Next Article in Journal
A Demonstration of Pt L3-Edge EXAFS Free from Au L3-Edge Using Log–Spiral Bent Crystal Laue Analyzers
Next Article in Special Issue
Improved CO-PROX Performance of CuO/CeO2 Catalysts by Using Nanometric Ceria as Support
Previous Article in Journal
Solid-Supported Palladium Catalysts in Sonogashira Reactions: Recent Developments
Previous Article in Special Issue
Preferential CO Oxidation in H2 over Au/La2O3/Al2O3 Catalysts: The Effect of the Catalyst Reduction Method

Catalysts 2018, 8(5), 203;

Ru–Pd Bimetallic Catalysts Supported on CeO2-MnOX Oxides as Efficient Systems for H2 Purification through CO Preferential Oxidation
Dipartimento di Scienze Chimiche, Università di Catania, Viale A. Doria 6, 95125 Catania, Italy
I.N.S.T.M. UdR of Catania, Viale A. Doria 6, 95125 Catania, Italy
Author to whom correspondence should be addressed.
Received: 9 April 2018 / Accepted: 9 May 2018 / Published: 12 May 2018


The catalytic performances of Ru/ceria-based catalysts in the CO preferential oxidation (CO-PROX) reaction are discussed here. Specifically, the effect of the addition of different oxides to Ru/CeO2 has been assessed. The Ru/CeO2-MnOx system showed the best performance in the 80–120 °C temperature range, advantageous for polymer-electrolyte membrane fuel cell (PEMFC) applications. Furthermore, the influence of the addition of different metals to this mixed oxide system has been evaluated. The bimetallic Ru–Pd/CeO2-MnOx catalyst exhibited the highest yield to CO2 (75%) at 120 °C whereas the monometallic Ru/CeO2-MnOx sample was that one with the highest CO2 yield (60%) at 100 °C. The characterization data (H2-temperature programmed reduction (H2-TPR), X-ray diffraction (XRD), N2 adsorption-desorption, diffuse reflectance infrared Fourier transform spectroscopy (DRIFT), X-ray photoelectron spectroscopy (XPS)) pointed out that the co-presence of manganese oxide and ruthenium enhances the mobility/reactivity of surface ceria oxygens accounting for the good CO-PROX performance of this system. Reducible oxides as CeO2 and MnOx, in fact, play two important functions, namely weakening the CO adsorption on the metal active sites and providing additional sites for adsorption/activation of O2, thus changing the mechanism from competitive Langmuir–Hinshelwood into non-competitive one-step dual site Langmuir–Hinshelwood/Mars–van Krevelen. As confirmed by H2-TPR and XPS measurements, these features are boosted by the simultaneous presence of ruthenium and palladium. The strong reciprocal interaction of these metals between them and with the CeO2-MnOx support was assumed to be responsible of the promoted reducibility/reactivity of CeO2 oxygens, thus resulting in the best CO-PROX efficiency at low temperature of the Ru-Pd/CeO2-MnOx catalyst. The higher selectivity to CO2 found on the Ru–Pd system, which reduces the undesired H2 consumption, represents a promising result of this research, being one of the key aims of the design of CO-PROX catalysts.
CO preferential oxidation (CO-PROX); fuel cells; ruthenium; palladium; ceria

1. Introduction

The modern energy crisis and urgent development of green technologies and energies have driven in the last decade intensive research in fuel cell technologies both for stationary and mobile uses. In particular, polymer-electrolyte membrane fuel cells (PEMFC), which work in the 80–100 °C temperature range, are among the most promising devices for automotive purposes [1].
The hydrogen used as fuel in PEMFC is currently produced by steam reforming of hydrocarbons or alcohols and a subsequent water–gas shift reaction. The anode of the PEMFC is, however, easily poisoned even at very low concentrations of CO (less than 10 ppm) [2]. Different technologies have been investigated to purify H2 from traces of CO including: catalytic methanation [3], membrane separation [4] and preferential oxidation of CO in excess of hydrogen (CO-PROX reaction) [5,6,7]. The last one, considered highly valuable of investigation, involves two competitive reactions, namely the desired CO oxidation to CO2 and the undesired H2 oxidation to water. Therefore, the catalyst of this process must be highly selective towards the first reaction. Noble-metal catalysts, such as Pd [8], Rh [9], Ru [10,11], Au [12,13,14] and Pt [15,16], have revealed good CO-PROX performance. The selection of the proper support has been also found crucial in addressing the catalytic activity. Recently, the use of a reducible/active support, such as cerium oxide or iron oxide, resulted in remarkably low-temperature CO-PROX activities [12,17]. The peculiar red-ox properties of CeO2 involving the facile exchange between Ce3+ and Ce4+ states and the high mobility of O2– ions in the lattice, are the key factors to explain the high relevance of this oxide as a metal support in the PROX reaction [6,12,13,18].
In order to optimize and increase the efficacy of ceria through the rise of the CeO2 redox properties, one of the most used strategies has been the addition of chemical promoters or the mixing with another oxide such as, for example, CuO [19,20]. In particular, the addition of Mn into a CeO2 crystal lattice was found to increase the thermal stability and to improve the redox properties of ceria by generating a more efficient Ce3+/Ce4+ redox couple [21]. For these reasons, the CeO2-MnOx mixed oxides have reported good catalytic activity for various oxidation reactions [22,23,24]. To the best of our knowledge, few papers deal with the PROX performance of Ru-based catalysts supported on CeO2 or CeO2-based materials, although it has been reported that the Ru-based catalysts were more active and selective than Pt-based ones below 150 °C [10,25], an optimal temperature range for a possible use of these catalysts for the hydrogen purification in the PEMFC or for the alkaline fuel cells (AFC).
On the basis of the above considerations, here we report a study of the catalytic performance in the PROX reaction of Ru supported on ceria and ceria-mixed oxide catalysts. In particular, the effect of the addition of another oxide or another metal to Ru/CeO2 has been explored both in terms of catalytic activity and chemico-physical properties.

2. Results

2.1. Catalytic Activity

A preliminary screening of the PROX activity of monometallic ruthenium catalysts supported on different ceria-based mixed oxides was carried out to determine the best-performing system. The results of investigated monometallic Ru catalysts in terms of CO and O2 conversions and selectivity and yield towards the CO oxidation as a function of reaction temperature are depicted in Figure 1.
Figure 1a shows the CO conversion against the reaction temperature. Generally, CO conversion on all samples displays a volcano shape behavior as a function of the reaction temperature, i.e., the CO conversion reaches a maximum and then decreases. Reasonably at high temperature, the reverse water–gas shift (RWGS) reaction (CO2 + H2 ↔ CO + H2O) becomes significant (Ea = 120–160 kJ/mol, higher than that found for PROX, 70–100 kJ/mol [5,25]). In fact, on Ru-based catalysts RWGS has been reported to occur at T > 150 °C [10,25], therefore justifying the drop of activity at higher temperatures. Specifically, it is worth noting that the CO conversion upper value and its temperature rely on the mixed-oxide support used. This happens also for selectivity to CO2 (Figure 1c). To comprehend this behavior, the fact that cerium oxide has a strong tendency to provide active oxygens with strong oxidation power [6,12,25,26], which are however reactive towards both CO and H2, must be taken into account. This causes a drop of selectivity at higher temperature due to the higher activation energy of H2 oxidation compared to that of CO [27,28,29,30].
Interestingly, the Ru/CeO2-MnOx sample exhibited the highest value of CO conversion at lower temperature (70.6% at 100 °C), which is higher than those found for Ru/CeO2-CuO (62.5% at 170 °C), Ru/CeO2 (54% at 140 °C) and Ru/CeO2-Fe2O3 (45.6% at 140 °C) samples. In the case of the Ru/CeO2-CuO catalyst, CO conversion shifted to a higher temperature, probably due to the fact that Cu catalysts require higher temperatures to promote the CO oxidation [12,13,25]. However, it cannot be fully ruled out that the low activity of the Ru/CeO2-CuO catalyst can be related to an unsuitable pretreatment of the CuO-CeO2 system, for which calcination at 450 °C (adopted here for all samples) could not be ideal for the formation of the active Cu+ sites [19,20].
The Ru/CeO2 catalyst is, instead, the most active as to the O2 conversion (Figure 1b), which is due to both CO and H2 oxidation with 100% conversion reached at about 120 °C, i.e., 50 °C less than on Ru/CeO2-Fe2O3 and Ru/CeO2-CuO, whereas the Ru/CeO2-MnOx sample reached 80.9% conversion at 170 °C. As shown in Figure 1c, the above behavior results in the much higher selectivity of the Ru/CeO2-MnOx sample towards the preferential CO oxidation in the 70–140 °C temperature range, with a maximum at 100 °C. This indicates that the contemporaneous presence of reactive oxygens of cerium and manganese oxides leads to a very good selectivity at low temperature. Accordingly, CO2 yields as a function of temperature (Figure 1d) clearly show that the Ru/CeO2-MnOx catalyst is the most efficient among all investigated systems for PROX in the 80–120 °C temperature range.
The other monometallic samples were far less active, with only the Ru/CeO2-CuO sample reaching 20% of CO2 yield in the 140–170 °C temperature range. Therefore, the CeO2-MnOx mixed oxide was chosen as a support to investigate other mono (Pt or Pd) and bimetallic (Ru-Pd) catalysts. Figure 2 displays the CO conversion (Figure 2a), the O2 conversion (Figure 2b), the selectivity towards the CO oxidation (Figure 2c) and the yield to CO2 (Figure 2d) of Ru/CeO2-MnOx, Pt/CeO2-MnOx, Pd/CeO2-MnOx and Ru–Pd/CeO2-MnOx. The Pd/CeO2-MnOx catalyst exhibited an increased CO conversion with the temperature reaching the maximum of 62% at 140 °C whereas the Pt/CeO2-MnOx showed the lowest activity in the inspected temperature range (Figure 2a). Pt/CeO2-MnOx reached 100% O2 conversion (Figure 2b) at lower temperature (100–120 °C) compared to Ru/CeO2-MnOx and Ru-Pd/CeO2-MnOx catalysts; therefore, CO selectivity (Figure 2c) and CO2 yield (Figure 2d) did not exceed 30%. It is noteworthy that the Ru–Pd system leads to higher CO conversion at high temperature (T > 100 °C) compared to the corresponding monometallic samples (Figure 2a), providing at 120 °C the highest values of CO conversion (85%) (Figure 2a), CO selectivity (88.5%) (Figure 2c), and CO2 yield (75.3%) (Figure 2d) among all catalysts. It must be stressed that the increased activity of the Ru–Pd system cannot be related to the concentration of the metal species, which on both mono and bimetallic samples remains 1 wt % (0.5–0.5% on bimetallics and 1% on monometallics). It has been seen that bimetallics can be often better performing than the related monometallics due to a synergy between the two metals and/or the support [6,12,31].

