SILICA GEL SUPPORTED TITANIUM DIOXIDE PHOTOCATALYST FOR METHYL ORANGE PHOTOREDUCTION

JOSHI M.M.1, MANGRULKAR P.A.2, LABHSETWAR N.K.3, RAYALU S.S.4*, PARWATE D.V.5
1Environmental Material Unit, National Environmental Engineering Research Institute, Nagpur, MS, India.
2Environmental Material Unit, National Environmental Engineering Research Institute, Nagpur, MS, India.
3Environmental Material Unit, National Environmental Engineering Research Institute, Nagpur, MS, India.
4Environmental Material Unit, National Environmental Engineering Research Institute, Nagpur, MS, India.
5Rashtrasant Tukadoji Maharaj Nagpur University Nagpur, MS, India
* Corresponding Author : s_rayalu@neeri.res.in

Received : 28-02-2012     Accepted : 06-03-2012     Published : 15-03-2012
Volume : 3     Issue : 1       Pages : 137 - 139
Int J Knowl Eng 3.1 (2012):137-139

Conflict of Interest : None declared

Cite - MLA : JOSHI M.M., et al "SILICA GEL SUPPORTED TITANIUM DIOXIDE PHOTOCATALYST FOR METHYL ORANGE PHOTOREDUCTION ." International Journal of Knowledge Engineering 3.1 (2012):137-139.

Cite - APA : JOSHI M.M., MANGRULKAR P.A., LABHSETWAR N.K., RAYALU S.S., PARWATE D.V. (2012). SILICA GEL SUPPORTED TITANIUM DIOXIDE PHOTOCATALYST FOR METHYL ORANGE PHOTOREDUCTION . International Journal of Knowledge Engineering, 3 (1), 137-139.

Cite - Chicago : JOSHI M.M., MANGRULKAR P.A., LABHSETWAR N.K., RAYALU S.S., and PARWATE D.V. "SILICA GEL SUPPORTED TITANIUM DIOXIDE PHOTOCATALYST FOR METHYL ORANGE PHOTOREDUCTION ." International Journal of Knowledge Engineering 3, no. 1 (2012):137-139.

Copyright : © 2012, JOSHI M.M., et al, Published by Bioinfo Publications. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution and reproduction in any medium, provided the original author and source are credited.

Abstract

TiO2 based photocatalysis has been widely investigated and has vital applications in energy and environmental remediation processes. In this connection research is being conducted in the zone of supported TiO2 based photocatalysts for development of visible light induced photocatalytic material. A series of materials were synthesized including zeolite based composite photocatalyst, N-doped mesopourous titania and investigated for dye degradation followed by hydrogen generation. Current research trend is towards supported photocatalyst therefore silica gel supported TiO2 photocatalyst was designed and developed also compared with alumina based photocatalyst. From the experimental data it was found that Silica based system has edge over the other synthesized photocatalysts with effective dye degradation of about 9.61 mg of MO reduced per g of TiO2 (0.508 mg of MO reduced per g of TiO2 for Degussa P-25). MO photoreduction is 19 times higher as compared to benchmark material Degussa P-25. Results well illustrate the formation of high dispersed metal oxide on silica framework.

Keywords

Supported photocatalyst, noble metal, methyl orange, hydrogen.

