Review Topical Sections

Titania based nanocomposites as a photocatalyst: A review

  • Titanium dioxide or Titania is a semiconductor compound having remarkable dielectric, electronic and physico-chemical surface properties. It has excellent photocatalytic efficiency in presence of UV light. The curious grey matter of scientists has forced them to focus their attention to make Titania capable of utilizing the whole visible spectrum of light also. The hurdle that they faced was larger band gap of 3 eV and more, for this, efforts were directed towards adding other materials to Titania. The present article reviews the recent advances in the synthesis of different Titanium-based nanocomposite materials and their photocatalytic efficiency so as to apply them for several applications such as removal of dyes, other water pollutants, microbes and metals. A brief explanation of the photocatalytic process and the structural properties of TiO2 are also touched upon. Various past and recent approaches made in these directions of utilizing Titania based nanocomposites for photocatalytic activities are reviewed. It is suggested that there is a need to establish the kinetics of photo-corrosion and thermodynamic part of the photo-corrosion of various composites developed by different group across the globe, so that Titania based nanocomposites could be commercially utilized.

    Citation: Madhuri Sharon, Farha Modi, Maheshwar Sharon. Titania based nanocomposites as a photocatalyst: A review[J]. AIMS Materials Science, 2016, 3(3): 1236-1254. doi: 10.3934/matersci.2016.3.1236

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  • Titanium dioxide or Titania is a semiconductor compound having remarkable dielectric, electronic and physico-chemical surface properties. It has excellent photocatalytic efficiency in presence of UV light. The curious grey matter of scientists has forced them to focus their attention to make Titania capable of utilizing the whole visible spectrum of light also. The hurdle that they faced was larger band gap of 3 eV and more, for this, efforts were directed towards adding other materials to Titania. The present article reviews the recent advances in the synthesis of different Titanium-based nanocomposite materials and their photocatalytic efficiency so as to apply them for several applications such as removal of dyes, other water pollutants, microbes and metals. A brief explanation of the photocatalytic process and the structural properties of TiO2 are also touched upon. Various past and recent approaches made in these directions of utilizing Titania based nanocomposites for photocatalytic activities are reviewed. It is suggested that there is a need to establish the kinetics of photo-corrosion and thermodynamic part of the photo-corrosion of various composites developed by different group across the globe, so that Titania based nanocomposites could be commercially utilized.


    In the medical field, it is of interest in measuring the uptake of certain fluids that are indicators of corresponding complications. One way to do so is placing a scaffold on the spot where those biological fluids may be present. Such scaffolds are typically of porous nature and may contain also nanoparticles for structure reinforcement. The porous scaffolds have their own properties depending on the porosity and nanoparticle content, besides the scaffold itself. The properties in question may be of thermal, electrical or mass diffusional nature. When the scaffold absorps some biological fluid, it is natural to say that this changes the aforementioned properties. We are interested here by the thermal properties. By introducing thermal pulses of high frequency on one side of such a porous scaffold and measuring the response on the other side, one is able to deduce from the response whether some biological fluid has been taken up. Since many factors may play a role in such an analysis, modelling can provide for useful tools that can be used to compose such sensors. It is well known that Fourier's law is not valid for high pulse responses. For information from biosensors in case of continuous monitoring, other models should be proposed. We propose a model that can be used for such purposes concerning a porous medium, in which nanoparticles are dispersed. Besides the model representing the evolution of the heat flux and the temperature, we need also a model that describes how the thermal diffusion through the porous medium is affected by the biological fluid uptake. We propose to do this by using an effective thermal conductivity, adapted from [1,2]. This effective thermal conductivity is valid at the condition that the thermal conductivity of the scaffold is much higher than that of air and the nanoparticles. This is justified since we use as scaffold a medium self-assembled from carbon nanotubes (CNT), wherein silica (SiO2) nanoparticles are embedded for reinforcement and alignment of the CNTs for a better conductivity [3]. The fabrication process and characterisation of this scaffold has been presented in previous work [3]. Since it is important to use a correct effective thermal conductivity, we validate this against experiments of self-assembled CNT-SiO2 porous nanocomposites.

    The self-assembly procedure is applied in various forms in many fields [4,5,6,7,8,9,10,11,12]. The one against which we validate the effective thermal conductivity is explained in details in [3]. Essentially it resumes to the following. By using drop-by-drop evaporation of aqueous solutions of CNT and SiO2, we deposit multiple self-assembled layers of CNTs and SiO2 on a substrate. The obtained dry residu is a porous structure that, depending on the initial parametric conditions, can have different properties. As mentioned before, the focus is on the thermal conductivity. The porosity of the scaffolds and the volume fraction of the nanoparticles are also determined from those experiments. The data are imported in our model, leading to a heat flux and temperature evolution depending on the porosity and volume fraction of the scaffold medium. Since in the model used for the effective thermal conductivity, the thermal conductivity of air and the nanoparticles are considered to be negligible with respect to that of CNT, it is solely dependent on the porosity and nanoparticles. The biological fluid that is being taken up in the scaffold has also a thermal conductivity negligible to that of CNT, so that it can be treated on the same level as the nanoparticles. So, an uptake of the biological fluid is equivalent to an increase of the volume fraction of nanoparticles in the scaffold. The idea is to impose high-frequency temperature pulses and calculating their response at the other side. By varying the volume fraction, one is able to calculate the response to a fixed heat pulse, being indicative of measuring biological fluid intake. Our model is developed in section 2 and the experimental data needed for the model in section 3. Section 4 discusses the results and section 5 concludes.

