Next Article in Journal
Exogenous Contrast Agents in Photoacoustic Imaging: An In Vivo Review for Tumor Imaging
Next Article in Special Issue
Date-Leaf Carbon Particles for Green Enhanced Oil Recovery
Previous Article in Journal
Nanoparticle-Induced m6A RNA Modification: Detection Methods, Mechanisms and Applications
Previous Article in Special Issue
Preparation of a Sustainable Shape-Stabilized Phase Change Material for Thermal Energy Storage Based on Mg2+-Doped CaCO3/PEG Composites
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Nanomaterials
Volume 12
Issue 3
10.3390/nano12030392
nanomaterials-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Influence of Surface Properties of Nanostructured Ceria-Based Catalysts on Their Stability Performance

by
Boyu Li
1,
Eric Croiset
1 and
John Z. Wen
2,*
1
Department of Chemical Engineering, University of Waterloo, Waterloo, ON N2L3G1, Canada
2
Department of Mechanical & Mechatronics Engineering, University of Waterloo, Waterloo, ON N2L3G1, Canada
*
Author to whom correspondence should be addressed.
Nanomaterials 2022, 12(3), 392; https://doi.org/10.3390/nano12030392
Submission received: 11 December 2021 / Revised: 20 January 2022 / Accepted: 21 January 2022 / Published: 25 January 2022
(This article belongs to the Special Issue Nanomaterials for Catalysis and Energy Storage)
Browse Figures
Versions Notes

Abstract

:
As the poor cycling stability of CeO2 catalysts has become the major obstacle for applications of diesel particulate filters (DPF), it is necessary to investigate how to reduce their structural and compositional changes during soot oxidation. In this study, different ratios of Samarium (Sm) were doped into the lattice of CeO2 nanoparticles to improve the catalytic performance as well as surface properties. The stability was investigated by recycling the catalyst, mixing it with soot again, and repeating the thermogravimetric analysis (TGA) tests seven times. Consistent observations were expected for more cycles. It was found that doping 5%, 10%, and 20% samarium into the CeO2 lattice can improve the catalyst stability but at the cost of losing some activity. While the catalyst became more stable with the increasing Sm doping, the 10% Sm-doped catalyst showed the best compromise between stability and activity. Ce3+ and Oα were found to play important roles in controlling catalytic soot oxidation activity. These two species were directly related to oxygen vacancies and oxygen storage capacity of the catalyst. Sm-doped catalysts showed a minimized decrease in the Ce3+ and Oα content when the fresh and spent catalysts were compared.

1. Introduction

Ceria has already been widely studied in soot oxidation because of its excellent redox properties and oxygen storage capacity (OSC). Previous studies have shown that metal-doped ceria can further improve the activity of ceria-based catalysts [1]. In a previous study that investigated the activities of iron-doped ceria catalysts at different doping ratios, we showed 5% iron doping prepared with the solution combustion synthesis (SCS) method performed best due to its highly reactive Fe–O–Ce sites [2].
It was reported that the active sites, crystal structures, and surface properties of ceria-based catalysts could change during the reactions, resulting in poor stability of ceria-based catalysts [3]. All studies acknowledged that pure CeO2 shows poor stability for soot oxidation, which has become a major obstacle for the wide-ranging applications of ceria-based catalysts [3,4,5,6]. Liang et al. [3] have studied the thermal stability of CeO2 for soot oxidation by aging the catalyst at 800 °C for 20 h in air. They found that the temperature corresponding to the maximum rate for CO2 production with an aged catalyst increased by about 60 °C compared to a fresh catalyst because of the highly reduced surface area and sintering. Aneggi et al. [4] observed that an aging CeO2 catalyst at 750 °C for 12 h in air decreased its activity for soot oxidation as it lost oxygen storage capacity. Liu et al. [5] investigated the deactivation of CeO2 for soot oxidation through isothermal conditions at 300 and 350 °C; they found that deactivation occurred at isothermal conditions and became more severe at higher temperature. The main reported reason for deactivation is inefficient O 2 − formation. Corro et al. [6] tested the stability of CeO2 towards soot oxidation during six cycles and found a slow and continuous deactivation of CeO2.
Therefore, the stability of CeO2-based catalysts for soot oxidation needs to be improved. Many studies have looked at the incorporation of metal dopants into the CeO2 lattice to improve stability, as described next. Wu et al. [7,8,9,10] added BaO or Al2O3 into transition-metal- (Mn, Cu) doped CeO2 to improve its thermal stability. They found that these metals could improve the thermal stability after aging at 800 °C for 24 h in air because they hinder crystal growth. Aneggi [4] and Liang et al. [3] incorporated ZrO2 into Fe–Ce and Cu–Ce mixed oxides and found enhanced thermal stability due to the formation of stable solid solutions. Gao et al. [11] aged a Nd–Ag/CeO2 catalyst at 700 °C for 48 h under 1% O2/10% H2O/N2, revealing Nd could prevent crystal growth, thus improving thermal stability of Ag/CeO2. Xiong et al. [12] added Y and La into a Zr/CeO2 catalyst and aged it from 700 to 1000 °C. The catalyst activity remained stable below 800 °C but decreased significantly above 900 °C. Zhang et al. [13,14] investigated the influence of thermal stability by adding Y into MnOx–CeO2 and introducing Al, La, Y, or Zr into Pt/MnOx–CeO2 after aging at 800°C for 12 h in air. They observed that the incorporation of dopants can prevent the sintering and slow down crystal growth. Peralta et al. [15,16] introduced Ba into alkali metals-modified ceria, such as K/CeO2, and obtained good thermal stability, as no deactivation was observed after aging at 800 °C. Noble metals, such as Ru, have also been investigated as dopants to successfully improve ceria-based catalyst stability after aging at 800 °C in O2 [17]. Although all the studies described previously investigated stability through accelerated thermal aging, only a few studies investigated stability through more realistic, albeit more cumbersome, soot oxidation cycles [18,19,20,21]. La loaded on CeO2–ZnO (five cycles) [21], K added into CeO2 (three cycles) [18], codoping of Ag and Mn into CeO2 (three cycles) [19], and Au-doped Ce0.8Zr0.2O2 (three cycles) [20] all showed enhanced stability of ceria-based catalysts for soot oxidation. These studies identified that resistance of sintering and crystal growth, ability of CO2 desorption, and oxygen-species replenishment play important roles regarding catalyst stability in soot oxidation.
The stability of ceria-based catalysts has also been investigated for applications other than soot oxidation [22,23]. One family of applications relates to catalytic combustion of different gases. Dai et al. [24] investigated the stability and deactivation of the CeO2 catalyst and found that T50 increased from 165 °C to 325 °C after nine cycles of trichloroethylene combustion. Zhang et al. [25] studied Al-, Zr-, La-, or Y-doped Pt/MnOx–CeO2 stability toward NO oxidation after aging and observed that the modified ceria catalyst showed better activity. Han et al. [23] investigated the stability of the ZrO2-doped CeO2-based catalyst for toluene combustion, revealing that ZrO2 can stabilize the surface active structure, thus improving stability. Polychronopoulou et al. [26] investigated Sm2O3/CeO2 catalysts for CO oxidation and found that adding Sm can significantly improve the thermal stability of the conventional CeO2 catalyst. Mandal et al. [27] have demonstrated enhanced stability of Gd–Sm–CeO2 for benzyl alcohol oxidation. Another important family of applications using ceria-based catalysts is in solid-oxide fuel cells (SOFCs) (and the reverse operation, solid-oxide electrolysis, SOEC) for intermediate temperatures (650–750 °C). The main ceria-based material investigated for SOFC and SOEC are samarium-doped ceria (SDC) [28,29] and gadolinium-doped ceria (GDC) [22,30]. Sm and Gd were essentially added to stabilize ceria during the operation at high temperature, while achieving good oxygen-ion conductivity, as they can inhibit crystal growth and prevent sintering [31].
From the above literature review on the stability of the ceria-based catalyst, it is somewhat surprising to see almost no studies on samarium-doped ceria despite proven long-term stability at high temperatures (750–850°C) in SOFC/SOEC. Granted, SDC in SOFC/SOEC has a different purpose (electrolyte to transport oxygen ion) than it would have in soot oxidation. Yet, SDC should be a promising stable catalyst for soot oxidation because of its thermal stability at high temperature. Very few papers studied Sm as a dopant to ceria for soot oxidation. Liu et al. [32], using a loose-contact condition, studied activity and thermal stability (calcination at 800 °C for 20 h) of a 20% Sm-doped ceria catalyst prepared through microwave-assisted heating decomposition. Sudarsanam et al. [33] carried out a similar study, except under a tight-contact condition and with the coprecipitation catalyst preparation method. Both reported increases in combustion temperatures after aging but are not conclusive regarding actual catalyst stability. Anantharaman et al. [34] studied the effect of Sm content on soot-oxidation reactivity for the Sm-doped ceria catalyst prepared by the EDTA-citrate method but did not investigate catalyst stability; they found that 10% Sm doping performed best on a fresh catalyst calcined at 600 °C for 5 h.
The present study aims to develop an optimum ratio of Sm doping into the CeO2 catalyst to improve catalyst stability for soot oxidation. Therefore, different ratios of Sm doping were investigated along with its influence on catalyst surface properties and activity. Characterizations were performed to understand surface and crystal properties of catalyst. Seven repeating reaction cycles were used to study the activity and stability of the Sm-doped CeO2 catalyst.

