Preparation of Cerium Modified Titanium Dioxide Nanoparticles and Investigation of Their Visible Light Photocatalytic Performance

Abstract

Mesoporous Ce[subscript]Ox[/subscript] /TiO2 nanoparticles have been successfully synthesized using titanate nanotubes as precursor through the hydrothermal-calcination method. The as-prepared materials were characterized by means of X-ray diffraction (XRD), X-ray photoelectron spectroscopy (XPS), transmission electron microscope (TEM), UV-vis diffuse reflectance spectra and nitrogen adsorption-desorption isotherm analysis. All the obtained Ce[subscript]Ox[/subscript] /TiO2 materials exhibit anatase phase. Ce element existed in two valance states of Ce3+ and Ce4+. Introduction of Ce species can effectively extend the spectral response from UV to visible light region. N2 adsorption-desorption analysis revealed that all the samples belong to mesoporous structure and have large BET surface area compared with P25. The Ce[subscript]Ox[/subscript] /TiO2 nanoparticles showed excellent photocatalytic activity in the degradation of MB under visible light irradiation.

Academic Editor:Wenjun Luo

Key Laboratory for Special Functional Materials, Henan University, Kaifeng 475004, China

Received 4 July 2014; Revised 21 August 2014; Accepted 8 September 2014; 1 December 2014

This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

1. Introduction

TiO₂ -based materials have been investigated intensively because of their outstanding physical and chemical properties and have been widely used in solar cells, gas sensors, photocatalysis, and other environmentally related applications [1-6]. However, the low utilization of the sunlight by titanium dioxide limits its practical application. Foreign ions doping is considered to be an effective approach to extend the light response to the visible light region of titanium dioxide [7-10]. Among these foreign ions, ceria (CeO₂ ), as an active system in the photodegradation of several molecules [11-13], has been intensively concerned. The redox shift between CeO₂ and Ce₂ O₃ can provide high capacity to store/release oxygen, which plays the role as an oxygen reservoir to exhibit excellent characteristics in transferring electrons. What's more, it also can shift the adsorption band toward to visible light range. Xiao et al. reported that mesoporous cerium doped TiO₂ nanofibers exhibited the highest photocatalytic activity under visible irradiation compared with the undoped TiO₂ nanofiber and the commercial Degussa P25 [14]. Xu et al. have reported that cerium doped titania could photocatalytically degrade formaldehyde under visible light [15]. Li et al. synthesized the ordered mesoporous CeO₂ doped TiO₂ photocatalyst by an evaporation-induced self-assembly method; their results showed that doping CeO₂ species into TiO₂ framework not only improves the thermal stability of the ordered mesoporous structure but also effectively extends the photoresponse of TiO₂ to the visible light region [16]. Nakamura et al. found that the Ti(IV)-O-Ce(III) bimetallic assemblies on mesoporous silica were an efficient visible light photocatalyst for the photooxidation of 2-propanol [17].

Nanotubes titanate acid (NTA) attracted much attention due to their many excellent properties, such as large BET surface area, strong adsorption capability, ion-exchange capacity, and one-dimensional structure. Recently, Viana et al. synthesized nanotubes titanate acid decorated with CeO₂ nanoparticles, and they reported that absorption region red-shifted apparently after decorating, and these composites can photodegrade the reactive blue 19 textile dye to a certain extent [18]. One of the main researches of our group focuses on the titanate nanotubes and their derivatives. Their morphology, structure, light absorption, thermal stability, formation mechanism, and photoelectrochemical and photocatalytic properties were investigated systematically through decades [19-22]. We found that the crystallinity of NTA was very poor and the photocatalytic activity was not good. However, the crystallinity and photocatalytic performance can be improved largely after thermal dehydration and structure reassemblage of NTA.

In this work, x % Ce_Ox /TiO₂ was prepared using NTA as the Ti precursor by the hydrothermal-calcination method. The doped Ce existed in the two valence states of Ce³⁺ and Ce⁴⁺ , which can act as the electron acceptor to improve the separation efficiency of the photogenerated electron-hole pairs. Moreover, the absorption of the visible light extended more apparently than that of the reference TiO₂ . The photodegradation yield of MB on Ce_Ox /TiO₂ was much higher than the commercial P25. The relationship between the morphology, structure, light absorption, and the photocatalytic performance was investigated in detail.

