ag and the self-sensitization effect of Ag clusters.
   Silver clusters have contributed not only to light absorption but also the separation of the excited carriers. The photoluminescence (PL) emission spectroscopy provides the separation efficiency of the electron-hole pairs and carrier lifetime in semiconductors [32]. The PL spectra of Ag-AgCl@TiO2, Ag-AgBr@TiO2, AgBr@TiO2, and AgCl@TiO2 (Fig. 5b) show two characteristic bands with peaks at 451 and 523 nm caused by the e-h recombination with 350 nm excitation, which correspond to the emission of TiO2 [33]. The PL spectra are much similar for the four samples except for the strength. The PL intensity of Ag-AgX@TiO2 shows a notable decrease compared with that of AgX@TiO2. Thus, the decrease of the PL intensity suggests that Ag-AgX@TiO2 NPAS possesses a longer carrier lifetime, which demonstrates the enhancement of the photoinduced electron/hole pair separation. It is responsible for the enhanced photocatalytic activity for the pollutant degradation.
3.2 Visible-Light Photocatalytic Activity

   MO is a kind of organic dye that is often used as a model pollutant to study the catalytic performance of photocatalysts. In this study, the photocatalytic activity of 20 mg Ag-AgX(X=Cl, Br)@TiO2 is assessed by observing the degradation of MO (14 mg L-1) vs. time under visible light illumination (Figs. 6 and 7). Before irradiation, the MO solution with the catalyst was kept in the dark for 30 min to reach the adsorption equilibrium. The concentration of the MO solution slightly decreases in the dark. Comparisons of photocatalytic activities among the Ag-AgCl@TiO2 samples with different R under 60 min irradiation are shown in Fig. 6a-b. The degradation activity of sample S1 (TiO2 NPAS) is hardly observed due to the larger band gap (Eg = 3.2 eV). But for the sample S2, S4, and S7, the corresponding degradation rates are 82%, 98%, and 85% under visible light irradiation, which is much higher than that of S0 (TiO2 NPAS under simulated sunlight, only 34.79%). It indicates that greatly improved photocatalytic activity is achieved by the heterostructure of Ag-AgCl@TiO2, and the S4 with R=20:1 exhibits highest activity for MO degradation as shown in Fig. 6a. The temporal evolution of the absorption spectra of MO aqueous solution in presence of S4 under visible light irradiation is shown in Fig. 6b. The characteristic peaks centered at 464 nm do not change in position in degradation process. It indicates complete photocatalytic degradation of MO aqueous solution by the Ag-AgCl@TiO2 NPAS during the reaction and the catalyzed degradation intermediates are almost not produced. Histogram of photocatalytic activities of Ag-AgCl@TiO2 NPAS with different R under visible light irradiation for 60 min are shown in Fig. 6c. The samples with a wide range R from 10:1 to 25:1 exhibit higher activity for MO degradation with a degradation rate about 98%, which indicates a wide R range for application. It is important to be stable under repeated applications for an economical photocatalys. Figure 6d shows the cycling performance of sample S4 for five cycles. The photocatalytic activity remains approximately 98%, revealing the excellent long-term photocatalytic stability of Ag-AgCl@TiO2 NPAS.

Fig. 6 a Comparisons of degradation rate with different samples in different stages; b Absorption spectrums of the degradation with sample S4 in different stages; c Comparisons of photocatalytic activities among the Ag-AgCl@TiO2 NPAS samples with different R under the visible light irradiation and TiO2 NPAS (S0) sample under the simulated sunlight irradiation in 60 min; d The result of the repeated experiments for five times with sample S4

Fig. 6 a Comparisons of degradation rate with different samples in different stages; b Absorption spectrums of the degradation with sample S4 in different stages; c Comparisons of photocatalytic activities among the Ag-AgCl@TiO2 NPAS samples with different R under the visible light irradiation and TiO2 NPAS (S0) sample under the simulated sunlight irradiation in 60 min; d The result of the repeated experiments for five times with sample S4