2. Materials and Methods

2.1. Catalysts’ Preparation

Smx/Ce1−x (x = 0.05, 0.10, and 0.20 in percent molar ratio) catalysts were prepared by the solution combustion synthesis (SCS) method. An aqueous solution of Samarium nitrate nonahydrate (Sigma-Aldrich, St. Louis, MO, USA, CAS: 13759-83-6, 99.999% trace metals basis), cerium nitrate hexahydrate (Sigma-Aldrich, CAS: 10294-41-4, 99.999% trace metals basis), and glycine (Sigma-Aldrich, CAS: 56-40-6) in a stoichiometric ratio was mixed under vigorous stirring at 90 °C to form a gel. The gel was then combusted on a heating plate. The combustion procedure was fast, producing nano powders (around 20 nm). The resulting samples were then calcined at 500 °C for 5 h. The pure CeO2-SCS catalyst was developed using a similar procedure.

2.2. Catalysts’ Activity and Stability Tests

Thermogravimetric analysis (TGA) was used to test the catalyst’s activity for soot oxidation through a TA Instrument Q500 apparatus (TA Instruments, New Castle, DE, USA). Printex-U carbon black was used as the model of soot. Catalyst and soot particles were weighted at a ratio of 9:1 to make sure soot can be fully oxidized, after a number of trials. They were then mixed by grinding them for 10 min to obtain a tight-contact condition [35]. For the first cycle of the TGA test, a weighted amount of a 40 mg sample was pretreated at 150 °C under 60 mL/min nitrogen for 30 min to remove water. Then, the sample was heated up to 600 °C under 40 mL/min air with a heating rate of 10 °C/min. The thermogravimetric curves were obtained by continuously recording the mass change, along with increased temperature. Soot oxidation in the absence of catalysts was performed for the comparison purpose. Note that from our past observations, heating the carbon-catalyst mixture to 600 °C is sufficient to achieve the soot conversion rate of 100% for ceria catalysts, while the pure carbon sample is completely oxidized after the temperature reaches 700 °C [2]. The catalyst’s activity was evaluated by T50. T50 is the combustion temperature, identified as the temperature when 50% of soot is oxidized [36,37,38,39].
The stability tests were performed through several soot oxidation cycles using the same catalyst. One cycle is defined by a step of mixing soot and catalyst particles, followed by a step of soot oxidation in the TGA. Once the first cycle soot-oxidation reaction was completed, the remaining catalyst was collected and remixed with soot particles again under a tight-contact condition with the same weighting ratio of 9:1. The TGA test was run again with the newly mixed sample. This procedure was repeated for several cycles. Note that after each cycle, it was inevitable that some amount of the catalyst is lost (mostly during the mixing step where several particles stick to the mortar and pestle). This means that for a given amount of fresh catalyst there will be a maximum number of cycles that can be investigated; for example, with our typical 36 mg of fresh catalyst (with 4 mg of carbon), it was hardly possible to go beyond seven cycles.

2.3. Characterization of the Catalysts

An X-ray powder diffraction (XRD) analysis was carried out using an X-ray powder diffractometer (German Bruker D4 (40 kV, 30 mA), Bruker, Billerica, MI, USA with a position-sensitive detector and CuKα radiation). The XRD patterns were recorded from 5° to 85° in steps of 0.01°. The XRD patterns were analyzed based on the Powder Data File database (International Centre of Diffraction Data, Newtown Square, PA, USA, accessed on: 1 September 2021). Specific surface areas were evaluated by N2 adsorption–desorption isotherms on a Beishide 3H-2000PS2 static-volumetric method analyzer, BEISHIDE Instrument Technology, Beijing, China. The Brunauer-Emmett-Teller (BET) method was used to calculate the catalysts’ surface areas. The catalysts’ morphologies and microstructures were characterized by a Field-emission scanning electron microscope (FE-SEM, Zeiss MERLIN with Gemini-II column, Zeiss, Oberkochen, Germany). The X-ray photoelectron spectroscopy (XPS) analysis was conducted on the ESCALab220i-XL electron spectrometer (VG Scientific Ltd., East Grinstead, UK) with a 300 W AlKα X-ray source to study the oxidation states and oxygen species on the catalysts’ surfaces. Binding energy was calibrated by standard C1s peaks at 284.8 eV. XPS peaks was analyzed using CasaXPS software, Version 2.3.24, Clearwater, FL, USA. The Raman spectra of catalysts were measured on a Renishaw inVia micro laser Raman spectrometer (Renishaw plc, Wotton-under-Edge, UK) with a 4 mW Ar+ laser source (λex = 532 nm) and a cooled CCD detector at room temperature to distinguish chemical structures. The scanning range was 200–800cm−1 with a 60 s acquisition time.