2. Experimental

2.1. Preparation of CeO_x /TiO₂

The titania precursor of nanotubular titanic acid (NTA) was prepared according to our previous reports [23]. A proper amount of Ce(NO₃ )₃ and 1 g of NTA were dissolved in 60 mL of deionized water and mixed by stirring. Then the resultant mixed suspension was transferred to the autoclave reactor and kept at 120°C for 4 h. The resultant mixture was transferred to a round bottom flask to evaporate water by a vacuum distillation and then the production was calcined at 400°C for 2 h. And as a result, the Ce_Ox /TiO₂ was obtained. The atomic ratio of Ce and Ti was designed as 0.1%, 0.3%, 0.5%, and 1%, and the samples were denoted as x % Ce_Ox /TiO₂ .

2.2. Characterization

The phase structure of various Ce_Ox /TiO₂ samples was analyzed by X-ray diffraction (XRD, Philips X'Pert Pro X-ray diffractometer; Cu-Kα radiation, λ = 0.15 nm). The X-ray photoelectron spectroscopic (XPS) measurement was carried out using ESCALAB210 with dual anode Mg X-ray source. All spectra were calibrated to the binding energy of the adventitious C 1 s peak at 285 eV. All samples were observed using a transmission electron microscopy (TEM, JEOL JEM-2100, accelerating voltage 200 kV). UV-vis diffuse reflectance spectra (DRS) were obtained on a Shimadzu U-3010 spectrometer, using BaSO₄ as a reference. The Brunauer-Emmett-Teller (BET) surface areas and average pore volumes were measured by automatic surface area and porosity analyzer (QUADRASORB SI).

2.3. Photocatalytic Reaction

The photocatalytic activity of each sample was evaluated in terms of the degradation of MB (10 mg/L). 0.1 g of photocatalyst was added into a 100 mL quartz photochemical reactor containing 100 mL of MB (10 mg/L) aqueous solution. The mixture was stirred for 1.5 h in dark to reach the adsorption-desorption equilibrium. A 300 W Xe lamp equipped with a UV cut-off filter (λ > 420 nm) was used as a visible light source. At given time intervals, the analytical samples were taken from the mixture and immediately centrifuged and then filtered to remove the particles. The concentration of MB was analyzed by checking the absorbance at 664 nm with a UV-vis spectrophotometer (UV-2500, Shimadzu, Japan). The photocatalytic behavior of Degussa P25 was also measured in the same conditions as a reference. The 4-chlorophenol (4-CP, 12 mg/L) was also selected as the colorless model pollutant to further evaluate the photocatalytic activity.

3. Results and Discussions

The XRD patterns of the series of Ce_Ox /TiO₂ samples with different content of Ce are shown in Figure 1. All of these Ce_Ox /TiO₂ samples show the typical anatase crystal phase; the typical diffraction peaks at 25.3°, 37.8°, 48.0°, 53.9°, 55.0°, and 62.7° corresponded to the (101), (104), (200), (105), (211), and (204) plane facet, respectively. Our previous work has reported that NTA belongs to an orthorhombic crystallinity [21]. From the above XRD results, we knew that NTA had been transformed to anatase TiO₂ completely through the hydrothermal-calcination process. The anatase peaks position of all samples undergoes almost no significant changes; this may be because the ionic radii of Ce³⁺ /Ce⁴⁺ (1.03/1.02 Å) are much bigger than that of Ti⁴⁺ (0.68 Å), so it is difficult for Ce³⁺ or Ce⁴⁺ to replace Ti⁴⁺ in the crystal lattice [14]. Thus, we inferred that cerium species should be in the form of cerium oxide modified on the surface of TiO₂ . However, the intensive peaks of all kinds of cerium species (CeO₂ /Ce₂ O₃ ) cannot be identified in XRD patterns. This should be due to the small content of cerium oxide species to be detected. Through calculation by the Scherrer formula, the particle sizes of Ce_Ox /TiO₂ are ca. 8-12 nm and there is no apparent difference between the samples with different content of Ce.

