World Journal of Nano Science and Engineering
Vol.05 No.04(2015), Article ID:62069,17 pages
10.4236/wjnse.2015.54018

Titania-Silica Composites: A Review on the Photocatalytic Activity and Synthesis Methods

Yuri Hendrix, Alberto Lazaro, Qingliang Yu, Jos Brouwers

Department of the Built Environment, Eindhoven University of Technology, Eindhoven, The Netherlands

Copyright © 2015 by authors and Scientific Research Publishing Inc.

This work is licensed under the Creative Commons Attribution International License (CC BY).

http://creativecommons.org/licenses/by/4.0/

Received 9 November 2015; accepted 18 December 2015; published 21 December 2015

ABSTRACT

The photocatalyic activity of titania is a very promising mechanism that has many possible applications like purification of air and water [1] -[4] . To make it even more attractive, titania can be combined with silica to increase the photocatalytic efficiency and durability of the photocatalytic material, while lowering the production costs [1] . In this article, relevant literature is reviewed to obtain an overview about the chemistry and physics behind some of the different parameters that lead to cost-effective photocatalytic titania-silica composites. The first part of this review deals with the mechanisms involved in the photocatalytic activity, then the chemistry behind certain methods for the synthesis of the titania-silica composites is discussed, and in the last and third part of this review, the influence of silica supports on titania is discussed. These three sections represent three different fields of research that are combined in this review to obtain better insights on the photocatalytic titania-silica composites. While many research subjects in these fields have been well known for some time now, some subjects are only more recently resolved and some subjects are still under discussion (e.g. the cause for the increased hydrophilic surface of titania after illumination). This article aims to review the most important literature to give an overview of the current situation of the fundamentals of photocatalysis and synthesis of the cost-effective photocatalyic composites. It is found that the most cost-effective photocatalytic titania-silica composites are the ones that have a thin anatase layer coated on silica with a large specific surface area, and are prepared with the precipitation or sol-gel methods.

Keywords:

Photocatalysis, Photocatalytic TiO2, Titania-Silica Composites, Low Cost Synthesis

1. Introduction

Composites made out of silica and titania can have the photocatalytic properties from titania, the high stability from silica and extra properties coming from chemical bonds between the two materials [1] . Titania is photocatalytic because it is able to absorb energy from light, and then use that energy to catalyze the degradation of organic molecules and the oxidation of some inorganic pollutants like nitrogen oxides (NOx) [1] - [12] . As the photocatalytic activity takes place only on the exposed surface area of titania, the amount of titania needed for the same photocatalytic efficiency can be reduced enormously by coating a thin layer of titania on silica [5] [13] - [42] . As the production of silica can be cheaper than that of titania, the costs of the photocatalyic material can then be significantly reduced. In addition to lower production costs, the durability increases as silica has a higher mechanical and thermal stability than titania. So when the composites are used instead of pure titania, the photocatalytic material can be used for a longer time with high photocatalytic efficiencies. In addition, because of the enhanced thermal stability, the photocatalytic material can be used in applications that require higher preparation temperatures. In addition to the lower costs and increased durability, the photocatalytic efficiency of the material can be increased with the addition of silica because silica can have a large specific surface area and is able to adsorb some pollutants and intermediates for a longer time than pure titania.

One promising application of the photocatalytic materials is the degradation of pollutants. The main reasons why using photocatalytic materials for air purification is promising include: lower costs of materials and energy needed than the other current purification methods, the ability of many photocatalytic materials to oxidize pollutants even if they are present in low concentrations, and the fact that the pollutants do not have to be stored but are converted into less harmful side-products (e.g. CO2 from organic molecules and NO3 from NOx after a complete photocatalytic oxidation (PCO)). The photocatalytic titania has been, and is being used in many other applications as well, including: photoelectrolysis of water, medical applications (where titania works as a disinfectant by destroying bacteria and viruses), municipal and industrial wastewater treatment, self-cleaning glass with anti-fogging abilities, and even in textiles that are self-cleaning.

A good method to have air purification is by the incorporation of photocatalytic material in building materials (including: concrete, wallpaper, gypsum and paint [2] -[4] [8] -[10] [43] -[51] ), due to the large illuminated surfaces areas that many building materials have. Investigations into the photocatalytic building materials showed that the concentration of pollutants close to photocatalytic building materials indeed significantly decreased. Since large areas of building materials are often illuminated anyway with sun-light or indoor light and because these building materials become self-cleaning, the maintenance costs of these materials can be very low. Because of the large illuminated area and low maintenance cost, the potential of the photocatalytic building material for air purification is very promising.

