The hybrid photocatalyst of TiO2–SiO2 thin film prepared from rice husk silica

The hybrid photocatalyst of TiO2–SiO2 thin film prepared from rice husk silica

Superlattices and Microstructures 51 (2012) 343–352 Contents lists available at SciVerse ScienceDirect Superlattices and Microstructures journal hom...

1MB Sizes 13 Downloads 60 Views

Superlattices and Microstructures 51 (2012) 343–352

Contents lists available at SciVerse ScienceDirect

Superlattices and Microstructures journal homepage: www.elsevier.com/locate/superlattices

The hybrid photocatalyst of TiO2–SiO2 thin film prepared from rice husk silica P. Klankaw a,⇑, C. Chawengkijwanich b, N. Grisdanurak c, Siriluk Chiarakorn d,⇑⇑ a Division of Environmental Technology, The Joint Graduate School of Energy and Environment, King Mongkut’s University of Technology Thonburi, Bangkok 10140, Thailand b Nanotechnology National Center, National Science and Technology Development Agency (NSTDA), Pathumthani 12121, Thailand c Department of Chemical Engineering, Faculty of Engineering, Thammasat University, Pathumthani 12121, Thailand d Division of Environmental Technology, School of Energy Environment and Materials, King Mongkut’s University of Technology Thonburi, Bangkok 10140, Thailand

a r t i c l e

i n f o

Article history: Received 24 February 2011 Received in revised form 16 November 2011 Accepted 19 December 2011 Available online 29 December 2011 Keywords: TiO2 Self-assembly SiO2 Photocatalytic process Thin film

a b s t r a c t The TiO2–SiO2 thin film was prepared by self-assembly method by mixing SiO2 precursor with titanium precursor solution and aged to obtain a co-precipitation of silica and titanium crystals. Dip coating method was applied for thin film preparation on glass slide. The X-ray diffraction (XRD) of the self-assembly thin film had no characteristic property of SiO2 and even anatase TiO2 but indicated new crystal structure which was determined from the Fourier Transform Infrared Spectrophotometer (FTIR) as a hybridized Ti–O–Si bonding. The surface area and surface volume of the self-assembly sample were increased when SiO2 was incorporated into the film. The self-assembly TiO2–SiO2 thin film exhibited the enhanced photocatalytic decolorization of methylene blue (MB) dye. The advantages of SiO2 are; (1) to increase the adsorbability of the film and (2) to provide the hydroxyl radical to promote the photocatalytic reaction. The self-assembly thin film with the optimum molar ratio (SiO2:TiO2) as 20:80 gave the best performance for photocatalytic decolorization of MB dye with the overall efficiency of 81%. Ó 2011 Elsevier Ltd. All rights reserved.

⇑ Corresponding author. Tel.: +66 2 470 8654; fax: +66 2 470 8660. ⇑⇑ Co-corresponding author. Tel.: +66 2 470 8654; fax: +66 2 470 8660. E-mail addresses: [email protected] (P. Klankaw), [email protected] (S. Chiarakorn). 0749-6036/$ - see front matter Ó 2011 Elsevier Ltd. All rights reserved. doi:10.1016/j.spmi.2011.12.004

