Reactive red 120 dye degradation over Fe-N-TiO2 photocatalysts by adsorption and reaction under visible irradiation

Main Article Content

อนุธิดา พวงปัญญา
พินิจ กิจขุนทด
กิติโรจน์ หวันตาหลา

Abstract

The aim of this research was to study the improvement of nitrogen titanium dioxide catalysts by doping with iron (Fe-N-TiO2) on degradation performance of reactive red 120 dye under visible light. Fe-N-TiO2 and N-TiO2 catalysts were prepared by hydrothermal method without calcination process. In this work, the catalysts were studied to compare the dye removal efficiency. The catalysts were titanium dioxide with doping 1 percent by weight of iron (1.0%Fe-N-TiO2), without iron doping catalyst (N-TiO2), and commercial catalyst (P25). The physical and chemical properties of catalysts such as crystal structure, crystallite size, morphology, specific surface area, oxidation state of elements, energy band-gap and magnetism value were characterized by X-ray diffraction (XRD), Field emission scanning electron microscope (FESEM), N2-adsorption-desorption, X-Ray photoemission spectroscopy (XPS), UV-vis diffuse reflectance spectroscopy (UV-DRs) and Versalab (VSM), respectively. The results found that N-TiO2 and P25 catalysts were mainly obvious the anatase crystalline phase with small amount of rutile phase. On the other hand, 1.0%Fe-N-TiO2 catalyst was found the decreasing of anatase crystallinity and disappearing of rutile phase. The doping with iron, the smaller anatase crystallite size was observed as about 10-11 nm. The morphology of catalysts prepared by the hydrothermal technique showed nearly spherical shape and nano-size. However, the catalyst with iron doping was obvious in smaller size than that without iron.  The specific surface area of the catalysts calculated by the Brunauer–Emmett–Teller (BET) equation was found that catalyst doping with iron has the highest specific surface area as about 115 m2/g. The oxidation state of iron was indicated in the Fe3+ electronic state. The iron doping (1.0%Fe-N-TiO2 catalyst) can reduce the energy band-gap from 2.94 eV (N-TiO2) to 2.70 eV. Moreover, the magnetism of 1.0%-Fe-N-TiO2 catalyst was about 0.011 emu/gram. The result of the reactive red 120 dye removal in both adsorption and photocatalytic reaction under visible light were found that the efficiency of the 1.0%-Fe-N-TiO2 catalyst was 99% degradation and gave the highest performance as compared with the N-TiO2 and P25 catalysts. It can be concluded that the nitrogen titanium dioxide catalyst modified by iron doping can actually be used to decompose pollutants under visible light.

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บทความวิจัย (Research Article)
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พินิจ กิจขุนทด

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References

[1] Wang C, Wu T. TiO2 nanoparticles with efficient photocatalytic activity towards gaseous benzene degradation. Ceramics International. 2015; 41(2): 2836–2839.
[2] Wu CH. Effects of operational parameters on the decolorization of C.I. Reactive Red 198 in UV/TiO2-based systems. Dyes and Pigments. 2008; 77(1): 31–38.
[3] Naghibi S, Faghihi Sani MA, Madaah Hosseini HR. Application of the statistical Taguchi method to optimize TiO2 nanoparticles synthesis by the hydrothermal assisted sol-gel technique. Ceramics International. 2014; 40(3): 4193–4201.
[4] Liu G, Han C, Pelaez M, Zhu D, Liao S, Likodimos V, et al. Synthesis, characterization and photocatalytic evaluation of visible light activated C-doped TiO2 nanoparticles. Nanotechnology. 2012; 23(29): 294003.
[5] Suwannaruang T, Kamonsuangkasem K, Kidkhunthod P, Chirawatkul P, Saiyasombat C, Chanlek N, et al. Influence of nitrogen content levels on structural properties and photocatalytic activities of nanorice-like N-doped TiO2 with various calcination temperatures. Materials Research Bulletin. 2018; 105(May): 265–276.
[6] Hassan ME, Liu G, Omer EOM, Goja AM, Acharya S. Silver embedded C-TiO2 exhibits improved photocatalytic properties with potential application in waste water treatment. Arabian Journal of Chemistry. 2018; 0–6.