However, in most of the research field of the applications of photocatalytic materials, only pure and doped titania are mentioned and not the titania-silica composites despite the large benefits these composites can have (e.g. lower costs, higher durability). An important reason for this absence of composites can be the complexity of the research field of the titania-silica composites. For the synthesis of the titania-silica composites alone, there are many different methods, each with their own parameters that can be changed in multiple ways. As many studies on the titania-silica composites have been done with different goals in mind, many different kinds of titania-silica composites have been produced [1] [5] [13] - [42] [52] - [84] , from which some are either not suitable for photocatalysis or have a very expensive production method. Since the photocatalytic activity of titania alone is already a complex system [3] [4] [6] [11] [85] -[89] , it can be understandable that adding more complexity to the system (for example, with silica) is not desirable. This review is written in order to provide insight on the low cost synthesis of titania-silica composites, and how each different parameter can be tuned to produce highly efficient photocatalytic material to show how the composites can be an attractive alternative to the titania for photocatalytic applications.

2. Photocatalytic Titania

2.1. Mechanism of Photocatalysis

The process of photocatalysis in titania starts when a photon is absorbed by an electron in the valance band of titania [3] [4] [6] [11] [85] -[89] . This electron is then excited to the conduction band, and by doing so, leaves a hole behind in the valance band (reaction 1). The valance and conduction bands of titania have the right energy levels for many important redox reactions. After the excitation of electrons, holes in the valance band have a redox potential of +2.53 V, which is enough for the oxidation of hydroxyl ions into OH (see reaction 2) or the oxidation of adsorbed organic molecules groups. The largest source of hydroxyl ions comes from the dissociation of water (see reaction 3). The redox potential of electrons in the conduction band is −0.52 V, which is strong enough to reduce oxygen to superoxide (see reaction 4). It is also possible that the excited electrons and holes will react with different adsorbed species depending on the environment. For example, if there is a high amount of adsorbed water, it is possible that more radical hydroxyls will form through the reaction of hydrogen peroxide as shown in reaction 5 and 6.

(1)

(2)

(3)

(4)

(5)

(6)

where e is an excited electron in the conduction band, h+ is a hole in the valance band, OH is a radical hydroxyl and is a superoxide. Radical hydroxyls and superoxides are strong oxidants that can react with certain inorganic pollutants like NOx and many organic molecules. In Figure 1, a schematic view is given for the photocatalytic mechanism.

An important property of titania, which influences the photocatalytic efficiency, is the amount of hydroxyl groups in its environment. In turn, the amount of hydroxyl groups is determined by the humidity in air, or the amount of water and its pH in liquids. This amount will determine how many hydroxyl groups will be chemically bonded to the surface of the titania. Bonded hydroxyl groups can either react with holes themselves and form radicals, or adsorb other hydroxyl groups and water molecules which can subsequently react with the holes and excited electrons [90] [91] . The photocatalytic activity in air can thus be higher with a higher humidity. However, it is also possible that a very high humidity will lower the photocatalytic activity by taking up more adsorption sides on the surface. For example, the photocatalytic oxidation of NOx depends on the adsorption to titania and is thus lower with a very high humidity.

2.2. Oxygen Vacancies, Hydrophilicity and Self-Cleaning Surfaces

By reacting Ti4+ and O2− into Ti3+ and O, excited electrons and holes can remain at the surface longer if there are no adsorbed species they can react with directly [3] . Because the difference in charge between titanium and oxygen atoms is then reduced, the oxygen atoms are much less stable and can, with relatively little energy, leave the crystal forming oxygen vacancies. These oxygen vacancies are important in titania for different mechanisms. For example, around an oxygen vacancy there is an excess of electrons, making titania a n-type semiconductor,

Figure 1. Schematic drawing of the photocatalytic activity of titania. 1: The absorption of a photon; 2: The excitation of an electron to the conduction band; 3: The transport of the electron and hole from the initial point to reach the surface of titania where the electron and hole can react with an adsorbed molecule.

which has a higher conductivity than when titania is an intrinsic semiconductor.

