Journal Information
Vol. 4. Issue 2.
Pages 133-143 (April - June 2015)
Download PDF
More article options
Vol. 4. Issue 2.
Pages 133-143 (April - June 2015)
Original Article
DOI: 10.1016/j.jmrt.2014.11.005
Open Access
Synthesis of spherical mesoporous titania modified iron-niobate nanoclusters for photocatalytic reduction of 4-nitrophenol
Tanmay K. Ghoraia,b
a Department of Chemistry, University of Gour Banga, Malda, India
b Department of Chemistry, West Bengal State University, Barasat, India
This item has received

Under a Creative Commons license
Article information
Full Text
Download PDF
Figures (11)
Show moreShow less
Tables (2)
Table 1. Resultant properties of FNT1, FNT2, FNT3, FNT4, NT, FT and P25 TiO2 nanoclusters.
Table 2. The surface atom concentration for oxygen, Cr, Nb and Ti atoms of the FexNbxTi1−2xO2−x/2 (x=0.01) by XPS.
Show moreShow less

Spherical mesoporous titania modified iron-niobate nanoclusters FNT1 [FexNbxTi1−2xO2−x/2 (x=0.01)], with relatively small particle size 10±2nm and SBET 145m2g−1 were prepared using a sol–gel method, from the reaction of titanium and niobium tartrate with triethanol amine and ferric nitrate solution. HRTEM of FNT1 shows coexistence of porous mesostructure and high symmetric order of crystallinity in the nanoparticles. The mesopore size is in the range of 4–5nm and the lattice fringes of 0.37nm is observed in the mesopore walls which correspond to the d-spacing between adjacent (101) crystallographic planes of FNT1 phase. This is supported by XRD studies. In the presence of UV light, FNT1 (0.1g/50mL) reduces the 4-nitrophenol (4-NP) (0.0139gL−1) to 4-aminophenol by using NaBH4 (0.054gL−1) in contrast to pure TiO2 and other composites of FexNbxTi1−2xO2−x/2 photocatalysts. The 4-NP is reduced to 4-aminophenol within 10min in the presence of FNT1 and UV light, but in the absence of the catalysts, it takes approximately 82min. The catalytic activity of FNT1 is enhanced significantly in the presence of UV light compared to the absence of UV light. We observed that the catalytic activity of the prepared catalyst also depends on crystal size, particle morphology and particle porosity, and dopant concentrations.

Titanium dioxide
Full Text

4-Nitrophenol (4-NP) is a very significant compound of NP group and considered as an important hazardous and toxic pollutant. Mostly they are used extensively in chemical industries for the production of different kinds of pesticides, pharmaceutical and synthetic dyes [1–6]. 4-NP can damage the central nervous system, liver, kidney and blood of animals and humans. Therefore, removal of 4-NP is essential to protect the human being. The easiest way to remove 4-NP from the environment is the reduction of 4-NP to 4-aminophenol (4-Amp). On the other hand, the reduced product 4-aminophenol is very useful in a wealth of applications that include analgesic and antipyretic drugs, photographic developer, corrosion inhibitor, anticorrosion lubricant, and so on [1]. In this context, mesoporous compounds have an important role in photochemical reactions for removal of such type of pollutants. Mesoporous titanium dioxide (TiO2) has continued to be highly efficient in photocatalytic applications, because of its high surface area and porous frameworks [7,8]. In the past decade, there have been few reports about mesoporous transition-metal oxides [9–11].

Generally, nanoparticles are used for the fabrication of mesoporous structure of TiO2. However, nanocrystalline TiO2 is a promising semiconducting material that have attracted considerable interest for their applications as electrodes [12], electronics [13], capacitors [14], optics [15,16], sensors [17,18], ceramics [19], solar cells [20–22], catalysis [23,24] and photocatalysis [25–28].

Therefore, many research scientists are now-a-days involved in the research work on the photocatalytic activity of TiO2 doped with different metal ions such as Ag [29], Au [30], Mn [31], Fe [32,33], Co [34], Ni [35,36], Cu [37,38], and Pd [39] etc. Recently, non-metals such as nitrogen doped La2Ti2O7[40,41], nitrate and nitrite doped TiO2 were shown to be good photocatalysts [42]. Ismail et al. found that TiO2 microspheres with porous structures have higher photocatalytic activity and they can be easily recovered for their re-use as catalysts [43]. Furthermore, photoactivity is highly dependent on surface area and crystallinity or crystal sizes, which are in turn influenced by the synthetic methods of titania synthesis [44,45].

The most recent studies show that the addition of small quantities of Nb2O5 into TiO2 lattice significantly increases the photocatalytic activity and surface acidity of TiO2[46,47]. On the other hand, Fe(III) doped photocrystaline titania have also been widely studied in the field of photocatalysis [32,33,48–50]. The effect of simultaneous doping of Fe and Nb dopants in TiO2 mesoporous structure and its photocatalytic activity has not yet been reported. Moreover, we are also interested to see how photocatalytic effect changes, when both iron and niobium are co-doped with TiO2. Non-conventional synthetic procedures such as: chemical vapor deposition [51], hydrothermal [52], microemulsion [53], sol–gel [54,55], coprecipitation [56], and chemical methods [26,33,38], were already adopted to produce such compositions.

In the present work, we report the synthesis and characterization of spherical mesoporous FexNbxTi1−2xO2−x/2 (x=0.01) (FNT1) with a surface area of up to 145m2g−1 prepared from a titanium/niobium tartrate with triethanol amine and ferric nitrate precursor by sol–gel method. Here, the role of Fe(III) in Fe–Nb–TiO2 composite is to compensate the charge imbalance caused by the replacement of Ti(IV) with Nb(V) in TiO2 crystals, which result in improving charge separation among the photo-produced hole–electron pairs. However, interestingly our study show that Fe and Nb doped TiO2 display good mesoporous nature and brings the photocatalytic reduction of 4-NP to 4-Amp in aqueous medium, containing NaBH4 and in the presence of UV light. The mesoporous FNT1 photocatalysts has good reduction catalytic activity compared to other prepared composites of FexNbxTi1−2xO2−x/2 and pure TiO2. FNT1 spheres have diameters of about 8–10nm and mesopores sizes are of about 4–5nm. The nano-sized photocatalysts were characterized by thermal analysis, X-ray diffraction, UV–visible spectroscopy, BET surface area, UV–visible diffuse reflectance spectra, EPR spectra and transmission electron microscopy (TEM) analyses.