[7] Komatsuda S, Asakura Y, Vequizo JJM, Yamakata A, Yin S. Enhanced photocatalytic NOx decomposition of visible-light responsive F-TiO2/(N,C)-TiO2 by charge transfer between F-TiO2 and (N,C)-TiO2 through their doping levels. Applied Catalysis B Environmental. 2018; 238(July): 358–364.
[8] Gar Alalm M, Samy M, Ookawara S, Ohno T. Immobilization of S-TiO2 on reusable aluminum plates by polysiloxane for photocatalytic degradation of 2,4-dichlorophenol in water. Journal of Water Process Engineering. 2018; 26(November): 329–335.
[9] Jaiswal R, Bharambe J, Patel N, Dashora A, Kothari DC, Miotello A. Copper and Nitrogen co-doped TiO2 photocatalyst with enhanced optical absorption and catalytic activity. Applied Catalysis B Environmental. 2015; 168–169: 333–341.
[10] Selvaraj A, Sivakumar S, Ramasamy AK, Balasubramanian V. Photocatalytic degradation of triazine dyes over N-doped TiO2 in solar radiation. Research on Chemical Intermediates. 2013; 39(6): 2287–2302.
[11] Ansari SA, Khan MM, Ansari MO, Cho MH. Nitrogen-doped titanium dioxide (N-doped TiO2) for visible light photocatalysis. New Journal of Chemistry. 2016; 40(4): 3000–3009.
[12] Barkul RP, Koli VB, Shewale VB, Patil MK, Delekar SD. Visible active nanocrystalline N-doped anatase TiO2 particles for photocatalytic mineralization studies. Materials Chemistry and Physics. 2016; 173(January): 42-51
[13] Asahi R, Morikawa T, Irie H, Ohwaki T. Nitrogen-doped titanium dioxide as visible-light-sensitive photocatalyst: Designs, developments, and prospects. Chemical Reviews. 2014; 114(19): 9824–9852.
[14] Razali NA, Othman SA. Synthesis and Characterization of Nitrogen Doped with Titanium Dioxide at Different Calcination Temperature by using Sol-Gel Method. Journal of Science and Technology. 2017; 9(3): 124–130.
[15] Majeed Khan MA, Siwach R, Kumar S, Alhazaa AN. Role of Fe doping in tuning photocatalytic and photoelectrochemical properties of TiO2 for photodegradation of methylene blue. Optics and Laser Technology. 2019; 118(March): 170–178.
[16] Hinojosa–Reyes M, Camposeco–Solis R, Ruiz F, Rodríguez–González V, Moctezuma E. Promotional effect of metal doping on nanostructured TiO2 during the photocatalytic degradation of 4-chlorophenol and naproxen sodium as pollutants. Materials Science in Semiconductor Processing. 2019; 100(December 2018): 130–139.
[17] Jaihindh DP, Verma A, Chen CC, Huang YC, Dong CL, Fu YP. Study of oxidation states of Fe- and Co-doped TiO2 photocatalytic energy materials and their visible-light-driven photocatalytic behavior. International of Journal Hydrogen Energy. 2019; 15892–15906.
[18] Karafas ES, Romanias MN, Stefanopoulos V, Binas V, Zachopoulos A, Kiriakidis G, et al. Effect of metal doped and co-doped TiO2 photocatalysts oriented to degrade indoor/outdoor pollutants for air quality improvement. A kinetic and product study using acetaldehyde as probe molecule. Journal of Photochemistry Photobiology A Chemistry. 2019; 371(November 2018): 255–263.
[19] Moradi H, Eshaghi A, Hosseini SR, Ghani K. Fabrication of Fe-doped TiO2 nanoparticles and investigation of photocatalytic decolorization of reactive red 198 under visible light irradiation. Ultrasonics Sonochemistry. 2016; 32: 314–319.
[20] Khan H, Swati IK. Fe3+-doped Anatase TiO2 with d-d Transition, Oxygen Vacancies and Ti3+ Centers: Synthesis, Characterization, UV-vis Photocatalytic and Mechanistic Studies. Industrial Engineering Chemistry Research. 2016; 55(23): 6619–6633.
[21] Rivera KKP, de Luna MDG, Suwannaruang T, Wantala K. Photocatalytic degradation of reactive red 3 and alachlor over uncalcined Fe–TiO2 synthesized via hydrothermal method. Desalination and Water Treatment. 2016; 57(46): 22017–22028.
