JWARPJournal of Water Resource and Protection1945-3094Scientific Research Publishing10.4236/jwarp.2010.211116JWARP-3190ArticlesEarth&Environmental Sciences Photocatalytic Degradation of Organic Dye Methyl Orange with Phosphotungstic Acid eipingWangShuijinYang** E-mail:yangshuijin@163.com(SY);291120100211979983September 29, 2010November 2, 2010 November 4, 2010© Copyright 2014 by authors and Scientific Research Publishing Inc. 2014This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/

Silicotungstic acid and phosphotungstic acid were prepared and characterized by Fourier Transform Infrared Spectroscopy (FTIR) and X-ray diffraction (XRD). The results showed that the prepared catalysts possess classical Keggin structure. The factors on the degradation of methyl orange, such as the kind of catalyst, the amount of catalyst, the original concentration of dye and illumination time were investigated under metal halide lamp. The degradation of methyl orange is up to 93.6% with phosphotungstic acid at the best reaction conditions at 8.89 g/L concentration of phosphotungstic acid, 5.56 mg/L concentration of methyl orange and 80 min illumination time.

Phosphotungstic Acid Photocatalytic Degradation Methyl Orange1. Introduction

The wastewater of textile dye draining into the river without treatment would bring out serious pollution of Water resource and threatening of ecology environment and human health. At present, the industrial methods for dye waste treatment include adsorption, precipitation, electrical remediation, oxidation, and biological degradation. But all these ways cost much money, and/or create secondary contamination [1]. Since the discovery of photoelectrochemical splitting of water on n-type TiO2 electrodes [2], photochemistry has possessed many practical applications, such as in optoelectronic devices or in the field of industrial and environmental catalysis [3-4]. Anatase TiO2 has attracted much attention due to their efficient decomposition ability for organic pollutants under irradiation with UV light with wavelength shorter than 387 nm [5-7]. In the same way, many POM systems share the same general photochemical characteristics as the semiconductor photocatalysts due to their combination of physical and chemical properties, in terms of molecular and electronic versatility, reactivity, and stability [5]. Zhu xiuhua [8-9] has studied the photocatalytic degradation of dye wastewater with phosphotungstic acid and silicotungstic acid. The photocatalytic reductive of Cr(VI) and organics using polyoxometalates was researched by E. Gkika [10]. Yoon [11] has reported the degradation of methyl orange (MO) in the TiO2 colloid adding to phosphotungstic acid aqueous solution, they found the catalytic activity increased remarkably due to the recombination optical excitation of POMs and TiO2. The most used optical source was high energy ultraviolet which consumed huge amounts of energy sources and needed strict instruments in the previous literature. In this paper, we prepared two catalysts, i.e. silicotungstic acid and phosphotungstic acid, organic dye MO was decomposed under a common metal halide lamp exciting the whole range of wavelength simulating the sun, and their catalysis activity was compared, the factors on the degradation of MO were investigated in detail.

2. Materials and Methods2.1. Materials

All the chemicals in the present work are of analytical grade and used as such without further purification. MO was obtained from Shanghai Reagent 3th Factory, Na2SiO3 ·9H2O was from Tianjing Tianda Chemical Reagent Factory, Na2WO4·2H2O was from Beijing Chemical Factory, Na2HP4·12H2O was from Chengdu Chemical Reagent Factory, H2SO4 was from Kaifeng Dongda Chemical Co. Ltd., HCl was from Xinyang Chemical Reagent Factory, ether was from Tianjin Shentai Chemical Reagent Co. Ltd.; metal halide lamp was obtained from Lianyungang Mantianxing Lighting Electrical Appliance Co. Ltd (power 400 W). All the solutions were prepared with deionized water.

2.2. Preparation of H<sub>4</sub>SiW<sub>12</sub>O<sub>40</sub>·xH<sub>2</sub>O and H<sub>3</sub>PW<sub>12</sub>O<sub>40</sub>·xH<sub>2</sub>O Photocatalyst

H4SiW12O40·xH2O (SiW) was prepared according to the following steps. Frist, 50 g Na2WO4·2H2O and 100 mL deionized water were added into 250 mL three-necked flask, dissolving under vigorously stiring and heating; then 4 g Na2SiO3 ·9H2O was slowly added into the threenecked flask; then, 25 ml HCl was added dropwise with constant voltage dropping funnel in water bath at 95℃ approximately, retaining at least 35 minutes, and continuing to heat 30 minutes; Silicic acid precipitate was got with water pump, transfering the cooling filtrate into separating funnel and adding into ether as the same volume of the filtrate; add dropwise 1:1.5 (V/V) H2SO4 5~10 ml until no extraction liquid dropped. Vibrating sufficiently, the lower levels grease was separated after standing. Extract repeatedly with ether and separate the grease on the evaporation pan (adding into 1~2mL water). Standing 12 hours in the fuming cupboard under room temperature, the white crystal was dried for 2 hours at 70℃; the product was H4SiW12O40·xH2O.

