Elsevier

Catalysis Today

Volume 212, 1 September 2013, Pages 75-80
Catalysis Today

Synthesis of solar light responsive Fe, N co-doped TiO2 photocatalyst by sonochemical method

https://doi.org/10.1016/j.cattod.2012.09.014Get rights and content

Abstract

Fe, N co-doped TiO2 photocatalyst has been synthesized by sonochemical method. The as-prepared samples were characterized by XRD, TEM, UV–vis-DRS, XPS, FT-IR and physisorption of N2. Experimental results show that the as-prepared TiO2 photocatalyst has the anatase TiO2 crystalline phase. The band-gap energy absorption edge of Fe, N co-doped TiO2 shifted to longer wavelength as compared to commercial TiO2–P25 and N–TiO2. The specific surface area of the TiO2 was increased to 75 m2 g−1 with the doping of Fe and N ions into the TiO2 framework. The photocatalytic activity of Fe, N co-doped TiO2 for degradation of indigo carmine dye (ICD) under solar simulator was enhanced as compared to TiO2–P25 and N–TiO2.

Highlights

► Sonochemical method is very useful for the synthesis of nanoparticles. ► Visible light active Fe–N–TiO2 photocatalyst was prepared by the sonochemical method. ► N and Fe co-doping on TiO2 lattice significantly red-shifted the UV–vis absorption. ► The Fe–N–TiO2 photocatalyst exhibited good photocatalytic activity on the degradation of indigo carmine under solar light irradiation.

Introduction

Since the discovery of the photosplitting of water on TiO2 electrode by Honda and Fujishima in 1972 [1], TiO2 photocatalyst has been widely applied for the removal of toxic agents in air and water [2], [3], [4]. However, TiO2 photocatalysts operate fundamentally under UV light of wavelengths shorter than 400 nm, which means only 3–5% of solar light can activate these wide band-gap materials [5]. It is, therefore, required to develop a photocatalytic system, which can work even under visible light irradiation. Recently, many studies have been devoted to the modification of TiO2 photocatalysts by the substitutional doping of metals or nonmetals in order to extend their absorption edge into the visible light region and to improve their photocatalytic activity [6], [7], [8], [9], [10], [11]. Among them, metals or nonmetals doping is a practical approach because the properties of the material are largely determined by chemical nature of the atoms or ions and of the bonds between them. The most popular dopants for modification of the optical and photoelectrochemical properties of TiO2 are nonmetal such as N [8], [12], F [13], C [14], S [9], [15] and Cl [16]. On the other hand, doping with metal ions is also a typical approach to extend the spectral response of TiO2 to the visible light region by providing defect states in the band gap [17], [18], [19]. Transition metal ions such as Fe, Cr, Mo, La, V and W have been reported as effective in enhancing visible light photocatalytic activity [20], [21], [22], [23]. Asahi et al. [8], [24] reported that the absorption edge of N-doped TiO2 could be red-shifted to 404 nm and that the N-doped TiO2 had good photocatalytic activity under visible light irradiation. However, due to strongly localized N 2p states at the top of valence band, the photocatalytic efficiency of N-doped TiO2 decreases because isolated empty states tend to trap photogenerated electrons, thereby reducing the photogenerated current [25]. Recently, co-doped TiO2 with two different elements, especially nonmetal and metal elements co-doping has become a rapidly growing field of interest for computational studies. Gai et al. [26] proposed using passivated co-doping of nonmetal and metal elements to extend the TiO2 absorption edge to the visible light range; because the defect bands are passivated, they will not be active as carrier recombination centers [27]. Because TiO2 doped with Fe3+ forms electron or hole traps to reduce the recombination probability of photon generated electron–hole pairs [28].

Sonochemistry has proven to be an excellent method in the preparation of amorphous and crystalline nanosized materials [29], [30]. The collapse of bubbles generates localized hot spots with transient temperatures of above 5000 K, pressure of about 20 MPa, and heating and cooling rates greater than 109 K s−1 [31]. These extreme conditions can obviously accelerate the hydrolysis or condensation reaction.

In the present study, the sonochemical method was used to prepare Fe–N–TiO2 photocatalysts with the assistance of high power ultrasound. The photocatalytic activity of the Fe–N–TiO2 was tested by degradation of indigo carmine dye (ICD) in aqueous model solution under solar light irradiation.

