Advances in Materials Science and Engineering

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Nano, Ceramic, and Metallic Materials for Energy Application

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Research Article | Open Access

Volume 2014 |Article ID 348427 |

Vorrada Loryuenyong, Natnapin Jarunsak, Thirawich Chuangchai, Achanai Buasri, "The Photocatalytic Reduction of Hexavalent Chromium by Controllable Mesoporous Anatase TiO2 Nanoparticles", Advances in Materials Science and Engineering, vol. 2014, Article ID 348427, 8 pages, 2014.

The Photocatalytic Reduction of Hexavalent Chromium by Controllable Mesoporous Anatase TiO2 Nanoparticles

Academic Editor: Ho Chang
Received28 May 2013
Accepted25 Oct 2013
Published20 Jan 2014


Titania (TiO2) nanoparticles with periodical mesopore size (up to 150 Å) have successfully been synthesized by sol-gel template method, using titanium(IV) tetraisopropoxide as a starting precursor and isopropanol as a solvent. Different quantities of activated carbon (0%, 5%, and 10% by weight) were used as templates to control the porosity and particle size of titania nanoparticles. The templates were completely removed during the calcination in air at 500°C for 3 hr. The results showed that the specific surface area of titania is increased with increasing activated carbon content. The optical bandgap of synthesized titania exhibits a blue shift by 0.3–0.6 eV when compared to the reported value for the bulk anatase and rutile phases. The photocatalytic activity of porous titania is determined with its reduction efficiency of hexavalent chromium (Cr6+). The reduction efficiency is optimized under ultraviolet illumination.

1. Introduction

In general, chromium has two stable oxidation states, that is, Cr(VI) and Cr(III). The toxicity is mainly caused by hexavalent chromium, Cr(VI), which is virtually found in wastewater from industrial processes such as leather tanning, paint making, electroplating, and chromate production. This oxidation state has been classified as a carcinogen and mutagen not only to humans but also to other creatures. In many countries, as a consequence, the wastewater must be treated until the limit of Cr(VI) is below 0.05 mg/L before releasing to the water source [1]. One solution method is to convert it into Cr(III), which is considered as a nontoxic and essential trace metal in human nutrition. By chemical process, Cr(VI) is precipitated into Cr(III) as Cr(OH)3 in neutral or alkaline solutions and removed as a solid waste [2, 3]. However, this process requires reducing agents such as ferrous sulfate, sodium hydrogen sulfite, sodium pyrosulfite, hydrazine hydrate, and sulfur dioxide, which are expensive and dangerous with human skin and to release other unwanted chemicals [1].

Recently, there are many research works related to the use of semiconducting materials such as TiO2 and ZnO as photocatalysts for various applications. This has many benefits including low cost, high efficiency, reusable performance, cleanliness, natural safety, and nontoxicity. The photocatalytic mechanism begins when a semiconducting material absorbs light with energy larger than its bandgap. As a consequence, electrons from the valence band would be excited to the conduction band, leaving holes behind. These electron-hole pairs could react with oxygen and water in air to produce free radicals such as hydroxyl radical, hydrogen peroxide, and superoxide anions. Such free radicals have an ability to destroy the structure of the bacteria, hold back the virus, and react with organic compound to become carbon dioxide and water. In addition, They can react with toxic gas and carcinogen such as acetaldehyde, benzene, and formaldehyde.

Due to an oxygen defect, titania (TiO2) exists naturally as an n-type semiconducting photocatalyst with an intrinsic bandgap of 3.0–3.2 eV. Among four major phases, anatase, rutile, brookite, and titania-B, anatase is generally the most photocatalytically active, owing to its wide bandgap, high specific surface area, and low recombination rates of electron-hole pairs [46]. On the other hand, rutile is a high-temperature stable phase and has high refractive index and weatherability. Nevertheless, many researchers have reported that the mixed phase of anatase and rutile has higher photocatalytic activity and better optical properties than pure anatase phase [7]. Despite phase, other important properties including well-controlled porosity and crystallinity are also desirable in photocatalytic applications [8].

In this research, activated carbon was used as a template for producing uniform mesoporous TiO2 with anatase phase by sol-gel method. The physical properties of synthesized TiO2 were studied. The reduction efficiency of Cr(VI) performance by synthesized TiO2 as a photocatalyst was determined. The effect of wavelength lighting source with photocatalytic performance was also discussed.