Introduction

Titanium dioxide is by far the most stable, non corrosive and non toxic semiconductor photocatalyst [1] . It is widely used and reported due to its unique photocatalytic nature. It has been used extensively in other applications like cosmetics, paints [2] , photoelectrodes, surface coating, water spitting [3] , organic pollutant degradation [4] etc. It also acts as, antialgal [5] antibacterial [6-7] , antifungal and deodorizing agent. In spite of all these properties, the photocatalytic activity of TiO2 is limited due to fast recombination of photo generated electrons and holes, low surface area while there is a significant activity in the ultra violet light. Many attempts have been made in order to i) improve the surface area, ii) to minimize the recombination reaction and improve its activity in visible region of spectrum.
The surface area can be improved by supporting TiO2 on a suitable matrix. Mesoporous materials are suitable host as they have better surface area for effective dispersion of TiO2 [8-9] . Attempts has been made to support TiO2 on various matrices such as hexagonal mesoporous silica, zeolite Y [10-12] , activated carbon [13] , porous ceramic tube [14] , glass [15] etc. Support material not only offers better surface area but also the support-TiO2 interface provides the site for effective electron transfer.
Siliceous materials are most suitable support as they have following properties-
1. Chemically inertness
2. High surface area and
3. Transparency to UV radiations.
There are very few reports in literature mentioning the use of silica gel as a support. Ding et-al [16] reported synthesis of silica gel supported TiO2 using chemical vapour deposition method. Silica gel/ TiO2 were also employed for degradation of trichloroethane (TCE) [17] . Silica gel as a support is advantageous in recovering the catalyst after completion of reaction [18] . Reports are also available for application of Silica- titania composites for removal of trace level of water pollutants [19] . CuO supported SiO2 is reported as effective photocatalyst for degradation of methylene blue [20] .
The other attempt widely being pursued is metal incorporation [21-22] . Photocatalytic response of TiO2 can be improved by metal doping. Many reports are available in literature for metal ion loading. Supported/ unsupported TiO2 was either loaded or doped with transition metals like Cr, V, Fe, Cu, Mn, Co, Ni, and Mo [23-24] , noble metals like Pd and Pt [25] , rare earth like La, Nd, Sm, Eu, Gd, and Yb [26] . Smaller metal particles deposited on TiO2 surface exhibits more negative Fermi level shift. These Fermi levels are closer to the conduction band of TiO2 resulting in more negative energy levels which are beneficial for reduction reaction.This improves the overall photoactivity of TiO2.
Here TiO2 was first supported on silica gel and then promoted with noble metals like Platinum and Ruthenium. Titania precursor was incorporated in silica gel by wet impregnation method and calcined at 500oC for developing anatase phase of TiO2. Noble metals were loaded on supported TiO2 by conventional wet impregnation route. Wet impregnation deposits the metal on a surface without material loss.
The synthesized photocatalyst was subjected to dye degradation under visible light irradiation. The methyl orange (MO) was completely degraded (100% photoreduction) by the as synthesized photocatalyst.

Experimental

A. Materials

The chemicals used for the synthesis were titanium (IV) isopropoxide (ACROS Organics USA), ruthenium chloride, methyl orange, ethanol and silica gel (Merck India Pvt. Ltd.) Tungsten lamps of 100, 200, and 500W were procured from Philips India Ltd, Mumbai.

B. Synthesis

a. Synthesis of Silica gel/TiO2 (10%)
5g of silica gel was mixed with 1.779 g titanium isopropoxide to attempt the 10% loading of TiO2. This mixture was ground thoroughly to get homogeneous mass and calcined at 500oC for 1h.
b. Synthesis of Silica gel/TiO2 (10%)/Pt
1g of Silica gel/TiO2 was mixed with platinum solution (0.5%w/w that is 0.005g of Pt on 1 g of Silica gel/TiO2). This mixture was heated at 60oC with constant stirring in order to evaporate the water content. Dried mass obtained was ground thoroughly to get homogeneous mass. Silica gel/TiO2 (10%)/Ru were also synthesized using similar method.

C. Characterization

X-ray diffraction patterns for Silica gel/TiO2, Silica gel/TiO2/Pt, Silica gel/TiO2/Ru, were obtained by Rigaku Miniflex II, Desktop X-ray diffractometer with Cu Kα radiations (λ = 0.5405). Specific surface area of photocatalyst was measured by N2 adsorption / desorption at 77 K using Micrometics USA ASAP 2000 instrument. Pore size and pore volume were analysed using Micrometics USA ASAP 2000 Specific surface area analyser. Scanning Electron Microscopic (SEM) images were obtained on a JEOL JSM-6380A Analytical Scanning Electron Microscope. UV-visible diffuse reflectance spectra (UV-DRS) and absorbance were obtained by Perkin Elmer Lambda 900 spectrophotometer.

D. Experimental method for photoreduction of methy

Experimental set-up is similar as described in previous studies by the authors [4] .