    A previously developed model from Extended Thermodynamics proposes constitutive equations for the thermal transport taking into account non-localities [13]. In case the system size is much larger than the mean free path of the thermal carriers, a one-dimensional version of the constitutive equation for the heat flux, q can be given by

    τrtq+q=λeffxT (1)

    where τr,t,x,λeff and T are the relaxation time of the heat flux, the time and space coordinates, the effective thermal conductivity and the temperature, respectively. The one-dimensional balance equation for energy is

    ρcptT=xq (2)

    with ρ and cp the density and heat capacity, respectively. In (1)-(2), the thermal conductivity for a porous structure is given by [2,14].

    λp=λ022ε2+ε. (3)

    where λ0 denotes the thermal conductivity for the bulk material, and ε stands for its porosity. If nanoparticles are homogeneously inserted in such a porous matrix (for instance, by depositing a droplet containing a mixture of CNTs and nanoparticles) then, for the thermal conductivity, (3) should be adapted:

    λeff=λp22φ2+φ=λ022ε2+ε22φ2+φ, (4)

    where λp=λ022ε2+ε is the volume fraction of the nanoparticles. Note that in (3)-(4), simplifications are introduced with respect to [2,14], because of the much higher thermal conductivity of CNT with respect to air and even with respect to the silica nanoparticles. The difference in the phonon relaxation times of CNTs, SiO2 and biological fluids being less important here than the difference in thermal conductivity, we will assume that its dependence on the volume fraction is negligible, so that:

    τr=τr0 (5)

    with τr0 the relaxation time of the bulk material. For computational purposes, our model is rendered dimensionless. We choose for the time scale τr0, for the spatial scale the system's size δ, for the heat flux λ0ΔTδ, and for the temperature TTT0ΔT. Herein, ΔT=TiT0, where the subscripts i and 0 indicate a maximum and minimum temperature to which the material is exposed to. In case there is an imposed oscillatory boundary temperature, Ti would stand for the peak maximum temperature and T0 for the peak minimum temperature, which is also chosen to be the initial one. This gives for heat transport, writing the same symbols for the dimensionless quantities, the following set of equations

    tq+q=22ε2+ε22φ2+φxT (6)
    tT=αthxq (7)

    with αth=τr0τth, the thermal diffusion characteristic time being defined by τth=δ2κth, with κth=λ0ρcp the thermal diffusivity. The boundary conditions are given by a zero-heat-flux condition, i.e. q = 0 (which means a zero-temperature-gradient in virtue of (1)) at the measuring point (x = 0) and an imposed oscillatory temperature at the other side (x = 1), with frequency ω=P/τr0, where P is a value determining the periodicity of the oscillations with respect to the relaxation time. The dimensionless versions are

    xT|x=0=0 (8)
    T|x=1=12(1cos(2Pπt)) (9)

    For convenience, the form of boundary condition (9) has been chosen as such to assure a positive value of T for all t.

    This section presents experimental data, which will serve in section 4 to validate the model for the effective thermal conductivity as a function of the porosity for a certain determined fixed volume fraction of dispersed nanoparticles.

    The process of the drop-deposition experiment is described by the deposition of droplets that contain nanomaterial, letting them evaporate at room temperature and ambient humidity (60% humidity) for seven hours. The duration of the process was needed not so much to evaporate the droplets as such, but rather to evacuate the water that is held back in the pores due to the capillary pressure, since the deposited nanomaterial creates a nano-porous network. The droplets, used for the depositions, contain a mixture of CNTs and SiO2 nanoparticles. The 3 g/L aqueous 5 nm multi-walled CNT dispersion has been supplied by Nanocyl and the 0.3 g/L aqueous 175 nm SiO2 has been supplied by Bangs-Laboratories. The CNT solutions are kept in homogeneous dispersion by the presence of anionic surfactants, which guarantee a long-lasting stable homogeneous aqueous dispersion of the CNTs. As for the SiO2 solutions, they are found to remain in a stable homogeneous aqueous dispersion due to Si-OH surface groups. As recommended by the fabricants, the aqueous solutions are sonicated before depositing the droplets. The position of the droplet is controlled by a motor with a precision of 0.01 mm. Each droplet is deposited by a syringe on a spot that is delimited by a groove, which creates pinning conditions. This results into 40 µL droplets with a diameter of 12 mm. The drop deposition setup has been developed in the lab (Physical Chemistry Group) and is made of a bi-dimensional translation stage (Moons STM17S-1AE) and a home-made double syringe pump using the same motorized stages. The software drives automatically the setup and acquires images of the drop after each deposition (camera JAI BM-500GE) to control the volume of the drop. As soon as the droplets are deposited, the start to evaporate, which induces convectional instabilities. The CNTs and SiO2 nanoparticles move along the flow lines. After the fluid has evaporated, the nanoparticles and CNTs settle on the substrate, forming a porous nanostructure.

    The porosity of the matrix is defined as

    ε=VpVtVnp=1VmVtVnp=1(Nd+1)cmVdρmπr2mδmNdCnpVdρnp (10)

    where Vp, Vm and Vnp are the pore volume (air in our case), the volume occupied by the matrix (CNT) and the volume occupied by the nanoparticles (SiO2), respectively (note that the total volume is Vt = Vp+Vm+Vnp). Moreover, Cm is the matrix material concentration in the deposited droplet (Cm = 3 g/L), Cnp is the silica concentration in the deposited droplet (Cnp = 0.3 g/L), ρm the CNT "tap" density (ρm = 1.6 kg/L), ρnp the silica density (ρnp = 2.65 kg/L) and Vd the volume of each deposited droplet (Vd = 40 µL). The term Nd+1 in (10) stands for the fact that before depositing the CNT-SiO2 mixtures, one layer of pure CNT is deposited [3]. The calculated porosity presents an error of less than 0.5% and is presented in Table 1 as a function of the number of deposited droplets. Furthermore, in (10), δm and rm are the thickness of the deposited material and the radius, respectively. The radius is measured to be rm = 6 mm and δm is measured by means of a confocal probe [3] and also given in Table 1.

