Asian Journal of Chemistry; Vol. 25, Supplementary Issue (2013), S69-S72 Synthesis of Gallium Doped Mesoporous KIT-6 for the Photocatalytic Degradation of Dyes† N.S. SANJINI and S.VELMATHI* Organic and Polymer Synthesis Laboratory, Department of Chemistry, National Institute of Technology, Tiruchirappalli-620 015, India *Corresponding author: Fax: +91 431 2500133; Tel: +91 431 2503640; E-mail: [email protected] AJC-12794 Gallium doped highly ordered three dimensional la3d mesoporous KIT-6 material was synthesized by simple impregnation procedure with an aqueous solution of Ga(NO3)3·H2O. Different concentrations of gallium were doped onto KIT-6. The incorporation of gallium on the surface of KIT-6 was confirmed by various characterization techniques such as X-ray diffraction, BET surface area, Fourier transform infrared spectroscopy and diffuse reflectance spectroscopy. The XRD confirms the 3D structure of the materials. KIT 6 and the gallium doped KIT 6 show very high surface area and pore diameter. The UV DRS spectrum of the prepared materials shows absorbance in UVvisible region indicates their potential application in photocatalytic reaction. Photodegradation of methylene blue with Ga-KIT-6 under visible and ultra violet light were followed by UV visible spectrophotometer. The complete degradation of methylene blue dye was observed within 135 min and the optimization studies for the photocatalytic degradation of dyes were also systematically done. Key Words: Gallium, KIT-6, Mesoporous material, Photodegradation, Methylene blue. INTRODUCTION The discovery of mesoporous materials exhibits wide applications in industrial catalytic reaction since they have high surface area, large pore volume, multidimensional structure and easy recycling. Incorporation of transition metal ions on mesoporous silica has become an excellent strategy to generate catalytic active sites1-3. Semiconductor like titania incorporated mesoporous silica has extensive application on photocatalysis because of wide band gap (3.2 eV for anatase phase)4-7. The major proportion of metal oxides can be activated only in the presence of UV light8-13. Mainly semiconductors (Ga3+, In3+, Se3+, Sb3+) with d10 electronic configuration shows better photocatalytic activity because of their conduction and valence bands are formed by sp hybridization with large band dispersion which leads to high charge mobility14-18. GaN, a well-known blue light emitting semiconductor which is having wide band gap (3.4 eV) is used for photocatalytic activity19. Colour is the main contaminant to be present in the waste water coming from industries. In most of the industries like food, leather, textile, paper, printing etc, dyes are used to colour the products. Various methods developed for removal of dye have been inspected such as physico-chemical methods, filtration techniques, advanced oxidation process and biological processes20. For all these process further water treatment and regeneration of adsorbent is needed which will cost more for these process. So far, numerous heterogeneous catalysts are used for the photodegradation of dyes. Heterogeneous photocatalysis is one of the attractive and highly efficient method to degrade the toxic and non-biodegradable organic compounds which are pollutant to the environment. Transition metal doped mesoporous silica MCM-41, MCM-48, SBA-15, etc. was used for degradation of stable dyes21,22. In this paper we synthesized gallium doped ordered mesoporous silica KIT-6 by simple impregnation method and examined the photocatalytic dye degradation property under visible and UV light. EXPERIMENTAL Methylene blue (MB), analytical grade dye was purchased and used for photo-catalytic degradation studies. Other chemical reagents such as pluronic acid P123 (MW 5800), hydrochloric acid (HCl), n-butanol, tetraethylorthosilicate (TEOS) and gallium nitrate hydrate (Ga(NO3)3·H2O) were received from Sigma Aldrich chemical company and used without further purification. X-ray powder diffraction (XRD) was conducted on a Philips Xpert diffractometer with CuKα (1.5404 Å) radiation. Scans were made in the 2θ range 0.5-10º with a scan rate of 2 º/min (low angle diffraction). BET surface area and pore size distributions were measured by N2 adsorption/desorption using †International Conference on Nanoscience & Nanotechnology, (ICONN 2013), 18-20 March 2013, SRM University, Kattankulathur, Chennai, India S70 Sanjini et al. C0 − C × 100 C0 where, C0 is the dye concentration at the beginning of illumination; C concentration