   Figure 7 exhibits the activity of Ag-AgBr@TiO2 NPAS for MO degradation. It can be seen the efficient removal ratio of 98.78% (for sample S11) in 40 min, which is also far superior to those of Ag-AgCl@TiO2 NPAS. Compared with Ag-AgCl@TiO2 NPAS, Ag-AgBr@TiO2 NPAS has an almost complete photocatalytic degradation of MO and a wider R range from 25:1 to 5:1. Ever after five cycles, there is only about 7.25% of photocatalytic activity decrease for S11, indicating that Ag-AgBr@TiO2 NPAS has excellent cycling photocatalytic activity.

Fig. 7 a Comparisons of degradation rate with different samples in different stages; b Comparisons of photocatalytic activities among the Ag-AgBr@TiO2 NPAS samples with different R and TiO2 NPAS sample under the visible light irradiation in 40 min; c Absorption spectrums of the degradation with sample S11in different stages; d The result of the repeated experiments for five times with sample S11

Fig. 7 a Comparisons of degradation rate with different samples in different stages; b Comparisons of photocatalytic activities among the Ag-AgBr@TiO2 NPAS samples with different R and TiO2 NPAS sample under the visible light irradiation in 40 min; c Absorption spectrums of the degradation with sample S11in different stages; d The result of the repeated experiments for five times with sample S11

3.3 Visible-Light Photocatalytic Mechanism of Ag-AgCl@TiO2
   To fully discuss the effects of the heterostructure on the photocatalytic activities of Ag-AgX(X=Cl, Br)@TiO2 NPAS, the energy band diagram of Ag, AgX, and TiO2 is presented in Fig. 8. AgCl has a direct band gap of 5.6 eV and an indirect band gap of 3.25 eV [21] and the band gap of AgBr is about 2.6 eV. Meanwhile Ag-AgCl@TiO2 NPAS can be excited by visible light as shown in Fig. 5a and it has self-photosensitive effect because of their point ionic defects and electron traps according to the Eqs. 1-5 [34, 13], which might help to photochemical decomposition. It is just similar to the research by Hu group that two electrons in one oxygen vacancy in CeO2 are respectively excited by two Ce atoms neighboring the vacancy [35]. However, some researchers proposed that plasma-resonance absorption of metallic Ag (or Pd) on the surface of semiconductor contributes to the effective visible absorption and segregation of electron/hole pairs, which results in the higher photocatalytic activity [9, 11, 12]. Liu et al. found that the double heterostructure Ag/TiO2 nanoparticles/TiO2 nanobelts have perfect photocatalytic properties under UV light irradiation with the dominant wavelength of 355 nm and Ag nanoparticles on the surface of the TiO2 act as a sink for electrons contributing to the interfacial charge–transfer separation [36]. However, the composite photocatalyst with a wide weight ratio of TiO2/Ag2O exhibits a higher photocatalytic activity, but a bad cyclic stability under UV light irradiation because Ag+ is reduced to Ag [37]. Therefore, the role of Ag on the photocatalytic performance in Ag-AgCl@TiO2 NPAS isn’t determined.

Fig. 8 The band structures and degradation mechanisms of a Ag-AgCl@TiO2 NPAS and b Ag-AgBr@TiO2 NPAS under visible-light

Fig. 8 The band structures and degradation mechanisms of a Ag-AgCl@TiO2 NPAS and b Ag-AgBr@TiO2 NPAS under visible-light