Section snippets

Preparation of the photocatalyst

Nitrogen doped anatase TiO2 crystalline phase was prepared by drop-wise addition method, similar to that used for only N-doped TiO2 reported in a previous paper [32]. An aqueous solution 1 M titanium sulfate (Kanto Chemical 97%) was hydrolyzed by the addition of ammonium hydroxide (J.T. Baker 28%) until the pH of the mixture reached 7. The obtained hydrolysis product was washed with distilled water several times until no SO42 was detected by adding 0.2 M Ba(NO3)2 solution to the washing

Results and discussion

Fig. 1 shows the XRD patterns of the as-synthesized powders. The X-ray diffraction peaks of Fe–N–TiO2 and N–TiO2 photocatalysts are well assigned to the anatase TiO2 crystalline phase (JCPDS 84-1286), no peaks for the rutile and brookite phases were detected. For comparative purpose the XRD pattern of TiO2–P25 is included in Fig. 1, which clearly shows the presence of typical anatase and rutile (JCPDS 21-1276) TiO2 crystalline phases. Further observation shows that with Fe and N doped TiO2, XRD

Conclusion

Visible light active Fe–N–TiO2 photocatalyst was successfully prepared by the sonochemical method. The co-doped TiO2 synthesized nanopowder was Fe and N preserved anatase crystalline phase, and possessed a specific surface area of 75 m2 g−1. The nitrogen and iron are possibly occupied into the TiO2 lattice, replacing some Ti4+ and O2−, respectively and extended the band gap excitation to the visible region. The absorption edge of the doped TiO2 has been red-shifted towards 600 nm The Fe–N–TiO2

Acknowledgements

This research was supported by the Global Research Laboratory (GRL) Program of the National Research Foundation of Korea (NRF) funded by the Ministry of Education, Science and Technology (MEST) of Korea (grant number: 2010-00339).

The use of the infrastructure of LINAN is also acknowledged. We would like to thank Nicolas Cayetano Castro, for their TEM technical assistance.

References (49)

  • A. Fujishima et al.

    Journal of Photochemistry and Photobiology C: Photochemistry Reviews

    (2000)
  • W.J. Ren et al.

    Applied Catalysis B: Environmental

    (2007)
  • T. Ohno et al.

    Applied Catalysis A: General

    (2004)
  • J.G. Yu et al.

    Journal of Solid State Chemistry

    (2005)
  • J.G. Yu et al.

    Applied Catalysis B

    (2009)
  • S. Yuan et al.

    Surface Science and Catalysis

    (2007)
  • K. Bhattacharyya et al.

    Journal of Alloys and Compounds

    (2009)
  • F.J. Ren et al.

    Applied Surface Science

    (2010)
  • S. Ramesh et al.

    Chemical Physical Letters

    (1998)
  • M.H. Zhou et al.

    Journal of Hazardous Materials

    (2006)
  • T. Ihara et al.

    Applied Catalysis B: Environmental

    (2003)
  • M.H. Zhou et al.

    Materials Chemistry and Physics

    (2005)
  • S. Karvinen et al.

    Journal of Molecular Structure: Theochem

    (2003)
  • S. Yin et al.

    Solid State Ionics

    (2004)
  • X. Li et al.

    Powder Technology

    (2011)
  • T. Ohno et al.

    Applied Catalysis A: Chemistry

    (2003)
  • H. Yamashita et al.

    Journal of Photochemistry and Photobiology A: Chemistry

    (2002)
  • K. Honda et al.

    Nature

    (1972)
  • M.R. Hoffmann et al.

    Chemical Reviews

    (1995)
  • M. Anpo et al.

    Research on Chemical Intermediates

    (1987)
  • A.L. Linsebigler et al.

    Chemical Reviews

    (1995)
  • E. Borgarello et al.

    Journal of the American Chemical Society

    (1982)
  • W.Y. Choi et al.

    Journal of Physical Chemistry

    (1994)
  • R. Asahi et al.

    Science

    (2001)
  • Cited by (105)

    • Visible light-responsive photocatalytic-based sustainable construction material for environmental remediation

      2023, Ceramics International
      Citation Excerpt :

      Fig. 5 demonstrates the results calculated for fresh P-25 TiO2 and Fe–TiO2 composite. The diffraction pattern shown in Fig. 5a represents the various rutile (R) and anatase (A) crystalline phases of TiO2 detected at planes 26°, 36°, 55°, and 25.4°, 37.8°, 48°, 55°, 62.6° respectively [107,108]. In addition to the before-mentioned phases of TiO2, a few peaks of iron titanium oxide (ITO) [109], sodium titanium oxide (STO), and silicon titanium oxide (SiTO) were also observed in the composite diffraction pattern.

    • An overview of synthesis techniques for functional photocatalysts

      2023, Advanced Functional Materials and Methods for Photodegradation of Toxic Pollutants
    View all citing articles on Scopus
    View full text