2.2. Catalysts Characterization

In order to find relations between catalytic performances and chemico-physical properties, we investigated the reducibility H2-temperature programmed reduction (H2-TPR), the structural and textural properties (diffuse reflectance infrared Fourier transform spectroscopy (DRIFT), X-ray diffraction (XRD) and Brunauer–Emmett–Teller (BET) surface area) and the surface properties (X-ray photoelectron spectroscopy (XPS)) of the most active Ru-based samples.

2.2.1. Temperature Programmed Reduction (H2-TPR)

Figure 3 shows the H2-temperature programmed reduction profiles of the analyzed samples between 50 °C and 500 °C. On the bare cerium oxide support, the H2 consumption starts at around 350 °C, due to the partial reduction of the CeO2 surface oxygen [12,13]. The reduction of bulk oxygen was reported to take place at temperatures higher than 700 °C [32] and, therefore, is not visible in the TPR curve of Figure 3. The profile of the Ru/CeO2 sample displays two reduction peaks at 165 °C and 190 °C and a shoulder at ca. 325 °C. According to literature data, the peak at 165 °C is characteristic of the reduction of the ruthenium precursor salt (Ru(NO)(NO3)3), while the peak at 190 °C is assigned to the reduction of well dispersed ruthenium oxide particles on the surface of the support [10,33]. The shoulder at 325 °C reasonably originates from the reduction of the ceria surface oxygens shifted to lower temperature as a result of the interaction with the ruthenium species.
A quite sharp reduction peak at 435 °C characterizes the TPR profile of the CeO2-MnOx catalyst. In this case, the reduction of ceria surface oxygen is anticipated by the presence of another reducible oxide as MnOx and probably includes the reduction of MnOx species to MnO [34,35,36], as confirmed also by the TPR quantification data (Table S1), being the total H2 uptake higher (around 1.8 times) than the bare CeO2. The presence of ruthenium (sample Ru/CeO2-MnOx), instead, leads to a wide multi-component peak in the 150–350 °C range, in which it is quite hard to distinguish and attribute with certainty the different reduction signals to each single component (Ru precursor, CeO2 and MnOx). The deconvolution procedure (Figure S1A) led to the distinction of three different components at around 199 °C, 246 °C and 314 °C, respectively. Reasonably, considering also the TPR quantification reported in Table S1, the low temperature feature at 200 °C can be attributed to the reduction of the Ru precursor shifted at higher temperature with respect to Ru/CeO2 due to a stronger metal–support interaction [37]; the signal at around 315 °C can be assigned to the reduction of ceria surface oxygen interacting with ruthenium and manganese oxide; and the feature at 245 °C is probably due to the reduction of manganese oxide species (Mn2O3 → Mn3O4) [36] overlapping with the reduction of dispersed RuOX particles on the surface of CeO2-MnOx. The Pd/CeO2-MnOx catalyst shows a wide reduction peak with maximum at circa 275 °C, attributable to the reduction of the PdO-CeO2-MnOX species strongly interacting with each other [38,39].
The bimetallic Ru–Pd/CeO2-MnOx sample shows a broad peak (around 210 °C) which is at a lower temperature compared to the monometallic palladium catalyst and much more intense than both Ru and Pd monometallics. Furthermore, the total H2 uptake of Ru–Pd/CeO2-MnOx is slightly higher (2106 µmol/gcat) than the sum of the H2 uptakes of Pd/CeO2-MnOx and Ru/CeO2-MnOx (2067 µmol/gcat). It is rational to assume that the reduction both of Ru and Pd species, together with that of the superficial oxygens of the mixed CeO2-MnOx support, contribute to this peak. The deconvolution of the Ru–Pd/CeO2-MnOx reduction peak (Figure S1B) revealed two other contributions, one at low temperature (140 °C) and one at high temperature (275 °C), probably due to the reduction of part of the metal precursors. It is possible in this case, in the same way as other bimetallic systems supported on cerium oxide reported in the literature [6,12], that a mutual interaction between the two metals leads a single reduction peak, distinct from the individual monometallic samples. Furthermore, this reduction peak being shifted at lower temperature than the monometallic Ru sample also suggests an increased reducibility/mobility of the ceria-manganese reactive oxygens [6,12,40].

2.2.2. Structural and Textural Properties

Figure 4 exhibits the XRD patterns of the bare CeO2 and CeO2-MnOx supports and of the Ru/CeO2, Ru/CeO2-MnOx, Pd/CeO2-MnOx and Ru-Pd/CeO2-MnOx mono and bimetallic samples. The signals at 2θ = 28.6° (1 1 1), 33.1° (2 0 0), 47.5° (2 2 0) and 56.4° (3 1 1) are assigned, according to the Joint Committee on Powder Diffraction Standards (JCPDS) data, to the typical fluorite structure of the CeO2. No peaks associated with metallic species or manganese oxide were detected. The absence of signals for the Ru and Pd species is plausibly due to the combination of the small size (less than 5 nm) and the low amount (1 wt %) of metals. With regard to manganese oxide, the low amount (5 wt %), the homogeneous distribution of this host oxide on the ceria, and the co-presence of CeO2 diffraction peaks overlapping with those of manganese oxide, having a similar structure [41], do not allow recognition of variations of the cerium oxide pattern upon addition of MnOx.
The size of the crystalline grains of investigated catalysts, calculated by the Scherrer equation referring to the main peak of cerium oxide at 2θ = 28.6° (1 1 1), their BET surface area and mean pore diameters, calculated with the Dollimore–Heal method [42], are reported in Table 1.
The precipitation method with KOH used to synthesize the bare CeO2 leads to a catalyst with relatively high surface area (107 m2/g) and small pores (3 nm) in line with literature data [43,44]. A small increase (around 10%) of surface area (119 m2/g) was noticed in the presence of manganese oxide, consistent with the decrease of the crystallite size (from 10 nm of the bare CeO2 to 8.5 nm of the mixed CeO2-MnOX oxide) and the pore diameter. Interestingly, the bimetallic Ru–Pd/CeO2-MnOx sample showed the highest surface area (123 m2/g) among all investigated samples. It is probable that the presence of a bimetallic phase, well spread on the mixed ceria-manganese oxide, favours the replacement of cerium ions with manganese ones in the fluorite structure, which is reasonably due to the crystal structure similarity [41]. Moreover, a part of the well dispersed bimetallic components can move into the interlayers of the ceria support.
The DRIFT spectrum (4000–500 cm−1) of the cerium oxide support is shown in Figure S2. On the basis of the literature, the signal at 3470 cm−1 can be assigned to the O–H stretching of H-bonded water [45]. The bands at 1585 and 1346 cm−1 are due to the O–C–O stretching vibrations whereas the features at 1057 and 852 cm−1 can be assigned to the C–O stretching, thus pointing to the presence of carbonate species on the oxide sample. Finally, the band at 600 cm−1 can be attributed to the O–Ce–O phononic vibration of the crystal lattice of the cerium oxide [46]. Figure 5a compares the DRIFT spectrum of the support with those of the investigated samples. It is evident that all mixed oxides reveal a shift of the bands assigned to carbonates. This is better highlighted in Figure 5b, where the zoomed 1800–1000 cm−1 region is reported. The presence of different carbonate species is typical of basic oxide materials, such as cerium oxide, owing to the interaction of basic sites with the atmospheric CO2 [43,44]. The inspection of literature data [47,48,49] points to the presence of variously coordinated carbonate species (O–C–O asymmetrical and symmetrical stretchings at 1600–1470 cm−1 and 1370–1300 cm−1, respectively) and un-coordinated H-bonded carbonate (νas CO32− at 1450–1420 cm−1). In the case of the CeO2 samples (CeO2 and Ru/CeO2), the coordinated carbonate bands were predominant, whereas for the CeO2-MnOx supported samples (CeO2-MnOx, Ru/CeO2-MnOx, Pd/CeO2-MnOx and Ru-Pd/CeO2-MnOx) the un-coordinated H-bonded carbonate band was the main feature. This behaviour suggests that the presence of manganese oxide significantly modified the acid-base properties of the system, causing a decrease of the basicity of the oxide support, thus strongly affecting the nature of CO2 adsorption sites.