   Thus, it is fascinating to consider how Ag/AgCl particles become an efficient and stable photocatalyst under visible light. To fully understand the photocatalysis process and the role of Ag nanoparticles during photocatalytic degradation MO, the XPS spectrum of the Ag-AgCl@TiO2 after five cycles are presented in Fig. 4h. The two strong peaks at 373.4 and 367.4 eV corresponding to Ag3d3/2 and Ag 3d5/2 of AgCl in Ag/AgCl @TiO2 becomes stronger, while the peaks at 374.2 and 368.4 eV corresponding to the metallic Ag of Ag 3d3/2 and Ag 3d5/2 become weaker. It indicates that some metallic Ag are oxidized to Ag+ and the self-sensitized effect of AgCl is suppressed during the photocatalysis reaction. Meanwhile the XPS analysis and the photocatalysis under visible light prove that AgCl is stable at the photocatalytic degradation MO.
   Therefore, the photocatalytic process of Ag-AgCl/TiO2 under the visible light is as following. Firstly, under visible light irradiation, electrons on valence band of AgCl can be excited to empty silver cluster energy levels below the conduction band of AgCl and form photogenerated electron–hole pairs due to the energy of light lower than the band gap of AgCl [30]. Subsequently, because the CB bottom (0.11 eV vs NHE) and VB top (3.04 eV vs NHE) of AgCl is below that of TiO2 (ECB =−0.41 eV, EVB = 2.37 eV) respectively [17], most of excited electrons coming from the surface plasmonic resonance of Ag cluster transfer to the conduction band AgCl and some excited electrons reach to the CB of TiO2. The excited electrons react with O2 adsorbed on the surface of the Ag-AgCl@TiO2 NPAS to produce •O2 and H2O2 that successively decompose the MO to the final products. Holes transferring to the AgCl surface oxidize Cl- ions to •Cl radicals, which recombine very fast to form Cl2 and then Cl2 is reduced to chloride ions by reacting with H2O under the applied conditions [30, 13]. Silver cations act as a catalyst for the decomposition of hypochloric acid into molecular oxygen, protons and chloride ions. Hypochloric acid can also degrade the MO into micromolecule. Meanwhile some holes also move to the valence band of TiO2. The holes on the surface of TiO2 can also oxidize OH- to yield •OH. Therefore, the degradation of MO could be attributed to the reaction with •O2, •OH, and H2O2 species during the photocatalysis. The excellent photocatalytic performance of Ag-AgCl@TiO2 NPAS could be due largely to the improvement of electron/hole pairs separation after loading Ag–AgCl on the TiO2. The reaction can be written as follows [17, 30],

9 49 公式56789

9 49 公式10111213

   Therefore, chlorine and hypochloric acid are inevitable during the photocatalytic reaction. Combination Eqs. (1) and (5-13), it indicates that the excellent stability of Ag-AgCl@TiO2 NPAS photocatalyst in the photocatalytic reaction under visible-light irradiation. Furthermore, it is well known that the Ag nanoparticles are likely to be slowly oxidized in the moist environment [30, 13]. Therefore, the XPS peaks of Ag+ becomes stronger after photocatalytic reaction.
   In summary, as a promising candidate, Ag-AgCl@TiO2 photocatalyst shows highly efficient and stable photocatalytic activities under visible light. Ag clusters play a significant role in the light harvesting and the double heterostructure also plays a role in the prevention of the recombination of photogenerated electron-hole pairs.
3.4 Visible-Light Photocatalytic Mechanism of Ag-AgBr@TiO2
   Figure 8b shows the band structure of Ag, AgBr [16, 18, 19, 38] and TiO2, which indicates the photocatalytic mechanism of the Ag-AgBr@TiO2 photocatalyst. Under visible light irradiation, electrons in AgBr (ECB =-0.67 and EVB =1.93 eV) are excited from VB to CB for the narrow band gap of 2.6 eV and the photogenerated electrons easily transfer into metal Ag nanoparticles because the CB potential of AgBr is more negative than that Fermi level of the loaded metal Ag. Then some of the electrons in Ag from the AgBr transfer to the conduction band of TiO2 (ECB =−0.41 eV, EVB = 2.37 eV) with the help of the Ag plasma resonance. The charge transfer process of AgBrAgTiO2 is similar to the efficient photosynthesis with charge flow steering [38-40]. The Ag clusters in the double heterojunction system act as a charge mediator for transferring electrons to the conduction band of TiO2 and keeping holes in the valence band of AgBr. The stronger photoresponse in visible region and efficient carrier separation of Ag-AgBr@TiO2 finally enhance the photocatalytic activity more than that of Ag-AgCl@TiO2.
   Since the XPS spectra of Br 3d5/2 and Br 3d3/2 in Ag-AgBr@TiO2 photocatalyst become weak after five cycles of photocatalytic degradation MO as shown in Fig. 4i, AgBr in Ag-AgBr@TiO2 NPAS is resolved into element Br and element Ag during the reaction of photocatalytic degradation MO according to the Eq. 2, which results in the decrease of Ag-AgBr@TiO2 NPAS on photocatalytic activity in degradation MO. However, the decomposition of AgBr doesn’t obviously affect the photocatalytic activity especially at the first three cycles because the photocatalytic degradation of MO.
Ag-AgBr@TiO2 NPAS are excellent in a wider range ratio (R=TiO2/AgBr) from 25:1 to 5:1 and then the stability of photocatalytic activity is gradually worse until R is larger than 25:1. The photocatalytic reaction of Ag-AgBr@TiO2 agrees with the report of Yue group [38].