Figure 1: XRD patterns of x % Ce_Ox /TiO₂ nanoparticles obtained from NTA.

[figure omitted; refer to PDF]

XPS analysis was conducted to understand the surface chemical state of Ce and Ti in the Ce_Ox /TiO₂ nanoparticles. The spectra of Ce 3d are shown in Figure 2(a). The spectra of Ce 3d are rather complex because of the hybridization of Ce 3d and Ti 2p orbitals and splitting of the peaks [24]. The labels v and u indicate Ce 3d_5/2 and 3d_3/2 , respectively. According to the previous reports, u[variant prime][variant prime][variant prime]/v[variant prime][variant prime][variant prime] doublet is due to the primary photoemission from Ce⁴⁺ -O₂ , and v/u and v[variant prime][variant prime]/u[variant prime][variant prime] doublets are resulting from the transfer of one or two electrons from a filled O 2p orbital to an empty Ce 4f orbital. v[variant prime]/u[variant prime] doublet is due to photoemission from Ce³⁺ cations [25, 26]. The broad peak around 894.4 eV also indicates the presence of Ce³⁺ [24]. Therefore, the mixture of Ce³⁺ /Ce⁴⁺ oxidation states exists on the surface of TiO₂ nanoparticles, which exhibited excellent characteristics in transferring charge carriers. The binding energies of Ti2p_1/2 and 2p_3/2 in Ce_Ox /TiO₂ are shown in Figure 2(b). All binding energy values are about 464.4 eV and 485.8 eV, indicating that the cations exist in the form of Ti⁴⁺ [27]. With the increasing of Ce content, the Ti 2p binding energies do not change much. The binding energy of Ti³⁺ is lower than that of Ti⁴⁺ about 1.8 eV [28], which is not observed in the Ti 2p XPS spectra of the Ce_Ox /TiO₂ nanoparticles. The XPS spectra of O 1 s are shown in Figure 2(c). The two peak values indicate that at least two kinds of oxygen species are present at the surface. The stronger peak about 529.6 eV is a characteristic peak of the metal oxide (Ti-O), while the wide peak about 532 eV can attribute to surface hydroxyl groups (Ti-OH) [29, 30]. The cerium content obtained by EDX in Ce_Ox /TiO₂ nanoparticles is listed in Table 1. With the increasing of the theory content, the actual measured content increased, and theoretical content is greater than the actual measured content; this may be due to the loss during the experiment.

Table 1: Effect of surface area, pore diameter, pore volume and cerium atom content of Ce_Ox /TiO₂ nanoparticles.

Sample	BET surface area (m2 /g)	Pore diameter (nm)	Pore volume (cm3 /g)	Cerium atom content (%)
P25	54.89	15.22	0 .27	-
0.1% CeOx /TiO2	120.92	3.88	0.31	0.11%
0.3% CeOx /TiO2	133.86	3.88	0.33	0.17%
0.5% CeOx /TiO2	139.35	3.90	0.38	0.39%
1% CeOx /TiO2	137.22	3.88	0.34	0.77%

XPS spectra of x % Ce_Ox /TiO₂ nanoparticles (a) Ce 3d: (A) 1% Ce_Ox /TiO₂ , (B) 0.5% Ce_Ox /TiO₂ , (C) 0.3% Ce_Ox /TiO₂ , and (D) 0.1% Ce_Ox /TiO₂ ; (b) Ti 2p; (c) O 1 s.