3. Results and Discussion

3.1. Fresh and Spent Catalysts’ Characterizations

The crystalline structures of catalysts were studied by XRD. Figure 1 presents the XRD pattern of fresh and spent Sm-doped CeO2 catalysts, as well as pure CeO2 for comparison. All XRD patterns show similar main diffractions peaks, which can be attributed to (111), (200), (220), (311), (222), (400), (331), and (420) planes. These peaks refer to typical cubic fluorite structures of pure CeO2 [40]. No peaks referring to Sm2O3 were found, even for 20% SDC, meaning that no individual Sm2O3-crystal structure was detected, indicating that the Sm forms a solid solution in the ceria lattice. For fresh catalysts, when increasing the Sm-doping ratio, the characteristic peaks shift to the lower 2 θ diffraction angles, further suggesting that Sm is incorporated into the CeO2 lattice and forms a solid solution. The unit-lattice parameters were calculated by Bragg’s law using the strongest peak (111), and the crystallite size was calculated by the Scherrer equation. With an increase in Sm-doping, the lattice parameter (as shown in Table 1) tends to increase because of the larger Sm (1.07 Å) substituting smaller ceria (0.97 Å) in the lattice, thus resulting in lattice expansion [41].
As seen in Table 1, the comparison of fresh and spent catalysts shows that the lattice parameters of spent catalysts slightly increase compared to those of fresh catalysts with the same doping ratio. Although those increases are very small, the trend is clear that the change in lattice parameters decreases as the amount of Sm increases: for pure ceria, 5%, 10%, and 20% Sm; the differences in lattice parameters between fresh and spent catalysts are 0.013, 0.006, 0.004 and 0.003 Å, respectively. While for fresh catalysts, the crystallite size clearly increases as the amount of Sm increases (from 12.3 nm for pure ceria to 13.6 nm for Sm0.2Ce0.8); such a clear trend was not observed for the spent catalysts where the crystallite size seems to converge for the size range of between 13.5 and 14.5 nm. The spent catalysts always show higher crystallite sizes than the fresh ones, indicating that there is an increase in crystallinity after several cycles of reactions on the catalyst. For all spent catalysts, Sm0.1Ce0.9 notably shows the lowest crystallite size.
The BET surface areas for Sm-doped ceria catalysts are listed in Table 1. For the fresh Sm-doped catalysts, except Sm0.1Ce0.9, they all have a surface area of 41–42 m2g−1, which are lower than that of fresh pure CeO2 (45.5 m2g−1). The fresh Sm0.1Ce0.9 catalyst shows the highest BET surface area of 48 m2g−1. When comparing fresh and spent catalysts, the BET surface area of pure CeO2 decreases the most (from 45.5 to 40.9 m2g−1). Sm-doped CeO2 catalysts also show a slight decline in the BET surface area (2–4% loss), regardless of the doping ratio. Interestingly, except for Sm0.1Ce0.9, all other spent catalysts, including pure ceria, have similar surface areas at around 40–41 m2g−1. There seems to be something particular for Sm0.1Ce0.9, which has the highest surface area for both fresh and spent catalysts. Note that this catalyst also stands out, having the lowest crystallite size after several cycles. Since the catalysts for XRD and BET characterization were made from different batches, it indicates that Sm0.1Ce0.9 presents interesting properties, which cannot be attributed to experimental error.
An SEM was used to study the morphologies of the produced catalysts. Figure 2 shows the SEM images of all fresh and spent catalysts. All fresh catalysts have spongy structures with large openings, which are due to their fast combustion reaction during the SCS procedure. The main effect of Sm doping on the catalyst morphology is to increase those openings. However, all spent catalysts lose the spongy structure and tend to agglomerate and in the end have very similar morphologies.
XPS was used to detect different oxidation states of each element. Figure 3 is the XPS spectra of all catalysts regarding their Ce3d, O1s, and Sm 3d5/2 spectra. The binding energies of XPS spectra were calibrated using the C1s peak at 284.8 eV. C1s spectra of all catalysts are provided in the Supplementary Materials. While performing the Ce3d deconvolution, the FWHM (full width at half maximum) was set to a narrow range of 2–2.7 eV, and the peak area of 3d5/2 to 3d3/2 was set to 3:2. Ce3d spectra can be split into 10 peaks for detailed analysis. The peaks labeled with “u” and “v” correspond to the spin-orbit splitting of Ce 3d5/2 and Ce 3d3/2, respectively. These peaks, v, v2, v3, u, u2, and u3, are the characteristic peaks for the Ce4+ species, and the peaks noted with v0, v1, u0, and u1 correspond to the Ce3+ species [42,43,44,45,46]. Detailed peak positions are provided in the Supplementary Materials. It is clear that ceria exists primarily as Ce4+ for each catalyst, with the coexistence of some Ce3+. Since oxygen vacancy is generated when Ce4+ is reduced to Ce3+, it is crucial to calculate the Ce3+ percentage to evaluate the generation of oxygen vacancy on the catalyst surface [37,46]. The calculations of the integrated peak areas can be used to quantitatively analyze XPS results. The ratio of Ce3+ was calculated by dividing the peak areas of Ce3+ by the total peak area. Table 2 shows the results of the Ce3+ percentage for fresh and spent catalysts. For fresh catalysts, it can be found that adding Sm into the CeO2 lattice decreases the Ce3+ percentage (about 17–19%) from that in pure ceria (24.2%). The 5% and 10% Sm doping possess similar Ce3+ percentages (18.8% and 19.3%) and the 20% Sm-doped catalyst has the lowest Ce3+ percentage (17.3%). Table 2 also shows that the Ce3+ percentage of the spent catalysts decreases when compared to fresh catalysts. Pure CeO2 in particular, shows a significant Ce3+ percentage decrease from 24.2% to 15.8%. In other words, it changes from the highest percentage to the lowest one. However, Sm-doped catalysts show a lower decrease (0.9% for 5% doping and 0.8% for 10% doping). The Ce3+ percentage for Sm0.2Ce0.8 catalysts only decreases by about 0.5%. Those results suggest that Sm helps establish a more stable catalyst surface, at least in terms of the Ce3+ content.
The O1s spectra were curve fitted into two peaks, including lattice oxygen, Oβ, at a lower binding energy of 529.5 eV and the surface oxygen species, Oα, at a higher binding energy of 531.7 eV [47]. The concentration of Oα is critical to evaluate the oxygen storage capacity (OSC) and the potential active oxygen for soot oxidation. The ratio, Oα/(Oα+ Oβ), was calculated by dividing the peak areas of Oα by the total peak areas, whose results are shown in Table 2. This table shows that for fresh catalysts, Sm doping up to 10% marginally decreases the Oα ratio (from 39.6% down to 39.1%). However, the decrease in the Oα ratio is more pronounced for 20% Sm doping (Oα ratio of 34.2%). The results regarding the Oα ratio are in agreement with that of the Ce3+ percentage. Regarding spent catalysts, the Oα ratio of pure CeO2 drops significantly compared to that of the fresh CeO2 catalyst (from 39.6% to 29.5%) and becomes the lowest among all spent catalysts. On the other hand, the Oα percentage for 5% and 10% Sm-doped ceria catalysts decreases by less than 2 percentage points. Finally, the 20% Sm-doped catalysts do not show a decrease in Oα content, although its final value is still lower than that of the other two Sm-doped ceria catalysts. Those results suggest that Sm doping considerably reduces the loss in surface oxygen after several cycles.
The peaks around 1082.6 eV in the Sm 3d5/2 spectra confirm that Sm is present as a +3-oxidation state in the catalyst, which agrees with the literature [48,49]. The surface ratio of Sm/Ce was calculated through XPS results. For fresh catalysts, the ratios are 0.059, 0.122, and 0.342, for 5%, 10%, and 20% Sm doping, respectively. Compared to the stoichiometric ratios of 0.053, 0.111, and 0.25 for 5%, 10%, and 20% Sm doping, respectively, the fresh catalysts show slightly higher values, indicating there is an enrichment of Sm on the detected surface of these catalysts. For spent catalysts, the Sm/Ce are 0.068, 0.138, and 0.355 for 5%, 10%, and 20% Sm doping, respectively. These ratios are greater in comparison with the fresh catalyst values, which is possibly due to Sm in the bulk catalysts tending to move to the surface of catalysts during the reactions. The 20% Sm doping shows the smallest change of Sm/Ce, suggesting a more stable catalyst surface.
The Raman spectra of Sm-doped CeO2 catalysts are depicted in Figure 4. The dominant band around 463 cm−1 corresponds to the F2g symmetric oxygen mode within a CeO2 cubic fluorite structure, which is in agreement with the XRD results [33]. With an increase of the Sm doping ratio, the F2g band shifts to lower frequencies due to the cell expansion in the catalysts. No peaks of Sm2O3 (~375 cm−1) were found, which reinforces that Sm-Ce forms a solid solution [27]. The weak peak around 596 cm−1 represents the surface defects, including the intrinsic oxygen vacancies caused by Ce3+ in the lattice [35]. The peak around 554 cm−1 refers to the extrinsic oxygen vacancy created by Sm3+ substituting Ce4+ to maintain charge neutrality [50]. With an increase in Sm doping, the peak intensity at 554 cm−1 becomes stronger, indicating that more Sm3+-associated oxygen vacancies are created. The ratio, I554/I596, represents, therefore, the ratio of oxygen vacancies originating from Sm3+ over that from Ce3+. The results pertaining to the I554/I596 ratio are shown in Table 3. For fresh catalysts, as expected, the incorporation of Sm increases the I554/I596 ratio. Note that for spent Sm0.2Ce0.8, this ratio is above 1, indicating more oxygen vacancies from Sm3+ than from Ce3+, whereas it is the opposite for Sm content below 10% (values of the I554/I596 ratios below 1).
After five cycles of reactions, the I554/I596 ratio for all catalysts further increases (by about 0.1). This indicates that after several cycles, the relative amount of oxygen vacancy correlated to Sm3+ increases (and its corollary, the relative amount of oxygen vacancy correlated to Ce3+ decreases). The peak intensity of the Raman spectra increases in all cases after five cycles, possibly due to the increase in crystal growth, which is in agreement with the XRD results. Another reason could be the lattice distortion of the spent catalysts leading to resonance with the inlet Ar+ laser source.