344

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

1. Introduction Recently, TiO2 has been widely used in the photocatalytic process due to the excellent properties such as high production of hydroxyl radicals, inexpensive, non-toxic and having physical and chemical stability [1]. However, the applications of TiO2 photocatalytic process have many limitations such as the recombination of electron and holes, easy agglomeration during the synthesis and the need of activation energy in a range of ultraviolet (UV) radiation for photocatalytic reaction [2]. Nevertheless, there are many researches focusing on the improvement of TiO2 qualities for photocatalytic reactivity by doping it with, such as, transition metals [3] and rare metals [4]. Although the transition metal doped TiO2 showed higher photocatalytic reactivity than pure TiO2, the toxicity or hazard of transition metals is a matter of environmental and health concern. Therefore, the development of TiO2 photocatalyst using less toxic dopant becomes more interesting issue. It was reported that a SiO2 group is able to boost photocatalytic reactivity of TiO2 [5–8]. Generally, the application of SiO2 with TiO2 in photocatalytic process for environmental abatement is in a powder form. Therefore, the method for recycling this catalyst after completion of photocatalytic process is a matter of concern. Normally, the process for recycling catalyst is very complex and expensive. To overcome the recycling and disposal problem of TiO2 powder catalyst, the process for immobilizing the catalyst on the substrate is essential. There are many processes such as sol–gel, Chemical Vapor Deposition (CVD) and Physical Vapor Deposition (PVD) which have been proposed to immobilize the catalyst on suitable substrates as thin film [9]. Nevertheless, the sol–gel technique is most attractive for preparation of thin film because the method is simple, inexpensive and practicable for working in atmospheric conditions [10–12]. Generally, the preparation process of TiO2–SiO2 precursor solution before immobilizing the thin film on the substrate can be conducted by impregnation (ex situ) and co-precipitation (self-assembly) method [13]. Both of this method provides the different properties of the thin film. Generally, the ex situ thin film sustain the characteristics of the both TiO2 and SiO2 while, the self-assembly thin film introduce a new hybrid materials between TiO2 and SiO2 enhance photocatalytic reactivity [5,13]. In this study, the self-assembly method was selected for preparation of TiO2–SiO2 precursor solution. The SiO2 precursor solution prepared from rice husk silica was dissolved in titanium solution at the initial process expecting to form a new hybrid material between SiO2 and TiO2 for enhancement of the photocatalytic reaction. The sol–gel dip coating technique was chosen for preparation of TiO2–SiO2 thin film on the glass slides. Additionally, the photocatalytic reactivity of the hybrid materials thin film was investigated by the decolorization of MB dye under UV irradiation. 2. Methodology 2.1. Chemicals All the chemicals used were analytical grade. Titanium (IV) butoxide (TBOT), obtained from Fluka Chemical, was used as titanium source. Rice husk silica was extracted from the acid leaching process following the method of Grisdanurak et al. [14]. The extracted silica was used as a silica source. Cetyltrimethylamoniumbromide (CTAB) obtained from Aldrich chemical was used as a directing agent for a template of TiO2–SiO2 synthesis. Ethanol and acetylacetone provided from Merck Chemical were used as a solvent in sol–gel process. 2.2. Synthesis of TiO2–SiO2 thin film by self-assembly method The preparation of TiO2–SiO2 thin film was started by dissolving TBOT in the mixed solvents (ethanol and acetylacetone) [15]. Simultaneously, the SiO2 precursor solution was prepared by mixing rice husk silica and CTAB with ethanol solution. After that, the two precursor solutions were mixed together under vigorous stirring at 80 °C for 96 h. The molar ratios of SiO2:TiO2 were varied from 0:100, 20:80, 50:50 and 80:20, respectively. Then preparation of the TiO2–SiO2 thin film on glass substrates was conducted by sol–gel dip coating technique. Before coating process, the substrates were cleaned with piranha solution (an oxidizing agent consisting of sulfuric acid and hydrogen peroxide)