(a) [figure omitted; refer to PDF]

(b) [figure omitted; refer to PDF]

(c) [figure omitted; refer to PDF]

The structural and morphological study was completed with the help of transmission electron microscopy technique. As shown in Figure 3, NTA displays uniform nanotube structure, the diameters of NTA are about 6-10 nm, and the surface of the nanotubes was much more smooth. Figure 3(b) indicated that the nanotubular morphology was kept after NTA was ion-exchanged with Ce(NO₃ )₃ , but some small particles were modified on the surface of NTA. After hydrothermal process, the nanotubular morphology transformed to octahedron, as shown in Figure 3(c). And the particle sizes increase and the octahedron changed to irregular particles after calcination at 400°C for 2 h. The formation process of Ce_Ox /TiO₂ nanoparticles from NTA was illustrated iconically in Figure 4.

TEM images of (a) NTA; (b) NTA ion-exchanged with Ce(NO₃ )₃ ; (c) 0.1% Ce_Ox /TiO₂ nanoparticles after hydrothermal method; (d) 0.1% Ce_Ox /TiO₂ nanoparticles after calcination.

(a) [figure omitted; refer to PDF]

(b) [figure omitted; refer to PDF]

(c) [figure omitted; refer to PDF]

(d) [figure omitted; refer to PDF]

Figure 4: Formation schematic diagram of Ce_Ox /TiO₂ nanoparticles.

[figure omitted; refer to PDF]

The UV-vis DRS of the as-prepared Ce_Ox /TiO₂ nanoparticles and the Degussa P25 reference are shown in Figure 5(a). By the increasing content of ceria, the UV-vis DRS of the Ce_Ox /TiO₂ nanoparticles are significantly shifted toward visible light as compared with that of P25. We have obtained a similar result with several researches. They reported that there would have a continuous increase of absorption in the visible region (going from ca. 380 to 500 nm) with increasing ceria content of the material [12, 31, 32]. Seen from our experimental results, the absorbance edge of the Ce_Ox /TiO₂ is shifted to high wavelength when the molar ratio of Ce/Ti is increased from 0 wt% to 1 wt%, which drives an apparent modification of the band gap. The band gap energy (Eg) was calculated from the UV absorption spectra taking into account that α(E) ∞ ^(E-Eg)m/2 , where α(E) is the absorption coefficient for a photon of energy E and m=1 for an indirect transition between bands [33]. The band gap energy is presented in Figure 5(b). This indicated that the hydrothermal-calcination method can effectively improve the optical properties.

(a) UV-vis DRS of P25 and the x % Ce_Ox /TiO₂ nanoparticles; (b) the plot of band gap energy and (αhν)^1/2 of P25 and Ce_Ox /TiO₂ nanoparticles.

(a) [figure omitted; refer to PDF]

(b) [figure omitted; refer to PDF]

The pore structure and surface areas of all samples are investigated by N₂ adsorption-desorption isotherm. As can be seen from Figure 6(a), all of these samples show isotherms of type IV, indicating the mesoporous structure of samples. The corresponding hysteresis loops are type H3 at a high relative pressure range of 0.75-1.0, suggesting the presence of slit-like pores [34, 35]. The generation of hysteresis loops is from the aggregation of the sheet-like TiO₂ nanoparticles. This result is also consistent with TEM images. In Figure 6(b), the pore distribution of 0.1% to 1% Ce_Ox /TiO₂ is in the range of 2-6 nm. The detailed BET surface area and pore volume for these samples are shown in Table 1. The series of Ce_Ox /TiO₂ nanoparticles prepared by NTA as precursor have large surface areas, which range from 120 to 137 m² g^-1 , while P25 only has 54 m² g^-1 . These large surface areas could provide much more adsorption sites for pollutant molecules, which is advantageous for improving the photocatalytic activity of the samples.

(a) Nitrogen adsorption-desorption isotherms of P25 and x % Ce_Ox /TiO₂ nanoparticles; (b) BJH pore-size distributions of P25 and x % Ce_Ox /TiO₂ nanoparticles.