3.2. Activity Test

TGA experiments were performed to study the activity of the fresh Sm-doped CeO2 catalyst for soot oxidation. Figure 5 depicts soot conversion as a function of temperature. The fresh pure CeO2 catalyst achieves the highest activity, as indicated by the lowest T50. Increasing the Sm content in the fresh catalysts tends to increase T50, revealing a loss in activity. In fact, the 5% and 10% Sm-doping ratios for the fresh catalyst show similar effects on catalyst activity, whereas the 20% Sm-doping sample leads to the worst activity. In comparison, soot oxidation without the catalyst was conducted under the same reaction condition (Printex-U in Figure 5), and it shows very little soot oxidation below 500 °C, suggesting that the catalyst investigated here significantly increases soot oxidation.
Since catalytic soot oxidation is a surface sensitive reaction, i.e., reaction only happens at the contact point of soot and catalyst, the crystallite size, specific surface area, and morphology can all play important roles on the catalyst activity [1,51]. From Figure 2, the morphology does not change significantly between pure ceria and Sm-doped catalysts, and thus cannot explain the difference in reactivity. Table 1 indicates that the BET surface area increases slightly when increasing the Sm content, but this would lead to higher activity at the higher Sm content, which is the opposite of what was observed; the BET surface area, thus, cannot explain the trend in activity here. Finally, Table 1 shows a modest change in the crystallite size when increasing the Sm content and without a clear trend. Crystallite size can, therefore, also be dismissed as an explanation for the activity trend for the fresh catalysts.
Soot oxidation on ceria-based catalysts occurs via the so-called Mars–van Krevelen mechanism [1], where the active surface oxygen reacts with soot through the catalyst-soot contact point. Once the active oxygen is consumed, an oxygen vacancy is generated at the surface, and bulk O2 fills this vacancy and create another active oxygen. Therefore, factors affecting the amount of active surface oxygen and oxygen vacancies can also play important roles in determining catalyst activity. The Ce3+ content is a good representation of oxygen-vacancy generation, which, in turn, can be a potential site for creating active surface oxygen. Here, surface oxygen and oxygen vacancies are related to the Ce3+ content, Oα percentage, and I554/I596 ratio. Those are discussed next.
Figure 6a shows the relation between T50 and the Ce3+ percentage, which indicates that the higher the Ce3+ content, the lower T50 (and thus, higher the activity). The highest Ce3+ ratio (24.2%) corresponds to the fresh pure CeO2 catalyst, which can be a reason for the highest activity of pure ceria. The activity results reported in Figure 5 for Sm-doped catalysts correlates very well with the Ce3+ content shown in Table 2: 5%- and 10%-doped CeO2 have identical Ce3+ content and also very similar activity (e.g., same T50), whereas Sm0.2Ce0.8 has a much lower Ce3+ content, as well as much lower activity (i.e., higher T50). Figure 6b shows the relation between T50 and the Oα percentage, which follows the trend of the Ce3+ content, indicating that surface-oxygen species are also vital for catalyst activity. It has been reported that the higher Oα concentration could result in superior catalyst activity, as it can evaluate the oxygen-storage capacity and potential active oxygen for the reaction. From Table 2, the Oα percentage slightly decreases for 5% and 10% Sm-doped catalysts, but it considerably decreases for 20% Sm doping when comparing with pure CeO2; the Oα percentage data also correlates very well with the activity results.
The relation between T50 and the I554/I596 ratio is illustrated in Figure 7, which shows that T50 increases when the I554/I596 ratio increases. This implies that Sm3+-associated oxygen vacancy decreases the catalyst activity. From the XPS results, it is already known that higher Ce3+-associated oxygen vacancy plays a key role in improving catalyst activity. Therefore, both the increase in oxygen vacancy around Sm3+ and the decrease of oxygen vacancy adjacent to Ce3+ lead to activity decline.