2Experimental2.1Chemicals required

Titanium dioxide (analytical reagent), Nb2O5 (analytical reagent), Fe(NO3)3 6H2O (analytical reagent), sodium hydroxide (analytical reagent), NH4OH (25%), HF (40%), tartaric acid, ethanol, triethanolamine (TEA) and 4-nitrophenol (4-NP) were of analytical reagent grade and were procured from B.D.H., India.

2.2Synthesis of FexNbxTi1−2xO2−x/2 nanoclusters

Spherical nanoclusters of FexNbxTi1−2xO2−x/2 (x=0.01, 0.05, 0.1, 0.2) were prepared by sol–gel method. The total synthesis was carried out in two steps. In the first step, the stock solutions of ferric nitrate, titanium tartrate and niobium tartrate solutions were prepared. The solution of the titanium and niobium tartrate complexes, which are not commercially available, were prepared in the laboratory from its hydrated oxide (Nb2O5·nH2O and TiO2·nH2O); the details of the preparation process are discussed elsewhere [26,33,57]. In the second step, stoichiometric amounts of titanium tartrate (100mL; 0.2545gL−1), niobium tartrate (1.72mL; 0.2167gL−1), ferric nitrate (0.088g, 0.21mmol) with triethanolamine (3mL) and 20mL of absolute ethanol solutions were taken in a beaker as per the predetermined chemical compositions (example shown for x=0.01) with constant stirring for 30min at room temperature. Then the mixture was adjusted to a pH of 9.0 with 6M NaOH solution, and stirred for 30min, yielding a stable light yellow homogeneous emulsion. The resulting mixture was transferred into a 100mL Teflon-lined stainless steel autoclave and heated to 150°C for 20h under auto generated pressure.

The reaction mixture was allowed to cool to room temperature and the precipitate was filtered, washed with distilled water five times, and dried in a vacuum oven at 100°C for 1h and then heated on furnace at different calcination temperatures for removing all the oxides of carbon and water vapors. The composites with different amounts of Fe and Nb doping will be denoted as the following: FexNbxTi1−2xO2−x/2, x=0.01 as FNT1, FexNbxTi1−2xO2−x/2, x=0.05 as FNT2, FexNbxTi1−2xO2−x/2, x=0.1 as FNT3, and FexNbxTi1−2xO2−x/2, x=0.2 as FNT4. For comparison, same method was used to synthesize Fe–TiO2, Nb–TiO2 and pure TiO2.

2.3Characterization of nanocatalysts

Thermogravimetric (TG) and differential thermal analyses (DTA) (model: DT-40, Shimadzu, Japan) of the precursor powders were carried out in static air at a heating rate of 10°C/min up to 1000°C using alumina crucible. The crystal structure of the prepared photocatalysts was measured by X-ray diffractometer (XRD) at room temperature, using a Philips PW1710 diffractometer with Cu Kα as target material using 40kV accelerating voltage, 30mA emission current and 4°/min scanning speed. The XRD spectrum of Si crystal was used as a standard to calibrate the scanning angles. Absorbance of 4-nitro phenol was measured with the help of UV–Vis spectrophotometer PerkinElmer Lambda 35 (Singapore). Specific surface area and mesoporous characters of the photocatalysts were determined through Brunauer–Emmett–Teller (BET) gas sorption analysis, which was carried out with a BECKMAN COULTIER SA3100 analyzer. The fine structure of the prepared powders was analyzed by Transmission Electron Microscopy (TEM) (TM-300, Philips). The Electron Paramagnetic Resonance (EPR) spectra were recorded with BRUCKER ER083CS at room temperature (ca. 298K). The zeta potential of nanopowders was measured by Zetasizer, Nano-ZS, Malvern, UK.

2.4Photocatalytic experiments

The photocatalytic experiments were carried out by using a 400W ultrahigh-pressure Hg lamp (PHILIPS-HPL-N, G/74/2, MBF-400) with a maximum emission at about 364nm as the light source. In all experiments, the reaction temperature was kept at 28±0.5°C. The photocatalytic activities of the metal oxides FexNbxTi1−2xO2−x/2 (x=0.01–0.2) were conducted as follows:

Reaction suspensions were prepared by adding each photocatalyst nanopowder (0.1g) into 50mL of aqueous solution of 4-NP (0.0139g, 0.1mmolL−1) in a 100mL quartz beaker in dark condition for about 1h to reach an adsorption equilibrium before photocatalysis. The photocatalytic reactions were carried out in a simple cubic system, where the beaker containing the sample was irradiated with UV light (λ>280nm) under constant magnetic stirring for varying durations of time. A small aliquot (1mL) of reactant liquid was picked out at regular intervals of time for analysis. The slurry was then centrifuged at 1500rpm for 15min, filtered through a 0.2μm-millipore filter to remove the suspended particles.

The recovered photocatalysts were re-used for the same experiments after proper washing with distilled water and calcining at 300°C to check the efficiency for further applications.

2.54-Nitrophenol adsorption studies of FexNbxTi1−2xO2−x/22.5.1Batch adsorption studies

Adsorption studies were carried out using a standard stock solution of 4-NP (15mgL−1) prepared by dissolving appropriate amount of 4-NP in deionized water. Batch adsorption studies were executed in the 100mL Erlenmeyer flasks by equilibrating 100mg of FexNbxTi1−2xO2−x/2 with 50mL of working solutions containing different initial 4-NP concentrations (0, 10, 20, 30, 100, 200, 300mgL−1). For these experiments, the flasks were capped and shaken at room temperature at 125rpm for 20h in a mechanical shaker in the dark condition to attain the adsorption equilibrium. Then, the supernatant was centrifuged, clear water was decanted and the concentration of 4-NP in the supernatant was determined, via UV–Vis spectrophotometer. The equilibrium adsorption capacity of FexNbxTi1−2xO2−x/2 was determined from the difference in initial and final 4-NP concentrations of the working solutions. All the adsorption experiments were performed in triplicate for checking reproducibility.