2.2.3. X-ray Photoelectron Spectroscopy (XPS) Measurements

The electronic structure of the Ru/CeO2, Ru/CeO2-MnOx and Ru–Pd/CeO2-MnOx samples was investigated by XPS, which provides information on the surface elemental composition, the oxidation status and the chemical surroundings of the studied species [50,51].
The Ru 3d states (Figure S3) overlap the C 1s levels, so we prefer to mainly discuss the XPS of the Ru 3p binding-energy region. The two Ru 3p3/2,1/2 spin-orbit components for Ru/CeO2 (Figure 6a) lie at 462.7 and 485.1 eV, respectively. These energy values and also the Ru 3d5/2 state, at 281.3 eV (Figure S3), are indicative of the presence of RuO2 on the surface sample [52,53,54,55]. RuO2 is also present on the surface sample of Ru/CeO2-MnOx since the Ru 3d5/2 state is at 281.5 eV and the two Ru 3p3/2,1/2 spin-orbit components are at 463.3 and 485.8 eV, respectively. It is important to stress that XPS is a surface-sensitive technique that probes a thickness of ~60 Å in our conditions. The above energy values are significantly lower in the case of Ru–Pd/CeO2-MnOx, being the Ru 3d5/2 state at 280.8 eV and the two Ru 3p3/2,1/2 spin-orbit components at 462.2 and 484.6 eV, respectively. All these latter values are consistent with the presence of metallic Ru in the Ru–Pd/CeO2-MnOx sample [56].
The Mn 2p3/2,1/2 spin-orbit levels are at 640.4 and 652.4 eV (Figure 6b), respectively, in both Ru/CeO2-MnOx and Ru–Pd/CeO2-MnOx systems. Moreover, there is evidence of satellite features at ~7 eV higher binding energy from the main peaks that are a fingerprint of the presence of MnO, since these satellites are absent in Mn2O3 and in MnO2 species [57].
Finally, Figure 6c shows the XPS of the Pd 3d states for the Ru–Pd/CeO2-MnOx system. The binding energy values of 335.3 and 340.6 due to the Pd 3d5/2,3/2 spin-orbit components can be unambiguously assigned to metallic palladium [58,59,60]. It must be noted that the full width at half maximum (FWHM) of the Ru 3p3/2 states for the Ru/CeO2 (Figure 6a) is 1.8 eV, that of the Mn 2p3/2 states for the Ru/CeO2-MnOx (Figure 6b) is 1.65 eV and that of the Pd 3d5/2 states for the Ru–Pd/CeO2-MnOx (Figure 6c) is 1.1 eV.
In all cases, the CeO2 system gave the expected XPS 3d signals as reported in Figure S4. Concerning the Ce(IV)/Ce(III) ratio, it must be noted that peaks at 882.0, 888.6 and 897.9 eV (Figure S4) are from the Ce 3d5/2 states and peaks at 900.5, 906.9 and 916.2 are from the 3d3/2 states. The first two peaks at 882.0 and 888.6 eV are due to a mixing configuration of 3d94f2(O 2p4) and 3d94f1(O 2p5) Ce4+ states, and the peak at 897.9 eV belongs to the 3d94f0(O 2p6) Ce4+ state. The series of peaks at 900.5, 906.9 and 916.2 are the related spin-orbit components of the 3d3/2 states of the same configurations. Moreover, there is no structure between the peaks at 882.0 eV, 888.6 eV and 897.9 eV, and this rules out any 3d94f1(O 2p6) Ce3+ final state [61].
The O1s peaks of the representative Ru/CeO2 can be fitted into two peaks referred to as the lattice oxygen O2− and the chemisorbed OH groups. The O1s peak at about 528.7 eV is due to the lattice oxygen (O2−) for CeO2, and that at 530.6 eV belongs to the chemisorbed OH species. In the case of the Ru/CeO2-MnOx the energy positions of these two peaks are 528.9 and 530.4 eV while in the case of Ru–Pd/CeO2-MnOx these two peaks lie at 529.2 and 530.8 eV. The intensity ratio between these two peaks (1.2–1.3) is almost the same in all the three different investigated systems, thus excluding different affluent oxygen species on the samples surface [61]. The deconvolution features are reported in the supporting information (Figure S5).
The XPS atomic concentration analysis of the three investigated systems clearly show some surface segregation of ruthenium [62] since the Ru/Ce is 0.18, 0.12 and 0.06 for the Ru/CeO2, Ru/CeO2-MnOx and Ru–Pd/CeO2-MnOx systems, respectively. The Mn/Ce is 0.07 and 0.03 for the Ru/CeO2-MnOx and Ru–Pd/CeO2-MnOx systems, respectively and, finally, the Pd/Ce is 0.02 for the Ru–Pd/CeO2-MnOx system. XPS also indicates that there is neither nitrogen, potassium nor chlorine signals in all these samples, thus inferring the purity of the samples with respect to the starting reagents (see Figure S6 with the survey spectrum of the Ru/CeO2 sample).