    Table 1.  Calculated ε and δm as a function of Nd.
    Nd 1 2 3 4 5 6 7
    ε 0.83 0.83 0.85 0.84 0.82 0.80 0.81
    δmm] 8.0 11.9 18.1 20.9 22.3 24.0 28.0

     | Show Table
    DownLoad: CSV

    The volume fraction of the nanoparticles used in the aforementioned material can be calculated via

    φ=CnpρnpρmCm+Cnp (11)

    which gives φ = 0.057.

    Since it is quite difficult to find the exact values for λ0, they will be taken from experimental findings from [3] of pure CNT depositions. It is found that for a pure monolayer nanoporous CNT, λp = 0.88 kW/Km. With a porosity (calculated from data from [3], with a droplet volume of 45 µL and using Eq (10) with Nd = 2 and δm = 20 µm) of ε = 0.85, we find easily from Eq (3) as approximation that λ0 = 8.4 kW/Km (which is, taking into account experimental uncertainty, not far from the 6600 W/Km found in the literature [14].

    The deposited nanostructures, for several number of deposited droplets (see Table 1), are measured for their effective thermal conductivity, λexp. The results are presented in Table 2.

    Table 2.  Measured thermal conductivities.
    Nd 1 2 3 4 5 6 7
    ε 0.83 0.83 0.85 0.84 0.82 0.80 0.81
    λ|| [kW/Km] 0.88 0.89 0.93 0.89 0.96 1.00 0.98

     | Show Table
    DownLoad: CSV

    Table 2 shows that, in overall, the thermal conductivities increase, with an overall decreasing porosity, which suggests indeed that a denser structure is obtained, which can be explained by a better alignment of CNTs. In general, a composite structure that becomes denser than the CNT structure, would lead to a relative increase of the thermal conductivity with respect to its initial value. As for the alignment of the CNTs, this is confirmed by SEM images in [3] and is not the subject of the present work. In general, as the degree of alignment of CNTs is higher, the thermal conductivity should increase in the axial direction of the nanotubes.

    For practical purposes (applications as biosensors, batteries, rather than insulators, semi-conductors), the interest lies more into the conductivities in the longitudinal direction of the CNTs. For a preferred substrate direction, even though the CNTs are not perfectly aligned, the longitudinal axis of the majority of the CNTs will still be in that preferred direction. The experimental data used for this purpose are taken from section 4.1. Nevertheless, for the sake of completeness, important details are represented next. With our model, the effective thermal conductivities are calculated from the model in section 2 and compared to the experimental values. The results are presented in Figure 1.

    Figure 1.  Effective thermal conductivity of the porous SiO2-CNT nanocomposite as a function of porosity. Squares are the experimental results from Table 2 and the lines represent our model.

    Figure 1 shows a good agreement between the model and the experiments, showing that a lower porosity corresponds to higher thermal conductivities. The results confirm the validity of the model for the effective thermal conductivities for the purposes of this work.

    In the expression of the thermal characteristic time, the thermal conductivity is that of the bulk material (i.e. λ0 = 6600 W/(Km)), whilst the density and heat capacity are those of the porous medium. Taking a volume-fraction-based weighted average (the densities of CNT and air are 1600 and 1.2 kg/m3, respectively, whilst the heat capacities of CNT and air are 620 [16] and 1005 J/(kgK), respectively), noting that the porosity is defined on volume basis and that ε = O(0.85), we find ρ = 241 kg/m3 and cp = 947 J/(kgK). The relaxation time for a CNT-SiO2 system is given in [17] to be τr0 = 85 ps. Taking for the thickness a value of the same order of magnitude as Table 1, let us say δ = O(10) µm, we find a thermal characteristic time of τth = 31 ns. This gives αth≈2.5*10-2. For this value, our model is used for the calculations by means of the programme Mathematica. Figure 2 shows a 3D example for φ = 0.057.

    Figure 2.  Temperature T across the one-dimensional porous nanocomposite layer x as a function of time t for αth≈2.5*10-2, φ = 0.057 and P = 0.5.

    Figure 2 shows that the oscillations at x = 1 (not clearly visible, because the period of the temperature oscillations is equivalent to 2t on a scale of 400t in the Figure) are quickly damped. This is due to the relaxation time being much smaller than the thermal diffusion time. Furthermore, this damping also results into a delayed response, due to the presence of a relaxation time in se. The temperature at the other side increases to a value equal to the mean value of the oscillatory temperature, i.e. T = 0.5. In order to visualize this more, it is more convenient to plot the response temperature (i.e. T at x = 0) as a function of time. We do this for four values of φ = 0.057, 0.1, 0.2 and 0.5. The results are presented in Figure 3.

    Figure 3.  Temperature T at x = 0 as a function of time t for αth≈2.5*10-2 and different values of the volume fraction φ (the volume fraction of the biological fluid uptake is given by φb = φ-0.057).