H3PW12O40·xH2O (PW) was prepared according to the following steps. Frist, 50 g Na2WO4·2H2O and 100 mL deionized water were added into 250 mL three-necked flask, dissolving under vigorously stiring and heating; then 11 g Na2HP4·12H2O was slowly added into the three-necked flask. 32 ml HCl was added drop with constant voltage dropping funnel in water bath at 95℃approximately, reacting for 2.5 hours; transfer the cooling reaction liquid into separating funnel and add into 100 mL ether with several times. Vibrating sufficiently, the lower levels grease was separated on the evaporation pan(adding into 1-2mL water). Standing for 12 hours in the fuming cupboard under room temperature, the pale yellow crystal was dried for 2 hours at 70℃; the product was H3PW12O40·xH2O.

2.3. Instruments of Characterization

The catalysts were characterized by various techniques like Fourier Transform Infrared Spectroscopy (FTIR) and X-ray diffraction (XRD). The FTIR spectra were recorded on a Nicolet 6700 FTIR spectrometer (USA) using KBr self-supported pellet technique. The XRD of catalysts were obtained by D8 ADVANCE X-Ray (Brook, Germany) using CuKα radiation from 2θ = 5°~70°.

2.4. Photocatalytic Experiments

The reaction tank is a airtight opaque cuboid iron box with capacity 650 mm × 350 mm × 525 mm. The light source vertically irradiate the reaction liquid with a distance of 140 mm. Cooling water surrounded the reactor to keep the reaction temperature stable.

A certain concentration of MO and a certain amount of catalyst were added into reactor. At given intervals of illumination, a sample of reaction solution was taken out and analyzed by U-3010 UV-Vis (Hitachi, Japan) spectrophotometer.

3. Results and Discussion3.1. Characterization of Catalysts

The range of characteristic absorption peaks of SiW are Si-O 920~928 cm-1; W-O 967~981 cm-1, W-Ob-W 878~ 894 cm-1, W-Oc-W 780~797 cm-1 respectively. There are four characteristic absorption peaks 926 cm-1, 982 cm-1, 883 cm-1 and 789 cm-1 respectively in Figure 1(a).

The range of characteristic absorption peaks of PW are P-O 1080~1081 cm-1, W-O 926~995 cm-1, W-Ob-W 890~900 cm-1, W-Oc-W 805~810 cm-1 respectively. There are four characteristic absorption peaks 1080 cm-1, 985 cm-1, 891 cm-1 and 804 cm-1 respectively in Figure 1(b). The results of spectra of FTIR are the same with the reports of literature basically [12].

The 2θ of XRD strong diffraction absorption peak of SiW are 8o~10o、20o~24o、26o~28o、32o~35o, respectively. The diffraction peak are 8.1o, 23.2o, 25.4o and 34.7o in figure 2(a); The 2θ of strong XRD diffraction absorption peak of PW are 6o~10o, 15o~22o, 24o~30o, 33o~36o. The diffraction peak are 10.3o, 20.7o, 25.3o and 34.6o in figure 2(b). The result proved that SiW and PW possessed Keggin structure [13,14].

3.2. Photocatalytic Activity3.2.1. Control Experiment

A certain of MO was added into reactor, stirring by magnetic force and irradiating under metal halide lamp, at given intervals of illumination, some reaction liquid was taken out to be detected on UV-Vis spectrophotometer.

The spectra of the reaction were superimposed (Figure 3(a)), the absorbance of MO didn’t change when there was no catalyst. It is suggested that MO didn’t decompose without catalyst.

A certain of MO and PW were added into reactor, stirring by magnetic force, at given intervals of illumination, some reaction liquid was taken out to be detected on UV-Vis spectrophotometer. The spectra of the reaction were also superimposed (Figure 3(b)), the absorbance of MO didn’t change when there was no illumination. It is suggested that MO didn’t decompose without illuminetion.