3. Discussion

In this paper the catalytic activity of ceria-based mixed oxides (CeO2-Fe2O3, CeO2-CuO and CeO2-MnOx) supported mono and bimetallic Ru-Pd samples was evaluated in the CO-PROX reaction. A preliminary comparison of the catalytic results among investigated mixed oxides supported Ru monometallic catalysts pointed out that the Ru/CeO2-MnOx sample was the most selective towards the CO oxidation (Figure 1c), providing the highest CO2 yield (Figure 1d) in the temperature range of PEM fuel cells (80–120 °C). Therefore, the CeO2-MnOx mixed oxide was chosen for further investigation focusing on Ru–Pd bimetallic systems.
As reported in the literature [63,64], the manganese oxide is a reducible oxide as ceria, and then it can provide, in addition to those of CeO2, beneficial reactive oxygens for oxidation reactions. Moreover, CeO2-MnOx mixed oxides can also show stronger redox properties than CeO2 alone, due to the multi-valence surface state and the mutual contact between ceria and manganese oxide [65,66]. It has been reported that the oxygen storage capacity of CeO2 is boosted by the presence of manganese oxide, with the surface oxygen mobility of ceria also improved by forming MnOx-CeO2 solid solution [67]. In our case, the occurrence of an interaction between ruthenium-CeO2 and MnOx itself, proved by TPR data, can be one of the reasons for the excellent performance of this catalyst in the CO-PROX reaction. Interestingly, the Ru/CeO2-MnOX exhibited better performance compared to the other investigated monometallic systems (Pt and Pd, Figure 2). Furthermore, the Ru–Pd/CeO2-MnOx system showed higher selectivity (Figure 2c) and yield to CO2 (Figure 2d) compared to the Ru/CeO2-MnOx catalyst at T > 100 °C, namely in the operative range of alkaline fuel cells (100–140 °C).
To elucidate the catalytic behavior of the investigated catalysts it is important to refer to the CO-PROX reaction mechanisms reported in the literature for reducible oxide-supported metal catalysts [5] and for non-reducible oxide-supported Ru catalysts [10].
For reducible oxide-supported metal catalysts, it was stated that the reaction occurs between CO and oxygen co-adsorbed on the surface-active sites. The oxygen can be activated at the metal/support-oxide interface and/or the reducible surface oxygens of the oxide can participate in the reaction [5]. However, it is necessary to clarify that a greater activation of oxygen does not directly mean a better yield for CO oxidation reactions: activated oxygen can in fact react with both CO and H2, which means that the two species are in strong competition between each other for the oxidation reaction. In order to obtain a good yield, it is then necessary to activate CO and not H2. It is well known that cerium oxide has good catalytic properties for oxidation reactions, since it has mobile/reducible oxygens [6,12,13,43,68]. The mobility of such oxygens can be increased by the presence of metals on the surface, which introduce crystalline defects that increase the mobility of these oxygens and increasing the oxidative power of the substrate [12,43,67]. Specifically, for the preferential oxidation of CO the most widely reported mechanism is that of Mars–van Krevelen (MvK) [6,13,43,68,69,70]. The aforesaid mechanism involves different reaction steps: the first is the formation of a chemical bond between the reagents (CO, O2 or H2) and the catalyst surface; then the formation and the desorption of products (CO2 and H2O) take place with the generation of oxygen vacancies in the bulk of the ceria, which can then be replaced by the subsequent oxygen adsorption from the gaseous phase. In this case, an important parameter is the reactivity of the support oxide (ceria) oxygens, which are directly involved in the reaction, being able to react at the metal/CeO2 interface with CO to form CO2. The reducibility of the cerium oxide reflects directly the mobility and therefore the reactivity of surface oxygens with an increased reducibility (mobility/reactivity) beneficial for the catalytic activity in the CO-PROX reaction [5,6,12,13,43,68,69,70].
For ruthenium or platinum-based catalysts supported on non-reducible (inert) oxides, as reported in the literature, the oxidation of CO occurs according to the Langmuir–Hinshelwood mechanism [71,72]. Both reagents (CO and O2) bind to the surface at the active sites of the metal species. In particular, the following mechanism was assumed on ruthenium-based catalysts:
Reactants’ adsorption on the Ru surface:
CO(g) + Ru → COad-Ru
O2(g) + Ru → O2(g)-Ru
Oxygen dissociation:
O2(g)-Ru → Oad-Ru
CO2 formation:
COad-Ru + Oad-Ru → CO2(g)-Ru
However, also in this case, it must be considered that the reaction mixture of CO-PROX contains considerable hydrogen excess (88 vol. %) and, therefore, H2 can also be activated by the metal surface sites, thus competing with CO in reacting with oxygen and influencing the selectivity of the CO-PROX reaction [10,73].
The mobility of the ceria oxygens can be increased both by interaction with a metal and by the presence of a host oxide [44,74,75]. From the TPR characterization (Figure 3), it is possible to infer that a strong interaction is established between Ru–Pd and the mixed oxide CeO2-MnOx support, thus enhancing the reducibility/reactivity of the ceria oxygens (the reduction peak of the bimetallic sample is at a lower temperature and more intense than the corresponding monometallic ones). This can explain the higher activity of this catalyst. As evidenced by the XRD measurements in both the monometallic and bimetallic samples, the small metal particle size (below 5 nm of diameter) and the good distribution of manganese oxide on the ceria can be decisive factors in explaining the excellent catalytic performances of Ru/CeO2-MnOx and Ru–Pd/CeO2-MnOx catalysts. The strong interaction between Ru–Pd and the mixed oxide CeO2-MnOx was, furthermore, confirmed by XPS measurements, with the Ru–Pd/CeO2-MnOx sample that showed the presence of metallic Ru and Pd species on the surface of the sample a key factor explaining the higher activity of this sample compared to the Ru/CeO2-MnOx and Ru/CeO2 samples where Ru4+ species were also detected. As reported in the literature, metallic Ru0 is more active compared to oxidized Run+ species [76,77]. In this case, the simultaneous presence of Pd0 also facilitates the redox process of the ceria-manganese oxide, thus favouring an easier CO activation.
To interpret the results obtained, it is then reasonable to hypothesize a mixed Langmuir–Hinshelwood/Mars–van Krevelen (LH/MvK) reaction mechanism. In this case, in fact, the reaction can take place in one step: the adsorbed CO (COad) reacts very quickly with the mobile/active oxygens of the mixed CeO2-MnOx oxide, also allowing the rapid desorption of the CO2 produced, while the oxygen vacancy is instantly replaced by the O2 adsorbed. The fast desorption of the produced CO2 can be favoured by the modification of the surface sites of the CeO2-MnOx with respect to the cerium oxide as revealed by the DRIFT data (Figure 5), while the adsorption of oxygen and CO from the gas phase is allowed by the increased surface area of the mixed oxide (Table 1).
In conclusion, the use of the mixed cerium-manganese oxide system allows excellent performance to be obtained in the preferential oxidation reaction of CO due, essentially, to: (1) a higher reducibility/reactivity of the ceria surface oxygen; (2) a higher surface area which favours an easier and fast adsorption of the reacting species and a faster desorption of the CO2 produced, due also to the modification of the surface adsorption sites. The strong interaction of the mixed oxide with Ru in the monometallic Ru/CeO2-MnOx and the effective synergism between Ru and Pd in the Ru–Pd bimetallic system allows the design of proper catalysts for the specific use of H2 purification in fuel cells working at low temperature (PEM and AFC). In particular, the Ru/CeO2-MnOx catalyst appears the most suitable for PEM fuel cells (operating temperature range of 80–120 °C) while the Ru–Pd/CeO2-MnOx system can be considered best for the AFC fuel cells (operating temperature range of 100–140 °C). It is interesting to note that the catalytic performances of these catalysts were comparable or even better, in terms especially of CO2 selectivity, with respect to ceria and ceria-manganese oxide-based catalysts reported in the literature for CO-PROX (see Table 2) [12,78,79,80,81,82], even though it must stressed that a realistic comparison is very difficult due to the different operative conditions of the various works. As displayed in Figure 7, the Ru/CeO2-MnOx and Ru-Pd/CeO2-MnOx catalysts were quite stable after 14 h of streaming both at 100 °C and 120 °C, whereas the monometallic Pd sample began to deactivate at 120 °C after 8 h. The higher selectivity to CO2 found on the Ru–Pd system, which reduces the undesired H2 consumption, represents a promising result of this research, being one of the key aims of the design of CO-PROX catalysts.

4. Materials and Methods

4.1. Catalyst Preparation

The bare cerium oxide support was synthesized upon precipitation with KOH (1 M) (Fluka, Buchs, Switzerland) from a water solution of Ce(NO3)3·6H2O (Fluka, Buchs, Switzerland), subsequent filtration, washing with water to ensure the removal of nitrates, and final calcination of the obtained solid at 450 °C in air for 4 h. Mixed oxides (CeO2-5wt%Fe2O3, CeO2-5wt%MnOx and CeO2-5wt%CuO) were obtained by co-precipitation with KOH following the same procedure used for the bare CeO2, adding together with the solution of Ce(NO3)3·6H2O the stoichiometric amount of Fe(NO3)3∙9H2O (Fluka, Buchs, Switzerland), Mn(NO3)2∙4H2O (Fluka, Buchs, Switzerland) or Cu(NO3)2·6H2O (Riedel-de Haën, Seelze, Germany).
The preparation of Ru/CeO2 and Ru/CeO2-mixed oxide catalysts (1 wt % Ru) was achieved by incipient wetness impregnation of the supports with an aqueous solution of the ruthenium precursor (Ru(NO)(NO3)3) (Alfa Aesar, Haverhill, MA, USA). In particular, the stoichiometric amount of Ru(NO)(NO3)3 was added dropwise to the support, to fill the pores. The slurry then obtained was placed in an oven at 110 °C to evaporate the excess of solvent. This process was repeated until addition of the required amount of Ru(NO)(NO3)3. Finally, the sample was dried overnight at 110 °C.
The same procedure was adopted for Pd (1 wt % Pd), Ru-Pd (0.5 wt % Ru, 0.5 wt % Pd) and Pt (1 wt % Pt) catalysts using PdCl2 (Sigma-Aldrich, Buchs, Switzerland) and/or H2PtCl6·6H2O (Alfa Aesar, Haverhill, MA, USA) as metal salt precursors for palladium and platinum, respectively. In the case of bimetallic samples, the metal precursors were added contemporaneously on the CeO2-MnOx support.

4.2. Catalytic Performance Test

Catalytic activity runs were executed in the gas phase at atmospheric pressure in a continuous flow mode, using a reactor loaded with the catalyst (0.05 g, 80–140 mesh) and 0.45 g of an inert glass powder. Catalysts were pre-reduced in H2 at 350 °C. The gas mixture (80 mL/min) was CO/O2/He/H2 (1/1/10/88 vol. %). A gas hour space velocity of 3.92 × 10−2 molCO h−1 gcat−1 was chosen. The effluent gases were analyzed online with gas chromatography (Trace GC, Thermo Finnigan, Waltham, MA, USA) with a Carboxen 1000 packed column and TCD detector.
CO and O2 conversions were estimated from the ratio of the consumed to the initial amount of each gas, whereas selectivity was determined in terms of ratio of O2 used for the CO oxidation and the whole O2 consumed, according to the subsequent formulas:
CO conversion (%) = ([CO2]out/[CO]in) × 100
O2 conversion (%) = (([O2]in − [O2]out)/[O2]in) × 100
Selectivity (%) = (0.5 × [CO2]out/([O2]in − [O2]out)) × 100
CO2 yield (%) = (Selectivity * CO conversion)/100

