Next Article in Journal
Synthesis of D-Limonene Loaded Polymeric Nanoparticles with Enhanced Antimicrobial Properties for Potential Application in Food Packaging
Previous Article in Journal
First Phenol Carboxylation with CO2 on Carbon Nanostructured C@Fe-Al2O3 Hybrids in Aqueous Media under Mild Conditions
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Niobium Modification of Au/CeO2 for Enhanced Catalytic Performance over Benzene Combustion

1
School of Materials Science and Engineering, Shanghai Jiao Tong University, Shanghai 200240, China
2
National Engineering Research Center for Nanotechnology, Shanghai 200241, China
*
Authors to whom correspondence should be addressed.
Nanomaterials 2021, 11(1), 189; https://doi.org/10.3390/nano11010189
Submission received: 17 November 2020 / Revised: 29 December 2020 / Accepted: 29 December 2020 / Published: 13 January 2021

Abstract

:
A novel Au/Nb-CeO2 was obtained by loading Au to Nb-modified CeO2 adopting a thermal decomposition method. The modification effect of Nb on the physicochemical properties and performance of Au/CeO2 for benzene combustion was systematically clarified. The incorporated Nb species are found to be present in the two forms of highly-dispersed state and bulk NbOx into CeO2 lattice in the obtained Au/Nb-CeO2 catalyst. They greatly enlarged the BET surface area, improved the redox property, and strengthened the Au–support interaction. The addition of Nb also promotes catalytic performance of Au/CeO2, especially high-temperature performance: T90% decreases by ca. 40 °C and Au/Nb-CeO2 exhibits superior stability to Au/CeO2 at 230 °C. The slightly improved Au dispersion and redox properties resulted in the small increase on initial activity of Au/Nb-CeO2, but the large BET surface area and the strong Au–support interaction greatly promoted the high-temperature performance improvement of Au/Nb-CeO2 for benzene combustion reaction.

1. Introduction

Environmental pollution caused by volatile organic compounds (VOCs) have great harm to human health [1,2]. Therefore, VOCs pollution control are imperative. Up to now, catalytic combustion for VOCs control has been the important research subject in environmental management field, among which heterogeneous catalysis study on the building of high-performance catalysts for benzene combustion reaction is of great significance for alleviating air pollution [3,4,5].
Au/CeO2-based catalytic materials have attracted extensive attention owing to excellent low-temperature catalytic ability of nano-Au [6,7,8,9] and strong oxygen storage capacity of cerium oxide [10,11,12]. There are also many reports devoting to improving its catalytic performance, mainly by modifying the properties of CeO2 [13,14,15,16]. Among them, metals doping to CeO2 [17,18] is reported to be an effective strategy, especially in catalytic oxidation reactions, since proper metal dopants can promote oxygen mobility of CeO2 and stabilize nano-Au. Au/V doped-CeO2 usually exhibited excellent catalytic performance among the derived Au/CeO2 catalysts [15,16]. However, the toxicity of V further limits their application. Therefore, it is urgently needed to explore potential human-friendly candidate dopants to enhance the catalytic performance of Au/CeO2 catalyst for benzene combustion.
Fortunately, of the same VB family with V, Nb and its compounds performed beneficially to various catalytic reactions in the past decades, such as hydrocarbon oxidative dehydrogenation, ammonia oxidation, and nitric oxide removal [17,19]. However, only few studies focused on the influences of niobium on Au/CeO2 in VOCs removal, as it is hard to guarantee uniformity of components due to difficult solubility of niobium-containing compounds in conventional solvents. Thus, Nb has great potential as an alternative regulator to improve the performance of Au/CeO2 catalyst for benzene oxidation once the abovementioned difficulties were overcome.
Herein, the purpose of this work concentrates on the preparation and characterization of a novel Au/Nb-CeO2 catalyst. In this work, Nb-CeO2 was prepared adopting a thermal decomposition method and then Au was loaded on the Nb-modified CeO2 support. The catalytic performances of Au/Nb-CeO2 for benzene combustion were then evaluated. Furthermore, the modification effect of Nb on Au/CeO2 was systematically studied. This present work will help to explore the application of niobium-containing compounds in VOCs’ removal, and broaden new ideas for optimal design of catalysts.