3Results and discussion3.1Thermal study of the precursors

Thermal analyses data (TG and DTA) of the precursor powder FNT2, heated at 100°C, is given in Fig. 1, which indicates that the FNT precursor powder decomposes exothermally, with a sharp peak at 208.8°C. This exothermic peak can be assigned to major decomposition of the metal-TEA complexes. From the graph, it is observed that the rate of mass change increases to a maximum in the temperature range 100–300°C. The entire thermal effect was accompanied by the evolution of various gases (such as oxides of carbon and nitrogen and water vapor, etc.), which were manifested by a single-step weight loss in the TG curves shown in Fig. 1. Above 400°C, there was no significant thermal effect as evident from the DTA curves, and the corresponding TG curves showed no weight loss, implying complete volatilization of carbon compounds.

Fig. 1.

DTA–TG and DTG of FNT2 precursor.

3.2XRD analysis software

X-Ray diffraction (XRD) was employed to further investigate the crystalline phase and particle size of the mesoporous TiO2 modified iron-niobate sphere arrays. The XRD patterns of FNT1, FNT2, FNT3 and FNT4 (Cu-Kα radiation, λ=1.5408Å) (Fig. 2a) exhibit diffraction peaks at 2θ of 25.2°, 27.2°, 35.9°, 37.8°, 41.2°, 47.8°, 54.2°, 55.2°, and 62.4°, which can be readily indexed to the mixture of anatase and rutile phases of TiO2[58,59]. The peaks position of 25.2°, 37.8°, 47.8°, 54.2°, 55.2°, 62.4° for anatase (JCPDS card, No. 21-1272) and 27.2°, 35.9°, 41.2°, 54.2° for rutile (Card No. 21-1276) phases of TiO2. The XRD pattern of pure TiO2 shows the presence of only anatase phase. The samples NT and FT have XRD patterns, which matched exactly with anatase crystal reflections in TiO2. Fig. 2b shows the XRD patterns of FNT1 annealed at different temperatures. It indicates that at low temperature (300°C), FNT1 has a pure anatase TiO2 crystal structure, and there is no appearance of rutile phase. On increasing the calcination temperatures from 300 to 500°C, the anatase phase of FNT1 remain same and peak intensity of rutile phase is increased (Fig. 2b) and finally gives rise to a mixture of anatase and rutile phases along with grain growth. The crystalline size estimated using the Scherrer equation from the full width at half maximum (FWHM) of the (101) peak (2θ=25.2°) is ∼13.7nm, which is in agreement with the HRTEM observation. All the composites data of crystallite sizes obtained from the diffractograms are presented in Table 1.

Fig. 2.

(a) XRD patterns of FexNbxTi1−2xO2−x/2 (where; x= 0.01 (FNT1), 0.05 (FNT2), 0.1 (FNT3) and 0.2 (FNT4), Fe–TiO2 (FT), Nb–TiO2 (NT) and pure TiO2 photocatalyst at 300°C. (b) XRD of FNT1 at different temperatures.

Table 1.

Resultant properties of FNT1, FNT2, FNT3, FNT4, NT, FT and P25 TiO2 nanoclusters.

SampleFexNbx  Abbreviation  Reaction compositionk (×10−3min−1Reaction rate constantsTime required for degradation (min)SBET (m2g−1Crystallites size (nm) 
Ti1−2xO2−x/2      UVPre  UVAbs  UVPre  UVAbs     
X=0.01  FNT1  FNT1+NaBH4+4-NP  589.07  103.60  10  20  145.0  13.55 
X=0.05  FNT2  FNT2+NaBH4+4-NP  126.90  80.51  18  34  115.3  13.83 
X=0.1  FNT3  FNT3+NaBH4+4-NP  55.31  52.16  35  52  49.1  13.92 
X=0.2  FNT4  FNT4+NaBH4+4-NP  43.50  40.86  48  68  45.7  14.02 
Nb–TiO2  NT  NB+NaBH4+4-NP  39.35  34.94  65  75  52.6  12.14 
Fe–TiO2  FT  FT+NaBH4+4-NP  37.86  29.35  68  83  32.3  12.39 
P25–TiO2  –  TiO2+NaBH4+4-NP  32.62  20.48  80  90  49.0  12.42 
CatAbsence  –  NaBH4+4-NP  23.94  16.38  82  90  –  – 

UVPre, UV presence; UVAbs, UV absence; CatAbsence, catalysts absence.

Reaction rate constants were measured after 10min reduction of 4-nitrophenol to 4-aminophenol in the presence and absence of UV light, BET surface area measured by liquid nitrogen adsorption–desorption isotherm at room temperature. Time required in different conditions for reduction of yellow color of 4-nitrophenol to colorless 4-aminophenol.

3.3TEM analysis

TEM and HR-TEM were used to examine the mesoporous structure and crystallization of the FNT1 spheres. Fig. 3a shows a typical TEM image of these FNT1 spheres. Fig. 3b represents high magnification of FNT1 and clearly shows each particle's shape is a unique. Fig. 3c HRTEM of yellow and red marked of Fig. 3a particle and the inset figure indicates SAED pattern of the same sphere and the order of mesoporous structure can be observed in the same HR-TEM images. Fig. 3d shows one enlarged mesoporous spheres (from Fig. 3c), which is of yellow mark in the figure and reveals the coexistence of a porous mesostructure and high symmetric order of crystallinity in the FNT1 nanoparticles. The mesopore size is in the range of 4–5nm (Fig. 3c), and the FNT1 nanocrystallites have average diameter of 8–10nm. The lattice fringes of 0.37nm (Fig. 3d) observed in the mesopore walls correspond to the d-spacing between adjacent (101) crystallographic planes of anatase FNT1 phase.