3.3. Stability Tests for Sm-Doped CeO2 Catalysts

Figure 8 presents the results of stability on Sm-doped CeO2 for soot oxidation through seven cycles. This figure shows that T50 for the pure CeO2 catalyst increases after each cycle, going from the lowest value (379 °C) with the fresh catalyst to the highest one (462 °C) after seven cycles. The 5% Sm-doped catalyst also shows a continuous increase in T50 after each cycle but at a much lower rate than pure CeO2. The samples with 10% and 20% Sm doping follow very similar trends (as seen in Figure 8, they are almost parallel): first, a moderate increase in T50 after three or four cycles, followed by a near plateauing of T50. The differences in T50 between the initial and plateau values are 14 °C for 10% Sm and 8 °C for 20% Sm, respectively. Those results indicate good stability for Sm doping above 10%. As a plateau is reached after the fifth cycle, it is expected that the T50 of catalysts containing more than 10% Sm doping would have a very limited change for more cycles. Considering activity and stability together, the 10% Sm-doped catalyst performs best among all catalysts, with a stability comparable to the 20% Sm but with the lowest T50 after seven cycles (412 °C).
Figure 9 shows the relationship between the change of T50 (between first and seventh cycle) and the Sm-doping ratio. The spent CeO2 catalyst leads to an 83 °C change in T50, compared to the fresh one. T50 of 5% and 10% Sm-doped catalysts show smaller differences, which are about 27 °C and 18 °C, respectively. T50 for the 20% Sm-doped catalyst shows the lowest difference (13 °C). It is clear that the T50 difference decreases with higher Sm doping, indicating that richer Sm contributes to a more stable catalyst, albeit with lower activity.
As discussed previously, the Ce3+ content plays an important role for catalyst activity towards soot oxidation. Figure 10 illustrates the relationship between the Ce3+ content change (between first and fifth cycle) and the Sm-doping ratio. This figure indicates that the addition of Sm (even at 5%) results in a significant decrease in the change of Ce3+ between the fresh and spent catalysts. The Ce3+ content for pure ceria decreases from 24.2% to 15.8%, suggesting poor stability performance. In contrast, changes in the Ce3+ content of Sm-doped ceria catalysts are below 1%, with 20% Sm doping only 0.5%. This indicates that Sm doping is beneficial for improving catalyst stability and maintaining activity. Figure 10 also shows that the relationship between the change of the Oα percentage (between first and fifth cycle) and the Sm-doping ratio. It can be observed that with an increase in the doping ratio, the decrease of the Oα percentage becomes smaller. The 5% and 10% Sm-doped catalysts decrease by about 2%, whereas the 20% Sm catalyst does not show any change. This suggests that the higher Sm doping makes a more stable catalyst and prevents the decline of the Oα percentage. The Oα percentage of the fresh CeO2 catalyst is 39.6% and yields to 29.5% after five cycles. This indicates that the OSC of the CeO2 catalysts is not stable, and the significant decline of OSC after reacting with soot leads to poor stability of pure ceria catalysts.
Moreover, the XRD results have shown that Sm is incorporated into the CeO2 lattice and causes lattice expansion. The increased crystallite size of the spent catalyst compared with the fresh one indicates that recrystallization has occurred. However, the larger crystallite size does not benefit the catalyst activity towards soot oxidation, as smaller crystallite size could favor oxygen diffusion and provide more contact points. The Sm-doped catalyst shows a smaller change in crystallite size after reactions, and such a difference becomes lesser with higher amounts of Sm doping, indicating that adding Sm can inhibit this recrystallization process. Therefore, adding Sm can stabilize the catalyst crystal structure and helps maintain surface properties, such as the Ce3+ and Oα percentages.

4. Conclusions

Doping 5%, 10%, and 20% samarium into a CeO2 lattice was achieved using the solution combustion synthesis (SCS) method to improve the stability of the nanostructured ceria-based catalyst for soot oxidation. In general, at a higher Sm content (10% and 20%), the reactivity (represented by T50) nearly plateaued after five cycles. However, increasing the Sm content was accompanied with a decrease in activity for soot oxidation. Considering the effects of Sm doping in both stability and activity, the 10% Sm-doped catalyst showed the best compromise between the catalyst stability and activity. Ce3+ and Oα were found to play an important role in controlling catalytic soot-oxidation activity, which agrees with the expectation that they are directly related to the oxygen vacancies and oxygen storage capacity of the catalyst. Sm-doped catalysts, especially at 10% and 20% Sm, showed a minimized decrease in Ce3+ content and Oα percentage between the fresh and spent catalysts after five cycles. Good stability in maintaining the crystallite size between the fresh and spent catalysts can also contribute to the greater stability for Sm-doped ceria catalysts. However, our experimental data did not indicate a clear correlation between the crystallite size and activity for these fresh and spent catalysts. Therefore, crystallite size growth is not considered here as a primary parameter for catalyst deactivation over cycling.

Supplementary Materials

The following are available online at https://www.mdpi.com/article/10.3390/nano12030392/s1: Figure S1. C1s spectra for all catalysts, Table S1. Peak position of Ce 3d spectra for fresh and spent catalysts.

Author Contributions

Conceptualization, methodology, validation, and original draft preparation, B.L.; review and editing and supervision, E.C. and J.Z.W. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by BioFuelNet Canada, Project No. 7A-7.