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

345

at 80 °C for 0.5 h and rinsed with deionized water and acetone. After that, the substrate was dipped into the TiO2–SiO2 precursor solution at constant withdrawn speed of 10 cm min1. Then, the coated substrates were calcined at 550 °C for 5 h under an air flow in an electrical furnace. After dipping, the residual solution was collected by evaporation of solvents at room temperature until the solution turned into slurry. Then, the slurry was dried at 103 °C for 1 h in an oven before calcination at 550 °C for 5 h to obtain TiO2–SiO2 powder. 2.3. Thin film characterizations The physical and chemical properties of TiO2–SiO2 thin film and powder were characterized by various instruments. The crystal structure of the thin film was characterized by XRD (Rigaku Model D/ Max III with Cu Ka radiation in angular range (2h) from 1° to 60 ° with 15 mA and 30 kV). FE-SEM (Hitachi S-4800) was used to reveal the surface morphology, smoothness and thickness of the thin film. The UV–Visible absorption pattern of the thin film was examined by UV–Visible spectrophotometer (Shimadzu ISR-2200). The inner constructible properties such as porous arrangement pore size diameter and pore distribution of TiO2–SiO2 powder were monitored by TEM (TECHNAI F12 Philips with 27 mA and 80 kV). The functional groups of TiO2–SiO2 powder were investigated by FTIR (Perkin Elmer Spectrum One). Finally, the porosity of TiO2–SiO2 powder such as specific surface area, specific volume and pore size diameter were examined by nitrogen adsorption analyzer (Micromeritics ASAP 2010) following Brunauer Emmett Teller (BET) technique. 2.4. Photocatalytic decolorization of MB dye This experiment was designed for investigating the photocatalytic reactivity of the prepared TiO2– SiO2 thin film. The TiO2–SiO2 thin film was put into 20 ml of 105 M MB solution. The determination of adsorption of thin film was carried out in the dark by measuring the reduction of absorbance intensity of methylene blue solution at 663 nm, which is the kmax of MB. The 3 ml of MB solution was taken every 20 min and return to the reservoir after finishing a measurement of the changed wavelength absorption intensity by using UV–Visible spectrophotometer. After the adsorption equilibrium, the samples were irradiated with 20 W mercury lamps; the UV intensity of 0.6 W cm2 with kmax at 330 nm. The photocatalytic reactivity was determined by monitoring the reduction of absorbance intensity of MB every 20 min. The rate of photocatalytic decolorization of MB solution was calculated by the equation below based on the assumption that the photocatalytic decolorization of MB is the first order reaction.

lnðA0 =AÞ ¼ kt where A0 and A are the initial absorbance and the absorbance after irradiation of MB solution, t is an irradiation time and k is the first-order rate constant. 3. Results and discussion 3.1. Thin film characterization The crystalline phase characterized by XRD of bare TiO2 (SiO2:TiO2 = 0:100) thin film showed the anatase phase at 2h equal to 25°, 38° and 48°. Whiles, the TiO2–SiO2 thin film prepared from selfassembly method demonstrated the new crystalline peak at 2h equal to 31° and 45° (Fig. 1). It is possible that the inter lattice between Ti, O and Si are formed during the self-assembly process when the two precursor solution are mixed before crystal precipitation takes place. This result is different from the study of TiO2–SiO2 thin film prepared by the ex situ method, which reported from other results for preparation of TiO2–SiO2 [1,2,5,16]. To identify these new observed peaks, the FTIR technique was employed to confirm the existing of Ti–O–Si bonding which will be discussed later. If the hybridized bonding exists, it is interesting to figure out whether this band has significant effects on the photocatalytic reactivity of the film.

346

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

Fig. 1. XRD patterns of TiO2–MCM-41 thin films at various molar ratios.

The FE-SEM images of TiO2–SiO2 thin film revealed the homogeneous phase between the TiO2 and SiO2 particles (Fig. 2). The surface morphology of these thin films showed porosity, which increased as SiO2 was increased. Similarly the thickness of the thin film increases corresponding with an increase of SiO2 contents. The thickness of the thin film (1 cycle) stayed in a range of nano-thin film. For the molar ratio of SiO2:TiO2 equal to 0:100, 20:80, 50:50 and 80:20, the thickness was observed to be 57, 62, 79 and 87 nm, respectively (Fig. 3). The TEM images of the self-assembly TiO2–SiO2 powder showed the homogeneous crystal phase between TiO2 and SiO2. The image (Fig. 4) revealed the homogeneous crystallinity of TiO2–SiO2 particles. The results indicated that adding SiO2 contents caused decreasing in the crystal size of the photocatalyst from 20 nm to 10 nm. However, this hypothesis will be confirmed by the FTIR instrument during characterization of the functional group of the substance.