(a) [figure omitted; refer to PDF]

(b) [figure omitted; refer to PDF]

Photodegradation of MB was used as the probe reaction to evaluate the photocatalytic activity of samples under visible light irradiation (Figure 7(a)). All the Ce_Ox /TiO₂ samples showed relatively higher activities as compared with P25. The reason for this result may have three points as follows. The first one is that the samples prepared by NTA as precursor have relative larger BET surface area. This can have much more adsorption sites for MB on the sample surface. The second is Ce_Ox , which enhanced the visible absorption of the samples. And the last one is Ce element existing as a mixture of Ce³⁺ /Ce⁴⁺ oxidation states, which can act as the electron acceptor for the photogenerated charge carriers, thereby improving the separation efficiency of the electron-hole pair. In particular, 0.1% Ce_Ox /TiO₂ exhibits the best photocatalytic activity, having a photodegradation yield of ca. 68% for MB dye. The stability of 0.1% Ce_Ox /TiO₂ on the photodegradation reaction was investigated. As shown in Figure 7(b), the degradation yield of MB on 0.1% Ce_Ox /TiO₂ had no significant difference in the consecutive three cycles. Therefore, 0.1% Ce_Ox /TiO₂ showed a very good stability in the degradation of MB.

Photocatalytic activity for MB (a) and stability (b) of P25 and x % Ce_Ox /TiO₂ nanoparticles; (c) detection of the active species of electrons and holes; (d) photocatalytic degradation yield of 4-CP on P25 and 0.1% Ce_Ox /TiO₂ nanoparticles.

(a) [figure omitted; refer to PDF]

(b) [figure omitted; refer to PDF]

(c) [figure omitted; refer to PDF]

(d) [figure omitted; refer to PDF]

With the increase of the doping amount with Ce, the photodegradation yield of MB decreased. In order to clarify the reasons for this result, the active species in photodegradation process of MB were detected. Methanol and silver nitrate solution were added into MB dyes solution to capture electrons and holes, respectively. As can be seen from Figure 7(c), the degradation yield of MB decreased to a certain extent when the electrons or holes were captured. And more significant change of activity decreased largely when the electrons were eliminated. So we speculated that both electrons and holes are involved in the photocatalytic degradation of MB dyes, and the contributions of electrons are larger than that of holes.

Based on the above experimental results, a possible mechanism for MB degradation on Ce_Ox /TiO₂ samples was proposed in Figure 8. Under visible light irradiation, the electrons can be excited from the valence band (VB) of Ce modified titania samples into conduction band (CB) and holes are left in the valence band. Ce element existed as a mixture of Ce³⁺ /Ce⁴⁺ oxidation states. The Ce⁴⁺ can act as the electron acceptor for the photogenerated charge carriers. So, the separation efficiency of the electron-hole pair can be improved. For the pure titania, both electrons and holes participate in photodegradation of MB organic pollutants. The excited electrons react with the adsorbed oxygen to form oxidizing species. MB was mineralized into carbon dioxide and water by the oxidizing species as well as holes. While part of the excited electrons would be trapped by Ce 4f orbitals, and cannot participate in the photocatalytic reaction. And the others not trapped by Ce and the holes would participate in the photocatalytic reaction (as shown in Figure 8); we come to the conclusion that the electrons play a predominance role in the progress of photodegradation of MB organic pollutants. So the electrons trapped by Ce 4f orbitals decrease the photocatalytic activity.

Figure 8: The proposed photocatalytic mechanism of Ce_Ox /TiO₂ nanoparticles for the degradation of MB under visible light.

[figure omitted; refer to PDF]

Besides MB, the colorless 4-chlorophenol (4-CP) was also selected as a model pollutant. The results were shown in Figure 7(d). Compared with P25, 0.1% Ce_Ox /TiO₂ showed much higher photocatalytic activity after irradiating for 6 h. The photodegradation yield of 4-CP on 0.1% Ce_Ox /TiO₂ reached ca. 79%, while the degradation yield on P25 was only 40%.