4.3. Catalysts’ Characterization

H2-TPR was carried out heating 0.05 g of the sample (dried in a oven at 110 °C) at 10 °C min−1 in a home-made flow apparatus with a TCD detector using 5 vol. % H2 in Ar [10]. The system employed an oxygen adsorbent to purify the reducing mixture and an acetone trap (−80 °C) to block the water and other gases released during TPR.
X-ray photoelectron spectra (XPS) of the powder samples, compressed on indium foil were measured with a PHI 5600 Multi Technique System (Chanhassen, MN, USA) (base pressure of the main chamber 3 × 10−8 Pa) [83,84]. Samples were excited with the Al-Kα X-ray radiation using a pass energy of 5.85 eV. The instrumental energy resolution was ≤0.5 eV. XPS peak intensities were obtained after a Shirley background removal. Spectra calibration was achieved by fixing the main C 1s peak at 285.0 eV. Structures due to the Al-Kα X-ray satellites were subtracted prior to data processing. The atomic concentration analysis was performed by taking into account the relevant atomic sensitivity factors. The fittings of the C 1s and O 1s XP spectra were carried out using Gaussian envelopes after subtraction of the background until there was the highest possible correlation between the experimental spectrum and the theoretical profile. The residual or agreement factor R, defined by R = [Σ(Fobs − Fcalc)2/Σ(Fobs)2]1/2, after minimization of the function Σ(Fobs − Fcalc)2, converged to the value of 0.02. The catalysts for XPS measurements were introduced in the XPS antechamber under vacuum as soon as they were reduced in H2 at 350 °C.
Diffuse reflectance infrared (IR) spectra were recorded in the range 4000–600 cm−1 with a Perkin-Elmer FT-IR System 2000 (Perkin-Elmer, Waltham, MA, USA) using the specific set-up and mirrors for the diffuse reflectance measurements, KBr being employed to obtain the background spectrum.
XRD analysis was performed with a Bruker AXSD5005 (Bruker, Karlsruhe, Germany) X-ray diffractometer using a Cu Kα radiation. Peaks of crystalline phases were compared with those of standard compounds reported in the JCPDS Data File (Bruker, Diffrac. Suite™ Software package, Karlsruhe, Germany). Before the measurements, the well-grounded samples were placed in the powder sample holder. The analysis was made in locked couple mode.
Surface area determination was achieved with a Sorptomatic series 1990 (Thermo Quest, Milano, Italy) adopting the BET N2 adsorption method. All samples were previously outgassed (10−3 Torr) at 120 °C.

5. Conclusions

Different CeO2-mixed oxides were synthesized by the co-precipitation method and ruthenium was subsequently added by incipient wetness impregnation. Among monometallic samples, the Ru/CeO2-MnOx catalyst showed the highest activity in the CO-PROX reaction at 100 °C. The performance of the bimetallic Ru–Pd system on the ceria-manganese support was successively studied. The bimetallic sample exhibited the highest CO2 yield at 120 °C. On the basis of characterization data, a one-step Langmuir–Hinshelwood/Mars–van Krevelen mechanism was proposed. The high mobility of ceria surface oxygens was enhanced by the simultaneous presence of manganese oxide and ruthenium. The increased reducibility/reactivity of CeO2 oxygen was further promoted by the occurrence of a strong interaction between ruthenium and palladium, resulting in an increased CO-PROX activity of the Ru–Pd/CeO2-MnOx catalyst.

Supplementary Materials

The following are available online at, Figures S1: H2-TPR profiles with peaks deconvolution for Ru/CeO2-MnOx (A) and Ru-Pd/CeO2-MnOx (B) samples; Table S1. H2-TPR quantification for the investigated catalysts; Figure S2. Drift spectra of bare CeO2; Figure S3. Al Kα excited XPS of the 1% Ru/CeO2 in the Ru 3d – C 1s energy region. The peak at 281.3 eV is due to the Ru 3d5/2 state, the peak at 285.0 eV is due both to the adventious carbon and Ru 3d3/2 state; Figure S4. Al Kα excited XPS of the Ru/CeO2 in the Ce 3d energy region; Figure S5A. Al Kα excited XPS of the Ru/CeO2 in the Ru 3d – C 1s energy region; the black line refers to the experimental profile; the green line refers to the background; the peaks at 281.3 and 285.4 eV (blue line) represent the Ru 3d5/2,3/2 spin-orbit components, the peak at 285.0 eV (cyan line) refers to the adventitious carbon; the red line, superimposed to the experimental profile, refers to the sum of the Gaussian components; Figure S5B. Al Kα excited XPS of the Ru/CeO2 in the O 1s energy region. The black line refers to the experimental profile; the green line refers to the background; the cyan line refers to the 528.7 eV peak; the blue line refers to the 530.6 eV peak; the red line, superimposed to the experimental profile, refers to the sum of the Gaussian components; Figure S6. XPS survey spectrum of Ru/CeO2.

Author Contributions

R.F. planned and performed the catalytic experiments and H2-TPR, DRIFT and N2-adsorption-desorption measurements, A.G. and L.S. performed and discussed the XPS analysis, S.S. conceived the idea of writing the paper, supervised the work and edited the article.


The authors would like to acknowledge the research group of G.G. Condorelli (University of Catania) for the XRD measurements.

Conflicts of Interest

The authors declare no conflict of interest.