Fig. 3.

(a) TEM images of FNT1, (b) high magnification of FNT1 TEM, (c) HRTEM of yellow and red marked of (a) particle and SAED pattern of same sphere of FNT1, (d) enlarged one mesoporous spheres from (c).

3.4Specific surface area analysis

The surface area and porosity of the iron-niobate modified TiO2 microspheres are investigated using the nitrogen adsorption and desorption isotherm (Fig. 4). It can be seen from this figure that there is one hysteresis loop that appears in the isotherm. The isotherm can be classified as type IV nature curve with a type H2 hysteresis loop, indicating the presence of mesoporous materials [60]. The inset in Fig. 4 shows the pore size distribution calculated by the Barrett–Joyner–Halenda (BJH) method using the desorption isotherm. The average pore diameter of the mesoporous FNT1 spheres is 4.6nm. The BET surface area and pore volume of the mesoporous FNT1 spheres are 145m2g−1 and 0.246cm3g−1, respectively. In addition, the mesopore size distribution is in the range of 3–7nm, and such a narrow distribution implies substantial homogeneity of the mesopores for the TiO2 spheres. The BJH pore size distribution results agree well with the TEM and HR-TEM characterizations. The BET surface areas (SA) of other composites of FexNbxTi1−2xO2−x/2 are 115.3, 49.1 and 45.7m2g−1 for FNT2, FNT3 and FNT4 respectively. However, attempts made to prepare the solid solution using the co-precipitation method were unsuccessful.

Fig. 4.

An N2 adsorption–desorption isotherm and (inset) a pore size distribution curve of FNT1.

3.5Zeta potential measurement

The surface charges of the FNT1 material at various pHs have been investigated by measuring the electrokinetics (zeta potential) of the particles. A plot of the zeta potential against pH in Fig. 5 reveals that the isoelectric point for FNT1 is at pH 5.8 and its zeta potential value is −21mV at pH 7 and gave high surface area. The mesoporous coating imparts a continuous positive charge over the lower pH range (below the isoelectric point) that may be due to the presence of protonated surface hydroxyl groups (Ti–OH2+). Thus, the increased positive charge density on the surface of the adsorbent at lower pH increases the zeta potential value, whereas, at higher pH, the protonated surface sites decrease and the zeta potential becomes more negative.

Fig. 5.

The zeta-potential of FNT1 at various pHs.

3.6EPR study

From the EPR spectrum of FNT1 at 295K, which is shown in Fig. 6, a signal at a g-tensor value of 1.991 is obtained, indicating the presence of Nb(V) in TiO2[61]. But at a lower g-factor value a small hump or EPR signal was observed in the same spectrum, which suggested Fe(III) might be present in the composition [62]. We conclude that Fe and Nb doped in TiO2 lattice are responsible for photochemical reactions, but it is not yet clear if one contributes than other. No EPR signal was detected on pure TiO2.

Fig. 6.

EPR of FNT1.

3.7X-ray photoelectron spectroscopy (XPS) analysis

Fig. 7 shows the XPS spectra of FNT1 in a range (binding energy 355–750eV) covering the photoemission peaks. The photoelectron peak of Nb(3p3/2) at 365.2eV in Fig. 7a indicates +5 oxidation state of Nb. There are two peaks in the Ti(2p) binding energy region shown in Fig. 7b. The peak located at a binding energy of 458.9eV is assigned to Ti(2p3/2) and another one located at 464.5eV corresponds to the Ti(2p1/2). The splitting between Ti(2p3/2), and Ti(2p1/2) core levels is 5.6eV, indicating a normal state of Ti4+ in the anatase FNT1. Fig. 7c shows the photoelectron peaks at 529.8eV corresponding to the O(1s). Fig. 7d shows the XPS spectra covering the Fe(2p) peaks. The Fe(2p) core level are split into Fe2p3/2 and Fe2p1/2 due to spin orbit coupling and appear at their normal positions at 710.8 and 724.7eV, respectively. The XPS spectra do not show any elemental Fe peak. A hump at ∼719eV is characteristic of the presence of Fe3+. The above results reveal that spectrum of FexNbxTi1−2xO2−x/2 corresponds to Fe2O3, Nb2O5 and TiO2 specimens on the surface. It indicates that the metal ions exist as Fe(III), Nb(V) and Ti(IV). The surface atomic concentration of FexNbxTi1−2xO2−x/2 (x=0.01) estimated from XPS is shown in Table 2. The surface concentrations for oxygen, iron, niobium and titanium atoms together with the atomic ratio for Fe/Ti (1.05), and Nb/Ti (1.04) were obtained from the results of XPS analysis.

Fig. 7.

XPS spectra of FNT1 [(a) Nb3p3/2, (b) Ti2p3/2 and Ti2p1/2, (c) O1s and (d) Fe2p3/2 and Fe2p1/2].

Table 2.

The surface atom concentration for oxygen, Cr, Nb and Ti atoms of the FexNbxTi1−2xO2−x/2 (x=0.01) by XPS.

