- Research article
- Open Access
Photocatalytic effect of TiO2and the effect of dopants on degradation of brilliant green
© Munusamy et al.; licensee Chemistry Central Ltd. 2013
- Received: 14 February 2013
- Accepted: 18 April 2013
- Published: 22 May 2013
Photocatalysis speeds up the photoreaction in the presence of a catalyst. TiO2 has low toxicity, less resistance and less corrosion and has semiconductor properties. Its strong oxidative potential of the positive holes oxidizes water to create hydroxyl radicals. Moreover, TiO2 has been proven to be a tremendous photocatalyst compound by which many organic substrates have been shown to be oxidatively degraded under UV irradiation. In this research the photocatalytic effect of TiO2 on degradation of Brilliant Green (BG) was studied. In conjunction the effect of dopants such as Zn and Cu on photocatalysis of TiO2 were also studied. Structural and morphological properties of TiO2 were characterized by SEM and XRD. From this research the initial concentration of sample, pH of samples, chemical structure of dyes and catalyst loading were most valuable parameters for dye degradation. TiO2 showed excellent result on degradation of BG compared with doped TiO2. 99% degradation was obtained in presence of TiO2, followed by TiO2/Zn for 87% and TiO2/Cu for 46%. TiO2 doped with transition metals can increase or decrease photocatalytic degradation of dyes.
- UV irradiation
- Brilliant green
Environmental pollutant is the major cause for most of health illness. Water is the main source of contamination and pollution which effects health through biomagnification. Water gets polluted by harmful chemicals, dyes, oils etc. All the wastewater that contains harmful chemicals is drained into nearby water bodies. This causes water pollution and will lead to various health problems to flora and fauna. Among the pollutants of water, dyes play a major role. Most of the dyes released from the pharma and textile industries are mutagenic, toxic and teratogenic that can cause serious health hazards to humans and live stock . Dyes released into environment can impart color to water and also decrease or stop capacity of water reoxygenation by blocking sunlight thereby increasing BOD value. Therefore these conditions can prevent or disturb the growth of aquatic plants and animals [2, 3]. The color removal from wastewater from industries is the main concern in green chemistry . Removal of dyes from wastewater has become a tough issue due to their stable character under harsh condition and biodegradation resistance . There have been reports on usage of natural materials like coconut husk, sunflower stalks, barley husk, lemon peels, rice husk to remove dyes . Advanced oxidation process (AOP) of photocatalysis is really efficient in industrial effluent treatment process with more success rates. Many studies reported that TiO2 nanoparticles are an excellent photocatalysts for decolorization of dyes. TiO2 microparticles are less toxic, less resistance and less corrosive than other photocatalysts [7, 8]. TiO2 oxidation is also known as a type of “green” or environmental friendly method . TiO2 nanoparticles are used extensively because of its intensity and very high refractive index. We used dopants such as Zn and Cu to observe the efficiency of TiO2 microparticles on dye degradation. Doping techniques are used to incorporate metal ions to enhance photocatalytic effects of TiO2 nanoparticles. Metal ions such as Cobalt, Iron, Nickel, Tungsten, Zinc can be incorporated during preparation [10, 11].