2. Materials and Methods

2.1. Sample Preparation

CeO2, NbOx, and Nb-CeO2: In brief, an appropriate amount of aqueous solution of Ce(NO3)3·6H2O (0.03 mol/L) and NaOH (0.15 mol/L) were mixed under vigorous stirring at 60 °C for 2 h. Then the precipitates were collected and washed until pH = 7. It was then dried at 70 °C for 12 h and calcined at 400 °C for 2 h to obtain CeO2. A certain amount of niobium oxalate were calcinated at 400 °C for 2 h to obtain NbOx. Nb-CeO2 was prepared by a thermal decomposition method. In brief, a certain amount of niobium oxalate and CeO2 with molar ratio of Ce:Nb = 15:1 were mechanically mixed for 30 min, then calcined at 400 °C for 2 h to obtain Nb-CeO2.
Au/CeO2, Au/Nb-CeO2, and Au/NbOx: 1 wt% Au/CeO2 and Au/Nb-CeO2 was synthesized by a deposition-precipitation method. In brief, 1 g of CeO2 or Nb-CeO2 powder was added to an appropriate amount of aqueous solution of HAuCl4 (containing 0.01 g Au) under vigorous stirring at 60 °C. 0.05 mol/L NaOH solution was added into the suspension solution to adjust pH to 9. Then the obtained solution was kept stirring for 2 h at 80 °C. The precursor was collected, washed, dried under vacuum at 70 °C for 12 h and then calcined at 400 °C for 2 h to obtain Au/CeO2 or Au/Nb-CeO2 catalyst. Au/NbOx (Au loading was 1 wt %) was prepared by an impregnation method. In brief, 1 g of NbOx powder obtained by directly calcined niobium oxalate was added to aqueous solution of HAuCl4 (containing 0.01 g Au) under vigorous stirring at 80 °C. Then the suspension was kept stirring until water was completely evaporated. The obtained precursor was thoroughly washed with dilute ammonia solution, and then dried under vacuum at 70 °C for 12 h and calcined at 400 °C for 2 h to obtain Au/NbOx catalyst.

2.2. Catalyst Characterization

The X-ray diffraction (XRD) patterns were recorded on a D/MAX-2600PC diffractometer (Rigaku, Science of Japan Co., Ltd., Tokyo, Japan) operated at 40 kV and 100 mA with a scanning angle (2θ) of 20–90° at a scanning speed of 5 °/min. The BET specific surface of the prepared samples were determined by adsorption–desorption of N2 at liquid nitrogen temperature using a Micromeritics ASAP 2010 analyzer (Micromeritics, Norcross, GA, USA). The actual mass fraction of the Au in as-prepared catalysts was determined by inductive coupled plasma (ICP) on an iCAP7600 instrument (Thermo Fisher Scientific, Waltham, MA, USA). Transmission electron microscopy (TEM), high resolution transmission electron microscope (HRTEM), and scanning TEM images were performed on a JEM-2100 (JEOL) analyzer at an accelerating voltage of 200 kV. Raman spectra were recorded using an inVia reflex laser Raman instrument equipped with a charge coupled device (CCD) detector (Renishaw, Pliezhausen, Germany). The excitation source was the 514.5 nm line of Ar ions laser at a laser power of ca. 3 mW. H2-TPR experiments and CO pulse adsorption were carried out on an Auto Chem II chemisorption 2920 analyzer (Micromeritics, Norcross, GA, USA) apparatus equipped with a thermal conductivity detector (TCD). H2 temperature programming reduction (H2-TPR) experiments were carried out by heating catalysts (100 mg) in 10% H2-Ar flow (30 mL/min) at a heating rate of 10 °C/min from 40 to 900 °C. Before CO pulse adsorption experiment, 100 mg of catalyst was reduced at 300 °C for 2h in 10% H2-Ar atmosphere and then cooled to 50 °C, Next, the catalyst was swept with a He flow (50 mL/min). Finally, the catalyst was purged with a 10% CO-He flow. XPS measurements were made on an Axis Ultra DLD (Kratos, Hadano, Japan) spectrometer with a monochromatic Al Kα radiation (1486.6 eV). The charging effect of samples was corrected by setting the binding energy of adventitious carbon (C 1s) at 284.6 eV.

2.3. Catalytic Activity Measurements

The catalytic activity measurements for the catalytic oxidation of benzene were carried out at an ambient pressure in a quartz tubular fixed bed reactor (ID 8 mm), where 80 mg of catalyst (40–60 mesh) was placed. A thermocouple to monitor the reaction temperature was fixed near the reactor. The catalytic reaction was carried out from 80 °C to 400 °C. The inlet flow to the reactor was 40 mL/min with the weight hourly space velocity (WHSV) of 30,000 mL g−1 h−1. The feed gas was composed of benzene 1000 ppm balanced with air. The gaseous reactant of benzene was generated by causing N2 to flow into a vapor saturator. For comparison, the related activity tests were also carried out under different conditions. The concentration of effluent gas was analyzed by a gas chromatograph (Varian GC-450) (Varian Inc., Palo Alto, CA, USA) equipped with a flame ionization detector (FID). The yield to CO2 was measured using a mass spectrometer, HPR20 model (Hiden, Warrington, UK).