Another reason why oxygen vacancies are important is because the surface of titania becomes more hydrophilic when water molecules occupy these oxygen vacancies. After a water molecule occupies the vacancy, one hydrogen atom of the water molecule can react with a neighboring oxygen atom forming two hydroxyl groups [3] . The increase in hydroxyl groups can lead to an increase in photocatalytic efficiency and to an increase in hydrophilicity of the surface. This increase in hydrophilicity, was first reported by Wang et al. [92] in 1997 with a titania coating on glass. By illuminating the coated glass with UV-light, the glass became transparent since the water fog that was present on the glass, defogged as the contact angle between the water droplets and the glass decreased to zero. They also showed that after keeping the hydrophilic surface away from any light source for some days, the glass became more hydrophobic, which means that the formation of a hydrophilic surface is a reversible process. However, it has been reported that oxygen vacancies are not solely responsible for the hydrophilicity, as some studies showed that hydrophilicity was independent in some cases on the number of oxygen vacancies [93] [94] . While it is possible that the degradation of organic materials on the surface can also play a role on the hydrophilicity increase, it nevertheless has been shown not to be a determining factor [95] .

The hydrophilicity and the degradation of organic materials on the surface of titania are two reasons why titania can be used for self-cleaning applications [3] . The degradation of organic materials through photocatalytic oxidation prevents organic substances to accumulate on the surface and can prevent the growth of bacteria and fungi. The hydrophilicity of the surface increases the water adsorption so that it can replace other adsorbed species and it lowers the energy required for water to slide over the surface so that contaminants can be washed off more easily.

2.3. Effect of Different Crystal Forms of Titania on the Photocatalytic Efficiency

Titania has several forms, but the two main crystal structures that most researchers focus on are rutile and anatase [3] . These two crystal forms are both tetragonal structures in which titanium atoms are 6-coordinated in an octahedral formation. The band gap of rutile is 3.0 eV and the band gap of anatase is 3.2 eV. For rutile and anatase to become photocatalytically active, they need to absorb electromagnetic radiation with wavelengths smaller than 413 nm and 387 nm respectively. While rutile is thus able to absorb more light in the visible range, anatase is more photocatalytically active. Luttrell et al. [96] showed this higher photocatalytic efficiency by studying the difference in PCO efficiencies of anatase and rutile thin films of different sizes for the PCO of methyl orange. They showed that for films thinner than 2.5 nm the difference was not significant between the two forms, but for thicker films, the anatase thin film had a higher efficiency. They measured that the maximum thickness, where the photocatalytic efficiency increases with increasing size, is 2.5 nm for rutile and 5 nm for anatase. Thus, from this study it can be concluded that excited electrons and holes in anatase can travel farther than in rutile so that more electrons and holes can reach the surface. The ability of exited electrons and holes to travel longer distances in anatase was contributed to a longer lifetime and higher conductivity [96] - [98] .

An important reason why excited electrons and holes have a longer lifetime and higher conductivity in anatase is because of the differences between the oxygen vacancies that form in anatase and rutile. Oxygen vacancies cause extra energy levels within the band gap. Calculations done by Mattioli et al. [97] showed that oxygen vacancies in an anatase crystal can cause both shallow delocalized energy levels and deep localized energy levels in the band gap, while in rutile only deep localized levels can form. Since anatase has also shallow delocalized energy levels in its band gap, it has a higher conductivity and the excited electrons and holes have longer lifetimes than in rutile as they are less trapped in the deep localized energy levels where the chance of recombination is higher.

While anatase has a high photocatalytic efficiency, amorphous titania has the lowest efficiency [99] . The main reason for this lower efficiency is because, in amorphous titania, there are many spots where recombination of the electron-hole pair can happen. The recombination through defects is the most common way electrons and holes are lost. Thus, amorphous titania has a much higher recombination capacity. In addition, conductivity in amorphous materials is very low since energy levels in amorphous materials are much more localized. The high recombination rate and low conductivity means that only electrons which are excited directly at the surface play a part in the photocatalytic activity in amorphous titania.

Some researchers have measured higher PCO efficiencies in titania that contains both rutile and anatase than in titania with only anatase. Degussa P25 nanoparticles, which are commercial titania nanoparticles made out of around 80% anatase and 20% rutile, are well known for their high photocatalytic activity [100] and are often used as a reference material. The conduction band of rutile has been measured to start at a higher energy level than that of anatase even though its band gap is smaller, which is why titania with both crystal forms can have a higher photocatalytic efficiency [101] . Since electrons always go to a lower energy state if possible, excited electrons in rutile will go to the conduction band of anatase. As electron holes can be viewed as opposite electrons, electron holes in anatase will flow to the valance band of rutile because its top lies above the energy level of the valance band from anatase. Because holes move from anatase to rutile and excited electrons from rutile to anatase, the recombination chance is reduced and a difference in electron density is produced at the interface between the two forms, causing an increase in conductivity and lifetimes for the electrons and holes, resulting in a higher photocatalytic efficiency.