2. Materials and Methods

2.1. Synthesis of TiO2 Nanoparticles

The synthesis was carried out as reported in the literature [6, 7]. All reagents including titanium(IV) tetraisopropoxide (TIP) (Sigma-Aldrich, USA) as a Ti precursor, 37% HCl (Merck KGaA, Germany) as a sol-gel catalyst, isopropanol (Merck KGaA, Germany) as a solvent, and activated carbon (CGO-200, C. Gigantic Carbon) as a template were used without further purification.

5.5 mL TIP was dissolved in 71.8 mL isopropanol, and then, if applicable, 0.073 g (5% activated carbon by weight of synthesized TiO2) or 0.145 g activated carbon (10% by weight of synthesized TiO2) was added to the solution. The mixed solution of 19 mL water and 1.68 mL HCl was then added dropwise to titania-activated carbon suspensions under vigorous stirring at room temperature. The mixture was further stirred for 3 hr, and the obtained gel was centrifuged, washed to remove excess reactants and catalyst, and dried in the oven at 80°C for 24 hr. The dried samples were grinded and calcined at 500°C for 3 hr at the heating rate of 5°C/min. The samples would be labelled as 0% AC, 5% AC, and 10% AC for TiO2 synthesized with 0%, 5%, and 10% activated carbon, respectively.

2.2. Characterization

Thermogravimetric analysis (TGA) (TGA7, Perkin Elmer) was used to characterize the thermal stability of the samples by measuring the change in weight as a function of temperature. Fourier transform infrared spectroscopy (FTIR) (Vertex70, Bruker Optics) was used for studying the functional groups in the samples. X-ray diffraction (XRD) patterns were obtained on a Miniflex II, Rigaku diffractometer. Transmission electron microscope (TEM) (JEM-1230, JEOL) was employed to study the morphology of the synthesized samples. The specific surface area, the pore size distribution, and the average pore size of samples were evaluated by nitrogen adsorption and desorption as a function of relative pressure, using Brunauer-Emmett-Teller (BET) and Barrett-Joyner-Halenda (BJH) methods. The % absorbance of samples was analyzed by UV-Vis spectrophotometer (UV-1800, Shimazu).

2.3. Reduction of Cr(VI)

In order to prepare 50 mg/L K2Cr2O7 aqueous solution, 50 mg K2Cr2O7 was added to a 1000 mL volumetric flask, and then the deionized water was poured until the solution level reached the 1000 mL mark on the neck of the flask. 0.02 g TiO2 (0%, 5%, or 10% AC) was then added to 20 mL K2Cr2O7 solution in separated 50 mL beakers. The suspensions were maintained at pH = 5 and vigorously stirred for 5 minutes before being illuminated by a light source. The illumination was performed at 150 watts and at a distance of 11 cm, measured from the tip of the lamp, using Newport's Oriel Solar simulator with actual spectral irradiance reported elsewhere (150 W low cost solar simulator, Newport Corporation). The absorbance of illuminated suspension was measured every 10 minutes for a total of 120 minutes. The effects of UV light illumination were conducted by the use of filter with light absorbance spectrum shown in Figure 1.

3. Results and Discussions

Figure 2 shows TGA and DTA graphs of synthesized TiO2 nanoparticles before calcination. The graph illustrates a weight loss at 100°C due to the release of the humidity and organic compounds. The samples synthesized with 5% and 10% activated carbon template, however, show two clearly defined steps of weight loss. Additional weight loss at the second step occurs at 500°C due to the decomposition of activated carbon. After calcination, as shown in Figure 3, it is found that the weight loss at 500°C disappears, confirming that activated carbon template is completely decomposed.

Figure 4 shows FTIR spectra of synthesized TiO2 nanoparticles before calcination. It is observed that all of the graphs have 3 main peaks: (1) O–H stretching at 3400 cm−1, (2) O–H bending at 1635 cm−1, and (3) Ti–O stretching at 700–400 cm−1. After calcination, however, the intensity of peaks at 3400 cm−1 and 1635 cm−1 is decreased due to the condensation of Ti–OH followed by the formation of a TiO2 network structure (Figure 5). In addition, the intensity of the peak at 700–400 cm−1 is evidently increased due to the stretching vibration of Ti–O–Ti in anatase phase.

Figure 6 shows the X-ray diffraction (XRD) patterns of TiO2 nanoparticles. All the XRD peaks could be indexed as (101), (004), (200), (105), (211), (118), and (315) at 2-theta = 25, 38, 48, 53, 55, 63, and 75°, respectively, which corresponds to an anatase phase. The particle size of TiO2 was calculated with the Scherrer formula using the XRD peak of anatase (101) plane as shown in Table 1. Smaller particle size is observed with the use of activated carbon template. In comparison to P25 Aeroxide TiO2 which contains anatase and rutile phases, the results show that pure anatase TiO2 could be made via the hydration of titanium(IV) isopropoxide using a sol-gel technique and activated carbon template.