Sample  Atomic surface concentration obtained by XPS (%)
  Fe  Nb  Ti  Fe/Ti  Nb/Ti 
FexNbxTi1−2xO2−x/2 (x=0.01)  90.05  0.104  0.105  9.741  1.06  1.07 
3.8Photocatalytic activity of FexNbxTi1−2xO2−x/2

Photocatalytic activity of FexNbxTi1−2xO2−x/2 nanoclusters is as follows: a freshly prepared aqueous solution of NaBH4 (0.502mol dm−3) is introduced into each of the eight sets of 100mL beaker containing 50mL of aqueous solution of 4-nitrophenol (4-NP). Before introducing NaBH4 solution into the mixture, the reaction container was kept in dark for about 1h to reach adsorption equilibrium. In aqueous medium 4-NP dissolved slowly forming a light yellow solution. Upon addition of NaBH4 dissolution was quick with the development of a deep yellow color. To the mixture, 0.1g of each of the FexNbxTi1−2xO2−x/2 is added and then stirred continuously. In the absence of catalysts the 4-NP was reduce to 4-aminophenol (4-Amp) very slowly under UV light. Fig. 8a–d represents the reaction rate constant and reduction efficiency of 4-nitrophenol, both in the presence and absence of UV light and catalysts, respectively. Inset of Fig. 8a represents the reduction of 4-NP at small time interval (2.5min) in the presence of FNT1. The result shows that yellow color of 4-NP disappears just after 10min in the presence of the FNT1 and UV light. But in the absence of UV light it takes about 20min for reduction. The other compositions FNT2 and FNT3 took much more time i.e. 18 and 35min in the presence of UV light respectively, and their corresponding titanates (Nb–TiO2 and Fe–TiO2) and prepared TiO2 takes much more time for formation of 4-Amp (shown in Table 1). With only 4-NP and NaBH4 but without the catalyst it takes 82 and 90min for the reduction to occur in the presence and the absence of UV light, respectively. The catalytic activity of TiO2, and the formation of 4-AmP were not observed in presence of UV light. Therefore, FNT1 catalysts give much faster reaction kinetics (5.89×10−5min−1) than that of FNT2, FNT3, FNT4 and their corresponding Fe/Nb titanates and TiO2 due to high porousness of the materials and small particle sizes. It has been well established that photocatalysis is a surface-based reaction, therefore a higher surface area improves the photocatalytic efficiency because of the availability of more reaction sites [63]. As a consequence, it enhanced photocatalytic activity through efficient adsorption of the reactant on the catalyst surface. FNT1 catalyst led to a significant decrease of the absorption peak at 416nm and increase of absorbance peak at 282nm in UV–vis spectra corresponding to 4-NP. During the reduction, the yellow color faded with the simultaneous formation of a slight shifted peak position and a new peak grows at 228nm assigned to 4-AmP in UV–vis spectra (Fig. 9) [64,65]. The complete disappearance of the UV–vis absorption peak at 416nm of 4-NP occurred at 10min, which indicates to the complete reduction of 4-NP in to 4-AmP. However, the reduction of 4-NP was not accomplished well even under the condition which uses large excess of NaBH4 in the absence of the catalyst. It is also observed that the dopant concentrations of Fe and Nb (0.5mol%) in TiO2 is not much more photoactive compared to FNT1. Therefore, the optimal loading of Fe and Nb in TiO2 is 1mol%.

Fig. 8.

(a)–(d) represents the reaction rate constant and reduction efficiency of 4-nitrophenol, in the presence and absence of UV light and catalysts.

Fig. 9.

UV–vis absorbance changes during the reaction in the presence of catalyst and UV-light and also changes the color of the p-NP solution.

3.9Proposed mechanism

NaBH4 itself reduces 4-NP to 4-AmP but in the presence of the catalyst the rate of reduction is much faster (Fig. 9). Fe, Nb and Ti exist as Fe(III), Nb(V) and Ti(IV) oxidation state (supported by XPS) in the FNT composites. Both Fe(III) and Nb(V) are active in UV light, so we cannot precisely say which ions are responsible for the generation of e/h+ pairs. TiO2 itself is EPR inactive but in the presence of Fe and Nb in the composites it shows good EPR signal (proved by EPR spectrum). It shows Fe and Nb to be responsible for the generation of electron/hole pair through mutual charge transfer from Fe(III) and Nb(V) with Ti(IV) ion in the presence of irradiance, with light energy (photon), which is equal to or greater than its band-gap energy, ΔEg of the photocatalyst, the excited electron in the valence band (Fe3+/Nb5+) is transferred to the empty conduction band (Fe2+/Nb4+). Hence, this Fe2+/Nb4+ reduces faster p-nitrophenol to 4-AmP. Furthermore, the activity of the nanostructured Fe0.01Nb0.01Ti0.98O1.995 catalyst is reasonably high, due to high surface area, and is largely dependent on their microstructure (mesoporous characters). In the nanoparticle phase, the surface to volume ratio increases drastically and the surface atoms include an increasing fraction of the total particulate volume having high defect structures. Thus, they are expected to show drastically improved catalytic properties.

3.10Effect of temperature

The effect of annealing temperature of mixed oxides on the photocatalytic activity was also investigated. Fig. 10 shows the profiles of the photo-reduction of 4-NP under UV light irradiation using FNT1, calcined at 300°, 400° and 500°C. The samples calcined at 300°C showed the highest photocatalytic activity as compared to other temperatures. This may be primarily due to the anatase structure and secondly the high surface area is also responsible for the photocatalytic activity. Above 300°C the activity of catalyst decreases with rise of calcination temperatures. This phenomenon can be related to the collapsing of pores as FNT1 particles grow at higher temperatures. In other words, although a higher calcination, temperature results in greater crystallinity, which should improve photocatalytic performance; it can also lead to a drastic decrease of surface area, which results in reduced photocatalytic performance.

Fig. 10.

The effect of calcinations temperature of FNT1 on p-nitrophenol under UV light, the catalyst concentration is Ccatalysts=1g/l. 4-NP concentration is C4NP=10mM.

3.11Stability of the FexNbxTi1−2xO2−x/2 (FNT) photocatalyst

To examine the stability of the FNT photocatalyst, the photocatalytic reduction ability was investigated by repeating p-nitrophenol degradation experiments five times. After each cycle, the FNT photocatalysts were washed thoroughly with water, and a fresh solution of p-nitrophenol was added before each photocatalytic run in the reactor. Fig. 11 indicates that the photocatalytic efficiency of FNT decreased slowly with increase in the repetition of the cycles. After the fifth cycle, the efficiency of the FNT catalysts decreased about 1.5% compared to the total reduction of 4-nitrophenol. This is attributable to the loss of catalysts resulting from washing of the catalysts with water, which was not observed in the naked eye. This suggests that the FNT photocatalysts have excellent stability and reliability for photo reduction of pollutants.