3. Results and Discussion

Figure 1 shows XRD patterns of as-prepared catalysts. NbOx presents amorphous structure whereas CeO2 exhibits a typical cubic fluorite structure (JCPDS no. 81-0792) [20]. After Nb was added to CeO2, Nb-CeO2 presented the almost same structure as CeO2. When Au was loaded on CeO2 and Nb-CeO2, both Au/CeO2 and Au/Nb-CeO2 also mainly exhibit CeO2 crystal structure, whereas no significant diffraction peaks from Au (ca. 38°) were obviously observed in their XRD patterns, indicating the small particle size of gold species on CeO2 and Nb-CeO2. Additionally, XRD patterns of Nb-CeO2 and Au/Nb-CeO2 did not show obvious diffraction peaks from NbOx, suggesting that Nb-contained species are amorphous or highly dispersed states in these samples. By analyzing the XRD patterns, the lattice parameter of CeO2 is slightly larger in Au/Nb-CeO2 (5.4163 Å) than in Au/CeO2 (5.4127 Å). As Nbn+ is smaller than Cen+, its partial incorporation into the CeO2 lattice is expected, resulting to the expansion of the lattice [21]. Moreover, the decrement of crystalline size of CeO2 for Au/Nb-CeO2 compared with Au/CeO2 (Table 1) indicates that Nb-addition hinders grain growth of CeO2. The decreased crystalline size is further confirmed by BET results that Au/Nb-CeO2 has a much larger BET specific surface area (203 m2 g−1) than Au/CeO2 (71 m2 g−1) (Table 1). Also, it is seen from Table 1 that the Au/Nb-CeO2 has larger real Au loading than Au/CeO2, indicating that Nb dopant is beneficial to the high-dispersion of supported Au particles.
Figure 2 shows the microstructure morphology of Au/Nb-CeO2 and Au/CeO2. Obviously, Au/Nb-CeO2 presents smaller CeO2 particle size than Au/CeO2 (Figure 2a,b), which further confirms XRD results that Nb addition leads in decreased crystalline size. It is also seen from Figure 2c that Au is highly dispersed on Nb-CeO2 surface. Additionally, Nb-CeO2 support mainly exposes (111) crystal plane of CeO2, and there presents amorphous structure (red-marked) affiliated to NbOx (Figure 2d,e), which are consistent with XRD results. It is worth noting that the amorphous NbOx seems to have an effect on Au anchoring or interaction between Au and supports (denoted as IMS) from Figure 2e, which will be further elaborated.
Figure 3 is Raman spectra of as-obtained samples. CeO2 exhibits a strong F2g vibration peak at 457 cm−1 and a weak oxygen vacancy defect-induced vibrational peak at 596 cm−1 [20], while the typical peaks at 133, 226, 300, 693, and 813 cm−1 could be associated with NbOx species [21,22]. Obviously, for Nb-CeO2 and Au/Nb-CeO2 samples, weak peak at 133, 226, 300, and 693 cm−1 are still observed apart from characteristic peak of CeO2, indicative of separate NbOx present in both of them. It is reported that 693 cm−1 is assigned to octahedrally coordinated niobium oxide compound [NbO6] of Nb2O5 [22]. In addition, there is a slight red-shift of F2g Raman band from CeO2 to Nb-CeO2, indicative of a longer Ce-O bond distance with Nb dopant [23]. In the meanwhile, increased band intensity at 596 cm−1 is observed on the Raman profile of Nb-CeO2, representative of more oxygen vacancies.
Compared with the corresponding ones of Au/CeO2, the F2g Raman band of CeO2 in Au/Nb-CeO2 does not shift to lower frequency as expected in Nb-CeO2, but it becomes widened (Table 2). The different modification effect of Nb on the Au/Nb-CeO2 and Nb-CeO2 might be due to the varied IMS since nano-Au is strongly dependent on support properties [24]. This is in agreement with morphology observation. The widening of F2g band is attributed to increased oxygen vacancies [25,26]. The structural and morphology analysis suggests that some niobium oxide species are present in the form of separate NbOx species while other niobium oxides are into the lattice of CeO2.
Figure 4 presents H2-TPR profiles of catalysts, where Au/CeO2 and Au/Nb-CeO2 exhibit very similar reduction behavior at <200 °C (peak I) and >600 °C (peak IV), whereas a peak in the range 250–350 °C is present in the TPR curve of Au/CeO2 (peak II) and another one in the range 400–500 °C in the TPR curve of Au/Nb-CeO2 (peak III). It is reported that peak I is ascribed to the reduction of Auδ+ to Au0 and to the superficial Ce4+ to Ce3+, whereas peak II, III, and IV are affiliated to reduction of remaining Ce4+ to Ce3+ on the surface, superficial Nb5+ to Nb4+ and reduction of deeper CeO2 or NbOx layers, respectively [27,28]. Compared with Au/CeO2, peak II disappears and peak I becomes larger and shifts to lower temperature in the TPR curve of Au/Nb-CeO2. Moreover, Au/Nb-CeO2 has larger H2 consumption amount than Au/CeO2 at <200 °C (Table 1). Slightly lowered reduction temperature and increased H2 consumption amount are attributed to Nb-promoted surface ceria reduction, showing that incorporated NbOx species slightly improve the redox ability of surface oxygen species on the modified ceria surface. Additionally, the peak IV shifts to lower temperature over Au/Nb-CeO2 than over Au/Nb-CeO2, indicating the improvement of the lattice oxygen mobility due to the formation of more oxygen vacancies resulted by NbOx addition. These are consistent with XRD and Raman results.
Figure 5 shows the XPS spectra of Au 4f, Nb 3d, Ce 3d, and O 1s for as-obtained samples. It is seen that surficial Nb/Ce molar ratio is 0.37 in Au/Nb-CeO2, much larger than 0.07 of ICP result (Table 1), indicating that the majority of NbOx species are highly dispersed on CeO2 surface. Further from the Nb 3d XPS deconvolution of Au/NbOx, it is revealed that there are two principal signals present at binding energies 206.7 eV and 205.5 eV, characteristic of Nb5+ and Nb4+, respectively [29,30,31], indicative of two valence of Nb species in Au/Nb-CeO2 [20,32]. It is also observed that the obvious deviation of Nb 3d XPS to lower binding energy over Au/Nb-CeO2 than Nb-CeO2 suggests that Au admission enhances decreased potential energy, and makes valence-electrons migration become much easier.