after photodegradation. Photodegradation yield (%) = RESULTS AND DISCUSSION The small angle X-ray pattern of samples KIT-6 and GaKIT-6 in Fig. 1a shows high intensity Brag peaks which corresponds to (211 ), (220) and (322) reflections. These are the well distinguished reflections for 3-D cubic structure. So this indicates the body centered cubic la3d space group of the prepared samples. After doping Ga3+ substituted in to lattice of Si4+ sites as well as the interstitial sites creates nonuniform strain within the doped KIT-6 which reflects in the peak Intensity (a.u.) Intensity (a.u) KIT-6 Ga-KIT-6 300 200 100 0 2 4 6 8 10 2 Theta (Degree) 2θ θ (º) Fig. 1. Low angle XRD pattern of KIT-6 and Ga-KIT-6 broadening in XRD pattern. The doped mesoporous silica once more maintained cubic structure which proves the efficacy of the impregnation method. N2 adsorption/desorption isotherm of Ga-KIT-6 samples are shown in Fig. 2 is type IV isotherm which is typical for mesoporous material with narrow pore size distribution. The surface area of Ga-KIT-6 was 383.9 m2/g are found to be decreased with those of KIT-6, 705.7 m2/g which confirms the large amount of distribution of dopant in the pores of KIT-6 while retaining a high ordered mesostructure. 400 300 5 dV/dD cm 3/g.nm Adsorption studies: Before starting the photodegradation experiment, the adsorption study was demonstrated to ensure the adsorption /desorption equilibrium. Ga-KIT-6 suspended methylene blue solution (100 mL) was stirred for 0.5 h in the darkness. The samples before and after adsorption were examined by UV-visible spectrophotometer with a range of 200 to 800 nm. λmax of methylene blue is 665 nm. Photodegradation studies: The photodegradation studies were conducted in visible photo reactor (> 400 nm) and UV immersion type photo reactor (254 nm and 365 nm). Visible reactor is a batch reactor with 350 W xenon lamps. UV reactor consists of a glass vessel made of borosilicate glass, wherein the solution to be degraded was placed. This glass housed with a double walled quartz vessel to hold lowpressure mercury lamp. 100 mL of aqueous methylene blue (10 mg/L) solution with 25 mg of Ga-KIT-6 catalyst was stirred either in visible (350 W) photo chamber or in UV reactor. The maximum absorbance wavelength of methylene blue dye was measured before and after degradation using UV-visible spectrophotometer. The degradation yield was calculated as follows, 400 3 General experimental procedure for photodegradation 500 Amount adsorbed (cm /g) 3 Amount adsorbed cm /g Micromerritics Gemini V -2380 surface area analyzer. Prior to the analysis samples were degassed at 300 ºC for 1 h. IR spectra were recorded by KBr pellet method on a Perkin-Elmer Spectrum One FTIR spectrometer instrument. UV-visible diffuse reflectance was measured at room temperature in air on a SHIMADZU UV-2600 UV-Vis spectrophotometer over the range from 200 to 800 nm. Synthesis of Ga-KIT-6: To 4 g of P123, 150 g of distilled water and 7.9 g of conc. HCl were added and stirred for 2 h at 35 °C. Then 4 g of n-butanol was added and stirred for another 1 h followed by the addition of 9 g of TEOS and stirred for 24 h. The resultant gel was allowed to stand for crystallization under static hydrothermal condition at 100 ºC for 24 h in a Teflon parr reactor. The white coloured solid product was filtered off, washed with warm distilled water several times and dried at 100 ºC overnight. The as-synthesized solid product was calcined at 540 ºC in presence of air for 24 h. 0.05 g of prepared KIT-6 was soaked in different mol/L solution of Ga(NO3)3·H2O by ultrasonication for 2 h. The material was filtered, dried at 100 ºC, calcined in a muffle furnace maintained at 750 ºC for 6 h and named as Ga-KIT-6. Asian J. Chem. 4 Ga-KIT-6 3 2 1 0 5 200 10 15 20 25 30 35 Pore diameter (nm) 100 0.0 0.2 0.4 0.6 0.8 1.0 Relativepressure pressure (P/PP/P ) o Relative 0 Fig. 2. N2 adsorption isotherm of Ga-KIT-6 FTIR spectrum (Fig. 3) of calcined samples shows broad peak around 3441 cm-1 for silanol group which play an important role in photo degradation process. The peak at 457, 761 and 1007 cm-1 corresponds to rocking, bending and asymmetric stretching of Si-O-Si bonds respectively and 588 cm-1 for Ga-O-Ga bond vibration. The abundance of surface hydroxyl groups play an important role in photodegradation of organic pollutants through their interaction with photo generated holes. The diffuse reflectance spectrum of Ga-KIT-6 mesoporous material is given in Fig. 4 which is in agreement for