   Owing to the self-sensitization, AgBr is easily decomposed into Ag and Br under visible light irradiation. As a strong oxidant, Br photodegrades MO into CO2 and H2O. As a self-sacrificing of AgBr in Ag-AgBr@TiO2 photocatalyst, the photodegradation of MO with Ag-AgBr@TiO2 is similar to the Ag2O/TiO2 nanobelts reported by Liu et al. [25]. Therefore, the stability of Ag-AgBr@TiO2 photocatalyst is slightly worse than that of Ag-AgCl@TiO2.

4 Conclusions

   In this paper, Ag-AgX(X=Cl, Br)@TiO2 NPAS synthesized by a facile sol-gel technique and post photoreduction method. On the basis of their efficient and stable photocatalytic activities, these photocatalysts could be widely used for environmental purification of organic pollutants in aqueous solution. As a self-sensitization material, both AgCl and AgBr have perfect photoresponse in visible light, especially AgBr. Both of them can efficiently separate excited electrons and holes via the fast electron transfer to metal Ag nanoparticles on the surface of heterostructure. The photocatalytic activity of Ag-AgBr@TiO2 is higher than Ag-AgCl@TiO2 at the first stage. This work indicates that, as an electronic transmission medium, metallic Ag can enhance photocatalytic activity not only via forming heterostructure with narrow band gap photocatalysts (e.g. Eg = 2.6 eV) but also for wide band gap photocatalysts (e.g. Eg = 3.2 eV) through the different roles. Ag nanoparticles on the surface of AgCl can effectively help to absorb visible light by self-sensitization and SPR, and maintain stability of AgCl. While Ag nanoparticles in Ag-AgBr@TiO2 system act as a charge mediator for transferring electrons from AgBr to TiO2.

Acknowledgments

This work is supported by the China Postdoctoral Science Foundation (2016M602647),  the Science and Technology Research Project of Chongqing Municipal Education Commission of China (KJ1400607), the Fundametal Research Funds for the Central Universities (CQDXWL-2014-001), NSFCQ (cstc2015jcyjA20020), NSFC (51572040, 51402112), National High Technology Research and Development Program of China (2015AA034801).