Acknowledgments

The authors acknowledge useful discussions with Henry Zhu at Cestoil Chemical Inc. The authors would also like to thank Taiyuan University of Technology for its characterization technique support.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Liu, S.; Wu, X.; Weng, D.; Ran, R. Ceria-based catalysts for soot oxidation: A review. J. Rare Earths 2015, 33, 567–590. [Google Scholar] [CrossRef]
  2. Li, B.; Raj, A.; Croiset, E.; Wen, J.Z. Reactive Fe-O-Ce Sites in Ceria Catalysts for Soot Oxidation. Catalysts 2019, 9, 815. [Google Scholar] [CrossRef] [Green Version]
  3. Liang, Q.; Wu, X.; Weng, D.; Lu, Z. Selective oxidation of soot over Cu doped ceria/ceria–zirconia catalysts. Catal. Commun. 2008, 9, 202–206. [Google Scholar] [CrossRef]
  4. Aneggi, E.; de Leitenburg, C.; Dolcetti, G.; Trovarelli, A. Promotional effect of rare earths and transition metals in the combustion of diesel soot over CeO2 and CeO2–ZrO2. Catal. Today 2006, 114, 40–47. [Google Scholar] [CrossRef]
  5. Liu, S.; Wu, X.; Liu, W.; Chen, W.; Ran, R.; Li, M.; Weng, D. Soot oxidation over CeO2 and Ag/CeO2: Factors determining the catalyst activity and stability during reaction. J. Catal. 2016, 337, 188–198. [Google Scholar] [CrossRef]
  6. Corro, G.; Flores, A.; Pacheco-Aguirre, F.; Pal, U.; Bañuelos, F.; Ramirez, A.; Zehe, A. Biodiesel and fossil-fuel diesel soot oxidation activities of Ag/CeO2 catalyst. Fuel 2019, 250, 17–26. [Google Scholar] [CrossRef]
  7. Bueno-López, A. Diesel soot combustion ceria catalysts. Appl. Catal. B Environ. 2014, 146, 1–11. [Google Scholar] [CrossRef] [Green Version]
  8. Palmisano, P.; Russo, N.; Fino, P.; Fino, D.; Badini, C. High catalytic activity of SCS-synthesized ceria towards diesel soot combustion. Appl. Catal. B Environ. 2006, 69, 85–92. [Google Scholar] [CrossRef]
  9. Liu, W.; Flytzanistephanopoulos, M. Total oxidation of carbon monoxide and methane over transition metal fluorite oxide composite catalysts: I. Catalyst composition and activity. J. Catal. 1995, 153, 304–316. [Google Scholar] [CrossRef]
  10. Małecka, M.A.; Kępiński, L.; Miśta, W. Structure evolution of nanocrystalline CeO2 and CeLnOx mixed oxides (Ln = Pr, Tb, Lu) in O2 and H2 atmosphere and their catalytic activity in soot combustion. Appl. Catal. B Environ. 2007, 74, 290–298. [Google Scholar] [CrossRef]
  11. Gao, Y.; Duan, A.; Liu, S.; Wu, X.; Liu, W.; Li, M.; Chen, S.; Wang, X.; Weng, D. Study of Ag/CexNd1-xO2 nanocubes as soot oxidation catalysts for gasoline particulate filters: Balancing catalyst activity and stability by Nd doping. Appl. Catal. B Environ. 2017, 203, 116–126. [Google Scholar] [CrossRef]
  12. Xiong, L.; Yao, P.; Liu, S.; Li, S.; Deng, J.; Jiao, Y.; Chen, Y.; Wang, J. Soot oxidation over CeO2-ZrO2 based catalysts: The influence of external surface and low-temperature reducibility. Mol. Catal. 2019, 467, 16–23. [Google Scholar] [CrossRef]
  13. Zhang, H.; Wang, J.; Cao, Y.; Wang, Y.; Gong, M.; Chen, Y. Effect of Y on improving the thermal stability of MnOx-CeO2 catalysts for diesel soot oxidation. Chin. J. Catal. 2015, 36, 1333–1341. [Google Scholar] [CrossRef]
  14. Zhang, H.; Yuan, S.; Wang, J.; Gong, M.; Chen, Y. Effects of contact model and NOx on soot oxidation activity over Pt/MnOx-CeO2 and the reaction mechanisms. Chem. Eng. J. 2017, 327, 1066–1076. [Google Scholar] [CrossRef]
  15. Peralta, M.; Milt, V.; Cornaglia, L.; Querini, C. Stability of Ba, K/CeO2 catalyst during diesel soot combustion: Effect of temperature, water, and sulfur dioxide. J. Catal. 2006, 242, 118–130. [Google Scholar] [CrossRef]
  16. Peralta, M.A.; Zanuttini, M.S.; Querini, C.A. Activity and stability of BaKCo/CeO2 catalysts for diesel soot oxidation. Appl. Catal. B Environ. 2011, 110, 90–98. [Google Scholar] [CrossRef]
  17. Kurnatowska, M.; Mista, W.; Mazur, P.; Kepinski, L. Nanocrystalline Ce1−xRuxO2–Microstructure, stability and activity in CO and soot oxidation. Appl. Catal. B Environ. 2014, 148, 123–135. [Google Scholar] [CrossRef]
  18. Wenjuan, S.; Lihua, Y.; Na, M.; Jiali, Y. Catalytic activity and stability of K/CeO2 catalysts for diesel soot oxidation. Chin. J. Catal. 2012, 33, 970–976. [Google Scholar]
  19. Li, S.; Yan, S.; Xia, Y.; Cui, B.; Pu, Y.; Ye, Y.; Wang, D.; Liu, Y.-Q.; Chen, B. Oxidative reactivity enhancement for soot combustion catalysts by co-doping silver and manganese in ceria. Appl. Catal. A Gen. 2019, 570, 299–307. [Google Scholar] [CrossRef]
  20. Wei, Y.; Zhao, Z.; Li, T.; Liu, J.; Duan, A.; Jiang, G. The novel catalysts of truncated polyhedron Pt nanoparticles supported on three-dimensionally ordered macroporous oxides (Mn, Fe, Co, Ni, Cu) with nanoporous walls for soot combustion. Appl. Catal. B Environ. 2014, 146, 57–70. [Google Scholar] [CrossRef]
  21. Nascimento, L.F.; Lima, J.F.; Filho, P.C.D.S.; Serra, O.A. Effect of lanthanum loading on nanosized CeO2-ZnO solid catalysts supported on cordierite for diesel soot oxidation. J. Environ. Sci. 2018, 73, 58–68. [Google Scholar] [CrossRef] [PubMed]
  22. Kim, S.J.; Kim, S.W.; Park, Y.M.; Kim, K.J.; Choi, G.M. Effect of Gd-doped ceria interlayer on the stability of solid oxide electrolysis cell. Solid State Ion. 2016, 295, 25–31. [Google Scholar] [CrossRef]
  23. Lu, H.-F.; Zhou, Y.; Han, W.-F.; Huang, H.-F.; Chen, Y.-F. High thermal stability of ceria-based mixed oxide catalysts supported on ZrO2 for toluene combustion. Catal. Sci. Technol. 2013, 3, 1480–1484. [Google Scholar] [CrossRef]
  24. Dai, Q.; Wang, X.; Lu, G. Low-temperature catalytic combustion of trichloroethylene over cerium oxide and catalyst deactivation. Appl. Catal. B Environ. 2008, 81, 192–202. [Google Scholar] [CrossRef]