    Note that the volume fraction for the biological uptake is given by φb = φ-0.057. So, φ = 0.057 is the reference state (the value corresponding to the silica nanoparticles), where no biological fluid has been taken up yet. We can see indeed that no oscillations are present (fully damped) and that the uptake of the biological fluid (φ > 0.057) results into a decrease of the temperature response, which is attributed to the decrease in the effective thermal conductivity. A way to measure the evolution of the uptake of biological fluid would be following the gradient of the temperature evolution, indicative for the time needed to attain the final value of T = 0.5. For illustrative purposes, we perform the same calculations also for δ = O(3.5), δ = O(1.5) and δ = O(1) µm, so that αth = O(0.2), αth = O(1) and αth = O(2.5), respectively. These results are presented in Figures 4 to 6, respectively.

    Figure 4.  Temperature T at x = 0 as a function of time t for αth = 0.2 and different values of the volume fraction φ (the volume fraction of the biological fluid uptake is given by φb = φ-0.057).
    Figure 5.  Temperature T at x = 0 as a function of time t for αth = 1 and different values of the volume fraction φ (the volume fraction of the biological fluid uptake is given by φb = φ-0.057).
    Figure 6.  Temperature T at x = 0 as a function of time t for αth = 2.5 and different values of the volume fraction φ (the volume fraction of the biological fluid uptake is given by φb = φ-0.057).

    Figure 4 shows that a higher value of αth (the thermal diffusion time becomes smaller than in the previous case, which could be due to another material or another thickness of the same material) results into a small "left-over" of the imposed oscillations, but keeping approximately the same incremental tendency.

    Figure 5 shows that, for a relaxation time of the order of magnitude of a thermal diffusion time, the incremental behaviour is only slightly visible, but rather the oscillatory behaviour of the temperature response becomes more important. As such, for higher values of φ (higher uptake of the biological fluid), the measurement could be indicated by a phase lag of the oscillations. This phase lag becomes even more important when augmenting αth in Figure 6. There, the incremental behaviour has completely vanished and only the phase lag is observable as an indication of biological fluid uptake.

    Figures 4 to 6 show that, depending on the ratio of the thermal relaxation time and the thermal diffusion characteristic time, the detection of the biological fluid uptake can be monitored by two distinctive ways. If the thermal diffusion time is smaller for a certain relaxation time, the fluid uptake can be monitored by a gradient of the temperature response, whilst for larger thermal diffusion times the uptake can be followed by measuring the phase lag of an oscillatory temperature response. This can open ways to several types of biosensors.

    In this work, a study on the response of an imposed temperature oscillation at high frequency is performed, using as material a porous carbon nanotube-silica nanocomposite. The purpose is to measure the uptake of biological fluids by noting that the temperature response can be altered by the thermal properties of the material, which depends also on the uptake of the biological fluids. For this study, a heat flux from Extended Thermodynamics has been employed, combined with an energy balance and an equation for the effective thermal conductivity. It is important to note that the evolution equation for the heat flux, although taken from developments from Extended Thermodynamics and neglecting thereby non-local effects [1], corresponds also to Cattaneo's equation for heat transport [18]. The model for the effective thermal conductivity has been satisfactorily validated against experiments of a porous CNT-SiO2 nanocomposite. The experiments concern a procedure of self-assembled porous nanocomposite structures, of which the thermal conductivities have been measured.

    Subsequently, the temperature response (induced by the imposed oscillatory temperature) is calculated using the heat transport equations. The ratio of the relaxation time and the thermal diffusion time is also varied in order to appreciate the effect the thickness of a material could have on the response. The uptake of the biological fluid has an influence on the effective thermal conductivity, which will change the temperature response. Although, for a final application, such methodology should be implemented in electrical circuits (implying indirectly induced temperature pulses), the source of the temperature pulses is not the subject of this study. Rather, it provides the mathematical and conceptual tools allowing such possible implementations. It appeared indeed that the uptake of biological fluid, simulated here by an increase of the volume fraction, alters clearly the temperature response, and this even in two distinct ways. It appeared that this response was of oscillatory nature with a phase lag when the thermal diffusion time was much lower than the relaxation time. On the other hand, when the thermal diffusion time was much higher than the relaxation time, the response was rather of exponential growing nature towards an asymptotic value.

    Financial support from BelSPo is acknowledged.

    All authors declare no conflicts of interest in this paper.