Fig. 2. FE-SEM images (1000) of TiO2–MCM-41 thin film (A) MCM-41:TiO2 = 20:80, (B) MCM41:TiO2 = 50:50 and (C) MCM41:TiO2 = 80:20.

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

347

Fig. 3. Thickness of TiO2–MCM-41 thin film (A) MCM-41:TiO2 = 0:100, (B) MCM41:TiO2 = 20:80, (C) MCM-41:TiO2 = 50:50 and (D) MCM-41:TiO2 = 80:20.

Fig. 4. TEM image (100,000) of TiO2–MCM-41powders (A) MCM-41:TiO2 = 0:100, (B) MCM-41:TiO2 = 80:20.

The FTIR spectra of TiO2–SiO2 powder prepared from self-assembly method showed the noticeable absorption feature around 910 and 1200 cm1, which belong to the absorption band of Ti–O–Si and Si– O–Si (Fig. 5) [17]. Additionally, the spectra intensity of Ti–O–Si band is dominant when TiO2 content increases. The spectra of Si–O–Si increased when SiO2 content was increased. According to the FTIR

348

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

Fig. 5. FTIR spectra of TiO2–MCM-41 thin films at various molar ratios.

results the sample containing SiO2:TiO2 equal to 20:80 obviously shows the presence of Ti–O–Si bonding. This result corresponds with the other results, which revealed the increasing of spectral intensity of Ti–O–Si band with increasing molar ratio of TiO2 [18]. The proposed mechanism for Ti–O–Si bond formation can be explained as the following reactions.

TiðOC4 H9 Þ2 þ C2 H5 OH ! Ti—OHðHydrolysis reactionÞ SiO2 þ C2 H5 OH ! Si—OH Ti—OH þ Ti—OH ! Ti—O—TiðCondensation without SiÞ Si—OH þ Si—OH ! Si—O—Si ðCondensation without TiÞ Ti—OH þ Si—OH ! Ti—O—SiðCondensation with the combination of Ti and SiÞ The hydrolysis reaction of TBOT and SiO2 in ethanol produces Ti–OH and Si–OH. After that, the condensation reaction between two precursors such as Ti–OH and Ti–OH or between Si–OH and Si–OH and the combination of Ti–OH and Si–OH occur depending on the molar ratio of Si and Ti. Table 1 shows the improvement of porosity properties such as specific surface area, specific volume and pore size diameter of TiO2 powder after incorporating with SiO2. The results from BET analyzer of TiO2–SiO2 powder showed the increase of specific surface area, specific volume and the decrease of pore size diameter than the pure TiO2 thin film. These results are corresponding with many reports, which explained the phenomena of increased surface area, increased specific volume and reduced pore size diameter of TiO2 when SiO2 was added [19–21]. The larger surface area is supposed to enhance the photocatalytic reactivity of TiO2–SiO2 thin film especially in the initial stage in which the adsorption plays a significant role.

Table 1 Nitrogen adsorption characteristics of TiO2–MCM-41 powder. Molar ratio (SiO2:TiO2)

Specific surface area (m2 g1)

Specific volume (cm3 g1)

Pore size diameter (nm)

0:100 20:80 50:50 80:100

48 120 292 487

11.13 27.31 65.49 110.92

3.782 3.749 3.234 2.238

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

349

Fig. 6. Wavelength absorption of TiO2–MCM-41 thin film at various molar ratios.