Fig. 11.

Photocatalytic stability of FNT1 at same time interval and use fresh 4-NP solution for five times.


In summary, we have developed a conceptually different method to incorporate nanocluster mixtures {Fe(III) and Nb(V) species} onto TiO2 lattice and initially found that both the efficient photocatalytic reduction of 4-nitrophenol under UV light can be achieved in our materials. Moreover, the detailed structure for our nanoclusters was comprehensively characterized by TEM analysis, and the possible mechanism of the reduction properties could be explained. The balance between Fe(III) and Nb(V) with Ti(IV) states in FexNbxTi1−2xO2−x/2 is critical to achieve efficient p-nitrophenol reduction. This is probably due to efficient generation of electron and hole under UV light through mutual charge transfer from Fe(III) and Nb(V) ion in the clusters. As a result Fe(III) transform to Fe(II) and Nb(V) convert to Nb(IV), where electron resides in the conduction band and a hole is captured forming Fe2+/Nb4+. Therefore, this Fe2+/Nb4+ reduce quickly p-nitrophenol to p-aminophenol. Furthermore, mesoporous FNT1 has continued to be highly active in photocatalytic applications because it is beneficial for promoting the diffusion of reactants and products, as well as for enhancing the photocatalytic activity by facilitating access to the reactive sites on the surface of photocatalyst.

Conflict of interest

The author declares no conflicts of interest.


The author is grateful to the Department of Science and Technology (DST) as “Fast Track Scheme for Young Scientists” (SR/FT/CS-021/2010), New Delhi, India for the financial grant offered in support of this work.