Both Ce3+ (ca. 885.2 eV and 903.2 eV) and Ce4+ are present in Nb-CeO2, Au/CeO2 and Au/Nb-CeO2 from Ce 3d XPS curves, and the surface Ce3+/Ce4+ ratio is slightly higher for Au/Nb-CeO2 than for Au/CeO2 (Table 1), representative of more oxygen defects on the surface of Au/Nb-CeO2. Two fitted peaks with binding energy located at ~530.0 eV and 531.7 eV, correspond to lattice oxygen (Olatt), and chemisorbed OH species (Osup) [33] are observed in the O 1s XPS spectra of Au/Nb-CeO2 and Au/CeO2, and the former shows higher Osup/Olatt molar ratio. This suggests that Nb incorporation promoted generation of surface active oxygen species. The Ce 3d and O 1s XPS results are in accordance with TPR and Raman results.
There is a slightly decreased Au 4f7/2 BE and increased Auδ+/Au ratio after Nb addition to Au/CeO2, indicative of the stronger interaction between Au and Nb-CeO2 [34,35]. By comparing the corresponding XPS spectra of Au/Nb-CeO2 and Nb-CeO2, there is slightly increased surface content of Ce3+ and surface active oxygen, contributing to the interaction between Au and Nb-CeO2. It is also seen that surface Nb/Ce ratio is 0.67 for Nb-CeO2 and 0.37 for Au/Nb-CeO2 (Table 1), respectively, indicating that Au admission promoted part of Nb into the CeO2 lattice. Thus, Nb addition also generated the strong interaction between Au and Nb-CeO2, confirming Raman results and morphology observation.
Thus, according to the data, NbOx are mainly present in the forms of two states: the majority are highly dispersive on the support surface and the minority are into the lattice. They are largely amorphous and present two valence states, Nb4+ and Nb5+. Both niobium oxide species modify the properties of Au/Nb-CeO2 by lattice distortion and modified interaction between Au and the support. Firstly, as found in XRD, Raman and XPS results, Nb dopant hinders the grain growth of CeO2, lengthens Ce-O bond and increases oxygen vacancy. These lead in much larger surface area (203 m2 g−1 for Au/Nb-CeO2 and 71 m2 g−1 for Au/CeO2) and better reducibility of Au/Nb-CeO2 than that of Au/CeO2 (H2-TPR results). Secondly, more small Au particles could be highly dispersed on the surface of modified Nb-CeO2 (morphology observation and Au dispersion data). Thirdly, confirmed by Raman and XPS data, compared with Au/CeO2, Au/Nb-CeO2 exhibited stronger Au–support interaction.
Next, we measured the activity of the novel Au/Nb-CeO2 sample for model reaction-benzene total oxidation, and the results are shown in Figure 6. For comparison, the activity test over Au/NbOx for this reaction was also firstly carried out. CO2 and H2O were the only products. From Figure 6, under the condition of 1000 ppm benzene and 30,000 mL/(g h) space velocity, Au/NbOx exhibits a poor activity with T10% (the temperature at 10% of benzene conversion) of 358 °C. From Figure 6, there are close T10% and T50% value for the Au/CeO2 and Au/Nb-CeO2, but T90% of Au/Nb-CeO2 decreases by ca. 40 °C than Au/CeO2. As the reaction temperature elevated to higher temperature, increasing activity increase was shown for the two samples. The T10%, T50%, and T90% for Au/CeO2 and Au/Nb-CeO2 are 147 °C, 215 °C, and 294 °C; and 144 °C, 207 °C, and 258 °C, which decreased by 3 °C, 8 °C, and 36 °C after Nb addition, respectively. That is, large activity improvement turned up at relatively high reaction temperature for benzene oxidation, especially after reaction temperature was elevated to above 200 °C. Thus, the Nb addition improved the catalytic activity of Au/CeO2, especially the high-temperature activity. Further the high-temperature performance improvement was verified by the long-term reaction at 230 °C. After 48 h of on-streams reaction at 230 °C, there is hardly any activity loss on Au/Nb-CeO2, whereas the conversion rate of Au/CeO2 begins to decrease obviously when benzene oxidation lasts for 20 h, indicating that Au/Nb-CeO2 presents much better long-term stability than Au/CeO2 at 230 °C.
Au dispersion of the fresh and the used Au/CeO2 and Au/Nb-CeO2 samples were further measured to analyze the reason for the above performance difference, which are shown in Table 3. Obviously, the Au dispersion is slightly higher for the fresh Au/Nb-CeO2 (72%) than Au/CeO2 (68%). Their TOFAu value was further calculated over moles of the surface Au atoms at 160 °C (at which the conversion is below 15%, where mass transfer limitation can be ignored). TOFAu values are 54.6 s−1 for Au/Nb-CeO2 and 53.4 s−1 for Au/CeO2, showing that nano-Au has approximately same catalytic capacity in the fresh two samples. After 1st run, the Au dispersion for Au/CeO2 decreased by 14% and the Au particle size grows by 0.43 nm, while no obvious Au dispersion and particle size growth were observed for the Au/Nb-CeO2-1st and even Au/Nb-CeO2-48 h (Table 3). That is, Au nanoparticles in Au/CeO2 tend to aggregate with each other but they could always be stabilized on the surface of Au/Nb-CeO2 during the benzene oxidation process. Even at high-temperature, the small Au nanoparticles could still be highly-dispersed on the Au/ Nb-CeO2 surface. These results demonstrated that the Nb addition are beneficial to keep the Au stabilization on the support surface.
It was reported that the property of gold catalysts is mainly determined by the size of gold particles and the nature of support [36,37]. The vacancy/surface lattice oxygen in the support could be the sites of oxygen adsorption/activation through Mars–van Krevelen mechanism. In the present system, compared with Au/CeO2, Nb dopant slightly increased the Au dispersion and the redox capacity of CeO2, which are the reasons for the small increase on the initial activity over the fresh Au/CeO2 and Au/Nb-CeO2 for benzene combustion reaction. According to the above characterization results, Nb addition greatly enlarged the BET surface area of Nb-CeO2, which is prone to highly spread Au nanoparticles on the surface and increases the contact of the catalyst with reactant molecular. As benzene combustion is an exothermic reaction, the extended reaction sites are easy to avoid heat concentration, which could help to prevent Au nanoparticles aggregation with each other. Furthermore, there are stronger Au–support interaction over Au/Nb-CeO2 than Au/CeO2, which is beneficial to stabilize nano-Au particles on catalyst surface. Thus, the slightly improved Au dispersion and redox properties resulted in the small increase on initial activity of Au/Nb-CeO2, but the large BET surface area and the strong Au–support interaction greatly promoted the high-temperature performance improvement of Au/Nb-CeO2 for benzene combustion reaction.