The maximum absorbance wavelength of methyl orange was shifed from 462 nm to 504 nm by comparation of A and B in Figure 3 because the maximum absorbance wavelength of methyl orange will increase in the presence of acid. The catalyst H3PW12O40 is a kind of strong Bronsted acid in this reaction system [15,16].

3.2.2. Choice of Catalysts

Most of the heteropolyacids possessed oxidability, however, they have different oxidability to different compounds. Therefore, it is important to found the appropriate catalyst for the target compound.

A certain of MO was added into two reactors, 50 mg PW and 50 mg SiW were added into respectively, stirring by magnetic force and irradiating under metal halide lamp, at given intervals of illumination, some reaction liquid was taken out to be detected on UV-Vis spectrophotometer. It is observed that (Figure 4) more than 90% of MO was decomposed with PW after 70 minutes, but only 21% of MO was decomposed with SiW after 140 minutes. It is suggested the photocatalytic activity of PW is better than SiW, so PW was chosen for the catalyst to decompose the MO. The result was the same with most literatures [1,15,17].

3.2.3. Effect of Catalyst Amount

It is waste to use too much catalyst and it will hinder the degradation of organic compound [18]. Meanwhile, too little catalyst will decrease the degradation. So, the choice of catalyst amount is important. The PW amounts 10 mg, 20 mg, 30 mg, 40 mg, 50 mg adding into 45 mL 5.56 mg/L MO were investigated for effective MO degradation (Figure 5). It is observed that, increasing

amounts 10 mg~50 mg, the degradation has increased but the increasing extent was smaller when the amount was 40 mg to 50mg. Considering to the practical cost, in the present study, 40 mg, i.e. 8.89 g/L, is found to be the optimum catalyst amount for efficient degradation of MO.

3.2.4 Effect of Original Concentration

The effect of MO concentration is an important parameter for photocatalytic degradation activity over known catalyst amount. The 4.54 mg/L, 5.56 mg/L, 6.52 mg/L, 7.53 mg/L, 10.00 mg/L concentrations of MO were studied with 8.89 g/L PW catalyst amount. It is seen from Figure 6 the degradation was higher when the concentration was lower. However, the degradation of 4.54 mg/L almost was the same with 5.56 mg/L at 70 minutes. According to the practical situation, it is useful to decompose higher concentration wastewater, hence, 5.56 mg/L MO was chosen for the degradation of MO.

3.2.5 Effect of Illumination Time

The effect of illumination time was also an important parameter for photocatalytic degradation activity. The degradation will decrease when concentration decrease and the efficiency is concerned with the illumination time. The illumination time was longer, the efficiency was lower. Figure 7 indicates the increased extend was

decreasing and the MO was almost decomposed entirely after 80 minutes. Hence, the optimum illumination time for degradation of MO is 80 minutes. Many compounds were decomposed entirely more than two hours [19], however, MO was decomposed almost entirely in 80 minutes in this system, it is suggested the catalyst was an efficient catalyst for the degradation of MO.

4. Conclusions

Two kinds of catalysts were prepared, i.e. Silicotungstic acid and phosphotungstic acid, it is suggested that the catalysts possessed classical Keggin structure according to the characterization of FTIR and XRD.

It is found that the photocatalytic degradation activity of PW exceeded SiW according to the degradation of MO under metal halide lamp with the prepared catalysts.

MO was decomposed almost entirely under metal halide lamp with PW, the result revealed that the degradation was up to 93.6% at 8.89 g/L concentration of catalyst, 5.56 mg/L concentration of MO, 80 minutes illumination time. The amount of catalyst was small, illuminetion time was short and the efficency was high. The research indicates that this kind of catalyst is very potential for photo-oxidation organic dye wastewater in industry.