Before studying the photocatalytic reactivity of TiO2–SiO2 thin film, the UV–Visible absorption pattern of the thin films was determined in order to select the optimum wavelength of the light source for the experiment. The absorption pattern of the film (cut off the interference of glass substrate) was obtained using UV–Visible spectrophotometer. The broad absorption band was found and it peaked at 320 nm for pure TiO2. When SiO2 content was increased, the blue shift of absorption was observed. The highest UV absorption was obtained for the sample SiO2:TiO2 (80:20) having peak at approximately 297 nm which is less than that of pure TiO2 (Fig. 6). This phenomenon can be explained in terms of the change in band gap energy of TiO2 due to SiO2. Many reports concluded that SiO2 causes the blue shift of TiO2 by two mechanism; (i) reduced particle size of TiO2 due to siliceous framework (quantum size effect) and (ii) forming Ti–O–Si bonds leading to the modification of the electronic structure [17,22,23]. Similar to those reports, increase of the BET surface area of the catalyst and the presence of Ti–O–Si observed in FTIR characterization study also provide the evidences that there is a decrease in particles size of TiO2 in our thin film. Thus, incorporating SiO2 into TiO2 framework should influence the performance of TiO2–SiO2 thin film in photocatalytic process. According to the UV absorption, the UV light with 330 nm was used for the photocatalytic experiment. 3.2. Photocatalytic decolorization of MB dye To understand the influence of SiO2 on the photocatalytic reaction, the experiment was designed as dark and UV irradiation phase. In dark phase, the adsorption of MB dye on the thin film occurred. After the adsorption equilibrium, the UV light was turn on and the photocatalytic reaction was performed. The adsorption capacity of these thin films was determined during the dark reaction and it increased as SiO2 content was increased. The adsorption equilibriums of TiO2–SiO2 thin film at the molar ratio of SiO2:TiO2 equal to 0:100, 20:80, 50:50 and 80:20 were 80, 120, 140 and 160 min, respectively (Fig 7). This effect can be explained by the role of SiO2, which enhances the specific surface area and increases active sites (hydroxyl group) on the surface of the photocatalyst [19,24]. However, it is noticeable that the sample containing SiO2:TiO2 equal to 20:80 and 50:50 have the highest adsorbability. This might be because of the limitation of amount of Si incorporating into Ti–O bonding. In case of the sample at the SiO2:TiO2 equal to 80:20, the excess silica probably leaches out from the thin film causing the reduction in adsorption capacity. During the UV irradiation phase, all of the molar ratios of the thin film were able to decolorize MB dye. But for the sample at molar ratio of SiO2:TiO2 equal to 20:80, the rate of photocatalytic decolorization of MB dye was higher than that of pure TiO2 (Fig 8). The calculated rate constants of TiO2–SiO2 thin film for the molar ratio of SiO2:TiO2 equal to 0:100, 20:80, 50:50 and 80:20 were 0.0028, 0.0034, 0.0022 and 0.0026 min1, respectively. This phenomenon can be explained by two mechanisms of photocatalytic process; (i) the adsorption process and (ii) irradiation process. Firstly, the molecules of MB dye is adsorbed on the surface of the catalyst. The ability of this process relies on the specific surface area of the photocatalyst. The irradiation process establishes

350

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

Fig. 7. Decolorization of MB dye of TiO2–MCM-41 thin film at various molar ratios.

Fig. 8. Rate of decolorization of MB dye of TiO2–MCM-41 thin film at various molar ratios.

the redox reactions for degradation of MB dye on the surface. The overalls efficiency of photocatalytic process depends not only on the adsorption capacity of the photocatalyst but also on the chemical bonding of the photocatalyst. The results of photocatalytic decolorization of MB dye indicated that in the part of adsorption phase the rate of reaction was influenced by the specific surface area of the photocatalyst, which facilitates the attraction of the molecules of MB dye onto the photocatalytic sites. After that, the rate of reaction could be controlled by the UV responsive chemical structure Ti–O– Si bonding of the photocatalyst. The improvement of overall photocatalytic reactivity is resulted from the combination of these factors (increased specific surface area and Ti–O–Si bonding). This result corresponded with the results of other researches [25,26], which showed the increasing of photocatalytic decolorization of MB dyes by the synergic effect between SiO2 and TiO2 when adding zeolite into TiO2. The samples with SiO2:TiO2 equal to 20:80 was proved to be the best photocatalyst among others even