3. Titania-Silica Composite Synthesis

3.1. Silica Sources

Many different types of silica from different sources can be applied as a support for titania including: fumed silica, precipitation silica from alkali silicates, silica produced with the Stöber method, zeolites, clays, glass, silica from the dissolution of silica minerals and more [1] [5] [13] -[42] [52] -[84] [102] - [107] . Fumed silica is formed at high temperatures where silica compounds, like chlorosilanes, are transformed into silica [108] [109] . Silica from alkali silicates is formed by neutralization of the alkali solutions so that the silicate polymerizes to silica and precipitates from the solution. In both fumed silica and precipitated silica, amorphous aggregates are formed. These aggregates can have very large specific surface areas but also have complex undefined structures. Another silica which is often used because of the more defined structure, is silica made with a sol-gel method. The Stöber method [110] is the best known example of a sol-gel method for producing silica. During this method, Tetraethyl orthosilicate (TEOS) is slowly added to a solution of ethanol, water and ammonia. Depending on the composition of the solution, silica colloids of varies sizes and shapes can be formed. The advantage of this silica is that the resulting shape and size of the silica can be well controlled. However, the disadvantage is that this silica has a smaller specific surface area than fumed and precipitated silica. For both well-defined shapes and high specific surface areas, researchers have also used zeolites as support. However compared to the other mentioned supports, the zeolites are more expensive. For very low production costs and a high specific surface area, silica made during the dissolution of olivine has a great potential [111] - [114] but is still in its developing stage.

3.2. Titania-Silica Chemistry

The reaction of titania precursors with silica happens either directly with silanols or indirectly through hydrolysis into titania monomers (Ti(OH)4) first and subsequently by condensation with silanols [1] [5] [13] -[42] [52] - [84] [109] [115] . Either way, the titania will form bonds with the silica through reaction 7.

(7)

where R is a side group of a titania precursor or a hydroxyl group of a titania monomer. The Si-O-Ti bond can be measured by using techniques like infra-red/Raman spectrometry and X-ray photoelectron spectroscopy [14] - [16] [32] - [34] [52] [56] - [60] . This condensation reaction between the titania precursor and the silica surface depends mostly on the hydroxyl groups of the silica [16] [56] [59] [63] [66] [67] since the rest of the silica is very inert. In turn, the amount of hydroxyl groups on the silica is dependent on the temperature during the pretreatment, the method used, and the amount of water and its pH used [67] [109] . For example, if the silica undergoes pre-heating temperatures higher than 800˚C and no water is used during the synthesis, there will be only a low amount of hydroxyl groups on the silica surface left so that only a few titanium atoms can be found on the silica after the reaction [67] . On the other hand, if lower temperatures are used, the density of hydroxyl groups will be high enough on the silica surface that hydrogen bonds between silanols can form. Titania precursors react more with these hydrogen bonded silanols than isolated silanols [66] [67] . These silanols are close enough to each other that a titania precursor can react with multiple hydroxyl groups, making the reaction of hydrogen bonded silanols favorable over the reaction of isolated silanol.

When water is used during the synthesis method of the titania-silica composites, the titania precursor undergoes hydrolysis first. During the hydrolysis, the side groups of the precursor are replaced by hydroxyl groups [116] - [119] . After a full hydrolysis at a neutral pH, Ti(OH)4 is the most common product, as titanium has four valance electrons. Below a pH of 4, the ions and can also be formed [116] [117] . It is also possible that, a double bonded oxygen atom which stays bonded during the hydrolysis, forms during the reaction of the precursor so that only two hydroxyl groups can bond to the titanium. Titanium hydroxides are titania monomers that can form larger titania molecules by polymerization through condensation with other monomers if their concentration is high enough.