4. Conclusions

Mesostructured Ce_Ox /TiO₂ nanoparticles with different Ce contents have been successfully synthesized using titanate nanotubes as precursor by hydrothermal-calcination method. Fine-crystallized Ce_Ox /TiO₂ could be obtained and crystal size was about 8-12 nm. And the Ce did not incorporate into the lattice of TiO₂ , which just existed as the cerium oxide modified on the surface of TiO₂ . XPS results indicated that Ce species were in the form of Ce³⁺ and Ce⁴⁺ . TEM images presented that the NTA nanotubes have transformed to TiO₂ nanoparticles completely. Introduction of Ce species can effectively extend the spectral response from UV to visible area of TiO₂ . N₂ adsorption-desorption analysis revealed that all the samples belonged to mesoporous structure and had large surface area. All the Ce_Ox /TiO₂ nanoparticles showed much higher photocatalytic activity compared with P25 in the degradation of MB aqueous solution under the visible irradiation, especially for the 0.1% Ce_Ox /TiO₂ samples. As the Ce content increases, the degradation yield of MB decreased gradually, which should be due to the capture of electrons by Ce⁴⁺ .

Acknowledgments

The authors gratefully acknowledge the support of the National Natural Science Foundation of China (nos. 21103042, 21471047, 20973054, and 21203054), Program for Changjiang Scholars and Innovation Research Team in University (no. PCS IRT1126), and the Specialized Research Fund for the Doctoral Program of Higher Education (no. 20114103120001).

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

References

[1] J. Zhang, Z. Zhao, X. Wang, "Increasing the oxygen vacancy density on the TiO₂ surface by La-doping for dye-sensitized solar cells," The Journal of Physical Chemistry C , vol. 114, no. 43, pp. 18396-18400, 2010.

[2] W. Tu, Y. Zhou, Q. Liu, S. Yan, S. Bao, X. Wang, M. Xiao, Z. Zou, "An in situ simultaneous reduction-hydrolysis technique for fabrication of TiO₂ -graphene 2D sandwich-like hybrid nanosheets: graphene-promoted selectivity of photocatalytic-driven hydrogenation and coupling of CO₂ into methane and ethane," Advanced Functional Materials , vol. 23, no. 14, pp. 1743-1749, 2013.

[3] T. L. Thompson, J. T. Yates Jr., "Surface science studies of the photoactivation of TIO₂ -new photochemical processes," Chemical Reviews , vol. 106, no. 10, pp. 4428-4453, 2006.

[4] X. Chen, S. S. Mao, "Titanium dioxide nanomaterials: synthesis, properties, modifications and applications," Chemical Reviews , vol. 107, no. 7, pp. 2891-2959, 2007.

[5] G. Dagan, M. Tomkiewicz, "Titanium dioxide aerogels for photocatalytic decontamination of aquatic environments," Journal of Physical Chemistry , vol. 97, no. 49, pp. 12651-12655, 1993.

[6] Z. G. Zou, J. H. Ye, K. Sayama, H. Arakawa, "Direct splitting of water under visible light irradiation with an oxide semiconductor photocatalyst," Nature , vol. 414, no. 6864, pp. 625-627, 2001.

[7] Y. Cao, T. He, L. Zhao, E. Wang, W. Yang, "Structure and phase transition behavior of sn⁴⁺ -doped TiO₂ nanoparticles," Journal of Physical Chemistry C , vol. 113, no. 42, pp. 18121-18124, 2009.

[8] J. Zhu, W. Zheng, B. He, J. Zhang, M. Anpo, "Characterization of Fe-TiO₂ photocatalysts synthesized by hydrothermal method and their photocatalytic reactivity for photodegradation of XRG dye diluted in water," Journal of Molecular Catalysis A: Chemical , vol. 216, no. 1, pp. 35-43, 2004.

[9] M. A. Debeila, N. J. Coville, M. S. Scurrell, G. R. Hearne, "The effect of calcination temperature on the adsorption of nitric oxide on Au-TiO₂ : drifts studies," Applied Catalysis A: General , vol. 291, no. 1-2, pp. 98-115, 2005.

[10] W. Ren, Z. Ai, F. Jia, L. Zhang, X. Fan, Z. Zou, "Low temperature preparation and visible light photocatalytic activity of mesoporous carbon-doped crystalline TiO₂ ," Applied Catalysis B: Environmental , vol. 69, no. 3-4, pp. 138-144, 2007.