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

351

comparing to pure TiO2. The overall efficiency for photocatalytic decolorization of the hybrid thin films containing SiO2:TiO2 equal to 0:100, 20:80, 50:50 and 80:20 were 72%, 81%, 79% and 75%, respectively. 4. Conclusion The TiO2–SiO2 thin film prepared by the self-assembly method demonstrated the homogeneous thin film. This thin film hybrid photocatalyst demonstrated a new characteristic feature in it which occurred from chemical reaction between SiO2 and TiO2. The SiO2 enhanced the TiO2 photocatalytic decolorization of MB dye by increasing the specific surface area and established a chemical bonding with TiO2. The photocatalytic reactivity of the thin film for decolorization of MB dye relied on the increasing specific surface area and chemical structure of the photocatalyst. Acknowledgements This research was financially supported by the Joint Graduate School of Energy and Environment (JGSEE), the Thailand Graduate Institute of Science and Technology (TGIST) program, Thailand’s National Science and Technology Development Agency (NSTDA), Grant No. TG-55-20-51-031D throughout this project is gratefully acknowledged, the Thailand Research Fund (TRF) and the Commission of Higher Education. References [1] M.V.P. Sharma, V.D. Kumari, M. Subrahmanyam, TiO2 supported over SBA-15: an efficient photocatalyst for the pesticide degradation using solar light, Chemosphere 73 (2008) 1562–1569. [2] H. Yang, D. Deng, C. Du, Synthesis and optical properties of mesoporous MCM-41 containing doped TiO2 nanoparticles, Colloids and Surfaces A: Physicochemical and Engineering Aspects 339 (2009) 111–117. [3] E.P. Reddy, B. Sun, P.G. Smirniotis, Transition metal modified TiO2-loaded MCM-41 catalysts for visible- and UV-light driven photodegradation of aqueous organic pollutants, Journal of Physical Chemical B 108 (2004) 17198–17205. [4] C.H. Liang, F.B. Li, C.S. Lui, G.L. Lu, X.G. Wang, The enhancement of adsorption and photocatalytic activity of rare earth ions doped TiO2 for the degradation of Orange I, Dyes and Pigments 76 (2008) 477–484. [5] S. Artkla, W. Kim, W. Choi, J. Wittayakun, Highly enhanced photocatalytic degradation of tetramethylammonium on the hybrid catalyst of Titania and MCM-41 obtained from rice husk silica, Applied Catalysis B: Environmental 91 (2009) 157– 164. [6] Z.L. Hua, J.L. Shi, W.H. Zhang, W.M. Huang, Direct synthesis and characterization of Ti-containing mesoporous silica thin films, Materials Letters 53 (2002) 299–304. [7] M.V.P. Sharma, V.D. Kumari, M. Subrahmanyam, Photocatalytic degradation of isoproturon herbicide over TiO2/Al-MCM-41 composite systems using solar light, Chemosphere 72 (2008) 644–651. [8] M.S. Sadjadai, N. Farhadyar, K. Zare, Synthesis of nanosize MCM-41 loaded with TiO2 and study of its photocatalytic activity, Superlattices and Microstructures 46 (2009) 266–271. [9] V. Meille, Review on methods to deposit catalysts on structured surfaces, Applied Catalysis A: General 315 (2006) 1–17. [10] D.S. Hinczewski, M. Hinczewski, F.Z. Tepehan, G.G. Tepehan, Optical filters from SiO2 and TiO2 multi-layers using sol–gel spin coating method, Solar Energy Materials & Solar Cells 87 (2005) 181–196. [11] U. Cernigoj, U.L. Stangar, P. Trebse, U.O. Krasovec, S. Gross, Photocatalytically active TiO2 thin films produced by surfactantassisted sol–gel processing, Thin Solid Films 495 (2006) 327–332. [12] A. Lukowiak, R. Dylewicz, S. Patela, W. Strek, K. Maruszewski, Optical properties of SiO2–TiO2 thin film waveguides obtained by the sol–gel method and their applications for sensing purposes, Optical Materials 27 (2005) 327–332. [13] M. Popova, A. Szegedi, Z. Cherkezova-Zheleva, A. Mitov, N. Kostova, T. Tsoncheva, Toluene oxidation on titanium- and ironmodified MCM-41 materials, Journal of Hazardous Materials 168 (2009) 226–232. [14] N. Grisdanurak, S. Chiarakorn, J. Wittayakun, Utilization of mesoporous molecular sieves synthesized from natural source rice husk silica to chlorinated volatile organic compounds (CVOCs) adsorption, The Korean Journal of Chemical Engineering 20 (2003) 950–955. [15] P. Kajitvichyanukul, J. Ananpattarachai, S. Pongpom, Sol–gel preparation and properties study of TiO2 thin film for photocatalytic reduction of chromium (VI) in photocatalysis process, Science and Technology of Advanced Materials 6 (2005) 352–358. [16] S. Zhu, D. Zhang, X. Zhang, L. Zhang, X. Ma, Y. Zhang, M. Cai, Sonochemical incorporation of nanosized TiO2 inside mesoporous silica with high photocatalytic performance, Microporous and Mesoporous Materials 126 (2009) 20–25. [17] X. Gao, I.E. Wachs, Titania–silica as catalysts: molecular structural characteristics and physico-chemical properties, Catalysis Today 51 (1999) 233–254. [18] D.C.M. Dutoit, M. Schneider, A. Baiker, Influence of sol–gel and drying conditions on structural properties, Journal of Catalysis 153 (1995) 165–176. [19] H.J. Kim, Y.G. Shul, H. Han, Photocatalytic properties of silica-supported TiO2, Topics in Catalysis 35 (2005). [20] K. Gude, V.M. Gunko, J.P. Blitz, Adsorption and photocatalytic decomposition of methylene blue on surface modified silica and silica–titania, Colloids and Surfaces A: Physicochemical and Engineering Aspects 325 (2008) 17–20.

