Enhanced photocatalytic activity in anodized WO3-loaded TiO2 nanotubes

https://doi.org/10.1016/j.spmi.2014.12.008Get rights and content

Highlights

  • TiO2 and WO3-grafted TiO2 nanotubes were grown via single step anodizing of titanium foils.

  • We were able to control morphology and growth mode of TiO2 nanotubes by changing the electrolyte composition.

  • The grafting TiO2 nanotubes with WO3 enhances the photocatalytic activity.

Abstract

In this work, TiO2 and WO3-grafted TiO2 nanotubes were grown via anodizing of titanium substrates in tungstate containing electrolytes. The samples were characterized in detail by XRD, XPS, SEM, EDX, and UV–Vis spectrophotometry techniques. Besides, photocatalytic characteristics were evaluated through measuring the degradation rate of 4-chlorophenol to establish a correlation between structure and photochemical properties. We were able to control morphology and growth mode of nanotubes from a tubular to a worm-like structure by changing the electrolyte composition. The samples possessed an anatase–rutile matrix where the anatase/rutile ratio was found to increase with the concentration of tungstate in the electrolyte. We attributed this observation to change in electrical conductivity of the electrolyte and the heat generated on the substrates. It was unambiguously revealed that a composite of WO3 and TiO2 forms and, in parallel, tungsten is doped into the crystalline lattice of TiO2. The maximum photocatalytic reaction rate constant for TiO2 and WO3–TiO2 samples was determined to be 0.0131 and 0.0174 min−1 respectively. The grafting TiO2 nanotubes with WO3 enhances the photocatalytic activity mainly due to the hindrance of charge carrier recombination and the formation of a more acidic surface. We established a correlation between structure, stoichiometry, and photocatalytic characteristics of nanotubes.

Introduction

The development of photocatalysis has been the focus of considerable attention in recent years with photocatalysis being used in a variety of products across a broad range of research areas, including especially environmental and energy-related fields [1]. Of the many different photocatalysts, TiO2 is one of the most important known photocatalyst materials able to efficiently decompose almost any kind of environmental pollutants due to the position of its valence and conduction bands [2]. TiO2 possesses many advantages and unique functional properties compared with other semiconducting materials, such as low production cost, non-toxicity, self-cleaning property, ready availability, strong photocatalytic activity, and exceptional photo corrosion resistance [3], [4].

It is well known that there are many factors which can exert significant influence on photocatalytic performance, including the size, specific surface area, pore volume, pore structure, crystalline phase, and the exposed surface facets. The construction of TiO2 nano- or micro-structures with interesting morphologies and properties has recently attracted considerable attention [1]. TiO2 materials with one-dimensional structures, such as tubes, possess unique properties and advantages for photocatalytic reactions. In tubes, the higher surface-to-volume ratio enables a reduction in the hole–electron recombination rate and a high interfacial charge carrier transfer rate, with both of these effects being favorable for photocatalytic reactions [1], [5]. Different methods have been developed for synthesizing TiO2 nanotubes. These include sol–gel, microwave irradiation, hydrothermal processing, template synthesis and electrochemical oxidation. Among these, electrochemical anodization is a simple, cost effective and powerful technique that is widely used because it is controllable and reproducible. In addition, this method produces strongly adherent nanoporous TiO2 layer on the substrate, which is more desirable for many practical applications [6], [7], [8]. Following the anodization process, TiO2 nanotube arrays are formed on the foil surface and have straight channels against the foil [1].

However, one of the hindrances to the widespread use of TiO2 as a photoelectrode is the rapid recombination of photogenerated electron–hole pairs [3], [9]. The drawback cannot be overcome by only optimizing the dimensional features of TiO2 nanotubes [10]. It is well known that coupling TiO2 with metal oxides is an approach to improve the photocatalytic activity of TiO2 [11]. Because coupling two semiconductors with different redox energy levels can increase the charge separation for their corresponding conduction and valence bands [12]. Among the different metal oxides, tungsten trioxide (WO3) with the band gap of 2.8 eV, is one of the most important materials to be coupled with TiO2 for the enhancement of photocatalytic activity [11]. The suitable conduction band potential of WO3 allows the transfer of photo-induced electrons from TiO2 by facilitating effective charge separation [10].

Many studies highlighted that the coupling mechanism between WO3 and TiO2 could facilitate better charge separation. However, most of these studies involved WO3–TiO2 photocatalysts in the form of particles or spheres or thin films, and there are only a few studies focused on growth of the 1D highly ordered WO3–TiO2 nanotube arrays. Very recently, WO3–TiO2 nanotubes system have gained considerable attention, and various method such as sol–gel [9], hydrothermal [13], anodization [14] have been followed to incorporate WO3 on TiO2 nanotubes. Lai et al. [3], [10] synthesized TiO2 nanotubes by simple anodization and after that loaded WO3 on nanotubes via wet impregnation and radio frequency sputtering methods. These composite nanotube photo electrodes significantly enhanced their photo electrochemical (PEC) water-splitting performances compared with pure TiO2 nanotube photo electrodes. However, almost all methods using to incorporate WO3 are complicated, and long time is needed for their process. To the best of our knowledge, there is only one literature that synthesized TiO2–WO3 nanotubular composite via single-step anodization, which is done by Smith and coworkers [14]. They reported that the composite material was evaluated for photo electrochemical water splitting and demonstrated a 46% increase in conversion efficiency by incorporating WO3 compared to TiO2 nanotubes prepared under similar conditions. Therefore, more and detail studies are needed to investigate simple process for synthesizing WO3–TiO2 nanotubes and also their photocatalytic performance.