    [1] Hashimoto K, Irie H, Fujishima A (2005) TiO2 photocatalysis: An historical overview and future prospects. Jpn J Appl Phys 44: 8269–8285. doi: 10.1143/JJAP.44.8269
    [2] Chen X, Mao SS (2007) Titanium dioxide nanomaterials: synthesis, properties, modifications, and applications. Chem Rev 107: 2891–959. doi: 10.1021/cr0500535
    [3] Fox MA, Dulay MT (1993) Heterogeneous photocatalysis. Chem Rev 93: 341–357. doi: 10.1021/cr00017a016
    [4] Hoffmann MR, Martin ST, Choi W, et al. (1995) Environmental applications of semiconductor photocatalysis. Chem Rev 95: 69–96. doi: 10.1021/cr00033a004
    [5] Lee Y, Misook K (2010) The optical properties of nanoporous structured Titanium dioxide and the photovoltaic efficiency on DSSC. Mater Chem Phys 122: 284–289. doi: 10.1016/j.matchemphys.2010.02.050
    [6] Fujishima A, Honda K (1972) Electrochemical photolysis of water at a semiconductor electrode. Nature 238: 37–38. doi: 10.1038/238037a0
    [7] Gabor A, Somorjai A, Contreras M, et al. (2006) Clusters, surfaces, and catalysis. P Natl Acad Sci USA 103: 10577–10583. doi: 10.1073/pnas.0507691103
    [8] Mills A, Hunte SL (1997) An overview of semiconductor photocatalysis. J Photoch Photobiol A 108: 1–35. doi: 10.1016/S1010-6030(97)00118-4
    [9] Burda C, Chen X, Narayanan R, et al. (2005) Chemistry and properties of nanocrystals of different shapes. Chem Rev 105: 1025–1102. doi: 10.1021/cr030063a
    [10] Pelizzetti E, Minero C (1994) Metal oxides as photocatalysts for environmental detoxification. Comment Inorg Chem 15: 297–337. doi: 10.1080/02603599408035846
    [11] Hisatomi T, Kubota J, Domen K (2014) Recent advances in semiconductors for photocatalytic and photoelectrochemical water splitting. Chem Soc Rev 43: 7520–7535. doi: 10.1039/C3CS60378D
    [12] Ramírez H, Ramírez M (2015) Photocatalytic Semiconductors: Synthesis, Characterization, and Environmental Applications. Springer International Publishing, ISBN 978-3-319-10999-2.
    [13] Chen H, Nanayakkara CE, Grassian VH (2012) Titanium dioxide photocatalysis in atmospheric chemistry. Chem Rev 112: 5919–5948. doi: 10.1021/cr3002092
    [14] Pelaez M, Nolan NT, Pillai SC, et al. (2012) A review on the visible light active Titanium dioxide photocatalysts for environmental applications. Appl Catal B 125: 331–349. doi: 10.1016/j.apcatb.2012.05.036
    [15] Kalathil S, Khan MM, Ansari SA, et al. (2013) Band gap narrowing of Titanium dioxide (TiO2) nanocrystals by electrochemically active biofilm and their visible light activity. Nanoscale 5: 6323–6326. doi: 10.1039/c3nr01280h
    [16] Khan MM, Ansari SA, Pradhan D, et al. (2014) Band gap engineered TiO2 nanoparticles for visible light induced photoelectrochemical and photocatalytic studies. J Mater Chem A 2: 637–644. doi: 10.1039/C3TA14052K
    [17] Carp O, Huisman CL, Reller A (2004) Photoinduced reactivity of Titanium dioxide. Prog Solid State Ch 32: 33–177. doi: 10.1016/j.progsolidstchem.2004.08.001
    [18] Chen Q, Peng LM (2007) Structure and applications of titanate and related nanostructures. Int J Nanotechnol 4: 261–270.
    [19] Amaratunga P (2010) Synthesis and characterization of monolayer protected gold nanoparticles and a Gold-Titanium dioxide nanocomposite intended for photovoltaic degradation of environmental pollutants. Arch Microbiol 151: 77–83.
    [20] Jang JS, Sun S, Choi H, et al. (2006) A composite deposit photocatalyst of CdS nanoparticles deposited on TiO2 Nanosheets. J Nanosci Nanotechno 6: 3642–3646. doi: 10.1166/jnn.2006.073
    [21] Inumaru K, Kasahara T, Yasui M, et al. (2005) Direct nanocomposite of crystallite TiO2 particles and mesoporous silica as a molecular selective and highly reactive photocatalyst. Chem Commun 2005: 2132–1233.
    [22] Pradhan S, Ghosh D, Chen S (2009) Janus nanostructures based on Au-TiO2 heterodimers and their photocatalytic activity in the oxidation of methanol. ACS Appl Mater Inter 1: 2060–2065.
    [23] Fujishima A, Rao TN, Tryk DA (2000) Titanium dioxide photocatalysis. J Photoch Photobio C 1: 1–21.
    [24] Wang S, Zhou S (2011) Photodegradation of Methyl orange by photocatalyst of CNTs/P-TiO2 under UV and visible-light irradiation. J Hazard Mater 185: 77–85. doi: 10.1016/j.jhazmat.2010.08.125
    [25] Ibrahim SA, Sreekantan S (2010) Effect of pH on TiO2 nanoparticles via sol-gel method. Adv Mater Res 173: 184–189.
    [26] Niederberger M, Bartl MH, Stucky GD (2002) Benzyl alcohol and transition metal chlorides as a versatile reaction system for the nonaqueous and low-temperature synthesis of crystalline nano-objects with controlled dimensionality. J Am Chem Soc 124: 13642–13643. doi: 10.1021/ja027115i
    [27] Parala H, Devi A, Bhakta R, et al. (2002) Synthesis of nano-scale TiO2 particles by a non-hydrolytic approach. J Mater Chem 12: 1625–1627. doi: 10.1039/b202767d