3.3. Different Synthesis Methods

There are many different methods to synthesize the titania-silica composites. An indirect way to prepare them is by adding premade titania nanoparticles to a silica support [103] [120] [121] at a pH of around 3 - 4. At that pH, the titania and silica have opposite charges so that the titania and silica will have electrical attraction. However, for more stability and a better homogenous coating, direct methods are often more favorable. The vapor-deposi- tion methods (chemical vapor deposition (CVD) and physical vapor deposition (PVD)), for example, are such methods [5] [23] - [25] [66] - [70] . During the CVD method, the titania precursor is heated to the gas phase to react with dry silica in an inert environment and during the PVD method the titania is sputtered against a support surface for thin films. The impregnation [17] - [22] [52] [59] - [63] and the grafting [52] [64] [65] methods are also direct methods. During both these methods, the titania precursor is dissolved in an organic solvent like toluene or hexane. This solvent is then added to the silica support so that the precursor reacts with the silanols. During the grafting method, the solvent is removed through evaporation and during the impregnation method, the solvent is removed in some other way (e.g. filtration). During the vapor-deposition, the impregnation and the grafting methods, no water is used, which means that these methods do not have the option to form more than one layer of titania in one step, because no new hydroxyl groups can form on the coated titania during the reactions for further condensation. In addition, these methods are not optimal for low cost production since either very high temperatures or expensive organic solvents are required.

Methods that are more promising for low cost photocatalytic materials are the precipitation methods [13] - [16] [52] - [58] and the sol-gel methods [14] [32] - [42] [72] - [84] . These methods are capable of forming more than one monolayer titania on silica, and do not require expensive solvents. During the precipitation method, the titania precursor is dissolved in an aqueous solution with a low pH and low temperatures, where titania does not form. After mixing the aqueous solution containing the precursor with the silica, the solution is either neutralized with an alkaline solution and/or heated up to a specific temperature. This specific temperature depends on the pH and solvent used. By increasing the pH and/or temperature, titania slowly forms, which can be on a silica support for a coating if the hydrolysis is slow enough so that the concentration of titania monomers does not reach the critical supersaturation. Titanium chlorides (TiCl3, TiCl4) and titanium oxysulfate (TiOSO4) are the precursors, which are often used in the precipitation methods. During the sol-gel methods, titanium alkoxides (e.g. titanium isopropoxide, titanium n-butoxide) are often used. To form a titania coating, the precursor is slowly added to a silica dispersion in an organic solvent (ethanol, n-propanol) which contains a low amount of water or to which a low amount of water is added after the precursor is added.

An important parameter in the methods that involves hydrolysis is the pH. Below pH 6, part of the Ti(OH)4 is replaced by, and also by below pH 4. With decreasing pH, more Ti(OH)4 is replaced by the ions which lead to a higher solubility [116] . A higher solubility means that the equilibrium between monomers and condensed titania is then more to the side of the monomers. Thus, when a low pH is used, more precursor is needed for the same amount of the condensated titania, as some of the titania monomers stay dissolved [116] . Since it is mostly the removal of OH groups that lead to the formation of ions, hydrated, amorphous and small sized titania particles are more dissolvable than crystalline titania and titania bonded to larger particles like the silica [122] [123] . The peptizing method, which is a different kind of sol-gel method, uses this constant equilibrium between titania monomers and condensated titania in an aqueous solution and the difference in dissolvability. During this method, hydrated precipitates are first formed in an aqueous solution and then slowly dissolved by reducing the pH to around 2 - 4. Using the Ostwald ripening process, crystalline titania nanoparticles are then formed [122] [123] or coated on a silica support [15] .

Another way to use the sol-gel method for low cost photocatalytic material is by coating a support, like a glass plate, with a thin film using the dip-coating method [124] - [133] . During the dip-coating method, the support is dipped into a stable sol-gel mixture, and is then slowly pulled out of the mixture so that a thin layer of the mixture is adsorbed to the surface. During the drying, a thin titania film is then formed. Polymers (e.g. Poly (ethylene glycol)) can be used to obtain a higher porosity. By adding these large molecules in the sol-gel mixture, large pores are formed during the calcination step, when these molecules are removed.

Another method which is often used for the synthesis of titania-silica composites is the hydrothermal treatment [26] - [31] [71] [72] . The advantage of this method is that it can be used for both the coating step and the crystallization step (which will be discussed in 3.5). This method is done by adding a precursor, a solution containing some water and the silica (or silica source) to an autoclave. The solution is then heated up (e.g. to 200˚C) for both the reaction and crystallization step.

3.4. Controlling the Hydrolysis Rate

For a homogenous coating with the seeded-growth process, the concentration of titanium monomers should not exceed the critical supersaturation, and thus the hydrolysis rate needs to be controlled. In aqueous solutions with a neutral pH, the hydrolysis of titania precursors happens so fast that the concentration of the monomers reaches the critical supersaturation point almost instantly, causing the titania to precipitate randomly in the solution instead of slowly forming on the silica surface.