[11] M. D. Hernandez-Alonso, A. B. Hungria, A. Martinez-Arias, "Confinement effects in quasi-stoichiometric CeO₂ nanoparticles," Physical Chemistry Chemical Physics , vol. 6, no. 13, pp. 3524-3529, 2004.

[12] P. Ji, J. Zhang, F. Chen, M. Anpo, "Study of adsorption and degradation of acid orange 7 on the surface of CeO₂ under visible light irradiation," Applied Catalysis B: Environmental , vol. 85, no. 3-4, pp. 148-154, 2009.

[13] M. D. Hernandez-Alonso, A. B. Hungria, A. Martinez-Arias, M. Fernandez-Garcia, J. M. Coronado, J. C. Conesa, J. Soria, "EPR study of the photoassisted formation of radicals on CeO₂ nanoparticles employed for toluene photooxidation," Applied Catalysis B: Environmental , vol. 50, no. 3, pp. 167-175, 2004.

[14] G. Xiao, X. Huang, X. P. Liao, B. Shi, "One-pot facile synthesis of cerium-doped TiO₂ mesoporous nanofibers using collagen fiber as the biotemplate and its application in visible light photocatalysis," Journal of Physical Chemistry C , vol. 117, no. 19, pp. 9739-9746, 2013.

[15] Y. H. Xu, H. R. Chen, Z. X. Zeng, B. Lei, "Investigation on mechanism of photocatalytic activity enhancement of nanometer cerium-doped titania," Applied Surface Science , vol. 252, no. 24, pp. 8565-8570, 2006.

[16] G. Li, D. Zhang, J. C. Yu, "Thermally stable ordered mesoporous CeO₂ /TiO₂ visible-light photocatalysts," Physical Chemistry Chemical Physics , vol. 11, no. 19, pp. 3775-3782, 2009.

[17] R. Nakamura, A. Okamoto, H. Osawa, H. Irie, K. Hashimoto, "Design of all-inorganic molecular-based photocatalysts sensitive to visible light: Ti(IV)-O-Ce(III) bimetallic assemblies on mesoporous silica," Journal of the American Chemical Society , vol. 129, no. 31, pp. 9596-9597, 2007.

[18] B. C. Viana, O. P. Ferreira, A. G. Souza Filho, "Decorating titanate nanotubes with CeO₂ nanoparticles," The Journal of Physical Chemistry C , vol. 113, no. 47, pp. 20234-20239, 2009.

[19] Q. Li, R. Li, Y. Xing, L. Zong, J. Yang, "Incorporation of Sn²⁺ into titanic acid nanotubes and investigation of their visible-light-responsive photocatalytic activity," Science of Advanced Materials , vol. 5, no. 3, pp. 227-232, 2013.

[20] Y. Xing, R. Li, Q. Li, J. Yang, "A new method of preparation of AgBr/TiO₂ composites and investigation of their photocatalytic activity," Journal of Nanoparticle Research , vol. 14, no. 12, article 1284, 2012.

[21] J. Yang, Z. Jin, X. Wang, W. Li, J. Zhang, S. Zhang, X. Guo, Z. Zhang, "Study on composition, structure and formation process of nanotube Na₂ Ti₂ O₄ (OH)₂ ," Journal of the Chemical Society. Dalton Transactions , no. 20, pp. 3898-3901, 2003.

[22] Q. Y. Li, L. L. Zong, Y. Y. Xing, X. Wang, L. Yu, J. Yang, "Preparation of g-C₃ N₄ /TiO₂ nanocomposites and investigation of their photocatalytic activity," Science of Advanced Materials , vol. 5, no. 9, pp. 1316-1322, 2013.

[23] M. Zhang, Z. Jin, J. Zhang, "Effect of annealing temperature on morphology, structure and photocatalytic behavior of nanotubed H₂ Ti₂ O₄ (OH)₂ ," Journal of Molecular Catalysis A: Chemical , vol. 217, no. 1-2, pp. 203-210, 2004.