  25. Zhang, H.-L.; Zhu, Y.; Wang, S.-D.; Zhao, M.; Gong, M.-C.; Chen, Y.-Q. Activity and thermal stability of Pt/Ce0.64Mn0.16R0.2Ox (R = Al, Zr, La, or Y) for soot and NO oxidation. Fuel Process. Technol. 2015, 137, 38–47. [Google Scholar] [CrossRef]
  26. Polychronopoulou, K.; Zedan, A.F.; Katsiotis, M.; Baker, M.; AlKhoori, A.; AlQaradawi, S.Y.; Hinder, S.; AlHassan, S. Rapid microwave assisted sol-gel synthesis of CeO2 and CexSm1-xO2 nanoparticle catalysts for CO oxidation. Mol. Catal. 2017, 428, 41–55. [Google Scholar] [CrossRef]
  27. Mandal, S.; Bando, K.K.; Santra, C.; Maity, S.; James, O.O.; Mehta, D.; Chowdhury, B. Sm-CeO2 supported gold nanoparticle catalyst for benzyl alcohol oxidation using molecular O2. Appl. Catal. A Gen. 2013, 452, 94–104. [Google Scholar] [CrossRef]
  28. Wattanathana, W.; Veranitisagul, C.; Wannapaiboon, S.; Klysubun, W.; Koonsaeng, N.; Laobuthee, A. Samarium doped ceria (SDC) synthesized by a metal triethanolamine complex decomposition method: Characterization and an ionic conductivity study. Ceram. Int. 2017, 43, 9823–9830. [Google Scholar] [CrossRef]
  29. Stambouli, A.B.; Traversa, E. Solid oxide fuel cells (SOFCs): A review of an environmentally clean and efficient source of energy. Renew. Sustain. Energy Rev. 2002, 6, 433–455. [Google Scholar] [CrossRef]
  30. Nechache, A.; Cassir, M.; Ringuedé, A. Solid oxide electrolysis cell analysis by means of electrochemical impedance spectroscopy: A review. J. Power Sources 2014, 258, 164–181. [Google Scholar] [CrossRef]
  31. Gardini, D.; Christensen, J.M.; Damsgaard, C.D.; Jensen, A.D.; Wagner, J.B. Visualizing the mobility of silver during catalytic soot oxidation. Appl. Catal. B Environ. 2016, 183, 28–36. [Google Scholar] [CrossRef] [Green Version]
  32. Liu, J.; Zhao, Z.; Chen, Y.; Xu, C.; Duan, A.; Jiang, G. Different valent ions-doped cerium oxides and their catalytic performances for soot oxidation. Catal. Today 2011, 175, 117–123. [Google Scholar] [CrossRef]
  33. Sudarsanam, P.; Kuntaiah, K.; Reddy, B.M. Promising ceria–samaria-based nano-oxides for low temperature soot oxidation: A combined study of structure–activity properties. New J. Chem. 2014, 38, 5991–6001. [Google Scholar] [CrossRef]
  34. Anantharaman, A.P.; Geethu, J.; Dasari, H.P.; Lee, J.-H.; Dasari, H.; Babu, G.U.B. Ceria-samarium binary metal oxides: A comparative approach towards structural properties and soot oxidation activity. Mol. Catal. 2018, 451, 247–254. [Google Scholar] [CrossRef]
  35. Zhang, Z.; Han, D.; Wei, S.; Zhang, Y. Determination of active site densities and mechanisms for soot combustion with O2 on Fe-doped CeO2 mixed oxides. J. Catal. 2010, 276, 16–23. [Google Scholar] [CrossRef]
  36. Andana, T.; Piumetti, M.; Bensaid, S.; Russo, N.; Fino, D.; Pirone, R. Nanostructured ceria-praseodymia catalysts for diesel soot combustion. Appl. Catal. B Environ. 2016, 197, 125–137. [Google Scholar] [CrossRef]
  37. Venkataswamy, P.; Jampaiah, D.; Rao, K.N.; Reddy, B.M. Nanostructured Ce0.7Mn0.3O2−δ and Ce0.7Fe0.3O2−δ solid solutions for diesel soot oxidation. Appl. Catal. A Gen. 2014, 488, 1–10. [Google Scholar] [CrossRef]
  38. Miceli, P.; Bensaid, S.; Russo, N.; Fino, D. Effect of the morphological and surface properties of CeO2-based catalysts on the soot oxidation activity. Chem. Eng. J. 2015, 278, 190–198. [Google Scholar] [CrossRef]
  39. Piumetti, M.; Bensaid, S.; Russo, N.; Fino, D. Investigations into nanostructured ceria–zirconia catalysts for soot combustion. Appl. Catal. B Environ. 2016, 180, 271–282. [Google Scholar] [CrossRef]
  40. Tang, Y.; Qiao, H.; Wang, H.; Tao, P. Nanoparticulate Mn0.3Ce0.7O2: A novel electrocatalyst with improved power performance for metal/air batteries. J. Mater. Chem. A 2013, 1, 12512–12518. [Google Scholar] [CrossRef]
  41. Shannon, R.D. Revised effective ionic radii and systematic studies of interatomic distances in halides and chalcogenides. Acta Crystallogr. Sect. A Cryst. Phys. Diffr. Theor. Gen. Crystallogr. 1976, 32, 751–767. [Google Scholar] [CrossRef]
  42. Piumetti, M.; Bensaid, S.; Russo, N.; Fino, D. Nanostructured ceria-based catalysts for soot combustion: Investigations on the surface sensitivity. Appl. Catal. B Environ. 2015, 165, 742–751. [Google Scholar] [CrossRef]
  43. Larachi, F.; Pierre, J.; Adnot, A.; Bernis, A. Ce 3d XPS study of composite CexMn1−xO2−y wet oxidation catalysts. Appl. Surf. Sci. 2002, 195, 236–250. [Google Scholar] [CrossRef]
  44. Trudeau, M.; Tschöpe, A.; Ying, J. XPS investigation of surface oxidation and reduction in nanocrystalline CexLa1−xO2−y. Surf. Interface Anal. 1995, 23, 219–226. [Google Scholar] [CrossRef]
  45. Liu, B.; Li, C.; Zhang, G.; Yao, X.; Chuang, S.S.; Li, Z. Oxygen vacancy promoting dimethyl carbonate synthesis from CO2 and methanol over Zr-doped CeO2 nanorods. ACS Catal. 2018, 8, 10446–10456. [Google Scholar] [CrossRef]
  46. Li, H.; Li, K.; Wang, H.; Zhu, X.; Wei, Y.; Yan, D.; Cheng, X.; Zhai, K. Soot combustion over Ce1−xFexO2−δ and CeO2/Fe2O3 catalysts: Roles of solid solution and interfacial interactions in the mixed oxides. Appl. Surf. Sci. 2016, 390, 513–525. [Google Scholar] [CrossRef]
  47. Wei, Y.; Liu, J.; Zhao, Z.; Duan, A.; Jiang, G. The catalysts of three-dimensionally ordered macroporous Ce1−xZrxO2−supported gold nanoparticles for soot combustion: The metal–support interaction. J. Catal. 2012, 287, 13–29. [Google Scholar] [CrossRef]
  48. Jaoude, M.A.; Polychronopoulou, K.; Hinder, S.; Katsiotis, M.; Baker, M.; Greish, Y.; Alhassan, S. Synthesis and properties of 1D Sm-doped CeO2 composite nanofibers fabricated using a coupled electrospinning and sol–gel methodology. Ceram. Int. 2016, 42, 10734–10744. [Google Scholar] [CrossRef]
  49. Raaen, S. Adsorption of Carbon Dioxide on Mono-Layer Thick Oxidized Samarium Films on Ni(100). Nanomaterials 2021, 11, 2064. [Google Scholar] [CrossRef]