REFERENCESNOTESReferencesM. Q. Hu and Y. M. Xu, “Photocatalytic degradation of textile dye X3B by heteropolyoxometalate acids,” Chemosphere, Vol. 54, No. 3, 2004, pp. 431-434. A. Fujishima and K. Honda, “Electrochemical photolysis of water at a semiconductor electrode,” Nature, Vol. 238, No. 5358, 1972, pp. 37-38. A. Troupis, T. M. Triantis, E. Gkika, A. Hiski and E, Papaconstantinou, “Photocatalytic reductive–oxidative degradation of Acid Orange7 by polyoxometalates,” Ap- plied Catalysis B: Environmental, Athens, Vol. 86, No.1-2, 2009, pp. 98-107. P. Kormali, A. Troupis, T. Triantis, A. Hiskia and E. Papaconstantinou, “Photocatalysis by polyoxometallates and TiO2: A comparative study,” Catalysis Today, Vol. 124, No. 3-4, 2007, pp. 149-155. Y. Yang, Q. Y. Wu, Y. H. Guo, C. W. Hu and E. B. Wang, “Efficient degradation of dye pollutants on nanoporous polyoxotungstate–anatase composite under visible-light irradiation,” Journal of Molecular Catalysis A: Chemical, Vol. 225, No. 2, 2005, pp. 203-212. Y. Q. Wang, L. J. Wang and P. Y. Peng, “Photocatalytic degradation of L-acid by TiO2 supported on the activated carbon,” Journal of Environmental Sciences, Vol. 18, No. 3, 2006, pp. 562-566. I. M. Arabatzis, S. Antonaraki, T. Stergiopoulos, A. Hiskia, E. Papaconstantinou, M. C. Bernard and P. Falaras, “Preparation, characterization and photocatalytic activity of nanocrystalline thin ?lm TiO2 catalyststowards 3, 5-dichlorophenol degradation,” Journal of Photochemistry and Photobiology A: Chemistry, Vol. 149, No. 1-3, 2002, pp. 237-245. X. H. Zhu, W. Wang and H. C. Li, “Photocatalysis of phosphotungstic acid for dye solution degradation,” Shanghai Environmental Sciences, Vol. 20, No. 9, 2001, pp. 444-450. X. H. Zhu, H. C. Li and W. Wang, “Photocatalytic degradation of methyl orange solution with silicotungstic acid,” Journal of Dalian Railway Institute, Vol. 22, No. 1, 2001, pp. 101-104. E. Gkika, A. Troupis, A. Hiskia and E. Papaconstantinou, “Photocatalytic reduction of chromium and oxidation of organics by polyoxometalates,” Applied Catalysis B: En vironmental, Vol. 62, No 1-2, 2006, pp. 28-34. M. Yoon, J. A. Chang, Y. Kim, and J. R. Choi, “Heteropoly acid-incorported TiO2 collids as novel photocatalytic systems resembling the photo-synthetic reaction center,” Journal of Physical Chemistry B, Vol. 105, No. 13, 2001, pp. 2539-2545. S. J. Yang. and H. Y. Tang, “Catalytic synthesis of butanone 1,2-propanediol ketal from phosphotungstic acid/silica,” China Chemicals, No. 5, 2008, pp. 36-38. L. W. Lan, J. Li and Q. Y. Chen, “Photocatalytic Properties for Photocatalytic Water Splitting of H4SiW12O40/ TiO2,” Nonferrous Metals, No. 3, 2009, pp. 35-38. C. Trolliet, G. Coudurier and J. C. Vedrine, “In?uence of the nature and porosity of different supports on the acidic and catalytic properties of H3PW12O40,” Topics in Catalysis, Vol. 15, No. 1, 2001, pp. 73-81. A. Mylonas, A. Hiskia and E. Papaconstantinou, “Contribution to water purification using polyoxometalates aromatic derivatives, chloroacetic acids”. Journal of Molecular Catalysis A: Chemical, Vol. 114, No.1-3, 1996, pp. 191-200. Y. H. Guo and C. W. Hu, “Porous hybrid photocatalysts based on polyoxometalates,” Journal of Cluster Science, Vol. 14, No. 4, 2003, pp. 505-526. A. Mylonas, E. Papaconstantinou and V. Roussis, “Photocatalytic degradation of phenol and p-cresol by polyoxotungstates mechanistic implications,” Polyhedron, Vol. 15, No. 19, 1996, pp. 3211-3217. Y. B. Chen, X. X. Wang, X. Z. Fu and Y.L. Li, “Photocatalytic degradation process of azo dye congo red in aqueous solution,” Chinese Journal of Catalysis, Vol.26, No.1, 2005, pp. 37-42. Y. Yang, Y. H. Guo, C. W. Hu and E. B Wang, “Lacunary Keggin-type polyoxometalates-based macroporous composite ?lms: preparation and photocatalytic activity,” Applied Catalysis A: General, Vol. 252, No. 2, 2003, pp 305-314.