The most important parameters on which the hydrolysis rate of titania precursors is dependent are: the pH, temperature, concentration of the precursor and of water, and type of precursor used. For example, in an aqueous solution with a pH below 1 and a temperature below 20˚C, no titania will form [13] - [16] [52] - [58] . Having organic liquids (like n-propanol) [134] in the solvent increases the temperature and pH at which the titania is still soluble, because the dielectric constant of the solvent is then decreased. Having a low water content also prevents fast hydrolysis even when no acid is used [34] [81] [134] . However, as each hydrolysis-condensation reaction consumes a water molecule, enough water should be present, to add new hydroxyl groups on the surface of the forming silica-titania composites. Another way to slow down hydrolysis is by reacting the precursors first with molecules, like glycols, which are larger than the side-groups of the precursor. These molecules can replace the side-groups of the precursors [124] [135] if added in excess, so that new, less reactive titania precursors are formed. Depending on the exact method, another important variable is the speed at which a parameter is changed, for example, the change of pH during the neutralization method, the addition speed of a precursor during a sol-gel method and the speed at which the temperature increases during a hydrothermal treatment.

3.5. Transformation to Crystalline Titania

When the hydrolysis rate is very slow during the reaction, thermodynamics plays a more important role than kinetics. Since crystalline titania is more energetically favorable than amorphous titania, crystallization of the titania can then directly happen, especially at a low pH, where the solubility difference between amorphous titania and crystalline titania is larger [122] [134] [136] - [143] . However, the direct formation of crystalline titania is hard to control. If the hydrolysis is too slow, it can result in large rutile crystals with a low specific surface area, which is undesirable for the photocatalysis. In any other case, it is likely that most of the titania is amorphous titania after the reaction. Because amorphous titania has a much lower photocatalytic activity [96] [99] , it can be beneficial to either use calcination or hydrothermal treatment to transform it into anatase.

During the calcination of pure titania, the transformation of amorphous titania to anatase happens at a temperature of about 400˚C and at temperatures above 600˚C the transformation to rutile occurs [143] . At these high temperatures, chemically bonded hydroxyl groups condensate with each other so that more bonds are formed between the titanium and oxygen atoms. Through rearrangements, the crystal structures are then slowly formed. Once a crystal is large enough to be stable, it will further increase in size by taking up more titania atoms, either through more rearrangements, or by merging with other crystals.

Besides the calcination in dry air, it is also possible to use hydrothermal treatment for the formation of crystalline titania [25] - [31] [71] [72] [145] - [149] . Since the formation of crystalline titania takes place in an aqueous environment during a hydrothermal treatment hydroxyl groups are incorporated into the formed structure which can be helpful for the photocatalytic activity. Hydrothermal treatment works at lower temperatures than calcination because the water increases the mobility of the atoms, reduces surface tension of the titania and catalyzes nucleation of crystals [145] - [149] . Wang and Ying [147] showed that using a hydrothermal treatment on amorphous titania, smaller and more stable titania nanoparticles were produced than with calcination.

The exact temperature at which the transformation to either anatase or rutile happens during both calcination and hydrothermal treatment depends on the size of the particles (according to Banfield et al. [144] below a size of 14 nm, anatase is more thermodynamically stable than rutile), the pH and other chemicals (e.g. adsorbed polymers, salts) that can influence the mobility of the atoms [117] [134] [136] [140] [142] . The formation of anatase or rutile from amorphous titania does not start at a single point where all amorphous material crystallizes into anatase or into rutile. By using higher temperatures, more amorphous titania will transform into anatase. However, higher temperatures will also transform anatase into rutile and increase the growth rate of the crystals, which leads to a smaller specific surface area [72] [134] [136] - [143] .

When titania is chemically bonded to a substrate like silica, the substrate stabilizes the different structures of titania, and suppresses the transformation of amorphous titania to anatase and the transformation of anatase to rutile by decreasing the mobility of the titania atoms like an anchor [32] [33] [54] [72] [76] [80] [129] . Thus, higher temperatures are required to form anatase and rutile when titania is coated on silica. While more energy is needed for the formation of anatase from amorphous titania on a support, the anatase that is then formed has a higher thermal stability. It has even been reported that the anatase-rutile transformation only happens in some composites with a high temperature of 1000˚C [54] [129] . The increase in temperature required for the crystalline transformations depends on the thickness of the titania, since a thicker layer is less influenced by the support [54] . For the titania-silica composites, the crystal growth by calcination can cause shrinkage stress when the titania structure shrinks due to the density increase and removal of chemically and physically adsorbed water. As the silica works like an anchor against the shrinkage, stress is produced on the structure which can lead to the breakage of some Ti-O-Si bonds [150] .

