Lucía M. Toscaniab,
M. Genoveva Zimiczc,
Tereza S. Martinsd,
Diego G. Lamasef and
Susana A. Larrondo*ab
aUNIDEF, MINDEF, CONICET, Departamento de Investigaciones en Sólidos, CITEDEF, J. B. de La Salle 4397, 1603 Villa Martelli, Pcia. de Buenos Aires, Argentina. E-mail: slarrondo@citedef.gob.ar
bInstituto de Investigación e Ingeniería Ambiental, UNSAM, Campus Miguelete, 25 de Mayo y Francia, 1650 San Martín, Pcia. de Buenos Aires, Argentina
cInstituto de Física del Sur (IFISUR), Departamento de Física, Universidad Nacional del Sur (UNS), CONICET, Av. Alem 1253, 8000 Bahía Blanca, Pcia. de Buenos Aires, Argentina
dUniversidade Federal de São Paulo – UNIFESP. Departamento de Química, Instituto de Ciências Ambientais, Químicas e Farmacêuticas, Rua São Nicolau 210, 2nd Floor, 09913-030, Diadema, São Paulo, Brazil
eCONICET/Escuela de Ciencia y Tecnología, UNSAM, Campus Miguelete, 25 de Mayo y Francia, 1650 San Martín, Pcia. de Buenos Aires, Argentina
fDepartamento de Física de la Materia Condensada, Gerencia de Investigación y Aplicaciones, Centro Atómico Constituyentes, Comisión Nacional de Energía Atómica, Av. General Paz 1499, 1650 San Martín, Pcia. de Buenos Aires, Argentina
First published on 28th March 2018
In this work we analyze the effect of adding CuO to a NiO/Ce0.9Zr0.1O2 oxide by in situ X-ray absorption near-edge structure XANES technique in Ce L3, Ni K and Cu K absorption edges in terms of sample reducibility and catalytic activity. The oxidation states of Ce, Ni and Cu cations are followed up during temperature programmed reduction (TPR) experiments in diluted hydrogen and during catalytic tests for partial oxidation of methane (POM) reaction. Redox behavior was correlated to conventional fixed bed reactor results. The effect of firing temperature, crystallite size, CeO2–ZrO2 support and the presence of Cu and/or Ni as an active phase is also analyzed. Results showed a beneficial effect of CuO addition in terms of Ce and Ni reduction. A stronger interaction of NiO species with the support was revealed upon analysis of XANES reduction profiles in sample NiO/ZDC in contrast to bimetallic CuO–NiO/ZDC sample. Reduction onset temperature was found to depend on Ni crystallite size, being markedly promoted when samples exhibited low values of crystallite size both in supported and non-supported CuO–NiO species. In situ catalytic experiments for partial oxidation of methane showed a clear interplay between the redox behavior from the Ce in the CeO2–ZrO2 support and the Ni from the active phase. Sample NiO/ZDC exhibited a continuous reduction of Ce cations in CH4:O2 feed flow, carbon formation was detected in X-ray Powder Diffraction (XPD) patterns and Ni re-oxidation was found to take place, clear indications of catalyst deactivation. In contrast, sample CuO–NiO/Ce0.9Zr0.1O2 displayed a slight re-oxidation of Ce and no re-oxidation of Ni altogether with the suppression of carbon formation.
In particular, the development of IT-SOFC anodes is centered in the fabrication of materials with high electronic and ionic conductivity to allow for hydrocarbons to be used as fuels.1 These Mixed Ionic Electronic Conductors (MIECs) provide oxygen ions (O2−) to the reaction sites enabling the oxidation of the fuel to take place all over the surface of the electrode. In addition, anode performance can be further enhanced developing materials with catalytic activity toward fuel decomposition into CO and H2 mixtures that are easily electro-oxidizable into CO2 and H2O.2
CeO2–ZrO2 mixed oxides have been extensively studied due to their redox properties and oxygen storage capacity.3,4 In this regard, the material with composition Ce0.9Zr0.1O2 (‘zirconia-doped ceria’, ZDC) is active as a catalyst for total oxidation of methane (TOM) as well as a support for Ni-based catalysts for partial oxidation of methane (POM).5–8 In fact, material NiO (60 wt%)/Ce0.9Zr0.1O2 has been tested as an IT-SOFC anode, exhibiting an excellent performance due to the presence of cerium in its structure which contributed to the electrode enhanced reducibility and ionic conductivity due to the partial reduction of cerium cation.9,10 Nonetheless, in reducing atmospheres and due the elevated Ni content required to ensure electrical percolation, carbon formation is favored when hydrocarbons are used as fuels. Coke deposition takes place at adjacent Ni sites, which promote the nucleation and growth of carbon filaments blocking the active sites for fuel activation and, eventually, leading to the fracture of the device.8,11 In this sense, Zimicz et al. studied, in sample 60 wt% NiO/40 wt% Ce0.9Zr0.1O2, the evolution of the crystal structure with temperature and operating conditions and monitored the oxidation states of Ce and Ni by in situ X-ray absorption near-edge structure (XANES) and X-ray powder diffraction XPD experiments in reducing atmospheres.8 They reported a complete Ni reduction at temperatures above 650 °C and total conversion of methane to syngas at temperatures higher than 700 °C. Ni was confirmed to be the active center for POM and the ratio of Ce4+/Ce3+ was found to be responsible to deliver oxygen from the lattice to produce COx species. Nonetheless, experiments confirmed the formation of carbon filaments due to the large amount of NiO in the sample.
As a strategy to reduce carbon deposition, Ni-based bimetallic catalysts had been widely studied for hydrocarbon oxidation and reforming reactions.1,12 In particular, Cu–Ni catalysts stand as a promising alternative as they have shown enhanced reducibility and increased coke resistance due to the addition of Cu which is not active for CH4 decomposition.13–15
Cu active phase has been deposited over the traditional Ni/yttria-stabilized zirconia (YSZ) anodes suitable for high-temperature SOFC operation, and carbon formation during direct hydrocarbon utilization was considerably suppressed in Cu-containing materials.13 Afterward, in light of lowering anode operating temperature, CeO2-based supports have been tested in intermediate temperature SOFC conditions altogether with different ratios of Cu:Ni in the active phase.16,17 In particular, Hornés et al. studied the effect of partially substituting Ni by Cu in Ni/CeO2 and Ni/Ce0.9Gd0.1O2−x anodes in redox, catalytic and electro-catalytic performance.18 The authors performed in situ X-ray absorption spectroscopy (XAS) studies with CH4 as a fuel and reported a beneficial effect in the reduction of carbon deposits in Cu-containing samples and a promoting effect of the Gd present in the support in terms of the enhancement of oxygen transport properties in the material that led to an improved CH4 oxidation.
In the past few years, several studies have been conducted in order to understand the redox behavior of all Cu, Ni and Ce cations present in operating conditions, especially for catalytic applications where low metallic loadings and low calcination temperatures are sufficient to guarantee reactant conversion.13–20 Matte et al. studied 20 wt% Cu and 20 wt% Ni/CeO2 nanoparticles in reducing atmospheres by means of XAS and transmission electron microscopy (TEM) techniques and reported a strong interaction between Ni and CeO2 which enhanced Ni reducibility in diluted H2 feed flows.19 De Rogatis et al. studied 5 wt% Cu-5 wt% Ni/Al2O3 for POM applications and reported a beneficial effect of Cu addition to the system in terms of lowering the onset temperature for POM reaction and negligible carbon formation.15
Song et al. studied anodes with Cu, CuNi and Ni supported over Ce0.9Zr0.1O2 and over CeO2 and reported an improved electrochemical performance of CeO2–ZrO2 support when compared to CeO2 support in terms of thermal stability and anode activity.10 Furthermore, the bimetallic sample (40 wt% CuNi/ZDC) exhibited a superior electrochemical performance when compared to the monometallic one. However, no redox or catalytic tests were performed to analyze the effect of the species present in the anode in its effect in the electrode performance. In this sense, in a previous work, the authors studied the effect of the partial replacement of NiO for CuO in NiO (60 wt%)/Ce0.9Zr0.1O2 cermet in catalytic activity for POM and redox behavior in conventional laboratory tests showing the beneficial effect of Cu addition in the suppression of carbon formation and lowering of anode resistance in the bimetallic sample.14 However no detailed in situ studies have been performed to analyze the redox state of Ni, Cu and Ce and their effect on catalytic activity.
Therefore, the aim of this work is to study in detail, by means of in situ XANES spectroscopy experiments in dispersive mode, the oxidation state of the cations present both in the support and in the metallic phases in NiO/ZDC and CuO–NiO/ZDC cermets under diluted hydrogen and CH4/O2 atmospheres in order to correlate redox properties with catalytic activity. The effect of support and firing temperature is also discussed.
Solid structure was studied with XPD technique, using a Phillips PW3710 diffractometer operated with Cu-Kα radiation and a graphite monochromator. Data was collected in the angular region of 2θ = 20–80° with a step size of 0.03° and a time per step of 4 s. The average crystallite size was calculated by means of the Scherrer equation using the (111) reflection for the fluorite structure and the (111) and (101) reflections for the CuO and NiO phases respectively.
Sample morphology was studied by means of scanning electron microscopy (SEM) technique using a Zeiss Electron Beam SEM-Supra 40. The powdered samples were deposited over an adhesive carbon-filled conductive tape to avoid charging problems.
Conventional catalytic activity tests for partial oxidation of methane were performed in a quartz fixed bed reactor operated at atmospheric pressure in the temperature range: 500–750 °C. Reactor inlet feed consisted in a mixture of 3.1 mol% CH4, 1.2 mol% O2 with N2 balance; with a total feed flow of 436 cm3 min−1. These TPR and catalytic activity test results were previously reported but are included in the present work in order to compare and complement in situ TPR and catalytic activity experiments.14
In situ TPR experiments were carried out by heating the sample in a 5 mol% H2 (He balance) flow with a heating rate of 10 °C min−1 up to 800 °C following the same procedure used in conventional laboratory TPR experiments.
In situ catalytic tests were performed to assess sample activity towards partial oxidation of methane using a reactor inlet flow consisting of a mixture of: 1.3 cm3 min−1 O2, 3.4 cm3 min−1 CH4 and 104.3 cm3 min−1 He. Molar feed ratio (CH4:O2 = 2.6) was superior to the stoichiometric one for POM (CH4:O2 = 2) in order to work in a methane excess atmosphere, a prevailing condition in a SOFC anode. The spatial time used was of τ = 0.11 mg catalyst min cm−3. Measurements were performed in the temperature range: 500–750 °C, and a dwell time at each temperature of 30 min, following a heating ramp of 10 °C min−1. All catalytic tests were carried out emulating conventional laboratory experiments in order to further analyze the performance of the samples.
Data analysis was performed by means of the Athena software included in the IFEFFIT software package.22 A linear combination fitting of standard spectra was carried out in order to assess the fractions of reduced and oxidized species in the samples during the course of the experiments. Before proceeding with the linear combination fitting, background subtraction and spectrum normalization was carried out. For the data obtained in the Ce L3-edge, the fitting was performed using a Ce(NO3)3·6H2O disc as a Ce(III) standard and the initial spectrum of each sample as a Ce(IV) standard. By following this procedure, the degree of reduction of the samples is obtained and not the absolute Ce(III) content. In the case of Cu K and Ni K-edge experiments, Cu2O, CuO and NiO powders were used as a reference of Cu(I), Cu(II) and Ni(II) species respectively. To assess the amount of Ni0 and Cu0, the spectra corresponding to a Ni and a Cu foil were used as standards respectively. However, the fitting was also carried out using as standards of the reduced samples the last spectra recorded at 800 °C in H2 flow. The fitting results obtained by both procedures exhibited less than 5% error in the whole temperature range but the fitting was qualitatively improved. It should be noticed that Ni and Cu foils were recorded at 25 °C and reduced spectra were recorded at temperatures over 400 °C. High temperatures tend to diminish the intensity of oscillations in the absorption profile due to higher thermal disorder thus leading to slight differences between the standard spectra and reduced sample spectra.23
Sample | SBET (m2 g−1) | DXPD ZDC (nm) | DXPD NiO (nm) | DXPD CuO (nm) |
---|---|---|---|---|
ZDC (Tc = 600 °C) | 45 | 9 | — | — |
NiO/ZDC (Tc = 1000 °C) | 8 | 25 | 61 | — |
CuO–NiO/ZDC (Tc = 1000 °C) | 5 | 55 | 75 | 41 |
CuO/ZDC (Tc = 1000 °C) | 3 | 57 | — | 45 |
CuO–NiO/ZDC (Tc = 350 °C) | 19 | 10 | 20 | 49 |
In Fig. 3 a selection of XANES profiles of samples ZDC, CuO/ZDC, NiO/ZDC and CuO–NiO/ZDC are plotted against temperature. These spectra were obtained during in situ experiments in 5 mol% H2/He atmosphere upon heating up to 800 °C. It is clear, in the last spectra recorded at 800 °C, that the Ce(III) peak contribution is greater for NiO/ZDC, CuO–NiO/ZDC and CuO/ZDC samples compared to sample ZDC.
Fig. 3 In situ XANES profiles collected upon heating in 5 mol% H2/He for samples: (a) CuO–NiO/ZDC, (b) NiO/ZDC, (c) CuO/ZDC, and (d) ZDC. |
In Fig. 4 the degree of reduction of the three samples is plotted as a function of temperature. In all cases the degree of reduction rises with increasing temperatures. The reduction onset temperature was similar for all three samples at about 200 °C with no significant differences in their redox behavior in the temperature range: 25–650 °C. On the contrary, in the range 650–800 °C, sample ZDC exhibited the lowest degree of reduction (αCe) with a final value of 27%. In the case of NiO and CuO–NiO loaded samples, the final degree of reduction was of 41% for both samples and of 43% for the CuO-loaded sample at 800 °C. It is noteworthy that CuO/ZDC and CuO–NiO/ZDC samples presented higher reduction values in the whole temperature range, evidencing enhanced reduction kinetics for Cu-containing samples when compared to the NiO/ZDC sample.
In the inset of Fig. 4 a simulation of the TPR profiles is presented. This simulation was performed by fitting the reduction profiles presented in Fig. 4. Details from the fitting of reduction profiles and building of element specific TPR profiles are included in the ESI† section. A set of sigmoidal curves was used to adjust the data points and the resulting curve was then differentiated to obtain the TPR profile as a function of temperature. This method allows a straightforward comparison with most reported results regarding CeO2 reduction profiles performed with conventional TPR experiments with a TCD detector. Fitting was performed assuming that the Ce reduction takes place in two steps: the first step is generally attributed to the reduction of less coordinated surface species, whilst the high temperature step is usually associated to bulk reduction.24 The simulated TPR profiles are consistent with this assumption and exhibit two well defined peaks. In this case, the low temperature peak maximum was estimated at 589 °C, 439 °C, 431 °C and 416 °C for ZDC, NiO/ZDC, CuO/ZDC and CuO–NiO/ZDC respectively. This is an indication that the addition of NiO and/or CuO to the ZDC system shifts the reduction profile of ZDC toward lower temperatures. However, this effect is even more pronounced for the CuO-containing samples compared to the NiO/ZDC sample. This can be supported by the fact that the high temperature peak is also shifted toward lower temperatures when CuO is added to the system, being 712 °C and 761 °C the corresponding peak maxima temperatures for samples CuO/ZDC and CuO–NiO/ZDC respectively. It is worth noticing that in the temperature range analyzed the high temperature peak is not resolved neither for ZDC nor NiO/ZDC.
The enhancement in ceria reducibility has been reported in ceria-based supports combined with catalytically active metals and transition metals, in particular with Cu and Ni.25–27 The mechanism proposed to explain this effect is the dissociative adsorption of hydrogen on the surface of the metallic phase followed by hydrogen spillover onto the oxide support, enabling the reduction of Ce4+ at lower temperatures in contrast to the bare support.28 In particular, in the case of Ni supported on ceria-based supports, Sharma et al. observed by means of electron microscopy a preferential reduction of ceria in the surroundings of Ni particles evidencing the occurrence of hydrogen spillover from Ni to the oxide support.28 In the case of Cu–CeO2 systems, it has been proposed that H2 spills over highly dispersed copper species to promote the concomitant reduction of both CuO and CeO2 support.27,29 In line with this, the fact that ceria is more easily reduced in CuO–NiO/ZDC sample when compared to CuO/ZDC at low temperatures (T < 600 °C) can be related to the metallic loading in both samples since their BET specific surface areas are similar. The bimetallic sample contains only 30 wt% CuO whereas the monometallic sample contains 60 wt% CuO. This higher oxide content led to a more agglomerated sample since CuO has a high tendency toward sintering due to a low melting point compared to NiO.30 This agglomeration is visible in the sample crystallite sizes (41 and 45 nm for CuO–NiO/ZDC and CuO/ZDC respectively), in BET specific surface area values (5 m2 g−1 and 3 m2 g−1 for CuO–NiO/ZDC and CuO/ZDC respectively) and in SEM images presented in Fig. 5 where sample agglomeration is evident with increasing CuO content. This agglomeration can affect spillover mechanism as H2 is expected to spill over highly dispersed copper species, being most favored in the less agglomerated bimetallic sample when compared to the monometallic one.
Fig. 6 Degree of Ni reduction [α = Ni2+/(Ni2+ + Ni0)] obtained for the CuO–NiO/ZDC and NiO/ZDC samples during the course of the TPR experiment. In the inset: simulated Ni-TPR profiles. |
The Cu2+ → Cu0 (+0.34 V) reduction reaction has a lower reduction potential compared to the Ni2+ → Ni0 reaction (−0.26 V), which allows for the former reaction to take place at lower temperatures.32 As described in the previous section, one of the proposed mechanisms for bimetallic Cu–Ni samples supported on ceria-based materials includes a dissociative adsorption of H2 over the surface of highly dispersed Cu species followed by H2 spillover which triggers the concomitant reduction of CuO, NiO and CeO2. This can explain why Ni reduction in the bimetallic CuO–NiO/ZDC sample is markedly enhanced, especially in the lower temperature range (300–550 °C) when compared to the monometallic NiO/ZDC sample. It is interesting to point out that this enhancement in the sample reducibility was not a result of a crystallite size effect since sample CuO–NiO/ZDC exhibited a Ni particle size of 75 nm compared to the 61 nm of Ni crystallites in sample NiO/ZDC.
Finally, a difference in the initial stage of both reduction profiles can be acknowledged: NiO/ZDC sample exhibited virtually no lag phase whereas sample CuO–NiO/ZDC evidenced a pronounced induction phase. This feature resulted in a small peak in the simulated Ni-TPR profile, visible in Fig. 6. Further analysis on this feature will be addressed in the following section were the effect of support and firing temperature are discussed.
In order to analyze the effect of the ceria support on Ni reduction, a non-supported CuO–NiO sample prepared by the same glycine-nitrate route was synthesized and fired at 350 °C. The results from XANES TPR experiments performed with the three CuO–NiO samples, the two supported and the non-supported one, are presented in Fig. 8 where the degree of Ni reduction (αNi) is plotted against temperature. The reduction onset temperature is lowest for the non-supported sample and increases with firing temperature. Moreover, the kinetics of the initial stage of the reduction is visibly different: in the case of the CuO–NiO sample, the beginning of the reduction is quite abrupt, whilst for the supported sample fired at 350 °C there is a slight lag. This delay is even more pronounced for the sample fired at 1000 °C, evidenced with a small slope up to α = 20%.
Fig. 8 Degree of Ni reduction [α = Ni0/(Ni2+ + Ni0)] obtained for samples: CuO–NiO/ZDC fired at 350 °C and at 1000 °C and CuO–NiO (non-supported) fired at 350 °C during the course of TPR experiments. |
In all cases the reduction takes place in more than one step. This is an indication that there are different Ni species present in the samples, each with different redox capabilities. In the case of the CuO–NiO sample, even though there is no support, the interaction of Cu and Ni particles influence the reduction mechanism of Ni particles. Although Ni0 and Cu0 are completely miscible in each other, potentially allowing for uniform alloying to take place in reducing atmospheres, CuO reduction is thermodynamically favored when compared to NiO reduction.30 Li et al. studied Ni–Cu samples supported on TiO2 and reported that, although in most of the samples uniform alloying is obtained, a Ni or Cu surface enriched alloy can be formed, depending mainly on Cu reduction kinetics, which was found to markedly enhance Ni reduction.33 In our results, after TPR experiments, a Ni-rich alloy is formed altogether with non-alloyed Cu for CuO–NiO/ZDC sample as shown in Fig. 9, where XPD patterns of samples after TPR experiments are plotted. On the other hand, another reason that might account for a two-step reduction in the CuO–NiO sample might be the broad particle size distribution, affecting H2 diffusion with the concomitant delay in Ni2+ reduction.
Evidence presented in the literature is ambiguous regarding to the effect of CeO2-based supports on Ni reduction. A strong metal support interaction (SMSI) is frequently called upon to explain the different reduction profiles obtained.34 Both an electronic and a geometric factor effect of this SMSI have been reported to affect the reduction kinetics of Ni particles supported on ceria supports.19,35 The former involves an electronic charge transfer between the Ni nanoparticle and the support, whilst the latter implies the migration of Ce reduced species to the surface of the metallic nanoparticle thus modifying its catalytic properties.35 The electronic effect has been found to promote the reduction of CeO2-supported nanoparticles, whereas the geometric factor is detrimental for Ni reduction as a consequence of the physical blockage of active sites.
Matte et al. studied the effect of CeO2 support on Ni nanoparticles reduction. They studied Ni/CeO2 and non-supported Ni samples.19 In their work 20 wt% Ni was supported over CeO2 and no calcination stage was performed prior to reduction treatment, which led to a mean Ni crystallite size of 3.5 nm. They reported an enhanced reduction kinetics for Ni/CeO2 sample compared to the Ni nanoparticles after a mild reduction treatment in 5 mol% H2/He up to 500 °C. After the reduction treatment the authors found evidence of the geometrical SMSI effect on TEM images that evidenced the migration of Ce species over the Ni nanoparticles. However, they ascribe the enhanced reducibility of the supported samples to the electronic effect which is expected to facilitate reduction by charge transfer at low temperatures.
In our case, the opposite was found since the non-supported NiO particles were reduced at significantly lower temperatures in CuO–NiO than in CuO–NiO/ZDC sample. It is highly likely that the reason for this different behavior lies in the crystallite size. The three samples hereby compared presented different Ni crystallite sizes: <7 nm, 20 nm and 75 nm for samples CuO–NiO (Tc = 350 °C), CuO–NiO/ZDC (Tc = 350 °C) and CuO–NiO/ZDC (Tc = 1000 °C) respectively. It is therefore noteworthy that sample CuO–NiO with the lowest onset temperature for the reduction of Ni presented the smallest crystallite size. In this sense, the reduction profile of sample CuO–NiO/ZDC (Tc = 1000 °C) was shifted towards higher temperatures. Matte et al. tested samples with very small crystallite sizes that enabled a reduction at low temperatures (<200 °C) thus enabling the electronic effect to prevail at low temperatures, whilst the supported samples hereby tested exhibited Ni crystallite sizes larger than 20 nm.19
In Fig. 10 SEM images of fresh samples of CuO–NiO (Tc = 350 °C) and CuO–NiO/ZDC (Tc = 350 °C) are presented. Both samples present clear morphological differences. The non-supported sample is densely agglomerated whilst the supported sample exhibits a homogeneous morphology, an enhanced particle dispersion and high porosity. Therefore, it is clear that the addition of CeO2–ZrO2 to the system contributes to obtain a material with an improved texture and morphology. Nonetheless this is not enough to promote the reduction at lower temperatures than the ones achieved by the non-supported sample. Then, it is plausible that in addition to the crystallite size effect, the interaction of Ni particles with the CeO2–ZrO2 support can contribute to a delayed reduction kinetics.
Fig. 10 SEM images of (a) sample CuO–NiO (non-supported) fired at 350 °C and (b) sample CuO–NiO/ZDC fired at 350 °C. |
Finally, comparing results from sample CuO–NiO/ZDC fired at different temperatures, there is a visible shift in the Ni reduction profile towards lower temperatures for sample calcined at 350 °C when compared to sample calcined at 1000 °C. The first reduction step, which is usually ascribed to the reduction of surface species, as described in the previous section, is steeper and reaches a higher degree of reduction for CuO–NiO/ZDC (Tc = 350 °C) compared to sample CuO–NiO/ZDC (Tc = 1000 °C). This might be related to both textural and morphological features. First, sample CuO–NiO/ZDC (Tc = 350 °C) exhibited a larger BET specific surface area value (19 m2 g−1) compared to the value measured for sample CuO–NiO/ZDC (Tc = 1000 °C) (5 m2 g−1). This improved texture leads both to a more porous structure, triggering a more efficient H2 diffusion through the sample and also to a larger amount of gas-accessible Ni sites to facilitate the reduction process. In addition to this, a noteworthy difference between the two reduction profiles is the extent of the second reduction step, usually attributed to the reduction of bulk species or species strongly bound to the support. In the sample fired at low temperature the second reduction step is quite small, whilst for the sample fired at high temperature this step is considerable. This might be ascribed to a large aggregation of NiO species that are less prone to be reduced. The mean NiO crystallite size for the sample calcined at 1000 °C was of 75 nm whereas for sample calcined at 350 °C this value was of 22 nm. Therefore a larger crystallite size and a broader particle size distribution for sample CuO–NiO/ZDC (Tc = 1000 °C) could explain the differences in the extent of the second step. Not to mention the fact that the treatment at higher temperatures can sharpen the interaction between NiO and the support contributing to a slower reduction kinetics.
Fig. 11 XANES normalized absorption profiles of sample CuO–NiO/ZDC recorded during the in situ TPR experiments in the Cu K-edge. |
Fig. 12 (a) Degree of Cu2+ and Cu+ reduction of sample CuO–NiO/ZDC against temperature during the TPR experiment in the Cu K-edge. (b) Simulated TPR profile as a function of temperature. |
Finally, in Fig. 12b the simulated reduction profile of copper species is presented for the bimetallic sample. An asymmetric peak is observed which can be deconvoluted into two peaks. The first is usually ascribed to the reduction of highly dispersed copper species, while the second one to bulk CuO.38 It is worth noticing that these highly-dispersed species are thought to be responsible for enhancing both CuO, NiO and CeO2 reducibility in the CuO–NiO/ZDC cermet.27
Fig. 13 (a) Conventional laboratory TPR profiles using a TCD detector (b) simulated TPR profiles from XANES experiments. |
In Fig. 14a and b and the degree of Ce (αCe) and Ni (αNi) reduction are plotted against time altogether with the temperature profile for samples CuO–NiO/ZDC and NiO/ZDC respectively. Catalytic tests were performed altogether in a CH4:O2 = 2.6:1 mol ratio feed flow as detailed in the experimental section, implying that methane is in stoichiometric excess for POM reaction. The results from reference spectra fitting corresponding to XANES Ce L3-edge measurements show that both samples exhibit a low degree of Ce reduction (<4%) in the whole temperature range. It is evident that αCe profiles differ from sample CuO–NiO/ZDC to sample NiO/ZDC. The degree of reduction increases stepwise in the whole temperature range for the latter sample while in the case of CuO–NiO/ZDC αCe slightly decreases when temperature is increased to 600 °C and again when temperature is increased to 700 °C. Taking into consideration the Ni K-edge results, it is evident that αNi increases stepwise with temperature in the whole temperature range for both samples. However, Ni reduction onset temperature is 50 °C lower for sample NiO/ZDC compared to sample CuO–NiO/ZDC.
In Fig. 15 and Table 2 the results of catalytic experiments in a conventional laboratory fixed bed reactor, previously reported, are presented. CuO–NiO/ZDC sample exhibits activity toward TOM at temperatures higher than 550 °C with ca. 100% CO2 Selectivity at 600 °C and 650 °C.14 Furthermore, when temperature is increased to 700 °C POM begins to take place with the consequent production of H2 and CO. On the other hand, sample NiO/ZDC only exhibited activity towards POM after the light-off temperature of 700 °C was achieved, mainly detecting CO and H2 and only traces of CO2 as reaction products.
Fig. 15 Oxygen and methane conversion during catalytic experiments in conventional fixed bed reactor (conversion of x = [(Finx − Foutx)/Finx], with Fx the molar flux of x) CuO–NiO/ZDC. |
CuO–NiO/ZDC | NiO/ZDC | |||||||
---|---|---|---|---|---|---|---|---|
Temp. (°C) | SCO2 (%) | SCO (%) | SH2 (%) | RH2:CO | SCO2 (%) | SCO (%) | SH2 (%) | RH2:CO |
a SCOx = FCOoutx/(FCHin4 − FCHout4), SH2 = 0.5. FHout2/(FCHin4 − FCHout4), RH2:CO = FH2/FCO, with Fx the molar flux of x. | ||||||||
600 | 100 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
650 | 97 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
700 | 40 | 60 | 34 | 1.2 | 2 | 97 | 100 | 2.2 |
750 | 23 | 77 | 55 | 1.5 | 1 | 99 | 100 | 2.2 |
In line with this, it is interesting to correlate the XANES results in both Ce L3 and Ni K-edges with catalytic activity tests in fixed bed reactor: in the first place, between 500–550 °C CuO–NiO/ZDC sample exhibits a greater degree of Ce reduction when compared to the monometallic sample and is followed by a slight re-oxidation when increasing the temperature to 600 °C. At this same time Ni reduction is triggered for the bimetallic sample. This is a clear evidence of the interplay that exists between the redox behavior of both cations and the catalyst performance, being these redox changes strongly related to the activation of the sample toward TOM reaction. The fact that the ZDC present in CuO–NiO/ZDC sample is releasing oxygen from its lattice as a consequence of ceria reduction, might explain the delay in the reduction of the supported Ni2+. In this sense, when NiO reduction begins, part of the oxygen released might be captured by the Ce present in the material to partially re-oxidize itself. Not to mention that TOM products are detected at this stage which are oxidizing in its nature. Furthermore, it should be mentioned that when temperature is raised to 700 °C Ce begins to re-oxidize while Ni continues its reduction tendency.
Secondly, taking into consideration NiO/ZDC sample, when POM is activated in fixed bed reactor experiments at 700 °C, Ce and Ni reduction is slightly promoted, being the steps proportionally larger that the previous ones. This larger reduction extent might be related to a more reducing environment caused by the formation of POM products (CO and H2) and also possibly due to the H2 generated by methane cracking (CH4 → C + 2H2), one of the reactions related to carbon formation. In a previous work, carbonaceous residues were detected by XPD and SEM images of powders recovered after catalytic experiments with sample NiO/ZDC.14 These results, altogether with a continuous reduction of Ce4+ to Ce3+ might imply that, although this sample is able to provide oxygen from its lattice, the rate at which carbon is oxidized is not fast enough to prevent carbon deposition. Furthermore, in sample NiO/ZDC after each temperature increase the degree of Ni reduction is increased as well. However, when there is a temperature dwell at temperatures above 650 °C there is a continuous re-oxidation of the sample, evidenced in the negative slope in the plot of αNi vs. time. It is noteworthy as well that the most pronounced Ce reduction step (ca. ΔαCe = 1%) was registered when temperature was increased from 650 °C to 700 °C. This means that oxygen incoming either from the CeO2–ZrO2 lattice through Ce reduction or gas-phase oxygen are participating in the re-oxidation of Ni, a process strongly related to the catalyst deactivation.40 On the contrary, in sample CuO–NiO/ZDC, Ni continues its reduction process while Ce begins to re-oxidize. It should be mentioned that no carbon formation was detected by XPD or SEM in the bimetallic sample. In Fig. 16 XPD patterns of spent catalysts are plotted. The presence of a Cu–Ni alloy in sample CuO–NiO/ZDC is evidenced altogether with the formation of graphitic carbon in sample NiO/ZDC.
Catalyst deactivation in Ni-based catalysts is mainly caused by carbon deposition, particle sintering and metalic site oxidation.40 In our case, particle sintering was not a source of catalyst deactivation as samples were previously fired at 1000 °C and the maximum reaction temperature tested was 750 °C. In fact, a slight re-dispersion was found to take place due to sample reduction. Carbon formation was evidenced in monometallic NiO/ZDC sample both in SEM images with the presence of carbon filaments and in XPD patterns.14 This was not the case of sample CuO–NiO/ZDC in which carbon formation was suppressed. However, an interesting finding in this work is that NiO/ZDC catalyst exhibits re-oxidation of active sites at 700 °C and 750 °C, temperatures at which sample was found to be active for POM and methane cracking. In the case of CuO–NiO/ZDC no re-oxidation takes place. Crozier et al. studied by means of in situ environmental TEM partial oxidation of methane reaction over Ni/SiO2 catalysts.41 They found that even after a pre-reduction of the sample, when heated up to 700 °C a re-oxidation took place due to the high O2 partial pressures in the reactor. It should be noticed that they used a CH4:O2 ratio of 8:4, which corresponds to the POM stoichiometry. They attribute this behavior to the high chemisorption energy of O2 on Ni surface compared to CH4, which favors a major O surface occupancy enhancing the kinetics of NiO formation. Therefore, as metallic Ni is the active site for POM to take place, NiO formation can cause Ni deactivation due to the loss of active sites for the reaction. Kitla et al. studied bimetallic copper/nickel catalysts supported on zirconia and ceria/zirconia for methane decomposition and reported that upon the addition of Cu to the supported Ni samples, the surface area of exposed Ni is significantly reduced.42 They attributed this to the fact that upon reducing atmospheres a surface Cu-enriched CuNi alloy is formed. This process breaks up larger Ni ensembles that are supposed to be responsible for carbon formation. In addition, they reinforced the fact that the formation of this Cu-rich alloy modifies the properties of Ni, reducing the C–H bond breaking.
Mass spectrometry data collected during in situ XANES experiments for POM activity are plotted in Fig. 14c and d. In it, both catalysts exhibit CO2 production above 550 °C. In particular, a peak of CO2 and H2O production is observed each time temperature is increased. This might be an indication that the reaction mechanism pathway for methane decomposition is the one that involves first TOM, followed by both steam and CO2 methane reforming.43 In conventional laboratory tests only small traces of CO2 were detected with gas chromatography sampling for sample NiO/ZDC, while for sample CuO–NiO/ZDC activity towards total oxidation of methane was observed in the temperature range of 550 °C to 750 °C. In Fig. 14, CO production is evident above 600 °C for both samples while H2 production is only observable above 650 °C for sample NiO/ZDC and above 700 °C for sample CuO–NiO/ZDC. The fact that H2 is detected at higher temperatures than CO might indicate that H2 is participating in Ni reduction. Methane signal does not fluctuate appreciably until 700 °C, indicating an important uptake only at 750 °C due to the fact that this reactant is present in stoichiometric excess. However, O2 consumption is significant above 700 °C. Although in both cases a decrease in conversion for both reactants is observed, this might be related to the fact that a steady state has not been achieved in the 30 min temperature dwell. In fact, as analyzed above, the metallic phase in CuO–NiO/ZDC sample continues to reduce whilst the metallic phase in NiO/ZDC begins to re-oxidize.
In situ catalytic experiments for partial oxidation of methane showed a clear interplay between the redox behavior from the Ce in the CeO2–ZrO2 support and the Ni from the active phase. Ce reduction values remained low (<4%) during the experiments in the whole temperature range for both samples. However, clear behavior differences were detected in the Ce reduction profiles that shed light into the importance of the interaction of the support and the active phase in catalytic stability. At 750 °C a continuous reduction of Ce4+ to Ce3+ in sample NiO/ZDC and carbon formation detected in XPD patterns indicate that, although this sample is able to provide oxygen from its lattice, the rate at which carbon is oxidized is not fast enough to prevent carbon deposition. Furthermore, incoming oxygen either from the CeO2–ZrO2 lattice through Ce reduction or from gas-phase feed was found to favor re-oxidation of Ni at this temperature, a process strongly related to the catalyst deactivation. On the contrary sample CuO–NiO/ZDC exhibited a slight re-oxidation of Ce at 750 °C and no re-oxidation of Ni altogether with a clear suppression of carbon formation. These results were in agreement with those obtained through conventional catalytic tests performed in fixed-bed reactor, indicating that CuO addition to the NiO/ZDC system promotes stable catalytic activity and excellent resistance to formation of carbonaceous residues.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c8ra01528g |
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