References

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References

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[2]M. Boehme, W. Ensinger, Mixed phase anatase/rutile titanium dioxide nanotubes for enhanced photocatalytic degradation of methylene-blue. Nano-Micro Lett. 3(4), 236-241 (2011). doi:10.1007/BF03353678
[3]Y. Dong, J. Li. X. Li. B. Zhou, The promotion effect of low-molecular hydroxyl compounds on the nano-photoelectrocatalytic degradation of fulvic acid and mechanism. Nano-Micro Lett. 8(4), 320-327 (2016). doi:10.1007/s40820-016-0091-7
[4]M. Wang, W. Li, Y. Zhao, S. GuF. Wang, F.Z. Wang, H.D. Li, X.T. Liu, C.J. Ren, Synthesis of BiVO4-TiO2-BiVO4 three-layer composite photocatalyst: effect of layered heterojunction structure on the enhancement of photocatalytic activity. RSC Adv. 79(6), 75482-75490 (2016). doi:10.1039/C6RA16796A
[5]J. Liu, L. Ruan, S.-B. Adeloju, Y. Wu, BiOI/TiO2 nanotube arrays, a unique flake-tube structured p-n junction with remarkable visible-light photoelectrocatalytic performance and stability. Dalton Trans. 43(4), 1706-1715 (2014). doi:10.1039/C3DT52394B
[6]G.H Jiang, R.J. Wang, Y. Wang, X.K Sun, Preparation of Cu2O/TiO2 Composite porous carbon microspheres as efficient visible light-responsive photocatalysts. Powder Technol. 212(1), 284-288 (2011). doi:10.1016/j.powtec.2011.04.025
[7]A. Rahman, Y.C. Ching, K.Y. Ching, A.K. Chakraborty, N.S. Liou, Surface modification of natural fiber using Bi2O3/TiO2 composite for photocatalytic self-cleaning. Bioresources 10(4), 7405-7418 (2015). doi:10.15376/biores.10.4.7405-7418
[8]H. Hua, Y. Xi, Z.H. Zhao, X. Xie, C. Hu, H. Liu, Gram-scale wetchemical synthesis of Ag2O/TiO2 aggregated sphere heterostructure with high photocatalytic activity. Mater. Lett. 91(2), 81-83 (2013). doi:10.1016/j.matlet.2012.09.068
[9]A. Takai, P.V. Kamat, Capture, store, and discharge shuttling photogenerated electrons across TiO2-silver interface. ACS Nano 5(9), 7369-7376 (2011). doi:10.1021/nn202294b
[10]W.B. Li, F. X. Hua, J.G. Yue, J.W. Li, Ag@AgCl plasmon-induced sensitized ZnO particle for high-efficiency photocatalytic property under visible light. Appl. Surf. Sci. 285(12), 490-497 (2013). doi:10.1016/j.apsusc.2013.08.082
[11]F. Zhang, Z. Cheng, L. Cui, T. Duan, A. Anan, C. Zhang, L. Kang, Controllable synthesis of Ag@TiO2 heterostructures with enhanced photocatalytic activities under UV and visible excitation. RSC Adv. 6(3), 1844-1850 (2015). doi:10.1039/C5RA17762F
[12]R. Long, K. Mao, M. Gong, S. Zhou, J. Hu, et al., Tunable oxygen activation for catalytic organic oxidation: schottky junction versus plasmonic effect. Angew. Chem. Int. Ed. 53(12), 3205-3209 (2014). doi:10.1002/anie.201309660
[13]P. Wang, B. Huang, X. Qin, X.Y. Zhang, Y. Dai, J.Y. Wei, M.H. Whangbo, Ag@AgCl: a highly efficientand stable photocatalyst active under visible light. Angew. Chem. Int. Ed. 47(41), 7931-7933 (2008). doi:10.1002/anie.200802483
[14]J. Yu, G. Dai, B. Huang, Fabrication and characterization of visible-light-driven plasmonic photocatalyst Ag/AgCl/TiO2 nanotube arrays. J. Phys. Chem. C 113(37), 16394-16401 (2009). doi:10.1021/jp905247j