4. The Influence of Silica on Photocatalytic Titania in Low Titania Content Composites

Titania-silica composites have more different properties than pure titania than simply a higher stability and a higher specific surface area, especially when the titania content is very low. Many researchers have studied the low titania composites because of these different properties. Anpo et al. [5] were one of the first who studied them. Using the CVD method on a porous silica glass, they found some interesting results which include: 1) below three layers, no anatase could be measured with X-ray diffraction, while it could still be present; 2) the band-gap became larger (4.1 eV) for just a monolayer titania; 3) the titanium was 4-coordinated in a tetrahedral structure instead of the 6-coordinated octahedral structure in pure anatase or rutile; 4) the tetrahedral titania with a large band gap catalyzed different reactions like the decomposition of N2O as will be explained in Section 4.1; and 5) the photocatalytic efficiency per amount of catalyst was much higher for low titania content composites, which will be explained in Section 4.3.

4.1. The Larger Band Gap and Its Influence on the Photocatalytic Activity

The band gap of titania increases when going from bulk anatase to the tetrahedral titania. The normal band gap for crystalline titania is around 3.0 - 3.2 eV, but the measureable band gap from a very low amount of titania on the surface of silica can be much larger [5] [21] [68] [69] [151] [152] . There are two effects responsible for this increase. The first is the quantum size effect, which increases the band gap with decreasing crystal size, when the size is below 2 nm [68] . The second effect is caused by the difference in energy levels of the energy bands from silica and the energy bands from titania, close to the titania-silica interface [1] [21] [68] . Band gaps up to 4.1 eV [5] [69] could be measured due to these two effects. When the band gap becomes larger, electrons require more energy to be excited to the conduction band. For the applications that use sun-light or normal indoor light as the light source, this larger band gap is a disadvantage, since even less of the light spectra can then be absorbed.

On the other hand, the energy that is absorbed is used more efficiently because of the larger band gap. A larger band gap lowers the chance for recombination and increases the redox potentials of the excited electrons and holes. This higher redox potential increases the efficiency of the formation of the radical hydroxyl and superoxides molecules and enables the titania to catalyze different reactions [5] [17] - [20] . For example, Yamashita et al. [18] measured that pure titania transformed NO mostly into oxidized species, while NO decomposed to N2 and O2 in the presence of composites prepared with an ion-exchange method, in which titanium ions replaced silicon ions. In the same system [19] and similar systems with other zeolites [20] , the same observation was made with the reaction of CO2 and H2O. With the ion-exchange composites, methanol was mostly produced while methane was produced by the titania samples. Another example of the difference in catalytic reactions taking place is from a study by Gao et al. [17] who observed that in the presence of tetrahedral titania, methanol reacted to methyl formate (C2H4O2) and formaldehyde (CH2O) while in the presence of octahedral titania, methanol reacted to dimethyl ether (C2H6O). While photocatalytic titania has some potential in reducing the amount of greenhouse gasses in air [153] , these reactions show that the composites have an even greater potential to be useful against climate change.

4.2. Higher Density of Hydroxyl Groups

Binary metal oxides often have better catalytic properties than single metal oxides because they have extra acid sites on their surface in the form of hydroxyl groups [1] [154] . The titania-silica composites are one of those binary systems, and an increase in acid sites has been measured in several different studies [1] [18] [37] [56] [74] [80] [83] . The increase in hydroxyl groups is important for the photocatalytic activity and hydrophilicity as these depend on the amount of hydroxyl groups on the surface. Tanabe et al. [154] made the hypothesis that this increase in hydroxyl groups is caused by the difference in coordination numbers. The coordination number for silicon atoms in silica is 4 and for titanium atoms in crystalline titania it is 6. So when titanium atoms are introduced in, or on silica in low amounts and form the tetrahedral structure, an excess of negative −2 charge per titanium atom is created. This excess charge causes Brönsted acidity on the surface after absorbing enough protons to compensate the charge. Walter et al. [82] showed, using neutron diffraction, that the number of hydroxyl groups is indeed affected when titanium atoms are introduced into the silica structure by the difference in coordination number. They showed an increase in hydroxyl groups mainly caused by the increase in strain in the structure. Liu et al. [74] and Doolin et al. [80] both used the sol-gel method to make titania-rich and titania-poor composites and compared them to pure titania and silica. They measured indeed an increase in Brönsted acidity in the composites especially where there were Ti-O-Si bonds, which was in agreement with Tanabe. However, for the titania-poor composites, the increase in acidity was lower than for titania-rich composites, which is in disagreement with the model of Tanabe. So far, no model has been proposed yet, that explains the extra hydroxyl groups better than the model of Tanebe et al., but these studies about the extra hydroxyl groups do show that the mechanism is related with the Ti-O-Si bond [1] .