In this study, we report the formation of pure TiO2 and WO3–TiO2 nanotubular composites through a single-step anodization of titanium that exhibit enhanced photocatalytic properties. The samples are characterized in detail employing XRD, XPS, EDX, SEM, and UV–Vis spectrophotometry methods. A paradigm between structure and photocatalytic characteristics of the samples is established.

Section snippets

Experimental

Commercially pure grade II titanium foils were used as substrate. Prior to anodization, substrates were cleaned via a multi-step process including mechanical polishing, chemical etching in diluted HF solution (HF:H2O = 1:20 vol.%) at room temperature for 30 s, and ultrasonic cleaning for 15 min in acetone and ethanol, respectively. The substrates were washed by distilled water in between the steps. As-cleaned samples were clamped on a clip and immersed in the electrolyte and anodized at 20 V for 1 h

Morphology and structure

Fig. 1 shows the top and cross-section views of both pure and WO3 incorporated TiO2 samples where the formation of nanotubes is evident. It can be seen that (Fig. 1(a)) well-aligned TiO2 nanotube arrays with a 75 nm diameter and a 300 nm length have formed. The tubular structure provides superior photocatalytic decomposition of organic pollutant because it provides a large surface area, facilitates the diffusion of organic pollutions into the TiO2 nanotubes, and enhances the absorption yield of

Conclusions

  • 1.

    Pure TiO2 and WO3–TiO2 nanotubes with a diameter of 75 nm and a length of 300 nm were successfully synthesized by single-step anodization of Ti foils.

  • 2.

    It was observed that WO3–TiO2 nanotubes grown in low concentration of tungstate salt had a nanotubular structure like pure TiO2 nanotubes. However, at high concentrations of tungstate salt, the microstructure changed and a worm-like morphology was observed.

  • 3.

    XPS analysis demonstrated that both WO3 and Ti–O–W bonds were formed. Therefore, WO3 not only

References (25)

Cited by (28)

  • Novel TiO<inf>2</inf>-WO<inf>3</inf> self-ordered nanotubes used as photoanodes: Influence of Na<inf>2</inf>WO<inf>4</inf> and H<inf>2</inf>O<inf>2</inf> concentration during electrodeposition

    2021, Surface and Coatings Technology
    Citation Excerpt :

    In addition, its valence and conduction bands are lower than the ones obtained for TiO2, thus avoiding charge recombination [32]. Until the present, various techniques have been proposed to synthetize hybrid TiO2-WO3 nanostructures, such as sol-gel method, hydrothermal, anodization, wet impregnation, radiofrequency spraying, etc. [33]. In this study the fabrication of hybrid nanostructures will be carried out by electrochemical anodization of TiO2 and subsequent WO3 electrodeposition.

  • A study of photocatalytic and photoelectrochemical activity of as-synthesized WO<inf>3</inf>/g-C<inf>3</inf>N<inf>4</inf> composite photocatalysts for AO7 degradation

    2020, Materials Science for Energy Technologies
    Citation Excerpt :

    Additionally, the energy band levels of WO3 are agreeable with conduction band (CB) and valence band (VB) of g-C3N4 to diminish the recombination of photoexcited charge carriers which may help to obtain a high charge separation and also enhance the photocatalytic performance. Nazari et al. has successfully reported on designing of WO3/TiO2 nanotubes, that achieved an enhanced photodegradation of 4-chlorophenol than the pure TiO2 [30]. The monoazo dye acid orange 7 (AO7) was chosen for this work due to its toxic nature and also it is used in various industries of dyeing variety of materials such as nylon, aluminium, detergents, cotton fibers, paper, leather, cosmetics, wool and silk [31,32].

  • Synthesis of BiFeWO<inf>6</inf>/WO<inf>3</inf> nanocomposite and its enhanced photocatalytic activity towards degradation of dye under irradiation of light

    2018, Colloids and Surfaces A: Physicochemical and Engineering Aspects
    Citation Excerpt :

    Among these, water scarcity is prioritized as a crucial issue, as it is commonly being affected by various toxic organic pollutants such as herbicides, pesticides, pharmaceuticals and personal care products from different sources [3–5]. Though, there are various methods available for treating contaminated water, semiconductor based photocatalysis method is recognized as one of the green technique and has fascinated immense consideration due to its potential utilization of solar energy [6–9]. Several photocatalyst candidates with suitable band-energy levels have been considered for photocatalytic degradation of organic dyes with semiconductor based metal oxides [10–12].

  • Metal oxide photocatalysts

    2018, Metal Oxide-Based Photocatalysis: Fundamentals and Prospects for Application
View all citing articles on Scopus
View full text