photocatalytic activity. The absorbance starts around 400 nm and increases sharply around 600 nm. These are corresponds to Vol. 25, Suppl. Issue (2013) Synthesis of Gallium Doped Mesoporous KIT-6 for the Photocatalytic Degradation of Dyes S71 2.5 200 KIT-6 Ga-KIT-6 2.0 Absorbance Absorbance Transmittance (%) (%) Transmittance 250 150 100 50 0 4000 3500 3000 2500 2000 1500 1000 -1) Wavenumber (cm(cm ) Wavenumber 0 min 30 min 60 min 90 min 120 min 150 min 180 min 1.5 1.0 0.5 0.0 200 500 300 400 500 600 700 800 Wavelength (nm) Wavelength (nm) –1 Fig. 5. Methylene blue degradation in the absence of photocatalyst under visible light Fig. 3. FTIR spectra of KIT-6 and Ga-KIT-6 Bf ads 0 min 15 min 30 min 45 min 60 min 75 min 90 min 105 min 120 min 135 min 1.5 0.3 Absorbance Absorbance Absorbance Absorbance 0.4 KIT-6 Ga-KIT-6 0.2 0.1 0.0 200 1.0 0.5 0.0 300 400 500 600 700 800 200 300 Wavelength (nm) Wavelength (nm) 500 600 700 800 Wavelength (nm) Wavelength (nm) Fig. 4. DRS UV-visible spectra of KIT-6 and Ga-KIT-6 Fig. 6. Methylene blue degradation under visible light 100 Photodegradation rate Photodegradation rate (%) (%) absorption of light caused by excitation of electrons from valence band to the conduction band of Ga-KIT-6. Photocatalytic activity: The photocatalytic activities of prepared samples were estimated by measuring the degradation rate of methylene blue in the presence of UV and visible light irradiation. The absorbance spectra of methylene blue solution was recorded each 0.5 h in absence of photocatalyst under visible and shown in Fig. 5. The identical spectra suggesting that direct photolysis not occurs. This confirms the higher stability of methylene blue and inactivity under visible and UV light. 25 mg of Ga-KIT-6 with methylene blue solution treated under different conditions. The degradation of methylene blue solution as shown in Fig. 6 depicts the photodegradation of methylene blue with Ga-KIT-6 occurred within 135 min under visible light (350 W) whereas KIT-6 undergoes adsorption saturation after 120 min as shown in Fig. 7. The gallium distribution on the surface of KIT-6 makes it possible to degrade the dye properly. The Fig. 8 explained absolute degradation of methylene blue under UV light (254 nm and 365 nm) with same amount of Ga-KIT-6. The degradation was greatly enhanced under UV light irradiation; excess light energy is given off to generate electron-hole pairs through band to band transitions compared with visible light. 400 90 80 KIT-6 Ga-KIT-6 70 60 0 30 60 90 120 150 180 Irradiation time (min) Irradiation Time (min) Fig. 7. Methylene blue degradation with KIT-6 and Ga-KIT-6 under visible light The substitution of a Ga3+ into Si4+ sites will create oxygen vacancy, which serves as an electron trap and effectively enhances the lifetime of the hole, which, in turn, helps in the oxidative degradation of methylene blue. The dye molecules are easily adsorbed on the surface of Ga-KIT-6. The incident photons generate an electron-hole pair at the surface of Photodegradation rate (%) (%) hotodegradation rate S72 Sanjini et al. Asian J. Chem. 100 ACKNOWLEDGEMENTS 90 The authors expressed their sincere thanks to Dr. S. Sundarrajan, Director, NIT Trichy for his constant support and encouragement, DST- Nanomission (SR/NM/NS-27/2008) and DST-SR/ S1/OC-06/2011 (G) dated 29-06-2011 projects for financial assistance. 80 UV-365 (nm) UV-254 (nm) REFERENCES 1. 70 2. 3. 4. Fig. 8. Methylene blue degradation with Ga-KIT-6 under UV light (254 nm and 365 nm) 5. 6. P 160 0 20 40 60 80 100 120 140 Irradiation Time time (min) Irradiation (min) photocatalyst, the site which are active for reaction. The suppression of e–/h+ by charge trapping was created by gallium doping on mesoporous silica KIT-6. The holes at the valence band and electron at conduction band react with water and adsorbed oxygen to form hydroxyl radicals and super oxide radicals. Finally these radicals decomposed the methylene blue into CO2, H2O and inorganic products. Conclusion Highly ordered gallium doped mesoporous KIT-6 silica is synthesized by simple impregnation method. The 3D cubic structure of Ga-KIT-6 was confirmed by low angle XRD. The mesoporous nature, high surface area and pore diameter of Ga-KIT-6 were analyzed by N2 adsorption isotherm. The FTIR analysis verified the hydroxyl group on the surface of catalyst which is favourable for photodegradation. DRS UV-visible spectra confirmed the photocatalytic activity of Ga-KIT-6 in visible range. 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