352

P. Klankaw et al. / Superlattices and Microstructures 51 (2012) 343–352

[21] V. Mangalampalli, P. Sharma, V.D. Kumari, M. Subrahmanyam, TiO2 supported over porous silica photocatalysts for pesticide degradation using solar light: Part 2. Silica prepared using acrylic acid emulsion, Journal of Hazardous Materials 175 (2010) 1101–1105. [22] R.V. Grieken, J. Aguado, M.J. López-Muñoz, J. Marugán, Synthesis of size-controlled silica-supported TiO2 photocatalysts, Journal of Photochemistry and Photobiology A: Chemistry 148 (2002) 315–322. [23] Y.H. Hsien, C.F. Chang, Y.H. Chen, S. Cheng, Photodegradation of aromatic pollutants in water over TiO2 supported on molecular sieves, Applied Catalysis B: Environmental 31 (2001) 241–249. [24] S. Yoda, D.J. Suh, T. Sato, Adsorption and photocatalytic decomposition of benzene using silica–titania and titania aerogels: effect of supercritical drying, Journal of Sol–Gel Science and Technology 22 (2001) 75–81. [25] I. Paramasivam, A. Avhale, A. Inayat, A. Bosmann, P. Schmuki, MFI-type (ZSM-5) zeolite-filled TiO2 nanotubes for enhanced photocatalytic activity, Nanotechnology 20 (2009) 45. [26] D.I. Petkowicza, S.B.C. Pergherb, C.D.S. Silvac, Z.N.R. Rochac, J.H.Z. Santos, Catalytic photodegradation of dyes by in situ zeolite-supported titania, Chemical Engineering Journal 158 (3) (2010) 56.