1. Introduction

GSC

Green and Sustainable Chemistry

2160-6951

Scientific Research Publishing

10.4236/gsc.2019.92003

GSC-92403

Articles

Chemistry&Materials Science

A Rapid and Facile Synthesis Method for Nanosize Rutile Phase TiO2 with High Photocatalytic Activity

Priyanka

P. Bidaye

¹^*Julio

B. Fernandes

Department of Chemistry, Goa University, Taleigao Plateau, Goa, India

15052019

090227375, April 201913, May 2019 16, May 2019

2014

This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/

A green, rapid and facile method for synthesis of pure rutile TiO ₂ has been developed. Rutile TiO ₂ of high purity was synthesized by controlled hydrolysis of TiCl ₃in aqueous medium at room temperature. Addition of nitric acid to TiCl ₃ greatly increased the rate of TiCl ₃ hydrolysis, crystallization and surface area of the prepared TiO ₂ powder. The phase obtained in this way was identified by X-ray diffraction. TiO ₂ synthesized by this method showed a unique flower-like assembly of nanotubes, very high surface area and high photocatalytic activity under visible light irradiation.

TiCl3 Hydrolysis Rutile Nitric Acid Photocatalytic Activity

1. Introduction

Titanium dioxide is a versatile material with a range of applications associated with its unique optoelectronic and photochemical properties such as high refractive index, high dielectric constant, and excellent optical transmittance in the visible and near IR regions as well as its high performance as a photocatalyst [1] . Since TiO₂ is chemically and biologically inert, photocatalytically stable, easy to produce and use without risks to environment and human, it is the well-researched material for wastewater treatment from industries, factories, laboratories, degradation of textile dyes, pesticides and antimicrobial studies [2] [3] [4] .

It exists in three crystalline modifications anatase, rutile and brookite. Anatase and rutile are well-known photocatalysts with anatase generally showing higher photocatalytic activity [5] . Rutile form of TiO₂ has some advantages over the anatase form in terms of higher chemical stability, higher refractive index and is also comparable to anatase in application to dye-sensitized solar cells [6] . Applications of brookite are not much investigated probably because it is rarely obtained in a pure form.

Anatase TiO₂ has been synthesized by different precursors (Ti(OⁿBu)₄, Ti(OⁱPr)₄, TiCl₄, TiCl₃, Ti(SO₄)₂ and by different synthesis routes such as hydrothermal, thermohydrolysis and sol-gel process. Among the different methods of synthesis, the sol-gel method is considered advantageous and reproducible one as it leads to nanoparticles of high surface area [7] .

Rutile is generally obtained by calcination of the first crystallized anatase at temperatures higher than 500˚C. Direct formation of rutile is possible through long term aging of sols or exposure to high relative humidity or by direct hydrolysis of inorganic salts such as titanium tetrachloride (TiCl₄) in aqueous solutions under hydrothermal or moderate conditions [8] .

Anatase TiO₂ was mostly studied for photocatalytic degradation but lately Rutile TiO₂ has also shown promising results in photocatalytic studies. The high photocatalytic activity of rutile TiO₂ for decomposition of rhodamine-B in water is reported under artificial solar light irradiation [9] . Basca and Kiwi found that the presence of rutile TiO₂ showed enhanced catalytic activity compared to pure anatase TiO₂ during degradation of p-coumaric acid [10] . Rutile phase has also seen to be more active than anatase in photodecomposition of H₂S and photodecomposition of H₂O [11] [12] . The photovoltaic characteristics of rutile TiO₂ based DSSCs were found to be comparable to those of anatase TiO₂-based solar cells [13] [14] .

The present investigation is aimed to synthesize pure rutile phase photoactive Titania by a simplified procedure. Rutile is generally obtained by calcination of the first crystallized anatase at temperatures higher than 500˚C or by doping it with cations such as (Li⁺, Al³⁺, Zn²⁺, K⁺, Na⁺) [15] [16] . Direct formation of rutile is possible through long term aging of sols or exposure to high relative humidity or by direct hydrolysis of inorganic salts such as titanium tetrachloride (TiCl₄) in aqueous solutions under hydrothermal or moderate conditions or by using nano rutile as the seed [8] [17] . Photoactive rutile TiO₂ nanorods have been synthesized using titanium bis (ammonium lactate) dihydroxide as precursor by hydrothermal method and by decorating with anatase nanoparticles [18] . Controlled synthesis of rutile TiO₂ microspheres, nanoflowers, nanotubes, nanobelts and single crystal rutile TiO₂ nanotube/nanorod arrays is reported, via acid-hydrothermal synthesis [19] .