K.S. Shin, J.Y. Choi, C.S. Park, H.J. Jang, K. Kim.
Facile synthesis and catalytic application of silver-deposited magnetic nanoparticles.
Catal Lett, 133 (2009), pp. 1-7
S.G. Anju, K.P. Jyothi, J. Sindhu, Y. Suguna, E.P. Yesodharan.
Ultrasound assisted semiconductor mediated catalytic degradation of organic pollutants in water: comparative efficacy of ZnO, TiO2 and ZnO–TiO2.
Res J Recent Sci, 1 (2012), pp. 191-201
R. Zouaghi, B. David, J. Suptil, K. Djebbar, A. Boutiti, S. Guittonneau.
Sonochemical and sonocatalytic degradation of monolinuron in water.
Urol Survey, 18 (2011), pp. 1107-1112
W. Zhang, F. Tan, W. Wang, X. Qiu, X. Qiao, J. Chen.
Facile, template-free synthesis of silver nanodendrites with high catalytic activity for the reduction of p-nitrophenol.
J Hazard Mater, 217 (2012), pp. 36-42
S.K. Cushing, J. Li, F. Meng, T.R. Senty, S. Suri, M. Zhi, et al.
Photocatalytic activity enhanced by plasmonic resonant energy transfer from metal to semiconductor.
J Am Chem Soc, 134 (2012), pp. 15033-15041
D.S. Wang, Y.D. Duan, Q.Z. Luo, X.Y. Li, J. An, L.L. Bao, et al.
Novel preparation method for a new visible light photocatalyst: mesoporous TiO2 supported Ag/AgBr.
J Mater Chem, 22 (2012), pp. 4847-4854
T.K. Ghorai, P. Dhak.
New synthetic approach, mesoporous properties and photocatalytic activity of titania adapted chromium-niobate nanocatalysts.
Adv Mater Lett, 4 (2013), pp. 121-130
Z. Xiong, J. Ma, W.J. Ng, T.D. Waite, X.S. Zhao.
Silver-modified mesoporous TiO2 photocatalyst for water purification.
Water Res, 45 (2011), pp. 2095-2103
H. Luo, C. Wang, Y. Yan.
Synthesis of mesostructured titania with controlled crystalline framework.
Chem Mater, 15 (2003), pp. 3841-3846
H. Yun, K. Miyazawa, H. Zhou, I. Honma, M. Kuwabara.
Synthesis of mesoporous thin TiO2 films with hexagonal pore structures using triblock copolymer templates.
Adv Mater, 13 (2001), pp. 1377
P. Kluson, P. Kacer, T. Cajthaml, M. Kalaji.
Preparation of titania mesoporous materials using a surfactant-mediated sol–gel method.
J Mater Chem, 11 (2001), pp. 644
S.C. Hayden, N.K. Allam, M.A. El-Sayed.
TiO2 nanotube/CdS hybride electrodes: extraordinary enhancement in the inactivation of Escherichia coli.
J Am Chem Soc, 132 (2010), pp. 14406-14408
J. Ravez, C. Broustera, A. Simon.
Lead-free ferroelectric relaxor ceramics in the BaTiO3–BaZrO3–CaTiO3 system.
J Mater Chem, 9 (1999), pp. 1609-1613
A. Arshak, K. Arshak, D. Morris, O. Korostynska, E. Jafer.
Investigation of TiO2 thick film capacitors for use as strain gauge sensors.
Sens Actuators A: Phys, 122 (2005), pp. 242-249
S. Dutta, A.K. Patra, S. De, A. Bhaumik, B. Saha.
Self-assembled TiO2 nanospheres by using a biopolymer as a template and its optoelectronic application.
ACS Appl Mater Interfaces, 4 (2012), pp. 1560-1564
R. Shirley, M. Kraft.
Spectral properties of a spin-coherent Luttinger liquid.
Phys Rev B, 81 (2010), pp. 075111
Z. Li, H. Zhang, W. Zheng, W. Wang, H. Huang, C. Wang, et al.
Highly sensitive and stable humidity nanosensors based on LiCl doped TiO2 electrospun nanofibers.
J Am Chem Soc, 130 (2008), pp. 5036-5037
X. Du, Y. Wang, Y. Mu, L. Gui, P. Wang, Y. Tang.
A new highly selective H2 sensor based on TiO2/PtO–Pt dual-layer films.
Chem Mater, 14 (2002), pp. 3953-3957
M.T. Colomer, J.R. Jurado.
Structural, microstructural, and electrical transport properties of TiO2–RuO2 ceramic materials obtained by polymeric sol–gel route.
Chem Mater, 12 (2000), pp. 923-930
J. Yan, F. Zhou.
TiO2 nanotubes: structure optimization for solar cells.
J Mater Chem, 21 (2011), pp. 9406-9418
H.G. Jung, Y.S. Kang, Y.K. Sun.
Anatase TiO2 spheres with high surface area and mesoporous structure via a hydrothermal process for dye-sensitized solar cells.
Electrochim Acta, 55 (2010), pp. 4637-4641
U. Bach, D. Lupo, P. Comte, J.E. Moser, F. Weissortel, J. Salbeck, et al.
Solid-state dye-sensitized mesoporous TiO2 solar cells with high photon-to-electron conversion efficiencies.
Nature, 395 (1998), pp. 583-585
C.T. Kresge, M.E. Leonowicz, W.J. Roth, J.C. Vartuli, J.S. Beck.
Ordered mesoporous molecular sieves synthesized by a liquid-crystal template mechanism.
Nature, 359 (1992), pp. 710-712
S.A. Davis, S.L. Burkett, N.H. Mendelson, S. Mann.
Bacterial templating of ordered macrostructures in silica and silica-surfactant mesophases.
Nature, 385 (1997), pp. 420-42310
T.K. Ghorai, N. Biswas.
Photodegradation of rhodamine 6G in aqueous solution via SrCrO4 and TiO2 nano-sphere mixed oxides.
J Mater Res Technol, 2 (2013), pp. 10-17
T.K. Ghorai, D. Dhak, S.K. Biswas, S. Dalai, P. Pramanik.
Photocatalytic oxidation of organic dyes by nano-sized metal molybdate incorporated titanium dioxide (MxMoxTi1−xO6) (M=Ni, Cu, Zn) photocatalysts.
J Mol Catal A: Gen, 273 (2007), pp. 224-229
J. Li, S.K. Cushing, J. Bright, F. Meng, T.R. Senty, P. Zheng, et al.
Ag@Cu2O core–shell nanoparticles as visible-light plasmonic photocatalysts.
ACS Catal, 3 (2013), pp. 47-51
F. Meng, J. Li, S.K. Cushing, J. Bright, M. Zhi, J.D. Rowley, et al.
Photocatalytic water oxidation by hematite/reduced grapheme oxide composites.
ACS Catal, 3 (2013), pp. 746-751
H. Zhang, C. Liang, J. Liu, Z. Tian, G. Wang, W. Cai.
Defect-mediated formation of Ag cluster-doped TiO2 nanoparticles for efficient photodegradation of pentachlorophenol.
Langmuir, 28 (2012), pp. 3938-3944
S.T. Kochuveedu, D. Kim, D.H. Kim.
Surface-plasmon-induced visible light photocatalytic activity of TiO2 nanospheres decorated by Au nanoparticles with controlled configuration.
J Phys Chem C, 116 (2012), pp. 2500-2506
T.K. Ghorai, S. Pramanik, P. Pramanik.
Synthesis and photocatalytic oxidation of different organic dyes by using Mn2O3/TiO2 solid solution and visible light.
Appl Surf Sci, 255 (2009), pp. 9026-9031
B. Peng, X. Meng, F. Tang, X. Ren, D. Chen, J. Ren.
General synthesis and optical properties of monodisperse multifunctional metal-ion-doped TiO2 hollow particles.
J Phys Chem C, 113 (2009), pp. 20240-20245
T.K. Ghorai, S.K. Biswas, P. Pramanik.
Photooxidation of different organic dyes (RB, MO, TB, and BG) using Fe(III)-doped TiO2 nanophotocatalyst prepared by novel chemical method.
Appl Surf Sci, 254 (2008), pp. 7498-7504
J.K. Jakovljevic, M. Radoicic, T. Radetic, Z. Konstantinovic, Z.V. Saponjic, J. Nedeljkovic.