  50. Filtschew, A.; Hofmann, K.; Hess, C. Ceria and its defect structure: New insights from a combined spectroscopic approach. J. Phys. Chem. C 2016, 120, 6694–6703. [Google Scholar] [CrossRef]
  51. Li, B.; Sediako, A.D.; Zhao, P.; Li, J.; Croiset, E.; Thomson, M.J.; Wen, J.Z. Real-time observation of Carbon oxidation by Driven Motion of Catalytic Ceria Nanoparticles within Low pressure oxygen. Sci. Rep. 2019, 9, 8082. [Google Scholar] [CrossRef] [PubMed] [Green Version]
Nanomaterials 12 00392 g001 550
Figure 1. XRD results of fresh and spent catalysts after five cycles of reactions: (a) CeO2, (b) Sm0.05Ce0.95, (c) Sm0.1Ce0.9, (d) Sm0.2Ce0.8.
Figure 1. XRD results of fresh and spent catalysts after five cycles of reactions: (a) CeO2, (b) Sm0.05Ce0.95, (c) Sm0.1Ce0.9, (d) Sm0.2Ce0.8.
Nanomaterials 12 00392 g001
Nanomaterials 12 00392 g002 550
Figure 2. SEM images of all fresh and spent catalysts after five cycles: (a) CeO2 fresh; (b) Sm0.05Ce0.95 fresh; (c) Sm0.1Ce0.9 fresh; (d) Sm0.2Ce0.8 fresh; (e) CeO2 spent; (f) Sm0.05Ce0.95 spent; (g) Sm0.1Ce0.9 spent; (h) Sm0.2Ce0.8 spent.
Figure 2. SEM images of all fresh and spent catalysts after five cycles: (a) CeO2 fresh; (b) Sm0.05Ce0.95 fresh; (c) Sm0.1Ce0.9 fresh; (d) Sm0.2Ce0.8 fresh; (e) CeO2 spent; (f) Sm0.05Ce0.95 spent; (g) Sm0.1Ce0.9 spent; (h) Sm0.2Ce0.8 spent.
Nanomaterials 12 00392 g002
Nanomaterials 12 00392 g003 550
Figure 3. XPS results of (a) Ce3d of fresh catalysts, (b) Ce3d of spent catalysts, (c) O1s of fresh catalysts, (d) O1s of spent catalysts, (e) Sm 3d5/2 of fresh catalysts, (f) Sm 3d5/2 of spent catalysts.
Figure 3. XPS results of (a) Ce3d of fresh catalysts, (b) Ce3d of spent catalysts, (c) O1s of fresh catalysts, (d) O1s of spent catalysts, (e) Sm 3d5/2 of fresh catalysts, (f) Sm 3d5/2 of spent catalysts.
Nanomaterials 12 00392 g003
Nanomaterials 12 00392 g004 550
Figure 4. Raman results of fresh and spent catalysts after five cycles of reactions: (a) CeO2, (b) Sm0.05Ce0.95, (c) Sm0.1Ce0.9, (d) Sm0.2Ce0.8.
Figure 4. Raman results of fresh and spent catalysts after five cycles of reactions: (a) CeO2, (b) Sm0.05Ce0.95, (c) Sm0.1Ce0.9, (d) Sm0.2Ce0.8.
Nanomaterials 12 00392 g004
Nanomaterials 12 00392 g005 550
Figure 5. Soot conversion activity test of fresh Sm-doped ceria catalysts.
Figure 5. Soot conversion activity test of fresh Sm-doped ceria catalysts.
Nanomaterials 12 00392 g005
Nanomaterials 12 00392 g006 550
Figure 6. Effect of Ce3+ percentage and Oα percentage on activity for all catalysts: (a) T50 vs. Ce3+ percentage, (b) T50 vs. Oα percentage.
Figure 6. Effect of Ce3+ percentage and Oα percentage on activity for all catalysts: (a) T50 vs. Ce3+ percentage, (b) T50 vs. Oα percentage.
Nanomaterials 12 00392 g006
Nanomaterials 12 00392 g007 550
Figure 7. The relation between T50 and I554/I596.
Figure 7. The relation between T50 and I554/I596.
Nanomaterials 12 00392 g007
Nanomaterials 12 00392 g008 550
Figure 8. Stability of Sm-doped CeO2 for soot oxidation.
Figure 8. Stability of Sm-doped CeO2 for soot oxidation.
Nanomaterials 12 00392 g008
Nanomaterials 12 00392 g009 550
Figure 9. Relationship between T50 change (between first and seventh cycles) and Sm-doping ratio.
Figure 9. Relationship between T50 change (between first and seventh cycles) and Sm-doping ratio.
Nanomaterials 12 00392 g009
Nanomaterials 12 00392 g010 550
Figure 10. Relationship between Ce3+/Oα change and Sm-doping ratio.
Figure 10. Relationship between Ce3+/Oα change and Sm-doping ratio.
Nanomaterials 12 00392 g010
Table
Table 1. Texture results of Sm-doped ceria fresh and spent catalysts (after five cycles). Percentages for spent catalysts indicate relative changes compared to fresh catalysts.
Table 1. Texture results of Sm-doped ceria fresh and spent catalysts (after five cycles). Percentages for spent catalysts indicate relative changes compared to fresh catalysts.
Catalyst Crystallite Size/nmLattice Parameter/ÅSBET/m2g−1
CeO2-fresh12.33 (±0.09)5.405 (±0.0018)45.5 (±1.57)
Sm0.05Ce0.95-fresh12.43 (±0.19)5.424 (±0.0075)42.2 (±0.99)
Sm0.1Ce0.9-fresh11.89 (±0.17)5.432 (±0.0028)48.3 (±0.78)
Sm0.2Ce0.8-fresh13.61 (±0.06)5.442 (±0.0014)40.9 (±1.94)
CeO2-spent14.52 (±0.13)/+17.8%5.418 (±0.0015)40.9 (±1.43)/−10.1%
Sm0.05Ce0.95-spent14.71 (±0.07)/+18.3%5.430 (±0.0015)40.5 (±0.75)/−4.0%
Sm0.1Ce0.9-spent13.33 (±0.11)/+12.1%5.436 (±0.0032)46.2 (±2.36)/−4.3%
Sm0.2Ce0.8-spent14.26 (±0.12)/+4.8%5.445 (±0.0087)40.2 (±1.52)/−1.7%
Table
Table 2. Ce3+ percentages and Oα percentages of fresh and spent catalysts.
Table 2. Ce3+ percentages and Oα percentages of fresh and spent catalysts.
CatalystCeO2Sm0.05Ce0.95Sm0.1Ce0.9Sm0.2Ce0.8
Ce3+ (%)-fresh24.218.819.317.3
Ce3+ (%)-spent15.817.918.516.8
Oα (%)-fresh39.639.139.234.2
Oα (%)-spent29.537.437.634.2
Table
Table 3. I554/I596 of Raman results.
Table 3. I554/I596 of Raman results.
Sm0.05Ce0.95Sm0.1Ce0.9Sm0.2Ce0.8
I554/I596 fresh0.520.630.97
I554/I596 spent0.690.731.06
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Li, B.; Croiset, E.; Wen, J.Z. Influence of Surface Properties of Nanostructured Ceria-Based Catalysts on Their Stability Performance. Nanomaterials 2022, 12, 392. https://doi.org/10.3390/nano12030392

AMA Style

Li B, Croiset E, Wen JZ. Influence of Surface Properties of Nanostructured Ceria-Based Catalysts on Their Stability Performance. Nanomaterials. 2022; 12(3):392. https://doi.org/10.3390/nano12030392

Chicago/Turabian Style

Li, Boyu, Eric Croiset, and John Z. Wen. 2022. "Influence of Surface Properties of Nanostructured Ceria-Based Catalysts on Their Stability Performance" Nanomaterials 12, no. 3: 392. https://doi.org/10.3390/nano12030392

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