  1. Kim, D.J.; Jo, M.J.; Nam, S.Y. A review of polymer-nanocomposite electrolyte membranes for fuel cell application. J. Ind. Eng. Chem. 2015, 21, 36–52. [Google Scholar] [CrossRef]
  2. O’Connel, M.; Kolb, G.; Schelhaas, K.; Schuerer, J.; Tiemann, D.; Ziogas, A.; Hessel, V. The development and evaluation of microstructured reactors for the water gas shift and preferential oxidation reactions in the 5 kW range. Int. J. Hydrog. Energy 2010, 35, 2317–2327. [Google Scholar] [CrossRef]
  3. Park, E.D.; Lee, D.; Lee, H.C. Recent progress in selective CO removal in a H2-rich stream. Catal. Today 2009, 139, 280–290. [Google Scholar] [CrossRef]
  4. Tosti, S. Overview of Pd-based membranes for producing pure hydrogen and state of art at ENEA laboratories. Int. J. Hydrog. Energy 2010, 35, 12650–12659. [Google Scholar] [CrossRef]
  5. Liu, K.; Wang, A.; Zhang, T. Recent Advances in Preferential Oxidation of CO Reaction over Platinum Group Metal Catalysts. ACS Catal. 2012, 2, 1165–1178. [Google Scholar] [CrossRef]
  6. Fiorenza, R.; Crisafulli, C.; Condorelli, G.G.; Lupo, F.; Scirè, S. Au–Ag/CeO2 and Au–Cu/CeO2 Catalysts for Volatile Organic Compounds Oxidation and CO Preferential Oxidation. Catal. Lett. 2015, 145, 1691–1702. [Google Scholar] [CrossRef]
  7. Nguyen, T.S.; Morfin, F.; Aouine, M.; Bosselet, F.; Rousset, J.L.; Piccolo, L. Trends in the CO oxidation and PROX performances of the platinum-group metals supported on ceria. Catal. Today 2015, 253, 106–114. [Google Scholar] [CrossRef]
  8. Mariño, F.; Descorme, C.; Duprez, D. Noble metal catalysts for the preferential oxidation of carbon monoxide in the presence of hydrogen (PROX). Appl. Catal. B Environ. 2004, 54, 59–66. [Google Scholar] [CrossRef]
  9. Kim, Y.H.; Park, E.D.; Lee, H.C.; Lee, D.; Lee, K.H. Preferential CO oxidation over supported noble metal catalysts. Catal. Today 2009, 146, 253–259. [Google Scholar] [CrossRef]
  10. Sciré, S.; Fiorenza, R.; Gulino, A.; Cristaldi, A.; Riccobene, P.M. Selective oxidation of CO in H2-rich stream over ZSM5 zeolites supported Ru catalysts: An investigation on the role of the support and the Ru particle size. Appl. Catal. A Gen. 2016, 520, 82–91. [Google Scholar] [CrossRef]
  11. Di, L.; Wu, G.; Dai, W.; Guan, N.; Li, L. Ru/TiO2 for the preferential oxidation of CO in H2-rich stream: Effects of catalyst pre-treatments and reconstruction of Ru sites. Fuel 2015, 143, 318–326. [Google Scholar] [CrossRef]
  12. Fiorenza, R.; Crisafulli, C.; Scirè, S. H2 purification through preferential oxidation of CO over ceria supported bimetallic Au-based catalysts. Int. J. Hydrog. Energy 2016, 41, 19390–19398. [Google Scholar] [CrossRef]
  13. Scirè, S.; Crisafulli, C.; Riccobene, P.M.; Patanè, G.; Pistone, A. Selective oxidation of CO in H2-rich stream over Au/CeO2 and Cu/CeO2 catalysts: An insight on the effect of preparation method and catalyst pretreatment. Appl. Catal. A Gen. 2012, 417–418, 66–75. [Google Scholar] [CrossRef]
  14. Ilieva, L.; Petrova, P.; Pantaleo, G.; Zanella, R.; Sobczak, J.W.W.; Lisowski, W.; Kaszkur, Z.; Munteanu, G.; Yordanova, I.; Liotta, L.F.; et al. Alumina supported Au/Y-doped ceria catalysts for pure hydrogen production via PROX. Int. J. Hydrog. Energy 2018, in press. [Google Scholar] [CrossRef]
  15. Chen, H.; Liu, Y.; Yang, F.; Wei, M.; Zhao, X.; Ning, Y.; Liu, Q.; Zhang, Y.; Fu, Q.; Bao, X. Active Phase of FeOx/Pt Catalysts in Low-Temperature CO Oxidation and Preferential Oxidation of CO Reaction. J. Phys. Chem. C 2017, 121, 10398–10405. [Google Scholar] [CrossRef]
  16. Fukuoka, A.; Kimura, J.; Oshio, T.; Sakamoto, Y.; Ichikawa, M. Preferential Oxidation of Carbon Monoxide Catalyzed by Platinum Nanoparticles in Mesoporous Silica. J. Am. Chem. Soc. 2007, 129, 10120–10125. [Google Scholar] [CrossRef] [PubMed]
  17. Luengnaruemitchai, A.; Srihamat, K.; Pojanavaraphan, C.; Wanchanthuek, R. Activity of Au/Fe2O3–TiO2 catalyst for preferential CO oxidation. Int. J. Hydrog. Energy 2015, 40, 13443–13445. [Google Scholar] [CrossRef]
  18. Ilieva, L.; Petrova, P.; Pantaleo, G.; Zanella, R.; Liotta, L.F.; Georgiev, V.; Boghosian, S.; Kaszkur, Z.; Sobczak, J.W.; Lisowski, W.; et al. Gold catalysts supported on Y-modified ceria for CO-free hydrogen production via PROX. Appl. Catal. B. Environ. 2016, 188, 154–168. [Google Scholar] [CrossRef]
  19. Martínez-Arias, A.; Gamarra, D.; Hungría, A.B.; Fernández-García, M.; Munuera, G.; Hornés, A.; Bera, P.; Conesa, J.C.; Cámara, A.L. Characterization of Active Sites/Entities and Redox/Catalytic Correlations in Copper-Ceria-Based Catalysts for Preferential Oxidation of CO in H2-Rich Streams. Catalysts 2013, 3, 378–400. [Google Scholar] [CrossRef]
  20. Konsolakis, M. The role of Copper-Ceria interactions in catalysis science: Recent theoretical and experimental advances. Appl. Catal. B. Environ. 2016, 198, 49–66. [Google Scholar] [CrossRef]
  21. Liu, X.; Lu, J.; Qian, K.; Huang, W.; Luo, M. A comparative study of formaldehyde and carbon monoxide complete oxidation on MnOx–CeO2catalyst. J. Rare Earths 2009, 27, 418–424. [Google Scholar] [CrossRef]
  22. Delimaris, D.; Ioannides, T. VOC oxidation over MnOx–CeO2 catalysts prepared by a combustion method. Appl. Catal. B Environ. 2008, 84, 303–312. [Google Scholar] [CrossRef]
  23. Xingyi, W.; Qian, K.; Dao, L. Catalytic combustion of chlorobenzene over MnOx–CeO2 mixed oxide catalysts. Appl. Catal. B Environ. 2009, 86, 166–175. [Google Scholar] [CrossRef]
  24. Wang, Z.; Shen, G.; Li, J.; Liu, H.; Wang, Q.; Chen, Y. Catalytic removal of benzene over CeO2–MnOx composite oxides prepared by hydrothermal method. Appl. Catal. B Environ. 2013, 138, 253–259. [Google Scholar] [CrossRef]
  25. Mishra, A.; Prasad, R. A Review on Preferential Oxidation of Carbon Monoxide in Hydrogen Rich Gases. Bull. Chem. React. Eng. Catal. 2011, 6, 1–14. [Google Scholar] [CrossRef]
  26. Liao, X.; Chu, W.; Dai, X.; Pitchon, V. Bimetallic Au–Cu supported on ceria for PROX reaction: Effects of Cu/Au atomic ratios and thermal pretreatments. Appl. Catal. B Environ. 2013, 142–143, 25–37. [Google Scholar] [CrossRef]
  27. Trovarelli, A.; Fornasiero, P. Catalysis by Ceria and Related Materials, 2nd ed.; Graham, J.H., Ed.; Catalytic Science Series; Imperial College Press: London, UK, 2002. [Google Scholar]
  28. Cecilia, J.A.; Arango-Díaz, A.; Franco, F.; Jiménez-Jiménez, J.; Storaro, L.; Moretti, E.; Rodríguez-Castellón, E. CuO-CeO2 supported on montmorillonite-derived porous clay heterostructures (PCH) for preferential CO oxidation in H2-rich stream. Catal. Today 2015, 253, 126–136. [Google Scholar] [CrossRef]
  29. Kahlich, M.J.; Gasteiger, H.A.; Behm, R.J. Kinetics of the Selective Low-Temperature Oxidation of CO in H2-Rich Gas over Au/α-Fe2O3. J. Catal. 1999, 182, 430–440. [Google Scholar] [CrossRef]
  30. Schubert, M.M.; Kahlich, M.J.; Gasteiger, H.A.; Behm, R.J. Correlation between CO surface coverage and selectivity/kinetics for the preferential CO oxidation over Pt/γ-Al2O3 and Au/α-Fe2O3: An in-situ DRIFTS study. J. Power Sources 1999, 84, 175–182. [Google Scholar] [CrossRef]
  31. Crisafulli, C.; Scirè, S.; Maggiore, R.; Minicò, S.; Galvagno, S. CO2 reforming of methane over Ni–Ru and Ni–Pd bimetallic catalysts. Catal. Lett. 1999, 59, 21–26. [Google Scholar] [CrossRef]
  32. Tang, X.; Zhang, B.; Li, Y.; Xu, Y.; Xin, Q.; Shen, W. Carbon monoxide oxidation over CuO/CeO2 catalysts. Catal. Today 2004, 93, 191–198. [Google Scholar] [CrossRef]
  33. Wang, L.; Chen, J.; Patel, A.; Rudolph, V.; Zhu, Z. Catalytic performance of Ru nanoparticles supported on different mesoporous silicas for preferential oxidation of CO in H2-rich atmosphere. Appl. Catal. A Gen. 2012, 447–448, 200–209. [Google Scholar] [CrossRef]
  34. Ilieva, L.; Pantaleo, G.; Ivanova, I.; Maximova, A.; Zanella, R.; Kaszkur, Z.; Venezia, A.M.; Andreeva, D. Preferential oxidation of CO in H2 rich stream (PROX) over gold catalysts supported on doped ceria: Effect of preparation method and nature of dopant. Catal. Today 2010, 158, 44–55. [Google Scholar] [CrossRef]