Presence of room temperature ferromagnetism in CO2+ doped TiO2 nanoparticles synthesized through shape transformation.
J Phys Chem C, 113 (2009), pp. 21029-21033
M. Karimipour, J.M. Wikberg, V. Kapaklis, N. Shahtahmasebi, M.R.R. Abad, M. Yeganeh, et al.
Nanoparticles of Ni/NiO embedded in TiO2 synthesized by the complex-polymer sol–gel method.
Phys Scr, 84 (2011), pp. 035702
J. Li, F. Meng, S. Suri, W. Ding, F. Huang, N. Wu.
Photoelectrochemical performance enhanced by nickel oxide-hematite p–n junction photoanode.
Chem Commun, 48 (2012), pp. 8213-8215
X. Qiu, M. Miyauchi, K. Sunada, M. Minoshima, M. Liu, Y. Lu, et al.
Hybrid CuxO/TiO2 nanocomposites as risk-reduction materials in indoor environments.
ACS Nano, 6 (2012), pp. 1609-1618
T.K. Ghorai.
Photocatalytic degradation of 4-chlorophenol by CuMoO4-doped TiO2 nanoparticles synthesized by chemical route.
Open J Phys Chem, 1 (2011), pp. 28-36
Z. Zhang, Y. Yu, P. Wang.
Hierarchical top-porous/bottom-tubular TiO2 nanostructures decorated with Pd nanoparticles for efficient photoelectrocatalytic decomposition of synergistic pollutants.
ACS Appl Mater Interfaces, 4 (2012), pp. 990-996
F. Meng, Z. Hong, J. Arndt, M. Li, M. Zhi, F. Yang, et al.
Visible-light photocatalytic activity of nitrogen-doped La2Ti2O7 nanosheets originating from band gap narrowing.
Nano Res, 5 (2012), pp. 213-221
D.H. Wang, L. Jia, X.L. Wu, L.Q. Lu, A.W. Xu.
One-step hydrothermal synthesis of N-doped TiO2/C nanocomposites with high visible light photocatalytic activity.
Nanoscale, 4 (2012), pp. 576-584
F. Meng, J. Li, Z. Hong, M. Zhi, A. Sakla, C. Xiang, et al.
Photocatalytic generation of hydrogen with visible-light nitrogen-doped lanthanum titanium oxides.
Catal Today, 199 (2013), pp. 48-52
A.A. Ismail, D.W. Bahnemann.
Mesoporous titania photocalysst: preparation, characterization and reaction mechanism.
J Mater Chem, 21 (2011), pp. 11686
S. Senthilkumaar, K. Porkodi, R. Vidyalakshmi.
Photodegradation of a textile dye catalyzed by sol–gel derived nanocrystalline TiO2 via ultrasonic irradiation.
J Photochem Photobiol A, 170 (2005), pp. 225
W.J. Li, E.W. Shi, T. Fukuda.
Particle size of powders under hydrothermal conditions.
Cryst Res Technol, 38 (2003), pp. 847
H. Cui, K. Dwight, A. Weld.
Surface acidity and photocatalytic activity of Nb2O5/TiO2 photocatalysts.
J Solid State Chem, 1 (1995), pp. 187
M. Martos, B. Julian, H. Dehouli, D. Gourier, E. Cordoncillo, P. Escribano.
Synthesis and characterization of Ti1−2xNbxNixO2−x/2 solid solutions.
J Solid State Chem, 180 (2007), pp. 679-687
T.K. Ghorai, M. Chakraborty, P. Pramanik.
Photocatalytic performance of nano-photocatalyst from TiO2 and Fe2O3 by mechanochemical synthesis.
J Alloys Compd, 509 (2011), pp. 8158-8164
J. Virkutyte, R.S. Varma.
Visible light activity of Ag-loaded and guanidine nitrate-doped nano-TiO2: degradation of dichlorophenol and antibacterial properties.
RSC Adv, 2 (2012), pp. 1533-1539
J. Arana, J.M.D. Rodrıguez, O. Gonzalez-Dıaz, E.T. Rendon, J.A.H. Melian, G. Colon, et al.
Gas phase ethanol photocatalytic degradation study with TiO2 doped with Fe, Pd and Cu.
J Mol Catal A, 215 (2004), pp. 153
M. Okumura, S. Nakamura, S. Tsubota, T. Nakamura, M. Azuma, M. Haruta.
Chemical vapor deposition of gold on Al2O3, SiO2, and TiO2 for the oxidation of CO and of H2.
Catal Lett, 51 (1998), pp. 53-58
Y. Jing, L. Li, Q. Zhang, P. Lu, P. Liu, X. Lu.
Photocatalytic ozonation of dimethyl phthalate with TiO2 prepared by a hydrothermal method.
J Hazard Mater, 189 (2011), pp. 40-47
M. Andersson, L. Osterlund, S. Ljungstrom, A. Palmqvist.
Ion and solvent dynamics in gel electrolytes based on ethylene oxide grafted acrylate polymers.
J Phys Chem B, 106 (2002), pp. 10674-10679
K.B. Jaimy, S. Ghosh, S. Sankar, K.G.K. Warrier.
An aqueous sol–gel synthesis of chromium(III) doped mesoporous titanium dioxide for visible light photocatalysis.
Mater Res Bull, 46 (2011), pp. 914-921
C. Su, B.Y. Hong, C.M. Tseng.
Sol–gel preparation and photocatalysis of titanium dioxide.
Catal Today, 96 (2004), pp. 119
D.S. Lee, S.D. Han, S.M. Lee, J.S. Huh, D.D. Lee.
The TiO2-adding effects in WO3-based NO2 sensors prepared by coprecipitation and precipitation method.
Sens Actuators B, 65 (2000), pp. 331-335
A. Pathak, S. Mohapatra, S. Mohapatra, S.K. Biswas, D. Dhak, N.K. Pramanik, et al.
Preparation of nanosized mixed-oxide powders.
Am Ceram Soc Bull, 83 (2004), pp. 9301-9306
M. Addamo, M. Bellardita, A.D. Paola, L. Palmisano.
Preparation and photoactivity of nanostructured anatase, rutile and brookite thin films.
Chem Commun, (2006), pp. 4943-4945
S. Bakardjieva, J. Subrt, V. Stengl, M.J. Dianez, M.J. Sayagues.
Photoactivity of anatase-rutile TiO2 nanocrystalline mixtures obtained by heat treatment of homogeneously precipitated anatase.
Appl Catal B: Environ, 58 (2005), pp. 193-202
K.S.W. Sing.
Reporting physisorption data for gas/solid systems, with special reference to determination of surface area and porosity.
Pure Appl Chem, 54 (1982), pp. 2201
K.M. Reddy, D. Guin, S.V. Manorama, A.R. Reddy.
Selective synthesis of nanosized TiO2 by hydrothermal route: characterization, structure property relation, and photochemical application.
J Mater Res, 19 (2004), pp. 2567
C. Adan, A. Bahamonde, M. Fernandez-Garcia, A. Martinez-Arias.
Structure and activity of nanosized iron-doped anatase TiO2 catalysts for phenol photocatalytic degradation.
Appl Catal B: Environ, 172 (2007), pp. 11-17
X. Fan, T. Yu, L. Zhang, X. Chen, Z. Zou.
Photocatalytic degradation of acetaldehyde on mesoporous TiO2: effects of surface area and crystallinity on the photocatalytic activity.
Chin J Chem Phys, 20 (2007), pp. 733
S.C. Mitchel.
4th ed., (2000), pp. 580-604
H. Zhang, X. Yang.
Polym Chem, 1 (2010), pp. 670-677
Copyright © 2014. Brazilian Metallurgical, Materials and Mining Association
Journal of Materials Research and Technology

Subscribe to our newsletter

Article options
Cookies policy
To improve our services and products, we use cookies (own or third parties authorized) to show advertising related to client preferences through the analyses of navigation customer behavior. Continuing navigation will be considered as acceptance of this use. You can change the settings or obtain more information by clicking here.