    [28] Lei H, Hou Y, Zhu M, et al. (2005) Formation and transformation of ZnTiO3 prepared by sol-gel process. Mater Lett 59: 197–200. doi: 10.1016/j.matlet.2004.07.046
    [29] Arnal P, Corriu RJP, Leclercq D, et al. (1996) Preparation of anatase, brookite and rutile at low temperature by non-hydrolytic sol-gel methods. J Mater Chem 6: 1925–1932. doi: 10.1039/JM9960601925
    [30] Arnal P, Corriu RJP, Leclercq D, et al. (1997) A solution chemistry study of nonhydrolytic Sol-Gel routes to Titania.Chem Mater9: 694–698.
    [31] Hay JN, Raval HM (1998) Preparation of inorganic oxides via a non-hydrolytic sol-gel route. J Sol-Gel Sci Techn 13: 109–112. doi: 10.1023/A:1008615708489
    [32] Hay JN, Raval HM (2001) Synthesis of organic-inorganic hybrids via the non-hydrolytic sol-gel process. Chem Mater 13: 3396–3403. doi: 10.1021/cm011024n
    [33] Lafond V, Mutin PH, Vioux A (2002) Non-hydrolytic sol-gel routes based on alkyl halide elimination: Toward better mixed oxide catalysts and new supports—Application to the preparation of a SiO2-TiO2 epoxidation catalyst. J Mol Cata A-Chem 182: 81–88.
    [34] Trentler TJ, Denler TE, Bertone JF, et al. (1999) Synthesis of TiO2 nanocrystals by nonhydrolytic solution-based reactions. J Am Chem Soc 121: 1613–1614. doi: 10.1021/ja983361b
    [35] Byrappa K, Adschiri T (2007) Hydrothermal technology for nanotechnology. Prog Cryst Growth Ch 53: 117–166. doi: 10.1016/j.pcrysgrow.2007.04.001
    [36] Andersson M, Österlund L, Ljungström S, et al. (2002) Preparation of nanosize anatase and rutile TiO2 by hydrothermal treatment of microemulsions and their activity for photocatalytic wet oxidation of phenol. J Phys Chem B 106: 10674–10679. doi: 10.1021/jp025715y
    [37] Yong CS, Park MK, Lee SK, et al. (2003) Preparation of size-controlled TiO2 nanoparticles and derivation of optically transparent photocatalytic films. Chem Mater 15: 3326–3331. doi: 10.1021/cm030171d
    [38] Cot F, Larbot A, Nabias G (1998) Preparation and characterization of colloidal solution derived crytalline titania powder. J Euro Ceram Soc 18: 2175–2181. doi: 10.1016/S0955-2219(98)00143-5
    [39] Yang J, Mei S, Ferreira JMF (2000) Hydrothermal synthesis of nanosized titania powders: influence of peptization and peptizing agents on the crystalline phases and phase transitions. J Am Ceram Soc 83: 1361–1268. doi: 10.1111/j.1151-2916.2000.tb01394.x
    [40] Yang J, Mei S, Ferreira JMF (2001) Hydrothermal synthesis of nanosized titania powders: Influence of tetraalkyl ammonium hydroxide on particle characteristics. J Am Ceram Soc 84: 1696–1702.
    [41] Yang J, Di L (2002) Rapid synthesis of nanocrystalline TiO2/SnO2 binary oxide and their photoinduced decompositopn of methyl orange. J Solid State Chem 165: 193–198. doi: 10.1006/jssc.2001.9526
    [42] Yang TY, Lin HM, Wei BY, et al. (2003) UV enhancement of the gas sensing properties of nano-TiO2. Rev Adv Mater Sci 4: 48–54.
    [43] Liveri VT (2002) Reversed micelles as nanometer-size solvent media. In Nano-Surface Chemistry. Rosoff M, Ed. Marcel Dekker: New York, 473–385.
    [44] Zhang D, Limin Q, Jiming M, et al. (2002) Formation of crystalline nanosized titania in reverse micelles at room temperature. J Mater Chem 12: 3677–3680. doi: 10.1039/b206996b
    [45] Hong SS, LeeSL, Lee GD (2003) Photocatalytic degradation of p-Nitrophenol over Titanium dioxide prepared by reverse microemulsion method using non-ionic suefactant with different hydrophpsilic groups. React Kinet Cat Lett 80: 145–151.
    [46] Kim KD, Kim TH (2005) Comparison of the growth mechanism of TiO2-coated SiO2 particles prepared by Sol-gel process and water-in-oil type microemulsion method. Colloid Surface A 255: 131–137. doi: 10.1016/j.colsurfa.2004.12.036
    [47] Li GL, Wang GH (1999) Synthesis of nanometer-sized TiO2 particles by a microemulsion method. Nanostruct Mater 11: 663–668.
    [48] Li Y, Cureton LT, Sun YP (2004) Improving photoreduction of CO2 with homogeneously dispersed nanoscale TiO2 catalysts. Chem Commun 2004: 1234–1235.
    [49] Chen X, Mao SS (2007) Titanium dioxide nanomaterials:? Synthesis, properties modifications, and applications. Chem Rev 107: 2891–2959.
    [50] Lim KT, Ha SH (2004) Synthesis of TiO2 nanoparticles utilizing hydrated reverse micelles in CO2. Langmuir 20: 2466–2471. doi: 10.1021/la035646u
    [51] Yu JC, Zhang L, Yu J (2002) Direct sonochemical preparation and characterization of highly active mesoporous TiO2 with a bicrystalline framework. Chem Mater 14: 4647–4653. doi: 10.1021/cm0203924
    [52] Li XL, Peng Q, Yi JX, et al. (2006) Near monodisperse TiO2 nanoparticles and nanorods. Chem A Euro J 12: 2111–2395. doi: 10.1002/chem.200690023
    [53] Xu J, Ao Y, Fu D, et al. (2008) Synthesis of fluorinedoped titania-coated activated carbon under low temperature with high photocatalytic activity under visible light. J Phys Chem Sol 69: 2366–2370. doi: 10.1016/j.jpcs.2008.03.017