  35. Tu, Y.B.; Luo, J.Y.; Meng, M.; Wang, G.; He, J.J. Ultrasonic-assisted synthesis of highly active catalyst Au/MnOx–CeO2 used for the preferential oxidation of CO in H2-rich stream. Int. J. Hydrog. Energy 2009, 34, 3743–3754. [Google Scholar] [CrossRef]
  36. Stobe, E.R.; de Boer, B.A.; Geus, J.W. The reduction and oxidation behaviour of manganese oxides. Catal. Today 1999, 47, 161–167. [Google Scholar] [CrossRef]
  37. Fiorenza, R.; Scirè, S.; Venezia, A.M. Carbon supported bimetallic Ru-Co catalysts for H2 production through NaBH4 and NH3BH3 hydrolysis. Int. J. Energy Res. 2018, 42, 1183–1195. [Google Scholar] [CrossRef]
  38. Zhu, H.; Qin, Z.; Shan, W.; Shen, W.; Wang, J. Pd/CeO2–TiO2 catalyst for CO oxidation at low temperature: A TPR study with H2 and CO as reducing agents. J. Catal. 2004, 225, 267–277. [Google Scholar] [CrossRef]
  39. Jen, H.W.; Graham, G.W.; Chun, W.; McCabe, R.W.; Cuif, J.P.; Deutsch, S.E.; Touret, O. Characterization of model automotive exhaust catalysts: Pd on ceria and ceria–zirconia supports. Catal. Today 1999, 50, 309–328. [Google Scholar] [CrossRef]
  40. Tabakova, T.; Boccuzzi, F.; Manzoli, M.; Sobczak, J.W.; Idakiev, V.; Andreeva, A. A comparative study of nanosized IB/ceria catalysts for low-temperature water-gas shift reaction. Appl. Catal. A Gen. 2006, 298, 127–143. [Google Scholar] [CrossRef]
  41. Machida, M.; Uto, M.; Kurogi, D.; Kijima, T. MnOx−CeO2 Binary Oxides for Catalytic NOx Sorption at Low Temperatures. Sorptive Removal of NOx. Chem. Mater. 2000, 12, 3158–3164. [Google Scholar] [CrossRef]
  42. Dollimore, D.; Heal, G.R. An improved method for the calculation of pore size distribution from adsorption data. J. Appl. Chem. 1964, 14, 109–114. [Google Scholar] [CrossRef]
  43. Scirè, S.; Riccobene, P.M.; Crisafulli, C. Ceria supported group IB metal catalysts for the combustion of volatile organic compounds and the preferential oxidation of CO. Appl. Catal. B Environ. 2010, 101, 109–117. [Google Scholar] [CrossRef]
  44. Song, X.; Jiang, N.; Li, Y.; Xu, D.; Qiu, G. Synthesis and Characterization of Y-Doped Mesoporous CeO2 Using A Chemical Precipitation Method. J. Rare Earths 2007, 25, 428–433. [Google Scholar]
  45. Natile, M.M.; Boccaletti, G.; Glisenti, A. Properties and Reactivity of Nanostructured CeO2 Powders:  Comparison among Two Synthesis Procedures. Chem. Mater. 2005, 17, 6272–6286. [Google Scholar] [CrossRef]
  46. Rosynek, M.P.; Magnuson, D.T. Infrared study of carbon dioxide adsorption on lanthanum sesquioxide and trihydroxide. J. Catal. 1977, 48, 417–421. [Google Scholar] [CrossRef]
  47. Davydov, A. Molecular Spectroscopy of Oxide Catalyst Surfaces; Sheppard, N.T., Ed.; John Wiley & Sons Ltd.: Chichester, UK, 2003. [Google Scholar]
  48. Li, C.; Sakata, Y.; Arai, T.; Domen, K.; Maruya, K.I.; Onishi, T. Carbon monoxide and carbon dioxide adsorption on cerium oxide studied by Fourier-transform infrared spectroscopy. Part 1.—Formation of carbonate species on dehydroxylated CeO2, at room temperature. J. Chem. Soc. Faraday Trans. 1989, 85, 929–943. [Google Scholar] [CrossRef]
  49. Vayssilov, G.N.; Mihaylov, M.; Petkov, P.S.; Hadjiivanov, K.I.; Neyman, K.M. Reassignment of the Vibrational Spectra of Carbonates, Formates, and Related Surface Species on Ceria: A Combined Density Functional and Infrared Spectroscopy Investigation. J. Phys. Chem. C 2011, 115, 23435–23454. [Google Scholar] [CrossRef]
  50. Gulino, A.; Mineo, P.; Scamporrino, E.; Vitalini, D.; Fragalà, I. Spectroscopic and Microscopic Characterization and Behavior of an Optical pH Meter Based on a Functional Hybrid Monolayer Molecular System: Porphyrin Molecules Covalently Assembled on a Molecularly Engineered Silica Surface. Chem. Mater. 2006, 18, 2404–2410. [Google Scholar] [CrossRef]
  51. Gulino, A.; Condorelli, G.G.; Mineo, P.; Fragalà, I. An x-ray photoelectron spectra and atomic force microscopy characterization of silica substrates engineered with a covalently assembled siloxane monolayer. Nanotechnology 2005, 16, 2170. [Google Scholar] [CrossRef] [PubMed]
  52. Gulino, A.; Gupta, T.; Mineo, P.; van der Boom, M.E. Selective NOx optical sensing with surface-confined osmium polypyridyl complexes. Chem. Commun. 2007, 46, 4878–4880. [Google Scholar] [CrossRef]
  53. Zawadzki, M.; Okal, J. Synthesis and structure characterization of Ru nanoparticles stabilized by PVP or γ-Al2O3. J. Mater. Res. Bull. 2008, 43, 3111–3121. [Google Scholar] [CrossRef]
  54. Gulino, A.; Egdell, R.G.; Fragalà, I. Low-temperature stabilisation of tetragonal zirconia by antimony. J. Mater. Chem. 1996, 11, 1805–1809. [Google Scholar] [CrossRef]
  55. Motiei, L.; Lahav, M.; Gulino, A.; Iron, M.A.; van der Boom, M.E. Electrochemical Characteristics of a Self-Propagating Molecular-Based Assembly. J. Phys. Chem. B 2010, 114, 14283–14286. [Google Scholar] [CrossRef] [PubMed]
  56. Folkesson, B. ESCA studies on the charge distribution in some dinitrogen complexes of rhenium, iridium, ruthenium, and osmium. Acta Chem. Scand. 1973, 27, 287–302. [Google Scholar] [CrossRef]
  57. Biesinger, M.C.; Payne, B.P.; Grosvenor, A.P.; Lau, L.W.M.; Gerson, A.R.; Smart, R.S.C. Resolving surface chemical states in XPS analysis of first row transition metals, oxides and hydroxides: Cr, Mn, Fe, Co and Ni. Appl. Surf. Sci. 2011, 257, 2717–2730. [Google Scholar] [CrossRef]
  58. Militello, M.C.; Simko, S.J. Elemental Palladium by XPS. Surf. Sci. Spectra 1994, 3, 387–394. [Google Scholar] [CrossRef]
  59. Powell, C.J. Recommended Auger parameters for 42 elemental solids. J. Electron. Spectrosc. Relat. Phenom. 2012, 185, 1–3. [Google Scholar] [CrossRef]
  60. Pulm, H.; Hohlneicher, G.; Freund, H.-J.J. Charge distribution in some ternary vintl phases as studied by v-ray photoelectron spectroscopy. Less Common Met. 1986, 115, 127–143. [Google Scholar] [CrossRef]
  61. Ji, P.; Zhang, J.; Chen, F.; Anpo, M. Ordered Mesoporous CeO2 Synthesized by Nanocasting from Cubic Ia3d Mesoporous MCM-48 Silica: Formation, Characterization and Photocatalytic Activity. J. Phys. Chem. C 2008, 112, 17809–17813. [Google Scholar] [CrossRef]
  62. Gulino, A.; Dapporto, P.; Rossi, P.; Fragalà, I. Synthesis and Characterization of Liquid MOCVD Precursors for Thin Films of Cadmium Oxide. Chem. Mater. 2002, 14, 4955–4962. [Google Scholar]
  63. Chen, H.; Sayari, A.; Adnot, A.; Larachi, F. Composition–activity effects of Mn–Ce–O composites on phenol catalytic wet oxidation. Appl. Catal. B Environ. 2001, 32, 195–204. [Google Scholar] [CrossRef]
  64. Tang, X.; Li, Y.; Huang, X.; Xu, Y.; Zhu, H.; Wang, J.; Shen, W. MnOx-CeO2 mixed oxide catalysts for complete oxidation of formaldehyde: Effect of preparation method and calcination temperature. Appl. Catal. B Environ. 2006, 62, 265–273. [Google Scholar] [CrossRef]
  65. Solsona, B.; Hutchigns, G.J.; García, T.; Taylor, S.H. Improvement of the catalytic performance of CuMnOx catalysts for CO oxidation by the addition of Au. New J. Chem. 2004, 28, 708–711. [Google Scholar] [CrossRef]
  66. Jones, C.; Cole, K.J.; Taylor, S.H.; Crudace, M.J.; Hutchigns, G.J. Copper manganese oxide catalysts for ambient temperature carbon monoxide oxidation: Effect of calcination on activity. J. Mol. Catal. A Chem. 2009, 305, 121–124. [Google Scholar] [CrossRef]
  67. Arena, F.; Trunfio, G.; Negro, J.; Fazio, B.; Spadaro, L. Basic Evidence of the Molecular Dispersion of MnCeOx Catalysts Synthesized via a Novel “Redox-Precipitation” Route. Chem. Mater. 2007, 19, 2269–2276. [Google Scholar] [CrossRef]
  68. Laguna, O.H.; Centeno, M.A.; Arzamendi, G.; Gandía, L.M.; Romero-Sarria, F.; Odriozola, J.A. Iron-modified ceria and Au/ceria catalysts for Total and Preferential Oxidation of CO (TOX and PROX). Catal. Today 2010, 157, 155–159. [Google Scholar] [CrossRef]