[24] M. Nasir, Z. Xi, M. Xing, J. Zhang, F. Chen, B. Tian, S. Bagwasi, "Study of synergistic effect of Ce- and S-codoping on the enhancement of visible-light photocatalytic activity of TiO₂ ," The Journal of Physical Chemistry C , vol. 117, no. 18, pp. 9520-9528, 2013.

[25] H. Liu, M. Wang, Y. Wang, Y. Liang, W. Cao, Y. Su, "Ionic liquid-templated synthesis of mesoporous CeO₂ -TiO₂ nanoparticles and their enhanced photocatalytic activities under UV or visible light," Journal of Photochemistry and Photobiology A: Chemistry , vol. 223, no. 2-3, pp. 157-164, 2011.

[26] B. M. Reddy, A. K. Khan, Y. Yamada, T. Kobayashi, S. Loridant, J.-C. Volta, "Structural characterization of CeO₂ -TiO₂ and V₂ O₅ /CeO₂ -TiO₂ catalysts by Raman and XPS techniques," The Journal of Physical Chemistry B , vol. 107, no. 22, pp. 5162-5167, 2003.

[27] X. Gao, Y. Jiang, Y. Zhong, Z. Luo, K. Cen, "The activity and characterization of CeO₂ -TiO₂ catalysts prepared by the sol-gel method for selective catalytic reduction of NO with NH₃ ," Journal of Hazardous Materials , vol. 174, no. 1-3, pp. 734-739, 2010.

[28] N. J. Price, J. B. Reitz, R. J. Madix, E. I. Solomon, "A synchrotron XPS study of the vanadia-titania system as a model for monolayer oxide catalysts," Journal of Electron Spectroscopy and Related Phenomena , vol. 98-99, pp. 257-266, 1999.

[29] J. Fang, X. Bi, D. Si, Z. Jiang, W. Huang, "Spectroscopic studies of interfacial structures of CeO₂ -TiO₂ mixed oxides," Applied Surface Science , vol. 253, no. 22, pp. 8952-8961, 2007.

[30] S. K. Parayil, H. S. Kibombo, C. M. Wu, R. Peng, T. Kindle, S. Mishra, S. P. Ahrenkiel, J. Baltrusaitis, N. M. Dimitrijevic, T. Rajh, R. T. Koodali, "Synthesis-dependent oxidation state of platinum on TiO₂ and their influences on the solar simulated photocatalytic hydrogen production from water," Journal of Physical Chemistry C , vol. 117, no. 33, pp. 16850-16862, 2013.

[31] S. V. N. T. Kuchibhatla, A. S. Karakoti, D. R. Baer, S. Samudrala, M. H. Engelhard, J. E. Amonette, S. Thevuthasan, S. Seal, "Influence of aging and environment on nanoparticle chemistry: implication to confinement effects in nanoceria," The Journal of Physical Chemistry C , vol. 116, no. 26, pp. 14108-14114, 2012.

[32] M. Palummo, G. Giorgi, L. Chiodo, A. Rubio, K. Yamashita, "The nature of radiative transitions in TiO₂ -based nanosheets," The Journal of Physical Chemistry C , vol. 116, no. 34, pp. 18495-18503, 2012.

[33] A. E. Jimenez Gonzalez, S. Gelover Santiago, "Structural and optoelectronic characterization of TiO₂ films prepared using the sol-gel technique," Semiconductor Science and Technology , vol. 22, no. 7, pp. 709-716, 2007.

[34] K. Lv, Q. Xiang, J. Yu, "Effect of calcination temperature on morphology and photocatalytic activity of anatase TiO₂ nanosheets with exposed 001 facets," Applied Catalysis B: Environmental , vol. 104, no. 3-4, pp. 275-281, 2011.

[35] L. C. Liu, Z. Y. Ji, W. X. Zou, X. Gu, Y. Deng, F. Gao, C. Tang, L. Dong, "In situ loading transition metal oxide clusters on TiO₂ nanosheets as co-catalysts for exceptional high photoactivity," ACS Catalysis , vol. 3, no. 9, pp. 2052-2061, 2013.