4. Conclusions

Au/Nb-CeO2 catalyst was obtained by loading Au to Nb-modified CeO2 adopting a facile thermal decomposition method. NbOx species are mainly present in Au/Nb-CeO2 catalyst in the forms of highly dispersed states and bulk species. The two forms of NbOx species modify properties of the Au/Nb-CeO2 by generating lattice distortion and modulating Au–support interaction. Nb addition make Au/Nb-CeO2 has a larger surface area, better redox ability and stronger Au–support interaction than Au/CeO2. It is also found that Nb addition slightly enhanced the initial activity of Au/CeO2, but greatly improved its high-temperature performance. There are a much decreased T90% and enhanced stability on Au/Nb-CeO2 catalyst than Au/CeO2. The slightly improved Au dispersion and redox properties resulted in the small increase on initial activity of Au/Nb-CeO2, but the large BET surface area and the strong Au–support interaction greatly promoted the high-temperature performance improvement and durability of Au/Nb-CeO2 for benzene combustion reaction.

Author Contributions

Investigation, Z.L. and X.Z.; Writing—original draft preparation, Z.L. and X.Z.; Writing—review and editing, Z.L., J.Y., and W.L.; Formal analysis, T.C.; Project administration, K.Z.; Supervision, D.H. All authors have read and agreed to the published version of the manuscript.

Funding

This work was financially supported by National Natural Science Foundation of China (grant no. 21607098), Shanghai Rising-Star Program (grant no. 17QB1402800), China Postdoctoral Science Foundation (grant no. 2018M642021), Minhang District Science and Technology Project of Shanghai (grant no. 2019MHC017) and Shanghai Jiao Tong University (grant no. 18X100040017).