    [54] Wang X, Zhuang J, Peng Q, et al. (2005) A general strategy for nanocrystal synthesis. Nature 437: 121–124. doi: 10.1038/nature03968
    [55] Krishna KM, Paii VA, Marathe VR, et al. (1990) Atheoretical approach to design of reduced band gap non corrosive electrode for photoelectrochemical solar cell. Int J Quantum Chem 24: 419–427.
    [56] Sharon M, Krishna KM, Mishra MK, et al. (1992) Theoretical investigation of optimal mixing ratio for PbO2 and TiO2 to produce a low band gap noncorrosive photoelectrode. J Chem Phys 163: 401–412.
    [57] Krishna KM, Sharon M, Mishra MK (1995) Preparation and characterization of a PbTiO3 + PbO mixed oxide photoelectrode. J Electroanalytic Chem 391: 93–99. doi: 10.1016/0022-0728(95)03905-V
    [58] Sharon M, Krishna KM, Mishra MK (1996) Preparation and characterization of mixed oxides obtained from various molar mixtures of beta-PbO2 and TiO2. J Phys Chem Solids 57: 615–626. doi: 10.1016/0022-3697(95)00272-3
    [59] Sharon M, Krishna KM, Mishra MK (1996) Pb1?xTixO: a new photoactive phase. J Mater Sci Lett 15: 1084–1087.
    [60] Wei XX, Cui H, Guo S, et al. (2013) Hybrid BiOBr-TiO2 nanocomposites with high visible lightphotocatalytic activity for water treatment. J Hazard Mater 263: 650–658. doi: 10.1016/j.jhazmat.2013.10.027
    [61] Chakraborty AK, Hossain ME, Rhaman MM, et al. (2014) Fabrication of Bi2O3/TiO2 nanocomposites and their applications to the degradation of pollutants in air and water under visible-light. J Environ Sci 26: 458–465. doi: 10.1016/S1001-0742(13)60428-3
    [62] Khan B, Ashraf U (2015) Sol-gel synthesis and characterization of nanocomposites of Cu/TiO2 and Bi/TiO2 metal oxides as photocatalysts. Int J Sci Technol 4: 40–48.
    [63] Dresselhaus MS, Dresselhaus G (2001) Carbon nanotubes: Synthesis, Structure, Properties and Applications: Topics in Applied Physics, Springer-Verlag. ISBN 3-54041-086-4, Berlin.
    [64] Saleh TA, Gupta VK (2011) Functionalization of tungsten oxide into MWCNT and its application for sunlight-induced degradation of rhodamine B. J Colloid Interface Sci 362: 337–344. doi: 10.1016/j.jcis.2011.06.081
    [65] Yu JC, Zhang L, Zheng Z, et al. (2003) Synthesis and characterization of phosphate mesoporous Titanium dioxide with high photocatalytic activity. Chem Mater 15: 2280–2286. doi: 10.1021/cm0340781
    [66] Lin L, Lin W, Zhu YX, et al. (2005)Phosphor-doped titania—a novel photocatalyst active in visible light. Chem Lett 34: 284–285.
    [67] Korosi L, Oszko A, Galbacs G, et al. (2007) Structural properties and photocatalytic behavior of phosphate-modified nanocrystalline titania films. Appl Catal B 77: 175–183. doi: 10.1016/j.apcatb.2007.07.019
    [68] Lin L, Lin W, Xie JL, et al. (2007) Photocatalytic properties of phosphor-doped titania nanoparticles. Appl Catal B 75: 52–58. doi: 10.1016/j.apcatb.2007.03.016
    [69] Jin C, Zheng RY, Guo Y, et al. (2009) Hydrothermal synthesis and characterization of phosphorous-doped TiO2 with high photocatalytic activity for methylene blue degradation. J Mol Catal A 313: 44–48. doi: 10.1016/j.molcata.2009.07.021
    [70] Wang S, Zhou S (2011) Photodegradation of methyl orange by photocatalyst of CNTs/P-TiO2 under UV and visible-light irradiation. J Hazard Mater 185: 77–85. doi: 10.1016/j.jhazmat.2010.08.125
    [71] Sharon M, Datta S, Shah S, et al. (2007) Photocatalytic degradation of E. coli and S. aureus by multi walled carbon nanotubes. Carbon Letts 8: 184–190.
    [72] Oza G, Pandey S, Gupta A, et al. (2013) Photocatalysis-assisted water filtration: Using TiO2-coated vertically aligned multi-walled carbon nanotube array for removal of Escherichia coli O157:H7. Mater Sci Eng C-Mater 33: 4392–4400.
    [73] Cong Y, Li X, Qin Y, et al. (2011) Carbon-doped TiO2 coating on multiwalled carbon nanotubes with higher visible light photocatalytic activity. Appl Catal B-Environ 107: 128–134.
    [74] Mamba G, Mbianda XY, Mishra AK (2014) Gadolinium nanoparticles decorated multiwalled carbon nanotube/titania nanocomposite for degradation of methylene blue in water under simulated solar light. Environ Sci Pollut Res 21: 5597–5609.
    [75] Mamba G, Mbianda XY, Mishra AK (2015) Photocatalytic degradation of diazo dye naphthol blue black in water using MWCNT/Gd, N, S-TiO2 nanocomposite under simulated solar light. J Environ Sci 33: 219–228. doi: 10.1016/j.jes.2014.06.052
    [76] Czech B, Buda W (2015) Photocatalytic treatment of pharmaceutical wastewater using new multiwall-carbon nanotubes/TiO2/SiO2 nanocomposite. Environ Res 137: 176–184. doi: 10.1016/j.envres.2014.12.006
    [77] Ptrovic M, Radjenovic J, Postigo C, et al. (2008) Emerging contaminants in waste waters: sources and occurrence. In: Barcello D, Ptrovic M, Eds. Emerging contaminants from Industrial and Municipal Waste. Springer, Berlin, Heidelberg, 1–35.