BG is also known as Ethanaminium,N-[4-[[4(diethylamino) phenyl] phenylmethylene] -2,5-cyclohexadien-1-yli-dene]-N-ethyl-,sulfate. The chemical formula is C27H34N204S and molecular weight is 482.64 g/mol.BG is chiefly used in modern textile industries. They are also used in staining and biological applications such as large intestine staining, skin staining, to color fibers, printed circuit boards, inks and also used in antiseptic preparation which is active against Gram-positive bacteria. BG will cause some degree of hypersensitivity reactions, carcinogenicity, microbial and fish toxicity . TiO2 nanoparticles has been proven to be a tremendous photocatalyst by which many organic substrates have been shown to be oxidatively degraded and undergoes complete mineralization to give much safer byproduct Carbon dioxide (CO2) under UV exposure . Typically TiO2 nanoparticles are used and studied in the treatment of water such as textile waste water, ground water etc . Numerous studies have been conducted on performance of TiO2 nanoparticles, as they showed that relatively high surface area of catalyst per unit of reactor volume . In aqueous environment, TiO2 generates hydroxyl radicals, which endorse the oxidation of organics under UV irradiation . This has been successfully engaged in the mineralization of several hazardous chemicals such as dyes, phenols, haloaromatics, halogenated biphenyls and more. In this research for the first time TiO2 microparticles alone and TiO2 along with dopants such as Zn and Cu microparticles are used to check the photocatalytic activity for degradation of BG under UV radiation. This photocatalytic reaction takes place at room temperature and the intermediate products are less non-toxic because they are completely mineralized to CO2. Morphological and structural properties are evaluated using SEM and XRD respectively.
Preparation of Titanium dioxide microparticles
15 ml of titanium isopropoxide was transferred into 250 ml beaker and added with 30 ml of distilled water (DW). The contents were stirred for 20 minutes till the contents were clear. 2.2 g of CTAB was transferred into a 100 ml clean beaker and 20 ml of DW was added to it and the contents were stirred for 5 minutes till the solution was clear. The dissolved CTAB was added to the beaker containing titanium isopropoxide. Then, required quantity of NH4OH was transferred dropwise by means of burette into the beaker containing titanium isopropoxide and CTAB. The contents were continuously stirred with the help of magnetic stirrer for 2 hours after addition of NH4OH. After 2 hours, the contents were filtered using Wattman filter paper and precipitate was washed with DW for 10 to 15 times. After sufficient washing, the precipitate was dried in hot air oven for 5 hours at 90°C. The dried powder was annealed at 400°C for 3 hours in a furnace.
Titanium dioxide doped with 1 wt.% Zn microparticles and 1 wt.% Cu microparticles
The preparation was similar to that of TiO2 except that 1wt. % Zn and 1wt. % Cu were dissolved in DW and added to the mixture before adding NH4OH.
Preparation of dye sample and photocatalyst loading
4 ppm of BG was prepared by using DW as solvent. Absorption maximum of BG was determined at 624 nm by using UV–vis double beam spectroscopy (JAS.CO, V-630 model and having power AC100V-240 V, 50/60 Hz, Class 1 protect and made in Japan). 3 aliquots of 4 ppm BG were taken in beakers and in each aliquot 100 mg, 200 mg and 300 mg of TiO2 nanoparticles were suspended (similar procedure for TiO2/Zn and TiO2/Cu nanoparticles). Each aliquot is then subjected to continuous stirring. The reaction is carried out in presence of UV light (30 W). A small portion of sample is withdrawn from each aliquot and centrifuged (Hettich Zentrifugen – EBA 20) at 4000 rpm for 30 minutes. The supernatant solution was used for measuring the absorbance. Absorbance of each sample is measured at a time interval of 5 min, 30 min, 60 min, 120 min and 180 min.
Characterization of TiO2, TiO2/Zn and TiO2/Cu microparticles by using SEM
Photocatalysis of TiO2on Brilliant Green
Initially, the degradation of BG was fast, mostly between 30 min and 60 min. However, the increase of catalyst loading beyond the optimum may result in the agglomeration of catalyst particles, hence the part of the catalyst surface become unavailable for photon absorption and degradation rate decrease. Consequently, at certain minutes 3 g/L catalyst loading shows a slight decrease in further degradation. This may be due to the blockage of UV penetration in sample that lead to decrease in degradation rate. Optimum concentration is essential for efficient decolorization and degradation.
Photocatalysis of TiO2/Zn on Brilliant Green
1 g/L to 3 g/L of TiO2/Zn microparticles were added to 4 ppm BG to determine TiO2/Zn microparticles efficiency in degradation. Catalyst loading of 3 g/L showed better degradation rate than 1 g/L and 2 g/L. In this case, higher the catalyst loading higher the degradation rate. At 3 hours, under UV irradiation sample degradation of 70%, 77% and 87% was observed for 1 to 3 g/L respectively. The effect of Zn as dopant decreased the effect of TiO2 by 13%. The retardation effect of Zn on photodecomposition rate may be attributed to suppression of hydroxyl radicals due to entrapment of conduction band electrons by the adsorbed metal ions.
The presence of metal ions such as Cu2+ and Zn2+, decreased the rate of BG degradation. TiO2 showed an excellent degradation of 99% on BG at 2 hours for a catalyst loading of 2 g/L. whereas, TiO2/Zn showed only 87% with 3 g/L of catalyst loading and TiO2/Cu showed only 46% with catalyst loading of 1 g/L.
Photocatalysis of TiO2/Cu on Brilliant Green
Comparison between TiO2, TiO2/Zn and TiO2/Cu
TiO2 showed excellent result on degradation of BG compared with doped TiO2. 99% degradation was obtained in presence of TiO2, followed by TiO2/Zn for 87% and TiO2/Cu for 46%. TiO2 doped with transition metals can increase or decrease photocatalytic degradation of dyes. The percentage of dopant is necessary to be determined and the optimum % of dopant is between 0.06 and 1.0 for wastewater degradation . In this study TiO2 was doped with 1 wt.% of Zn and Cu. The effect of Zn as dopant decreased the effect of TiO2 by 13%. The retardation effect of Zn on photodecomposition rate may be attributed to suppression of hydroxyl radicals due to entrapment of conduction band electrons by the adsorbed metal ions. The presence of metal ions such as Cu2+ and Zn2+, decreased the rate of BG degradation these results are in accordance with Chiang et al., . Several reasons may be attributed for the effect of decreased activity in presence of dopant which includes nature of dye, pH, sample concentration, concentration of dopant etc.
In this research, a study has been carried out on photocatalytic activity of TiO2, TiO2/Zn and TiO2/Cu microparticles on BG their physical and chemical characterization was done by SEM and XRD. The obtained results comply with that of standard. Photocatalytic effect of unmodified and modified TiO2 nanoparticles were successfully studied in this work. Unmodified TiO2 is a good choice for cationic dye such as BG. The nature and structure of dyes were important parameter to choose a suitable photocatalyst. On other hand, catalyst loading should also be considered as a parameter. For different dyes different catalyst loading is needed. The degradation efficiency of unmodified TiO2 is 99% for BG at 2 g/L of catalyst loading during a period of 120 min under UV exposure.
The authors are grateful to the management of the Masterskill university of health science, Malaysia for promoting research and providing financial support in carrying out this investigation.
- Mekkawy HA, Ali MO, El-Zawahry AM: Toxic effect of synthetic and natural food dyes on renal and hepatic functions in rats. Toxicol Lett. 1998, 95: 155-View ArticleGoogle Scholar
- Song YL, Tai J, Bai B: TiO2-Assisted photodegradation of direct blue 78 in aqueous solution in sunlight. Water Air Soil Pollu. 2010, 213: 311-View ArticleGoogle Scholar
- Wang S: Oxidative degradation of dyes in water using Co2+/H2O2 and Co2+/peroxymonosulfate. Dyes Pigments. 2008, 76: 714-View ArticleGoogle Scholar
- Khehra MS, Saini HS, Sharma DK, Chadha BS, Chimni SS: Comparative studies on potential of consortium and constituent pure bacterial isolates to decolorize azo dyes. Water Res. 2005, 39: 5135-View ArticleGoogle Scholar
- Couto SR: Decolouration of industrial azo dyes by crude laccase from Trametes hirsute. J Hazard Mater. 2007, 148: 768-View ArticleGoogle Scholar
- Elizalde-Gonzailez MP, Pelaiez-Cid AA: Removal of textile dyes from aqueous solutions by adsorption on biodegradable wastes. Environ Technol. 2003, 24: 821-View ArticleGoogle Scholar
- Doll TE, Frimmel FH: Removal of selected persistent organic pollutants by heterogeneous photocatalysis in water. Catal Today. 2005, 101: 195-View ArticleGoogle Scholar
- Tsai WT, Lee MK, Su TY, Chang YM: Photodegradation of bisphenol- A in a batch TiO2 suspension reactor. J Hazard Mater. 2009, 168: 269-View ArticleGoogle Scholar
- Hoffmann MF, Martin ST, Choi W: Environmental application of semiconductor photocatalysis. J Chem Rev. 1995, 95: 69-View ArticleGoogle Scholar
- Tong T, Zhang J, Tian B, Chen F, He H: Preparation of Fe3+−doped TiO2 catalysts by controlled hydrolysis of titanium alkoxide and study on their photocatalytic activity for methyl orange degradation. J Hazard Mater. 2008, 155: 572-View ArticleGoogle Scholar
- The CM, Mohamed AR: Role of Titanium Dioxideand ion-doped Titanium dioxide on photocatalytic degradation of organic pollutants (phenolic compounds and dyes)-A Review. J Alloy Compd. 2011, 509: 1648-View ArticleGoogle Scholar
- Vachálková A, Novotný L, Blesová M: Polarographic reduction of some triphenylmethane dyes and their potential carcinogenic activity. Neoplasma. 1996, 43: 113-Google Scholar
- Fox M, Dulay M: Heterogenous photocatalysis. Chem Re. 1993, 93: 341-357.View ArticleGoogle Scholar
- Sayılkan F, Asilt¨urk M, Tatar P, Kiraz N, Arpac E, Sayılkan H: Photo-catalytic performance of Sn-doped TiO2 nanostructured mono and double layer thin films for Malachite Green dye degradation under UV and vis- lights. J Hazard Mater. 2007, 144: 140-146.View ArticleGoogle Scholar
- Rahman MA, Muneer M: Photodegradation of norfloxacin in aqueous suspensions of titanium dioxide. J Environ Sci Health. 2005, 40: 247-View ArticleGoogle Scholar
- Gnaser H, Huber B, Ziegler C: Encycl. Nanosci. Nanotechnol. Edited by: Nalwa HS. 2004, Los Angeles: American Scientific Publishers, 505-535. Vol.6Google Scholar
- Sohrabi MR, Ghavami M: Photocatalytic degradation of Direct Red 23 dye using UV/TiO2: Effect of operational parameters. J Hazard Mater. 2008, 153: 1235-View ArticleGoogle Scholar
- Concalves MST, Oliveira-Campos AMF, Pinto MMS, Plasencia PMS, Queiroz MJRP: Chemosphere. 1991, 39: 781-View ArticleGoogle Scholar
- Barakat MA, Schaeffer H, Hayes G, Ismat-Shah S: Photocatalytic … Metal ions in photocatalytic systems. Appl. Catal. B Environ. 2004, 57: 23-View ArticleGoogle Scholar
- Pouretedal H, Norozi A, Keshavarz MH, Semnani A: Nanoparticles of zinc sulfide doped with manganese, nickel and copper as nanophotocatalyst in the degradation of organic dyes. J Hazard Mater. 2009, 162: 674-View ArticleGoogle Scholar
- Akpan UG, Hameed BH: Parameters affecting the photocatalytic degradation of dyes using TiO2-based photocatalysts: a review. J Hazard Mater. 2009, 170: 520-View ArticleGoogle Scholar
- Chiang K, Amal R, Tran T: Photocatalytic degradation of cyanide using titanium dioxide modified with copper oxide. Adv Environ Res. 2002, 6: 471-View ArticleGoogle Scholar
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