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Piumetti, M.; Fino, D.; Russo, N. Mesoporous manganese oxides prepared by solution combustion synthesis as catalysts for the total oxidation of VOCs. Appl. Catal. B Environ. 2015, 163, 277–287. [Google Scholar] [CrossRef]
  2. Yang, C.; Miao, G.; Pi, Y.; Xia, Q.; Wu, J.; Li, Z.; Xiao, J. Abatement of various types of VOCs by adsorption/catalytic oxidation: A review. Chem. Eng. J. 2019, 370, 128–1153. [Google Scholar] [CrossRef]
  3. Jiang, W.; Feng, Y.; Zeng, Y.; Yao, Y.; Gu, L.; Sun, H.; Ji, W.; Arandiyan, H.; Au, C.-T. Establishing high-performance Au/cobalt oxide interfaces for low-temperature benzene combustion. J. Catal. 2019, 375, 171–182. [Google Scholar] [CrossRef]
  4. Li, J.; Zuo, S.; Qi, C. Preparation and high performance of rare earth modified Co/USY for benzene catalytic combustion. Catal. Commun. 2017, 91, 30–33. [Google Scholar] [CrossRef]
  5. Tang, W.; Wu, X.; Li, S.; Shan, X.; Liu, G.; Chen, Y. Co-nanocasting synthesis of mesoporous Cu–Mn composite oxides and their promoted catalytic activities for gaseous benzene removal. Appl. Catal. B Environ. 2015, 162, 110–121. [Google Scholar] [CrossRef]
  6. Zhang, J.; Jin, Y.; Li, C.; Shen, Y.; Li, H.; Hu, Z.; Di, X.; Liu, Z. Creation of three-dimensionally ordered macroporous Au/CeO2 catalysts with controlled pore sizes and their enhanced catalytic performance for formaldehyde oxidation. Appl. Catal. B Environ. 2009, 91, 11–20. [Google Scholar] [CrossRef]
  7. Tabakova, T.; Dimitrov, D.; Manzoli, M.; Vindigni, F.; Petrova, P.; Ilieva, L.; Zanella, R.; Ivanov, K. Impact of metal doping on the activity of Au/CeO2 catalysts for catalytic abatement of VOCs and CO in waste gases. Catal. Commun. 2013, 35, 51–58. [Google Scholar] [CrossRef]
  8. Xie, S.; Deng, J.; Zang, S.; Yang, H.; Guo, G.; Arandiyan, H.; Dai, H. Au–Pd/3DOM Co3O4: Highly active and stable nanocatalysts for toluene oxidation. J. Catal. 2015, 322, 38–48. [Google Scholar] [CrossRef]
  9. Kaminski, P.; Ziolek, M. Zr-oxides and its impact on total oxidation of methanol. Appl. Catal. B Environ. 2016, 187, 328–341. [Google Scholar] [CrossRef]
  10. Topka, P.; Delaigle, R.; Kaluža, L.; Gaigneaux, E.M. Performance of platinum and gold catalysts supported on ceria–zirconia mixed oxide in the oxidation of chlorobenzene. Catal. Today 2015, 253, 172–177. [Google Scholar] [CrossRef]
  11. Carltonbird, M.; Eaimsumang, S.; Pongstabodee, S.; Boonyuen, S.; Smith, S.M.; Luengnaruemitchai, A. Effect of the exposed ceria morphology on the catalytic activity of gold/ceria catalysts for the preferential oxidation of carbon monoxide. Chem. Eng. J. 2018, 344, 545–555. [Google Scholar] [CrossRef]
  12. Araiza, D.G.; Gómez-Cortés, A.; Díaz, G. Effect of ceria morphology on the carbon deposition during steam reforming of ethanol over Ni/CeO2 catalysts. Catal. Today. 2020, 349, 235–243. [Google Scholar] [CrossRef]
  13. Nedyalkova, R.; Ilieva, L.; Bernard, M.C.; Hugot-Le Goff, A.; Andreeva, D. Gold supported catalysts on titania and ceria, promoted by vanadia or molybdena for complete benzene oxidation. Mater. Chem. Phys. 2009, 116, 214–218. [Google Scholar] [CrossRef]
  14. Ying, F.; Wang, S.; Au, C.-T.; Lai, S.Y. Highly active and stable mesoporous Au/CeO2 catalysts prepared from MCM-48 hard-template. Microporous Mesoporous Mater. 2011, 142, 308–315. [Google Scholar] [CrossRef]
  15. Yang, S.M.; Liu, D.M.; Liu, S.Y. Catalytic combustion of benzene over Au supported on ceria and vanadia promoted ceria. Top. Catal. 2008, 47, 101–108. [Google Scholar] [CrossRef]
  16. Andreeva, D.; Nedyalkova, R.; Ilieva, L.; Abrashev, M.V. Nanosize gold-ceria catalysts promoted by vanadia for complete benzene oxidation. Appl. Catal. A Gen. 2003, 246, 29–38. [Google Scholar] [CrossRef]
  17. Xie, Q.; Chen, L.; Weng, W.; Wan, H. Preparation of MoVTe(Sb)Nb mixed oxide catalysts using a slurry method for selective oxidative dehydrogenation of ethane. J. Mol. Catal. A Chem. 2005, 240, 191–196. [Google Scholar] [CrossRef]