[15]J. Zhou, Y. Cheng, J. Yu, Preparation and characterization of visible-light-driven plasmonic photocatalyst Ag/AgCl/TiO2 nanocomposite thin films. J. Photoch. Photobio. A 223(2), 82-87 (2011). doi:10.1016/j.jphotochem.2011.07.016
[16]L. Ye, J. Liu, C. Gong, L. Tian, T. Peng, L. Zan, Two different roles of metallic Ag on Ag/AgX/BiOX (X = Cl, Br) visible light photocatalysts: surface plasmon resonance and Zscheme bridge. ACS Catal. 2(8), 1677-1683 (2012). doi:10.1021/cs300213m
[17]J. Cao, B. Xu, B. Luo, H. Lin, S. Chen, Preparation, characterization and visible-light photocatalytic activity of AgI/AgCl/TiO2. Appl. Surf. Sci. 257(16), 7083-7089 (2011). doi:10.1016/j.apsusc.2011.03.046
[18]Y. Fan, W. Ma, D. Han, S. Gan, X. Dong, L. Niu, Convenient recycling of 3D AgX/graphene aerogels (X = Br, Cl) for efficient photocatalytic degradation of water pollutants. Adv. Mater. 27(25), 3767-3773 (2015). doi:10.1002/adma.201500391
[19]B. Cai, J. Wang, D. Han, S. Gan, Q. Zhang, Z. Wu, L. Niu, Ternary alloyed AgClxBr1-x nanocrystals: facile modulation of electronic structures toward advanced photocatalytic performance. Nanoscale 5(22), 10989-10995 (2013). doi:10.1039/c3nr03365a
[20]H. Li, S. Gan, H. Wang, D. Han, L. Niu, Intercorrelated superhybrid of AgBr supported on graphitic C3N4-decorated nitrogen-doped graphene: high engineering photocatalytic activities for water purification and CO2 reduction. Adv. Mater. 27(43), 6906-6913 (2015). doi:10.1002/adma.201502755
[21]X. Wang, Y. Tang, Z. Chen, T.T. Lim, Highly stable heterostructured Ag–AgBr/TiO2 composite: a bifunctional visible-light active photocatalyst for destruction of ibuprofen and bacteria. J. Mater. Chem. 22(43), 23149-23158 (2012). doi:10.1039/c2jm35503e
[22]J. Tejeda, N.J. Shevchick, W. Braun, A. Goldmann, M. Cardona, Valence bands of AgCl and AgBr: UV photoemission and theory. Phys. Rev. B 12(12), 1557-1566 (1975). doi:10.1103/PhysRevB.12.1557
[23]S. Higashimoto, Y. Nakai, M. Azuma, M. Takahashi, Y. Sakata, One-pot synthesis of imine from benzyl alcohol and nitrobenzene on visible-light responsive CdS–TiO2 photocatalysts. RSC Adv. 4(71), 37662-37668 (2014). doi:10.1039/C4RA06231K
[24]H. Hua, C.G. Hu, Z.H. Zhao, H. Liu X. Xie, Y. Xi, Pt nanoparticles supported on submicrometer-sized TiO2 spheres for effective methanol and ethanol oxidation. Electrochim. Acta 105(26), 130-136(2013). doi:10.1016/j.electacta.2013.05.002
[25]G. Prieto, H. Tüysüz, N. Duyckaerts, J. Knossalla, G. Wang, F. Schüth, Hollow nano- and microstructures as catalysts. Chem. Rev. 116(22), 14056-14119 (2016). doi:10.1021/acs.chemrev.6b00374
[26]Q. Li, F. Wang, L. Sun, Z. Jiang, T. Ye, M. Chen. Q. Bai, C. Wang, X. Han, Design and synthesis of Cu@CuS yolk–shell structures with enhanced photocatalytic activity. Nano-Micro Lett. 9(3), 35 (2017). doi:10.1007/s40820-017-0135-7
[27]H. Wei, L. Wang, Z. Li, S. Ni, Q. Zhao, Synthesis and photocatalytic activity of one-dimensional CdS@TiO2 core-shell heterostructures. Nano-Micro Lett. 3(1), 6-11 (2011). doi:10.1007/BF03353645
[28]P. Zhang, L. Wang, X. Zhang, J. Hu, G. Shao, Three-dimensional porous networks of ultra-long electrospun SnO2 nanotubes with high photocatalytic performance. Nano-Micro Lett. 7(1), 86-95 (2015). doi:10.1007/s40820-014-0022-4