  69. Scirè, S.; Minicò, S.; Crisafulli, C.; Satriano, C.; Pistone, A. Catalytic combustion of volatile organic compounds on gold/cerium oxide catalysts. Appl. Catal. B Environ. 2003, 40, 43–49. [Google Scholar] [CrossRef]
  70. Doornkamp, C.; Ponec, V. The universal character of the Mars and Van Krevelen mechanism. J. Mol. Catal. A Chem. 2000, 162, 19–32. [Google Scholar] [CrossRef]
  71. Rosso, I.; Antonini, M.; Galletti, C.; Saracco, G.; Specchia, V. Selective CO-oxidation over Ru-based catalysts in H2-rich gas for fuel cell applications. Top. Catal. 2004, 30, 475–480. [Google Scholar] [CrossRef]
  72. Xu, J.; Xu, X.C.; Ouyang, L.; Yang, X.-Y.; Mao, W.; Su, J.; Han, Y.-F. Mechanistic study of preferential CO oxidation on a Pt/NaY zeolite catalyst. J. Catal. 2012, 287, 114–123. [Google Scholar] [CrossRef]
  73. Chin, S.Y.; Alexeev, O.S.; Amiridis, M.D. Preferential oxidation of CO under excess H2 conditions over Ru catalysts. Appl. Catal. A Gen. 2005, 286, 157–166. [Google Scholar] [CrossRef]
  74. Barbato, P.S.; Colussi, S.; Di Benedetto, A.; Landi, G.; Lisi, L.; Llorca, J.; Trovarelli, A. CO preferential oxidation under H2-rich streams on copper oxide supported on Fe promoted CeO2. Appl. Catal. A Gen. 2015, 506, 268–277. [Google Scholar] [CrossRef]
  75. Gao, Z.; Liu, Y.; He, Q.; Ma, H.; Li, Z.M. Preferential oxidation of CO and its subsequent methanation in H2-rich gas over CuO-NiO/CeO2 catalysts. Int. J. Hydrog. Energy 2016, 41, 4646–4659. [Google Scholar] [CrossRef]
  76. Kim, Y.H.; Park, E.D.; Lee, H.C.; Lee, D. Selective CO removal in a H2-rich stream over supported Ru catalysts for the polymer electrolyte membrane fuel cell (PEMFC). Appl. Catal. A Gen. 2009, 366, 363–369. [Google Scholar] [CrossRef]
  77. Alayoglu, S.; Nilekar, A.U.; Mavrikakis, M.; Eichhorn, B. Ru–Pt core–shell nanoparticles for preferential oxidation of carbon monoxide in hydrogen. Nat. Mater. 2008, 7, 333–338. [Google Scholar] [CrossRef] [PubMed]
  78. Pozdnyakova, O.; Teschner, D.; Wootsch, A.; Kröhnert, J.; Steinhauer, B.; Sauer, H.; Toth, L.; Jentoft, F.C.; Knop-Gericke, A.; Paál, Z.; et al. Preferential CO oxidation in hydrogen (PROX) on ceria-supported catalysts, part I: Oxidation state and surface species on Pt/CeO2 under reaction conditions. J. Catal. 2006, 237, 1–16. [Google Scholar] [CrossRef]
  79. Martínez, L.M.; Laguna, O.H.; López-Cartes, C.; Centeno, M.A. Synthesis and characterization of Rh/MnO2-CeO2/Al2O3 catalysts for CO-PrOx reaction. Mol. Catal. 2017, 440, 9–18. [Google Scholar] [CrossRef]
  80. Zhao, Z.; Bao, T.; Li, Y.; Min, X.; Zhao, D.; Muhammad, T. The supported CeO2/Co3O4–MnO2/CeO2 catalyst on activated carbon prepared by a successive-loading approach with superior catalytic activity and selectivity for CO preferential oxidation in H2-rich stream. Catal. Comm. 2014, 48, 24–28. [Google Scholar] [CrossRef]
  81. Chang, L.H.; Sasirekha, N.; Chen, Y.W.; Wang, W.J. Preferential Oxidation of CO in H2 Stream over Au/MnO2−CeO2 Catalysts. Ind. Eng. Chem. Res. 2006, 45, 4927–4935. [Google Scholar] [CrossRef]
  82. Cecilia, J.A.; Arango-Diaz, A.; Marrero-Jerez, J.; Nunez, P.; Moretti, E.; Storaro, L.; Rodiguez-Castellon, E. Catalytic Behaviour of CuO-CeO2 Systems Prepared by Different Synthetic Methodologies in the CO-PROX Reaction under CO2-H2O Feed Stream. Catalysts 2017, 7, 160. [Google Scholar] [CrossRef]
  83. Briggs, D.; Grant, J.T. Surface Analysis by Auger and X-Ray Photoelectron Spectroscopy; IM Publications: Chichester, UK; Surface Spectra Ltd.: Manchester, UK, 2003. [Google Scholar]
  84. Gulino, A. Structural and electronic characterization of self-assembled molecular nanoarchitectures by X-ray photoelectron spectroscopy. Anal. Bioanal. Chem. 2013, 405, 1479–1495. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Preferential oxidation (PROX) activity data over monometallic Ru catalysts supported on CeO2-based mixed oxides. (a) CO conversion, (b) O2 conversion, (c) selectivity towards CO oxidation, (d) yield to CO2.
Figure 1. Preferential oxidation (PROX) activity data over monometallic Ru catalysts supported on CeO2-based mixed oxides. (a) CO conversion, (b) O2 conversion, (c) selectivity towards CO oxidation, (d) yield to CO2.
Catalysts 08 00203 g001
Figure 2. PROX activity data over Ru/CeO2-MnOx, Pd/CeO2-MnOx, Pt/CeO2-MnOx and Ru–Pd/CeO2-MnOx catalysts. (a) CO conversion, (b) O2 conversion, (c) selectivity towards CO oxidation, (d) yield to CO2.
Figure 2. PROX activity data over Ru/CeO2-MnOx, Pd/CeO2-MnOx, Pt/CeO2-MnOx and Ru–Pd/CeO2-MnOx catalysts. (a) CO conversion, (b) O2 conversion, (c) selectivity towards CO oxidation, (d) yield to CO2.
Catalysts 08 00203 g002
Figure 3. H2-temperature programmed reduction (H2-TPR) profiles of investigated catalysts.
Figure 3. H2-temperature programmed reduction (H2-TPR) profiles of investigated catalysts.
Catalysts 08 00203 g003
Figure 4. X-ray diffraction (XRD) profiles of investigated catalysts.
Figure 4. X-ray diffraction (XRD) profiles of investigated catalysts.
Catalysts 08 00203 g004
Figure 5. Diffuse reflectance infrared Fourier transform (DRIFT) spectra of catalysts: (a) CeO2-based catalysts, (b) zoom of the carbonate zone.
Figure 5. Diffuse reflectance infrared Fourier transform (DRIFT) spectra of catalysts: (a) CeO2-based catalysts, (b) zoom of the carbonate zone.
Catalysts 08 00203 g005
Figure 6. X-ray photoelectron spectroscopy (XPS) of catalysts: (a) Ru/CeO2 in the Ru 3p energy region, (b) Ru/CeO2-MnOx in the Mn 2p energy region, (c) Ru–Pd/CeO2-MnOx in the Pd 3d energy region.
Figure 6. X-ray photoelectron spectroscopy (XPS) of catalysts: (a) Ru/CeO2 in the Ru 3p energy region, (b) Ru/CeO2-MnOx in the Mn 2p energy region, (c) Ru–Pd/CeO2-MnOx in the Pd 3d energy region.
Catalysts 08 00203 g006
Figure 7. Conversion of CO as a function of time on stream at 100 °C (a) and 120 °C (b) over Ru/CeO2-MnOx, Ru/CeO2-MnOx and Ru/CeO2-MnOx catalysts.
Figure 7. Conversion of CO as a function of time on stream at 100 °C (a) and 120 °C (b) over Ru/CeO2-MnOx, Ru/CeO2-MnOx and Ru/CeO2-MnOx catalysts.
Catalysts 08 00203 g007
Table 1. Structural and textural properties of investigated samples.
Table 1. Structural and textural properties of investigated samples.
CatalystsCeO2 Size by XRD (nm) *BET Surface Area (m2/g)Mean Pore Diameter (nm)Pore Volume (cm3/g)
* By Scherrer equation.
Table 2. Comparison of PROX performance of Ru and Ru–Pd supported CeO2-MnOx catalysts in this work and other ceria and ceria-manganese oxide-based catalysts reported in the literature.
Table 2. Comparison of PROX performance of Ru and Ru–Pd supported CeO2-MnOx catalysts in this work and other ceria and ceria-manganese oxide-based catalysts reported in the literature.
CatalystsMetals Loading (wt %)SupportSpace Velocity
Gas Mixture (vol. %)CO Conversion
CO2 Selectivity
molCO h−1 gcat−1
1 CO,
1 O2,
88 H2, rest He
41 (80 °C)
72 (100 °C)
65 (120 °C)
70 (80 °C)
84 (100 °C)
71 (120 °C)
this work
molCO h−1 gcat−1
1 CO,
1 O2,
88 H2, rest He
32 (80 °C)
52 (100 °C)
85 (120 °C)
56 (80 °C)
81 (100 °C)
88 (120 °C)
this work
Pt/CeO21CeO2not reported1 CO,
1 O2,
rest H2
65 (80 °C)
70 (100 °C)
60 (120 °C)
72 (80 °C)
68 (100 °C)
61 (120 °C)
Rh/MnO2-CeO2/Al2O3110 wt %MnO2,
40 wt %CeO2,
50 wt %Al2O3
60,000 cm3 h−1 gcat−11 CO,
1 O2,
50 H2, rest N2
15 (80 °C)
20 (100 °C)
38 (120 °C)
57 (80 °C)
55 (100 °C)
50 (120 °C)
CeO2/Co3O4-MnO2/CeO2-27.5 wt %Co on activated carbon
8:1 Co/Mn and Co/Ce (atom. ratio)
15,000 mL h−1 gcat−11 CO,
1 O2,
50 H2, rest Ar
82 (80 °C)
100 (100 °C)
100 (120 °C)
85 (80 °C)
80 (100 °C)
70 (120 °C)
Au/MnO2-CeO210.5MnO2 0.5CeO2 (atom. ratio)not reported1.33 CO, 1.33 O2, 65.33 H2, rest He90 (80 °C)
88 (100 °C)
86 (120 °C)
50 (80 °C)
47 (100 °C)
45 (120 °C)
CuO/CeO26PMMA as template22,000 h−11.25 CO, 1.25 O2, 50% H2, rest He92 (80 °C)
96 (100 °C)
97 (120 °C)
82 (80 °C)
80 (100 °C)
78 (120 °C)
molCO h−1 gcat−1
1 CO,
1 O2,
88 H2, rest He
90 (80 °C)
76 (100 °C)
50 (120 °C)
73 (80 °C)
44 (100 °C)
30 (120 °C)

© 2018 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (
Back to TopTop