  18. Rocha, A.S.; Forrester, A.M.S.; de la Cruz, M.H.C.; da Silva, C.T.; Lachter, E.R. Comparative performance of niobium phosphates in liquid phase anisole benzylation with benzyl alcohol. Catal. Commun. 2008, 9, 1959–1965. [Google Scholar] [CrossRef]
  19. Tanabe, K.; Okazaki, S. Various reactions catalyzed by niobium compounds and materials. Appl. Catal. A Gen. 1995, 133, 191–218. [Google Scholar] [CrossRef]
  20. Liu, Y.; Luo, L.; Gao, Y.; Huang, W. CeO morphology-dependent NbO–CeO interaction, structure and catalytic performance of NbO/CeO catalysts in oxidative dehydrogenation of propane. Appl. Catal. B Environ. 2016, 197, 214–221. [Google Scholar] [CrossRef]
  21. Wang, X.; Shi, Y.; Li, S.; Li, W. Promotional synergistic effect of Cu and Nb doping on a novel Cu/Ti-Nb ternary oxide catalyst for the selective catalytic reduction of NO with NH. Appl. Catal. B Environ. 2018, 220, 234–250. [Google Scholar] [CrossRef]
  22. Ma, Z.; Wu, X.; Si, Z.; Weng, D.; Ma, J.; Xu, T. Impacts of niobia loading on active sites and surface acidity in NbOx/CeO2–ZrO2 NH3–SCR catalysts. Appl. Catal. B Environ. 2015, 179, 380–394. [Google Scholar] [CrossRef] [Green Version]
  23. Qu, R.; Gao, X.; Cen, K.; Li, J. Relationship between structure and performance of a novel cerium-niobium binary oxide catalyst for selective catalytic reduction of NO with NH. Appl. Catal. B Environ. 2013, 142–143, 290–297. [Google Scholar] [CrossRef]
  24. Gong, J. Structure and Surface Chemistry of Gold-Based Model Catalysts. Chem. Rev. 2012, 112, 2987–3054. [Google Scholar] [CrossRef] [PubMed]
  25. Kosacki, I.; Suzuki, T.; Anderson, H.U.; Colomban, P. Raman scattering and lattice defects in nanocrystalline CeO2 thin films. Solid State Ion. 2002, 149, 99–105. [Google Scholar] [CrossRef]
  26. Graham, G.W.; Weber, W.H.; Peters, C.R.; Usmen, R. Empirical method for determining CeO2-particle size in catalysts by raman spectroscopy. J. Catal. 1991, 130, 310–313. [Google Scholar] [CrossRef]
  27. Wachs, I.E.; Chen, Y.; Jehng, J.M.; Briand, L.E.; Tanaka, T. Molecular structure and reactivity of the Group V metal oxides. Catal. Today 2003, 78, 13–24. [Google Scholar] [CrossRef]
  28. Wu, Z.L.; Li, M.; Overbury, S.H. On the structure dependence of CO oxidation over CeO2 nanocrystals with well-defined surface planes. J. Catal. 2012, 285, 61–73. [Google Scholar] [CrossRef]
  29. Wisniewska, J.; Ziolek, M.; Artioli, N.; Daturi, M. The effect of niobium and tantalum on physicochemical and catalytic properties of silver and platinum catalysts based on MCF mesoporous cellular foams. J. Catal. 2016, 336, 58–74. [Google Scholar] [CrossRef]
  30. Martínez-Méndez, S.; Henríquez, Y.; Domínguez, O.; D’Ornelas, L.; Krentzien, H. Catalytic properties of silica supported titanium, vanadium and niobium oxide nanoparticles towards the oxidation of saturated and unsaturated hydrocarbons. J. Mol. Catal. A Chem. 2006, 252, 226–234. [Google Scholar] [CrossRef]
  31. Boffa, V.; ten Elshof, J.E.; Garcia, R.; Blank, D.H.A. Microporous niobia–silica membranes: Influence of sol composition and structure on gas transport properties. Microporous Mesoporous Mater. 2009, 118, 202–209. [Google Scholar] [CrossRef]
  32. Paparazzo, E.; Ingo, G.M.; Zacchetti, N. X-ray induced reduction effects at CeO2 surfaces: An x-ray photoelectron spectroscopy study. J. Vac. Sci. Technol. A 1991, 9, 1416–1420. [Google Scholar] [CrossRef]
  33. López, J.M.; Arenal, R.; Puértolas, B.; Mayoral, Á.; Taylor, S.H.; Solsona, B.; García, T. Au deposited on CeO prepared by a nanocasting route: A high activity catalyst for CO oxidation. J. Catal. 2014, 317, 167–175. [Google Scholar] [CrossRef]
  34. Casaletto, M.P.; Longo, A.; Martorana, A.; Prestianni, A.; Venezia, A.M. XPS study of supported gold catalysts: The role of Au0 and Au species as active sites. Surf. Interface Anal. 2006, 38, 215–218. [Google Scholar] [CrossRef]