[29]W. Liu, D. Chen, S.H. Yoo, S.O. Cho, Hierarchical visible-light-response Ag/AgCl@TiO2 plasmonic photocatalysts for organic dye degradation. Nanotechnology 24(40), 405706 (2013). doi: 10.1088/0957-4484/24/40/405706
[30]G. Calzaferri, D. Brühwiler, S. Glaus, D. Schürch, A.o Currao, C. Leiggener, Quantum-sized silver, silver chloride and silver sulfide clusters. J. Imaging Sci. Technol. 45(4), 331-339 (2001).
[31]W.J. Zhou, L.G. Gai, P.G. Hu, J.J. Cui, X.Y. Liu, et al., Phase transformation of TiO2 nanobelts and TiO2 (B)/anatase interface heterostructure nanobeltswith enhanced photocatalytic activity. CrystEngComm 13(22), 6643-6649 (2011). doi:10.1039/c1ce05638g
[32]H.F. Dang, X.F. Dong, Y.C. Dong, Y. Zhang, S. Hampshire, TiO2 nanotubes coupled with nano-Cu(OH)2 for highly efficient photocatalytic hydrogen production. Int. J. Hydrogen Energy 38(5), 2126-2135 (2013). doi:10.1016/j.ijhydene.2012.11.135
[33]Y. Sang, Z. Zhao, J. Tian, P. Hao, H. Jiang, H. Liu, J.P. Claverie, Enhanced photocatalytic property of reduced graphene oxide/TiO2 nanobelt surface heterostructures constructed by an in situ photochemical reduction method. Small 10(18), 3775-3782 (2014). doi:10.1002/smll.201303489
[34]J.F. Hamilton, Physical properties of silver halide microcrystals. Photogr. Sci. Eng. 18(5), 493-500 (1974).
[35]Y. Kang, Q. Leng, D. L. Guo, D.Z. Yang, Y.P. Pu, C.G. Hu, Room-temperature magnetism of ceria nanocubes by inductively transferring electrons to Ce atoms from nearby oxygen vacancy. Nano-Micro Lett. 8(1), 13-19 (2016). doi:10.1007/s40820-015-0056-2
[36]W.J. Zhou, G.J. Du, P.G. Hu, G.H. Li, D.Z. Wang, et al., Nanoheterostructures on TiO2 nanobelts achieved by acid hydrothermal method with enhanced photocatalytic and gas sensitive performance. J. Mater. Chem. 21(22), 7937-7945 (2011). doi:10.1039/c1jm10588d
[37]W. Zhou, H. Liu, J.Wang, D. Liu, G. Du, J. Cui. Ag2O/TiO2 nanobelts heterostructure with enhanced ultraviolet and visible photocatalytic activity. ACS Appl. Mater. Interfaces 2(8), 2385-2392 (2010). doi:10.1021/am100394x
[38]X. Liu, D. Zhang, B. Guo, Y. Qu, G Tian, H. Yue, S. Feng, Recyclable and visible light sensitive Ag–AgBr/TiO2: Surface adsorption and photodegradation of MO. Appl. Surf. Sci. 353, 913-923 (2015). doi:10.1016/j.apsusc.2015.06.206
[39]S. Liu, C. Han, Z.R.Tang, Y.J. Xu, Heterostructured semiconductor nanowire arrays for artificial photosynthesis. Mater. Horiz. 3(4), 270-282 (2016). doi:10.1039/C6MH00063K
[40] J.L. Liu, C.L. Zhang, B. Ma, T. Yang, X. Gu, X. Wang, C.G. Hu, Rational design of photoelectron-trapped/accumulated site and transportation path for superior photocatalyst. Nano Energy 38, 271-280 (2017). doi:10.1016/j.nanoen.2017.05.052

Citation Information

Cuiling Zhang, Hao Hua, Jianlin Liu, Xiangyu Han, Qipeng Liu, Zidong Wei, Chengbin Shao, Chenguo Hu, Enhanced Photocatalytic Activity of Nanoparticle-Aggregated Ag-AgX(X=Cl, Br)@TiO2 Microspheres Under Visible Light. Nano-Micro Lett.(2017) 9: 49. http://dx.doi.org/10.1007/s40820-017-0150-8

History

Received: 5 June 2017 / Accepted: 25 June 2017


Additional Info