[22] Zou M, Xiong F, Ganeshraja AS, Feng X, Wang C, Thomas T, et al. Visible light photocatalysts (Fe,N) : TiO2 from ammonothermally processed, solvothermal self-assembly derived Fe-TiO2 mesoporous microspheres. Materials Chemistry and Physics. 2017; 195: 259–267.
[23] Aphairaj D, Wirunmongkol T, Niyomwas S, Pavasupree S, Limsuwan P. Synthesis of anatase TiO2 nanotubes derived from a natural leucoxene mineral by the hydrothermal method. Ceramics International. 2014; 40(7 PART A): 9241–9247.
[24] Suwannaruang T, Wantala K. Single-step uncalcined N-TiO2 synthesis, characterizations and its applications on alachlor photocatalytic degradations. Applied Surface Science. 2016; 380(January): 257–267.
[25] Xu C, Zhang Y, Chen J, Lin J, Zhang X, Wang Z, et al. Enhanced mechanism of the photo-thermochemical cycle based on effective Fe-doping TiO2 films and DFT calculations. Applied Catalalysis B Environmental. 2017; 204(December 2018): 324–334.
[26] Yao Y, Sun M, Yuan X, Zhu Y, Lin X, Anandan S. One-step hydrothermal synthesis of N/Ti3+ co-doping multiphasic TiO2/BiOBr heterojunctions towards enhanced sonocatalytic performance. Ultrason Sonochem. 2018; 49(May): 69–78.
[27] Fiorenza R, Bellardita M, Scirè S, Palmisano L. Effect of the addition of different doping agents on visible light activity of porous TiO2 photocatalysts. Molecular Catalysis. 2018; 455(May): 108–120.
[28] Yun HJ, Lee DM, Yu S, Yoon J, Park HJ, Yi J. Effect of valence band energy on the photocatalytic performance of N-doped TiO2 for the production of O2 via the oxidation of water by visible light. Journal Molecular Catalysis A Chemical. 2013; 378(November 2013): 221–226.
[29] Safari M, Talebi R, Rostami MH, Nikazar M, Dadvar M. Synthesis of iron-doped TiO2 for degradation of reactive Orange16. Journal of Environmental Health Science Engineering. 2014; 12(1): 1–8.
[30] Sood S, Umar A, Mehta SK, Kansal SK. Highly effective Fe-doped TiO2 nanoparticles photocatalysts for visible-light driven photocatalytic degradation of toxic organic compounds. Journal of Colloid and Interface Science. 2015; 450: 213–223.
[31] Kalantari K, Kalbasi M, Sohrabi M, Royaee SJ. Enhancing the photocatalytic oxidation of dibenzothiophene using visible light responsive Fe and N co-doped TiO2 nanoparticles. Ceramics International. 2017; 43(1): 973–981.
[32] Thommes M, Kaneko K, Neimark A V, Olivier JP, Rodriguez-reinoso F, Rouquerol J, et al. Physisorption of gases , with special reference to the evaluation of surface area and pore size distribution. IUPAC Technical Report. 2015;87:1051–1069.
[33] Suwannaruang T, Kidkhunthod P, Chanlek N, Soontaranon S. Applied Surface Science High anatase purity of nitrogen-doped TiO2 nanorice particles for the photocatalytic treatment activity of pharmaceutical wastewater. Applied Surface Science. 2019; 478(October 2018): 1–14.
[34] Zhang K, Wang X, Guo X. Preparation of highly visible light active Fe–N co-doped mesoporous TiO2 photocatalyst by fast sol–gel method. Journal of Nanopartical Research. 2014; 16(2): (1-9)
[35] Abbas N, Shao GN, Haider MS, Imran SM, Park SS, Kim HT. Sol–gel synthesis of TiO2-Fe2O3systems: Effects of Fe2O3 content and their photocatalytic properties. Journal of Industrial and Engineering Chemistry. 2016; 39(2016): 112-120
[36] Liang R, Shen L, Jing F, Qin N, Wu L. Preparation of MIL−53 (Fe)−Reduced Graphene Oxide Nanocomposites by a Simple Self−Assembly Strategy for Increasing Interfacial Contact: Efficient Visible-Light Photocatalysts. Applied Materials Interfaces 2018; 53(April 2015): 9507-9515.
[37] Moura KO. Tuning the surface anisotropy in Fe-doped NiO nanoparticles. The Royal Society of Chemistry 2013; 6(November): 352-357.
[38] Bharti B, Kumar S, Lee H, Kumar R. Formation of oxygen vacancies and Ti3+ state in TiO2 thin film and enhanced optical properties by air plasma treatment. Nature Publishing Group. 2016; (August): 1-12.