    [78] Gadipelly C, Perez-Gonzalez A, Yadav GD, et al. (2014) Pharmaceutical industry waste water—reviews of the technology for water treatment and re-use. Ind Eng Chem Res 53: 11571–11592. doi: 10.1021/ie501210j
    [79] Krishamoorthy K, Mohan R, Kim SJ (2001) Graphene oxide as photocatalytic material. Appl Phys Lett 98: 244101–114312.
    [80] Stengl V, Bakardjieva S, Gryger TM, et al. (2013) TiO2-graphene oxide nanocompositeas advanced photocatalytic materials. Chem Central J 7: 41–53.
    [81] Zhang Y, Zhou Z, Chen T, et al. (2014) Graphene TiO2 nanocomposite with high photocatalytic activity for degradation of sodium pentachlorophenol. J Environ Sci 26: 2114–2122. doi: 10.1016/j.jes.2014.08.011
    [82] Stein A (2003) Advances in microporous and mesoporous solids—Highlights of recent progress. Adv Mater 15: 763–775. doi: 10.1002/adma.200300007
    [83] Stein A, Melde BJ, Schroden RC (2003) Hybrid inorganic-organic mesoporous silicates—nanoscopic reactors coming of age. Adv Mater 12: 1403–1419.
    [84] Inumaru K, Kasahara T, Yasui M, et al. (2005) Direct nanocomposite of crystallite TiO2 particles and mesoporous silica as a molecular selective and highly active photocatalyst. Chem Commun 2005: 2131–2133.
    [85] Mohseni A, Malekina L, Fazaeli R, et al. (2013) Synthesis TiO2/SiO2/Ag nanocomposite by sonochemical method and investigation of photo-catalyst effect in waste water treatment. Nanocon 10: 16–18.
    [86] Li K, Huang C (2000) Selective oxidation of Hydrogen Sulfide to sulphur over LaVO4 catalyst: Promotional effect of Antimony oxide addition. Ind Eng Chem Res 45: 7096–7100.
    [87] Ye JH, Zhou ZG, Oshikiri M, et al. (2003) New visible light driven semiconductor photocatalyst and their application as functional eco-material. Mater Sci Forum 423: 825–830.
    [88] Huang H, Li D, Lin Q, et al. (2009) Efficient degradation of Benzene over LaVO4/TiO2 nano-crystalline heterojunction photocatalyst under visible light irradiation. Envron Sci Technol 43: 4164–4168. doi: 10.1021/es900393h
    [89] Visa M, Duta A (2013) Methyl orange and Cadmium simultaneous removal using fly ash and Photo-Fenton system. J Hazard Mater 244–245: 773–779.
    [90] Visa M (2012) Tailoring fly ash activated with bentonite as adsorbent for complex waste water treatment. Appl Surf Sci 263: 753–762. doi: 10.1016/j.apsusc.2012.09.156
    [91] Visa M, Andronic L, Duta A (2015) Fly ash-TiO2 nanocomposite material for multi-pollutants water treatment. J Environ Manage 150: 336–343.
    [92] Kaplan R, Erjavec B, Drazic G, et al. (2016) Simple synthesis of Anatase/rutile/brookite TiO2 nanocomposite with superior mineralization potential for photocatalytic degradation of water pollutants. Appl Catal B-Environ 181: 465–474. doi: 10.1016/j.apcatb.2015.08.027
    [93] Yu J, Qi L (2009) Template free fabrication of hierarchically flower like tungsten tri oxide assemblies with enhanced visible-light-driven photocatalytic activity. J Hazard Mater 169: 221–227.
    [94] Vicaksana Y, Liu S, Scott J, et al. (2014) Tungsten trioxide as a visible light photocatalyst for volatile organic carbon removal. Molecules 19: 17747–17762. doi: 10.3390/molecules191117747
    [95] Sajjad AKL, Sajjad S, Tian B, et al. (2010) Comparative studies of operational parameters of degradation of azo-dyes in visible light by highly efficient WOx/TiO2 photocatalyst. J Hazard Mater 177: 781–791.
    [96] Zhao G, Jr SES (1998) Multiple parameters for the comprehensive evaluation of the susceptibility of Escherichia coli to the silver ion. Biometals 11: 27–32. doi: 10.1023/A:1009253223055
    [97] Yamanaka M, Hara K, Kudo J (2005) Bactericidal actions of a Silver ion solution on Escherichia coli, studied by Energy-Filtering Transmission Electron Microscopy and Proteomic Analysis. Appl Environ Microb 71: 7589–7593. doi: 10.1128/AEM.71.11.7589-7593.2005
    [98] Jung WK, Koo HC, Kim KW, et al. (2008) Antibacterial activity and mechanism of action of the silver ion in Staphylococcus aureus and Escherichia coli. Appl Environ Microb 74: 2171–2178. doi: 10.1128/AEM.02001-07
    [99] Liu SX, Qu ZP, Han WX, et al. (2004) A mechanism for enhanced photocatalytic activity of silver loaded titania dioxide. Catal Today 93–95: 877–884.
    [100] Akhavan O (2009) Lasting antibacterial activities of Ag-TiO2/Ag/a-TiO2 nanocomposite thin film photocatalysts under solar light irradiation. J Colloid Interf Sci 336: 117–124. doi: 10.1016/j.jcis.2009.03.018
    [101] Xiang Q, Yu J, Cheng B, et al. (2010) Microwave hydrothermal preparation of Visible-light photocatalytic activity of Ag-TiO2 nanocomposite hollow sphere. Chem Asian J 5: 1466–1474.
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