SamplesSpecific surface area
Pore diameter
Pore volume
XRD particle size

0% AC69.2811.250.19132
5% AC94.347.920.19105
10% AC82.4610.210.21111

The morphologies of calcined TiO2 are shown in Figure 7. It is found that TiO2 nanoparticles are spherical in shape and do not agglomerate together. The particle size is similar to that predicted from XRD analysis. It could be predicted that the activated carbon as a template restrained the growth of TiO2 particles, consistent with that reported previously [7].

Figures 8 and 9 show the N2 adsorption/desorption isotherms and the corresponding BJH pore size distribution of titania nanoparticles, respectively. From the figure, it is observed that the isotherm of the synthesized TiO2 can be ascribed to type IV. A summary of BET results is illustrated in Table 1, in comparison with those of commercial P25 Aeroxide TiO2 nanoparticles. As shown, activated carbon templates are likely to increase the specific surface area. All of the samples exhibit monodispersed mesopore size distribution up to 150 Å. The specific surface area as high as 94 m2/g could be obtained with the addition of 5% AC template and by a simple and inexpensive sol-gel method.

The optical bandgap of TiO2 nanoparticles has been determined from the absorption spectrum (Figure 10) using the following Tauc relation for a direct bandgap: , where , , , , , and are the absorption coefficient, the thickness of the sample, frequency of the light, a constant, and the bandgap energy, respectively. The average bandgap was then estimated from the intercept of linear portion of versus , as shown in Figure 7 [9]. From the figure, the bandgap energy of TiO2 prepared using activated carbon in the amount of 0%, 5%, and 10% by weight was 3.58, 3.48, and 3.59 eV, respectively. Generally, the particle size of the TiO2 has the bandgap energy between 3.0 and 3.2 eV. The observed large bandgap could be due to the effect of restricted movement of electrons, called “electron confinement.”

In this experiment, the efficiency of catalytic TiO2 was tested by using the reduction of potassium dichromate (K2Cr2O7) as the model compound (Figure 11). The absorbance peaks of K2Cr2O7 are found at 273 nm and 350 nm. Without a photocatalyst, K2Cr2O7 is not degradable under the light irradiation using solar simulator (not shown here). With TiO2 as a photocatalyst, however, TiO2 can absorb photons with energy higher than its bandgap, causing electrons to jump across the bandgap into conduction band. These free electrons involved in the reactions with the K2Cr2O7 solution and Cr6+ could be reduced to Cr3+ in the form of Cr(OH)3, following the equations below [10, 11]:

As a result, the absorbance intensity decreased over exposure time.

In addition, it is found that the maximum peaks were red-shifted toward longer wavelength. This could be due to the transformation from dichromate K2Cr2O7 into chromate K2CrO4 caused by hydroxyl groups on the surface of TiO2 nanoparticles, following the equation

With optical filter, a decrease in absorbance intensity of K2Cr2O7 aqueous solution is less than that without filter. This indicates that the reduction is less likely to take place due to less energy from the light to sufficiently excite electrons across the bandgap. Comparison of reduction capacities of synthesized TiO2 (10% AC) with P25 Aeroxide TiO2, as shown in Figure 12, shows a higher photocatalytic activity. This suggests that the photocatalytic activity could be improved by changes in crystalline phase as well as specific surface area of photocatalytic materials.

4. Conclusions

TiO2 with controllable mesoporous anatase phase could be synthesized using sol-gel method and activated carbon template. The bandgap energy of synthesized TiO2 is 3.48–3.59 eV due to the effect of electron confinement. The performance of TiO2 as a photocatalyst gave a good result when using lighting source system in the UV region. Over irradiation time, the concentration was decreased, indicating an increase in reduction of Cr6+. Furthermore, there was evidence that the two main absorption peaks were red-shifted to the right due to the transformation of dichromate into chromate form by hydroxyl group on TiO2 surface.

Conflict of Interests

The authors declare that there is no conflict of interests.


The authors wish to thank the Department of Materials Science and Engineering, Faculty of Engineering and Industrial Technology, Silpakorn University, and the National Center of Excellence for Petroleum, Petrochemicals and Advanced Materials for supporting and encouraging this investigation. This work was supported by the Higher Education Research Promotion (HERP), the Office of the Higher Education Commission.


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Copyright © 2014 Vorrada Loryuenyong et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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