Results and discussion

A. Characterization of supported photocatalyst

XRD: The X-ray diffraction pattern for Silica gel/TiO2, Silica gel/TiO2/Pt, and Silica gel/TiO2/Ru along with Degussa P25 photocatalyst is given in [Fig-1] . Peaks having 2Ó¨ value of 25.4o, 38.6o, 47.96o, 48.60o correspond with TiO2 anatase phase.
Surface area- Surface area is determined by BET (Brunauer-Emmett-Teller) method, Pore size distribution is estimated using BJH (Barrett-Joyner-Halenda) method. Surface area of the bare silica gel is of about 204.87m2/g with pore volume and pore size of 0.42cm3/g and 121.98 Ao respectively. This confirms that the commercially available silica gel is mesoporous with high surface area. BET surface area of Silica gel/TiO2(190.69 m2/g), Silica gel/TiO2/Pt(185.07 m2/g), and Silica gel/TiO2/Ru (166.16 m2/g) is lowered due to the impregnation of TiO2, metals onto the silica framework.
Energy-dispersive X-ray spectroscopy: EDX spectra of the photocatalyst silica gel/TiO2/Pt and its chemical compositions are given in [Fig-2] . This data states that the commercially available silica gel consists of 71 and 29 mass-percent of silica and oxygen respectively (data not shown). A spectrum reveals the presence average 8.5 mass percent of TiO2, 0.47 mass percent of Pt in synthesized photocatalyst silica gel/TiO2/Pt.
UV-Visible diffused reflectance (UV- DRS) spectra- UV-Visible diffused reflectance spectra of Silica gel/TiO2, Silica gel/TiO2/Pt, and Silica gel/TiO2/Ru along with Degussa P25 TiO2 photocatalyst are given in [Fig-3] . The wavelength maxima observed for Silica gel/TiO2 and Silica gel/TiO2/Pt are 385, and 390nm respectively. λmax values indicate that the wavelength response range for Silica gel/TiO2/Pt is in visible region. In case of Silica gel/TiO2/Ru, the sample is dark greyish in colour so the spectrum shows absorption for complete range of light.

Photoreduction of methyl orange using Supported ph

All the three synthesized photocatalyst namely Silica gel/TiO2, Silica gel/TiO2/Pt, and Silica gel/TiO2/Ru along with Degussa P25 TiO2 photocatalyst were subjected to MO photoreduction. [Fig-4] shows the comparison of supported photocatalysts. MO photoreduction was observed to be 0.508, 5.344, 8.96 and 9.615 mg of MO reduced per g of TiO2 for Degussa P25 TiO2 photocatalyst, Silica gel/TiO2/ Ru, Silica gel/TiO2, and Silica gel/TiO2/Pt respectively. The photoactivity of all the supported photocatalyst is higher as compared to the benchmark Degussa P25 TiO2 photocatalyst. Silica gel/TiO2/Pt shows remarkable increase in the photoactivity by a factor of 19 as compared to the Degussa P-25 TiO2.

Conclusion

Supported photocatalyst such as Silica gel/ TiO2, Silica gel/ TiO2/Pt, and Silica gel/ TiO2/Ru were synthesized with predominant anatase phase. UV-DRS spectra show that the activity of the supported photocatalyst falls in visible region. The shift in absorption maxima could be due to the presence of metal on the surface of supported photocatalysts. The photocatalytic activity of the supported photocatalyst was evaluated by carrying out the photoreduction experiments. MO photoreduction by Silica gel/ TiO2/Pt is observed to the tune of about 9.61 mg of MO reduced per g of TiO2.

Acknowledgements

Financial support from the Department of Science and Technology (DST) Govt. of India is gratefully acknowledged. One of the authors (Meenal Joshi) is thankful to CSIR-India for providing financial assistance in the form of Senior Research Fellowship. The authors also thankfully acknowledge Director, NEERI Nagpur.

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Images
Fig: 1- XRD pattern of a) P25, b) Silica gel/TiO2/Pt, c)Silica gel/TiO2/Ru and d)Silica gel/TiO2.
Fig: 2- EDX spectra of Silica gel/TiO2/Pt
Fig: 3- UV-DRS spectra of (a) Degussa P25 TiO2 photocatalyst, (b) Silica gel/TiO2, (c) Silica gel/TiO2/Pt and (d) Silica gel/TiO2/Ru.
Fig 4- Comparison of MO photoreduction by P25, Silica gel/TiO2, Silica gel/TiO2/Pt and Silica gel/TiO2/Ru