We have earlier reported that TiCl₃ is a convenient precursor to obtain TiO₂ through a solid state decomposition route [20] . Recently TiCl₃ hydrolysis method has been investigated in detail for the synthesis of TiO₂ owing to simplicity of TiCl₃ hydrolysis method. TiO₂ nanoparticles have been synthesized by hydrolysis and oxidation of TiCl₃ at 60˚C in aqueous medium through mixed phenomena of precipitation and oxidation by varying the pH of the precursor between 0.5 pH and 6.5 pH [21] . 1d nano rutile TiO₂ has been synthesized by interfacial reaction using TiCl₃ and benzoyl peroxide by hydrothermal treatment at 80˚C for 6 hours [22] . Rutile TiO₂ was also obtained by direct oxidation of TiCl₃ [23] . The synthesis of rutile Titania by hydrothermal method using titanium isopropoxide has also been reported [24] . Flower-like rutile Titania nanocrystals were obtained via aqueous phase stirring of TiCl₄ and HCl at low temperature [25] . However, TiCl₄ is highly hazardous to handle as it fumes easily and hence not considered here.

The research to produce one step synthesis of anatase or rutile nanocrystalline powder at low temperature is of considerable significance. We hereby report for the first time rapid synthesis of photoactive pure rutile phase TiO₂ by hydrolysis of TiCl₃ in HNO₃ medium at 25˚C without using any harsh experimental conditions.

2. Experimental2.1. Catalyst Synthesis

A titanium trichloride solution in HCl (15%) was taken in a beaker and HNO₃ was added to it, till the colour of TiCl₃ changed from violet to clourless. To this distilled water was added such that the ratio of TiCl₃ and water was 1:9 (V/V). The resulting mixture was then kept on a magnetic stirrer for hydrolysis at room temperature. Hydrolysis of TiCl₃ in presence of nitric acid was complete in 10 hours. The obtained precipitate was washed free of chloride ions and calcined at 400˚C for 3 h. This sample was named as A1. A blank was kept with the same ratio as TiCl₃ and water (1:9) but without the addition of HNO₃. It took 48 hours for TiCl₃ hydrolysis in the absence of nitric acid medium.

2.2. Catalytic Activity Test

The photocatalytic activity of synthesized sample was investigated for the degradation of methylene blue dye (10⁻⁴ M) and congo red dye (3.5 × 10⁻⁶ M) using synthesized catalyst A1 and Degussa (Evonik) P-25 as a standard reference catalyst as per the procedure reported earlier [20] . The experiments were carried out simultaneously for both the catalysts in bright sunlight between 10.00 a.m. to 12.00 noon. Experiments were repeated simultaneously on three different days in order to confirm the consistency of results. In a typical run 50 mL of aqueous dye solution and 0.1 g of the activated catalyst was exposed to sunlight for the duration of the experiment. The solutions thus exposed to sunlight were stirred intermittently. After every 30 minutes, 2 mL aliquots were pipetted out, centrifuged and the absorbance of the clear supernatants was determined at 660 nm and 400 nm wavelength for methylene blue and congo red respectively against appropriate blanks using spectrophotometer.

2.3. Characterization

Thermogravimetric analysis (TGA) and differential thermal analysis (DTA) of precursors were carried out on Shimadzu DTG-60 thermal analyzer. The X-ray powder diffraction patterns (XRD) have been recorded on a Rigaku powder X-Ray diffractometer (Mini Flex II) with Cu Kα radiation at a scanning speed of 2˚/min. The crystallite size was determined by Scherrer’s formula, t = (0.9 λ/β cosθ) where λ is the wavelength characteristic of the Cu Kα radiation, β is the full width at half maximum (in radians) and θ is the angle at which 100 intensity peak appears. The BET surface area was measured by N₂ adsorption-desorption method on a Micromeritics Tristar 3000. FEI (model Tecnai F30) high resolution transmission electron microscope (HRTEM) operating at 300 kV was used for TEM measurements. The absorption edges and band gaps were determined from the onset of diffuse reflectance spectra of the samples measured using UV–VIS spectrophotometer (Shimadzu UV-2450).

3. Results and Discussions3.1. Characterization of Materials3.1.1. Thermogravimetric Analysis

TG-DTA thermogram of the white precursor obtained by hydrolysis reaction of TiCl₃ with nitric acid is given in Figure 1. It is clear from the TG profile that the decomposition of the precursor is completed between 300˚C - 400˚C. The weight loss at 120˚C is indicative of loss of water owing to partial dehydroxylation of the OH groups.

3.1.2. X-Ray Analysis

The XRD pattern of the synthesized sample is shown in Figure 2. The diffraction

peaks in this pattern can be indexed to rutile phase [JCPDS No. 76-1940]. Thus, sample A1obtained by precipitation of TiCl₃ in presence of nitric acid respectively, showed pure rutile phase.

Table 1 describes the synthesis of rutile phase Titania and its structural features. As evident from Table 1, hydrolysis of TiCl₃ in presence of nitric acid was complete in 10 hours (A1) as compared to the blank that took 48 hours. It is noted from literature [26] that relatively fast hydrolysis of TiCl₃ in presence of H₂O is possible only at elevated temperatures. It has been observed that the ratio inorganic precursor: Water:HNO₃ is an important factor for controlling the rate of hydrolysis and phase formation. In TiO₂ rutile structure, (110) plane is the most thermodynamically stable and the growth rate of the plane (110) occurs faster compared to other planes [19] . Thus rutile TiO₂ is formed in the stable Ti⁴⁺ acidic solution. In the present investigation a simple and rapid method is reported, to obtain TiO₂ from aqueous solutions of TiCl₃ at room temperature. The surface area of A1 is also significantly higher than Degussa (Evonik) P-25 (Table 1).

3.1.3. HRTEM Analysis

HRTEM micrographs of the synthesized sample are shown in Figure 3. HRTEM images of A1 (synthesized in presence of HNO₃) show the formation of flower-like structures. It reveals that these structures are a unique assembly of nanoflowers like structures with ~40 nm length and 10 - 15 nm diameter. It is observed that the reported synthesis process has a capability to produce self organized nanostructures with flower-like morphology without use of any templating agent.

Table 1 Synthesis and structural features of titania samples

Sr. No.	Code	Method	Hydrolysis time	%yield	% Rutile	Scherrer’s crystallite sizes (nm)	BET surface area (m²/g)
1	A1	TiCl₃:H₂O:HNO₃	10 hrs	100	100	16	103
2	Degussa (Evonik) P-25				16	20.59	50

The formation of nanoflower structured rutile TiO₂ may be related to the synthesis method applied in the procedure. The oxidation of the TiCl₃ (in 15% HCl solution) with HNO₃ produces Ti⁴⁺ ions in the aqueous acidic solution. The hydrolysis of Ti⁴⁺ ions in the acidic solutions results in the production of fewer TiO₂ polycrystalline seeds. Thus the solution consists of supersaturated solution of Ti⁴⁺ ions and fewer polycrystalline TiO₂ seeds. The crystal growth of seeds into nanorods occurs by the deposition of Ti⁴⁺ ions from the solution on the surface of this polycrystalline seeds. Subsequent crystal growth proceeds to form nanorods along specific directions and then self-assemble into nanoflowers through Ostwald ripening process [19] .

3.1.4. N2 Adsorption-Desorption Isotherm

The N₂ adsorption-desorption isotherms and pore distribution analysis for sample A1 (inset) is given in Figure 4. The adsorption-desorption isotherm of the synthesized materials shows Type IV physisorption isotherm with H2 hysteresis loop, which is the characteristic of mesoporous materials [27] . In the isotherm the pore filling step occurs at low relative pressure (P/P₀ = 0.44) and also the upper closure point of the hysteresis loop appeared at a relatively lower value of (P/P₀ = 0.72) which indicates that the sample contains smaller pores [28] . From pore size distribution it is observed that the pores are small and narrow with uniform pore size of 3.6 nm diameter. Sharp hysteresis loop and narrow pore size distribution in the porosity analysis confirmed the presence of smaller pores which may have formed by the ordered arrangement of nanosize rods of individual nanoflowers.

3.1.5. UV-Vis Absorption Study

Figure 5 shows the UV-Vis absorbance spectra of the synthesized Titania sample. It is clear that the samples showed absorption edge in the visible region (Table 2). The band gap of the samples was determined by the equation Eg = 1239.8/λ, where Eg is the band gap energy (eV) and λ (nm) is the wavelength of the absorption edges in the spectra [29] .

3.2. Photocatalysis Study

The percentage degradation profiles of methylene blue and congo red with time are shown in Figure 6(a) and Figure 7(a) respectively. A1 catalyst showed high photocatalytic activity almost equal as TiO₂ Degussa (Evonik) P-25 catalyst.

The time dependant UV-Vis spectra of methylene blue and congo red dye in presence of catalyst A1 is given in Figure 6(b) and Figure 7(b) respectively. It is clear from both the figures that the decolourisation of dye precedes with increase in time. A1 obtained by room temperature hydrolysis of TiCl₃ in presence of nitric acid medium showed a 100% rutile phase, yet it showed photocatalytic activity comparable to Degussa (Evonik) P-25 for photodegradation of methylene blue as well as congo red. This is probably the first report of a rutile phase showing such high photocatalytic activity for both cationic dye methylene blue and anionic dye congo red. This excellent photodegradation using A1 can be due to the presence of favorable parameters such as particle size, nanorod shape of the particles, crystalline phase and very high surface area. It also possesses small

Table 2 The calculated band gaps of the Titania samples

Catalyst	A1	Degussa (Evonik) P-25
Band gap (eV)	2.88	2.97

band gap (2.88) in comparison to the reported band gap of Degussa (Evonik) P-25 (3.14). It is earlier reported that for each titanium dioxide phase, some optimum size and shape exists where each phase presents high photocatalytic activity [30] . Thus, this investigation resulted in rapid synthesis of a nano rutile catalyst having excellent efficiency for degradation of methylene blue as well as congo red. The photocatalytic process mainly occurs on the surface of the photocatalyst and adsorption precedes photodegradation [31] . As seen from Table 1 catalyst A1 had a high surface area and a smaller crystallite size. Other factors such as narrow pore size distribution and lower band gap could have facilitated the adsorption and degradation of the dye in the visible region with enhanced photocatalytic activity comparable to that of Degussa (Evonik) P-25.

4. Conclusions

· TiO₂ can be rapidly synthesized at room temperature from aqueous solutions of TiCl₃ in presence of nitric acid;

· Controlled hydrolysis of TiCl₃ yields pure rutile phase TiO₂ with high surface area having flower-like assembly of nanosized rods;

· Rutile TiO₂ synthesized by a simple hydrolysis method showed excellent efficacy for degradation of cationic dye methylene blue as well as anionic dye congo red in the visible light;

· The ease of synthesis makes it an attractive and promising catalyst and its efficiency could further be explored for DSSC’s, water splitting, photocatalytic reduction of CO₂, etc. in future studies.

Acknowledgements

The authors are grateful for the financial support received from DST Nano Mission program, SR/NM/NS-86/2009.

Conflicts of Interest

The authors declare no conflicts of interest regarding the publication of this paper.

Cite this paper

Bidaye, P.P. and Fernandes, J.B. (2019) A Rapid and Facile Synthesis Method for Nanosize Rutile Phase TiO₂ with High Photocatalytic Activity. Green and Sustainable Chemistry, 9, 27-37. https://doi.org/10.4236/gsc.2019.92003

References1

Diebold, U. (2003) The Surface Science of Titanium Dioxide. Surface Science Reports, 48, 53-229. https://doi.org/10.1016/S0167-5729(02)00100-0

Silva, C.G., Wang, W. and Faria, J.L. (2006) Photocatalytic and Photochemical Degradation of Mono-, Di- and Tri-Azo Dyes in Aqueous Solution under UV Irradiation. Journal of Photochemistry and Photobiology A: Chemistry, 181, 314-324. https://doi.org/10.1016/j.jphotochem.2005.12.013

Allen, N.S., Edge, M., Verran, J., Caballero, L., Abrusci, C., Stratton, J., Maltby, J. and Bygott, C. (2009) Photocatalytic Surfaces: Environmental Benefits of Nanotitania. The Open Materials Science Journal, 3, 6-27. https://doi.org/10.2174/1874088X00903010006

Ahmed, O.B. (2018) Evaluation of the Antimicrobial Efficacy of Titanium Dioxide Nanoparticles on the Surfaces of Public Toilets. Green and Sustainable Chemistry, 8, 32-38. https://doi.org/10.4236/gsc.2018.81003

Linsebigler, A.L., Lu, G. and Yates Jr., J.T. (1995) Photocatalysis on TiO2 Surfaces: Principles, Mechanisms and Selected Results. Chemical Reviews, 95, 735-758. https://doi.org/10.1021/cr00035a013

Chen, X. and Mao, S.S. (2007) Titanium Dioxide Nanomaterials: Synthesis, Properties, Modifications, and Applications. Chemical Reviews, 107, 2891-2959. https://doi.org/10.1021/cr0500535

Parra, R., Goes, M.S., Castro, M.S., Longo, E., Bueno, P.R. and Varela, J.A. (2008) Reaction Pathway to the Synthesis of Anatase via the Chemical Modification of Titanium Isopropoxide with Acetic Acid. Chemistry of Materials, 20, 143-150. https://doi.org/10.1021/cm702286e

Hosono, E., Fujihira, S., Kakiuchi, K. and Imai, H. (2004) Growth of Submicrometer-Scale Rectangular Parallelepiped Rutile TiO2 Films in Aqueous TiCl3 Solutions under Hydrothermal Conditions. Journal of the American Chemical Society, 126, 7790-7791. https://doi.org/10.1021/ja048820p

Wang, Y., Zhang, L., Deng, K. and Zhou, Z. (2007) Low Temperature Synthesis and Photocatalytic Activity of Rutile TiO2 Nanorod Superstructures. Journal of Physical Chemistry C, 111, 2709-2714. https://doi.org/10.1021/jp066519k

Baca, R.R. and Kiwi, J. (1998) Effect of Rutile Phase on the Photocatalytic Properties of Nanocrystalline Titania during the Degradation of p-Coumaric Acid. Applied Catalysis B: Environmental, 16, 19-29. https://doi.org/10.1016/S0926-3373(97)00058-1

Beck, D.D. and Siegel, R.W. (1992) The Dissociative Adsorption of Hydrogen Sulfide over Nanophase Titanium Dioxide. Journal of Materials Research, 7, 2840-2845. https://doi.org/10.1557/JMR.1992.2840

Ohno, T., Haga, D., Fujihara, K., Kaizaki, K. and Matsumura, M. (1997) Unique Effects of Iron(III) Ions on Photocatalytic and Photoelectrochemical Properties of Titanium Dioxide. The Journal of Physical Chemistry B, 101, 6415-6419. https://doi.org/10.1021/jp971093i

Park, N.G., Schlichthorl, G., Lagemaat, J., Cheong, H.M., Mascarenhas, A. and Frank, A.J. (1999) Dye-Sensitized TiO2 Solar Cells: Structural and Photoelectrochemical Characterization of Nanocrystalline Electrodes Formed from the Hydrolysis of TiCl4. The Journal of Physical Chemistry B, 103, 3308-3314. https://doi.org/10.1021/jp984529i

Park, N.G., Lagemaat and Frank, A.J. (2000) Comparison of Dye-Sensitized Rutile- and Anatase-Based TiO2 Solar Cells. The Journal of Physical Chemistry B, 104, 8989-8994. https://doi.org/10.1021/jp994365l

Heald, E.F. and Weiss, C.W. (1972) Kinetics and the Mechanism of the Anatase/Rutile Transformation, as Catalyzed by Ferric Oxide and Reducing Conditions. American Minerologist, 57, 10-23.

Talavera, R.R., Vargas, S., Murillo, R.A., Campos, R.M. and Poniatowski, E.H. (1997) Modification of the Phase Transition Temperatures in Titania Doped with Various Cations. Journal of Materials Research, 12, 439-443. https://doi.org/10.1557/JMR.1997.0065

Li, Y., Fan, Y. and Chen, Y. (2002) A Novel Method for Preparation of Nanocrystalline Rutile TiO2 Powders by Liquid Hydrolysis of TiCl4. Journal of Materials Chemistry, 12, 1387-1390. https://doi.org/10.1039/b200018k

Kandiel, T.A., Dillert, R., Feldhoff, A. and Bahneman, D.W. (2010) Direct Synthesis of Photocatalytically Active Rutile TiO2 Nanorods Partly Decorated with Anatase Nanoparticles. The Journal of Physical Chemistry C, 114, 4909-4915. https://doi.org/10.1021/jp912008k

Zhou, W., Liu, X., Cui, J., Liu, D., Li, J., Jiang, H., Wang, J. and Liu, H. (2011) Control Synthesis of Rutile TiO2 Microspheres, Nanoflowers, Nanotrees and Nanobelts via Acid Hydrothermal Method and Their Optical Properties. Crystal Engineering Communication, 13, 4557-4563. https://doi.org/10.1039/c1ce05186e

Bidaye, P.P., Khushalani, D. and Fernandes, J.B. (2010) A Simple Method for Synthesis of S-Doped TiO2 of High Photocatalytic Activity. Catalysis Letters, 134, 169-174. https://doi.org/10.1007/s10562-009-0217-3

Casssaignon, S., Koelsch, M. and Joliver, J.P. (2007) From TiCl3 to TiO2 Nanoparticles (Anatase, Brookite and Rutile): Thermohydrolysis and Oxidation in Aqueous Medium. Journal of Physics and Chemistry of Solids, 68, 695-700. https://doi.org/10.1016/j.jpcs.2007.02.020

Li, X., Liu, Y., Li, T. and Zhang, Z. (2006) Synthesis of 1D Nanorutile (α-TiO2) by Interfacially Initiating Redox Reaction at Low Temperature. Chemistry Letters, 35, 898-899. https://doi.org/10.1246/cl.2006.898

Pedraza, F. and Vasquez, A. (1999) Obtention of TiO2 Rutile at Room Temperature through Direct Oxidation of TiCl3. Journal of Physics and Chemistry of Solids, 60, 445-448. https://doi.org/10.1016/S0022-3697(98)00315-1

Aruna, S.T., Tirosh, S. and Zaban, A. (2000) Nanosize Rutile Titania Particle via a Hydrothermal Method without Mineralizers. Journal of Materials Chemistry, 10, 2388-2391. https://doi.org/10.1039/b001718n

Li, Y., Liu, J. and Jia, Z. (2006) Morphological Control and Photodegradation Behavior of Rutile TiO2 Prepared by a Low-Temperature Process. Materials Letters, 60, 1753-1757. https://doi.org/10.1016/j.matlet.2005.12.012

Masuda, Y. and Koumoto, K. (2004) Deposition Mechanism of Anatase TiO2 from an Aqueous Solution and Its Site-Selective Deposition. Solid State Ionics, 172, 283-288. https://doi.org/10.1016/j.ssi.2004.02.068

Sing, K.S.W., Everett, D.H., Haul, R.A.W., Moscou, L., Pierotti, R.A., Rouquerol, J. and Siemieniewska, T. (1985) Reporting Physisorption Data for Gas/Solid Systems with Special Reference to the Determination of Surface Area and Porosity. Pure and Applied Chemistry, 57, 603-619. https://doi.org/10.1515/iupac.57.0007

Cejka, J., Zilkova, N., Rathousky, J. and Zukal, A. (2001) Nitrogen Adsorption Study of Organised Mesoporous Alumina. Physical Chemsitry Chemical Physics, 3, 5076-5081. https://doi.org/10.1039/b105603b

Regan, B.O. and Gratzel, M. (1991) A Low-Cost, High-Efficiency Solar Cell Based on Dye-Sensitized Colloidal TiO2 Films. Nature, 353, 737-740. https://doi.org/10.1038/353737a0

Melghit, K. and Al-Rabaniah, S.S. (2006) Photodegradation of Congo Red under Sunlight Catalysed by Nanorod Rutile TiO2. Journal of Photochemistry and Photobiology A, 184, 331-334. https://doi.org/10.1016/j.jphotochem.2006.05.004

Gandhe, A.R. and Fernandes, J.B. (2005) A Simple Method to Synthesize N-Doped Rutile Titania with Enhanced Photocatalytic Activity in Sunlight. Journal of Solid State Chemistry, 178, 2953-2957. https://doi.org/10.1016/j.jssc.2005.06.034