  35. Li, H.F.; Zhang, N.; Chen, P.; Luo, M.F.; Lu, J.Q. High surface area Au/CeO2 catalysts for low temperature formaldehyde oxidation. Appl. Catal. B Environ. 2011, 110, 279–285. [Google Scholar] [CrossRef]
  36. Haruta, M. Size- and support-dependency in the catalysis of gold. Catal. Today 1997, 36, 153–166. [Google Scholar] [CrossRef]
  37. Huang, H.B.; Xu, Y.; Feng, Q.Y.; Leung, D.Y.C. Low temperature catalytic oxidation of volatile organic compounds: A review. Catal. Sci. Technol. 2015, 5, 2649–2669. [Google Scholar] [CrossRef]
Figure 1. XRD patterns of Au/Nb-CeO2, Au/CeO2, Nb-CeO2, CeO2, and NbOx.
Figure 1. XRD patterns of Au/Nb-CeO2, Au/CeO2, Nb-CeO2, CeO2, and NbOx.
Nanomaterials 11 00189 g001
Figure 2. TEM (a,b), STEM (c), and HRTEM (d,e) images of Au/CeO2 (a) and Au/Nb-CeO2 (be).
Figure 2. TEM (a,b), STEM (c), and HRTEM (d,e) images of Au/CeO2 (a) and Au/Nb-CeO2 (be).
Nanomaterials 11 00189 g002
Figure 3. Raman profiles of Au/Nb-CeO2, Au/CeO2, Nb-CeO2, CeO2, and NbOx.
Figure 3. Raman profiles of Au/Nb-CeO2, Au/CeO2, Nb-CeO2, CeO2, and NbOx.
Nanomaterials 11 00189 g003
Figure 4. H2-TPR profiles of Au/CeO2, Au/Nb-CeO2, and Au/NbOx.
Figure 4. H2-TPR profiles of Au/CeO2, Au/Nb-CeO2, and Au/NbOx.
Nanomaterials 11 00189 g004
Figure 5. XPS spectra of Au 4f, Nd 3d, Ce 3d, and O 1s for as-obtained samples.
Figure 5. XPS spectra of Au 4f, Nd 3d, Ce 3d, and O 1s for as-obtained samples.
Nanomaterials 11 00189 g005
Figure 6. Activity and long-term stability results of as-obtained samples. Reaction conditions for stability test: 230 °C for 48 h, WHSV = 30,000 mL g−1 h−1, 1000 ppm benzene.
Figure 6. Activity and long-term stability results of as-obtained samples. Reaction conditions for stability test: 230 °C for 48 h, WHSV = 30,000 mL g−1 h−1, 1000 ppm benzene.
Nanomaterials 11 00189 g006
Table 1. Data of characterization of as-obtained catalysts.
Table 1. Data of characterization of as-obtained catalysts.
CatalystCrystalline Size (nm) aSBET (m2 g−1) bH2 Consumption (mmol g−1) cAu (wt%) dXPS Data
Auδ+/AuCe3+/Ce4+Osup/OlattNb/Ce
Au/CeO212715.130.920.320.310.70-
Au/Nb-CeO272035.790.99 (0.07) e0.410.321.330.37
Au/NbOx-44--0.12-0.65-
Nb-CeO2-----0.172.210.67
a: CeO2 Crystalline size calculated by Scherrer equation from index of (111) facet. b: BET surface area. c: calculated from H2-TPR profiles at <200 °C. d: ICP result. e: the value in bracket is Nb/Ce molar ratio.
Table 2. Full width at half maximum (FWHM) and frequency of the dominant CeO2 line in the Raman spectra of the sample.
Table 2. Full width at half maximum (FWHM) and frequency of the dominant CeO2 line in the Raman spectra of the sample.
CatalystFrequency (cm−1)FWHM (cm−1)
CeO245734
Nb-CeO245432
Au/CeO245251
Au/Nb-CeO245665
Table 3. Au dispersion of the obtained samples.
Table 3. Au dispersion of the obtained samples.
CatalystsAu/CeO2Au/Nb-CeO2Au/CeO2-1st aAu/Nb-CeO2-1stAu/Nb-CeO2-48 h b
Au dispersion (%)6872547271
Au particle size c (nm)1.721.632.151.631.67
a: Au/CeO2-1st refers to the Au/CeO2 after one run. b: Au/Nb-CeO2-48 h refers to the Au/Nb-CeO2 after 48 h test at 230 °C. c: calculated from CO pulse adsorption.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Liu, Z.; Zhang, X.; Cai, T.; Yuan, J.; Zhao, K.; Lu, W.; He, D. Niobium Modification of Au/CeO2 for Enhanced Catalytic Performance over Benzene Combustion. Nanomaterials 2021, 11, 189. https://doi.org/10.3390/nano11010189

AMA Style

Liu Z, Zhang X, Cai T, Yuan J, Zhao K, Lu W, He D. Niobium Modification of Au/CeO2 for Enhanced Catalytic Performance over Benzene Combustion. Nanomaterials. 2021; 11(1):189. https://doi.org/10.3390/nano11010189

Chicago/Turabian Style

Liu, Zhe, Xiaolan Zhang, Ting Cai, Jing Yuan, Kunfeng Zhao, Wenquan Lu, and Dannong He. 2021. "Niobium Modification of Au/CeO2 for Enhanced Catalytic Performance over Benzene Combustion" Nanomaterials 11, no. 1: 189. https://doi.org/10.3390/nano11010189

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop