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

Authors: Jinfeng Liu; Haiyan Li; Qiuye Li; Xiaodong Wang; Min Zhang; Jianjun Yang
Journal: International Journal of Photoenergy
 (2014)

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## Abstract

Mesoporous CeOx/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 CeOx/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 CeOx/TiO2 nanoparticles showed excellent photocatalytic activity in the degradation of MB under visible light irradiation.


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## Body

## 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 Ce2O3 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% CeOx/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 CeOx/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 CeOx/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 CeOx/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% CeOx/TiO2.


### 2.2. Characterization

The phase structure of various CeOx/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.


## 2.1. Preparation of CeOx/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 CeOx/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% CeOx/TiO2.


## 2.2. Characterization

The phase structure of various CeOx/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 CeOx/TiO2 samples with different content of Ce are shown in Figure 1. All of these CeOx/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/Ce2O3) 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 CeOx/TiO2 are ca. 8–12 nm and there is no apparent difference between the samples with different content of Ce.Figure 1
XRD patterns ofx% CeOx/TiO2 nanoparticles obtained from NTA.XPS analysis was conducted to understand the surface chemical state of Ce and Ti in the CeOx/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 3d5/2 and 3d3/2, respectively. According to the previous reports, u′′′/v′′′ doublet is due to the primary photoemission from Ce4+–O2, and v/u and v′′/u′′ doublets are resulting from the transfer of one or two electrons from a filled O 2p orbital to an empty Ce 4f orbital. v′/u′ 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 Ti2p1/2 and 2p3/2 in CeOx/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 CeOx/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 CeOx/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 CeOx/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 ofx% CeOx/TiO2 nanoparticles (a) Ce 3d: (A) 1% CeOx/TiO2, (B) 0.5% CeOx/TiO2, (C) 0.3% CeOx/TiO2, and (D) 0.1% CeOx/TiO2; (b) Ti 2p; (c) O 1 s.
(a)
(b)
(c)The structural and morphological study was completed with the help of transmission electron microscopy technique. As shown in Figure3, 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 CeOx/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% CeOx/TiO2 nanoparticles after hydrothermal method; (d) 0.1% CeOx/TiO2 nanoparticles after calcination.
(a)
(b)
(c)
(d)Figure 4
Formation schematic diagram of CeOx/TiO2 nanoparticles.The UV-vis DRS of the as-prepared CeOx/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 CeOx/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 CeOx/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 thex% CeOx/TiO2 nanoparticles; (b) the plot of band gap energy and (αhν)1/2 of P25 and CeOx/TiO2 nanoparticles.
(a)
(b)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% CeOx/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 CeOx/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 andx% CeOx/TiO2 nanoparticles; (b) BJH pore-size distributions of P25 and x% CeOx/TiO2 nanoparticles.
(a)
(b)Photodegradation of MB was used as the probe reaction to evaluate the photocatalytic activity of samples under visible light irradiation (Figure7(a)). All the CeOx/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 CeOx, 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% CeOx/TiO2 exhibits the best photocatalytic activity, having a photodegradation yield of ca. 68% for MB dye. The stability of 0.1% CeOx/TiO2 on the photodegradation reaction was investigated. As shown in Figure 7(b), the degradation yield of MB on 0.1% CeOx/TiO2 had no significant difference in the consecutive three cycles. Therefore, 0.1% CeOx/TiO2 showed a very good stability in the degradation of MB.Photocatalytic activity for MB (a) and stability (b) of P25 andx% CeOx/TiO2 nanoparticles; (c) detection of the active species of electrons and holes; (d) photocatalytic degradation yield of 4-CP on P25 and 0.1% CeOx/TiO2 nanoparticles.
(a)
(b)
(c)
(d)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 Figure7(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 CeOx/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 CeOx/TiO2 nanoparticles for the degradation of MB under visible light.Besides MB, the colorless 4-chlorophenol (4-CP) was also selected as a model pollutant. The results were shown in Figure7(d). Compared with P25, 0.1% CeOx/TiO2 showed much higher photocatalytic activity after irradiating for 6 h. The photodegradation yield of 4-CP on 0.1% CeOx/TiO2 reached ca. 79%, while the degradation yield on P25 was only 40%.


## 4. Conclusions

Mesostructured CeOx/TiO2 nanoparticles with different Ce contents have been successfully synthesized using titanate nanotubes as precursor by hydrothermal-calcination method. Fine-crystallized CeOx/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 CeOx/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% CeOx/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+.



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*Source: 695679-2014-12-01.xml*