4.3. Higher Photocatalytic Efficiency of Low Titania Content Composites

Other researchers [17] [35] [62] [67] [81] [83] found similar results as Anpo et al. [5] on different low titania content composites and these researchers often observed an increase in photocatalytic efficiency per amount of catalyst compared to pure titania. The high efficiencies of these low titania content composites, which do not even have enough titania for a full monolayer, are caused by: 1) the high specific surface area of the silica supports used; 2) the ability of the silica to adsorb many molecules for longer times than titania, especially with the extra hydroxyl groups; 3) the fact that the titania is used more efficiently since all the titania is at the surface; 4) the higher redox potentials of the electrons and holes; and 5) the fact that silica can scatter the light to the titania without being able to absorb its energy. In addition, during the photocatalytic measurements in these studies, UV-light was used. The measurements using UV-light might not represent the applications which use sun-light as the light source, since the decrease of possible light absorption caused by the increase in band gap is less with UV-light.

5. Conclusions

The titania-silica composites are interesting materials because they have the potential to make photocatalytic materials more cost-effective. For the same level of photocatalytic activity, fewer resources have to be invested with the titania-silica composites than with pure titania. The titania-silica composites can, with less and cheaper material, have the same photocatalytic efficiency as pure titania for a longer time since the composites can have a higher photocatalytic efficiency, lower production costs and increased durability. The applications of the photocatalytic material including the applications that degrade pollutants, become then more attractive for companies to produce on a larger scale which can eventually lead to an overall improvement of the quality of air and water.

To obtain this cost-effective photocatalytic material, the titania-silica composites need to be synthesized with a method that has low production costs but still produces composites which have a high photocatalytic efficiency.

・ For a high efficiency, the method needs to deposit an anatase layer with thickness of maximum 5 nm on a large specific surface area. Any layer larger than 5 nm will have titania, which does not contribute to the photocatalysis, since it is too far away from the surface.

・ If some of the crystal structure is rutile instead of anatase, it can have some increase in photocatalytic efficiency because of the separation of holes and electrons at the interface of the two forms. However, the amount of rutile should not be too high, as the lifetime and conductivity of excited electrons and holes in rutile are less favorable than in anatase.

・ When the crystal size is too small, the titania may have an increase in band gap. While it has been reported that such an increase in band gap can cause higher photocatalytic efficiencies, it is important to note that it will make the titania absorb less visible light.

・ The titania should be chemically bonded to a silica substrate which has a large specific surface area, high mechanical and thermal stability as well as low production costs.

・ The most promising methods for low cost photocatalytic composites are the ones that involve hydrolysis (precipitation and sol-gel methods), as these methods ensure that more than one layer of titania can form without the need of expensive materials. However, the hydrolysis of titania precursors can be hard to control. The most important parameters on which the hydrolysis rate is dependent are the pH, temperature, concentration of water and precursor, the speed at which these parameters are changed during the reaction (e.g. by addition of water) and the type of precursor used. How much influence each parameter has on the hydrolysis rate depends on the method used. It is important that the reaction speed of the hydrolysis should be slow enough so that the condensation of titania monomers on the substrate’s surface is more likely to happen than polymerization between monomers.

・ For the transformation of amorphous titania to anatase, calcination or hydrothermal treatment can be applied. The temperature and time required to obtain anatase crystals from amorphous titania depend on the mobility of the titania molecules, which can be influenced by: the chemical bonds to the silica, any nucleated crystals already present, and other chemicals present (e.g. adsorbed polymers, salts). While having more crystalline anatase is beneficial for the photocatalytic activity, crystallization does not always produce materials with a higher photocatalytic efficiency, since during the growth of the crystals, the specific surface area is reduced and anatase can transform into rutile at high temperatures.

When all these points are fulfilled, the resulting titania-silica composites will have the required properties to be a cost-effective material which can compete with pure titania in photocatalytic applications. Even with the increased complexity, the composites are an excellent alternative to pure titania nanoparticles.

Cite this paper

YuriHendrix,AlbertoLazaro,QingliangYu,JosBrouwers, (2015) Titania-Silica Composites: A Review on the Photocatalytic Activity and Synthesis Methods. World Journal of Nano Science and Engineering,05,161-177. doi: 10.4236/wjnse.2015.54018

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