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Effect of Redox Nature of Impregnated Ferrite Catalysts on Their Carbon Monoxide Oxidation Activity

TD Radhakrishnan Nair1*, and CU Aniz1,2

1School of Chemical Sciences, Kannur University-670 327, Kerala, India.

2Infectious diseases department, National Medical Center "La Raza", IMSS, Mexico City, Mexico

*Corresponding Author:
TD Radhakrishnan Nair
School of Chemical sciences
Payyanur Campus, Kannur University
Edat.P.O, Kannur-670327, Kerala, India
Telephone: +91 497 2806402
Fax: +91 497 6802402

Received: 19 September 2013 Accepted: 30 September 2013

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Abstract

Ferrite catalysts of Nickel, Cobalt and Copper were prepared by co-precipitation hydrothermal route and were impregnated with Palladium, Cerium and Lanthanum as promoters. These were characterized and found to be thermally stable. Bothe the ferrites and the impregnated samples were tested for carbon monoxide oxidation activities and the results correlated with the reducibility of the catalysts using temperature programmed reduction (TPR) studies. The reduction step of hematite phase of ferrites to magnetite was found shifted to lower temperature region and the catalytic activity was found to be enhanced upon Pd impregnation. The reason for the improved catalytic activity is explained on the basis of preferential adsorption, the strong synergic effects between the different metal components and the relative changes in the redox nature of the catalysts.

Keywords

Ferrospinels, Palladium impregnation, Redox nature, CO oxidation activity

Introduction

The ever growing demand for catalyst materials with desired properties in the field of environmental purification continues to prompt researchers globally for developing newer and newer materials. This is particularly necessary in the case of catalysts for use in automobile exhaust pollution control systems to protect the precious atmosphere. The significant aspect is that when a petrol engine starts from cold state, the exhaust manifold including the catalytic converter will be cold and hence the catalyzed reactions in the exhaust chamber are kinetically limited during ‘cold start’. Hence the harmful pollutants like carbon monoxide, due to its incomplete combustion, get released through the exhaust into the atmospheres before the catalyst system could reach the light off point where the oxidative conversion exceeds 50 percent.

Noble metal catalysts like platinum, palladium, rhodium, gold etc supported on ceria or alumina with good dispersions are currently being used as emission control three way catalysts. Even though a properly synthesized noble metal catalyst can give full CO conversion even at ambient reaction temperature [1,2], they are expensive and susceptible to sintering. Here lies the importance of developing and testing the cheaper and efficient materials [3]. The use of the ferrite spinels assume significant in such a context [4-6].

The oxidative capacity of some base metal oxides were reported earlier and their activity has been found enhanced by the addition of promoters like Palladium by impregnation [7,8]. Catalyst compositions with noble metal and base metal oxides, like Pd–(Cr, Cu)/(Ce, Zr)Ox/Al2O3, Pt–(MnOx, CoOx)/SiO2], Co–(Pt, Pd, Rh)/Ce–Al– O(Al2O3)], Pd–(Fe, Mn,Co, Ni,Cu)–Ox/NaZSM-5 and Pd/(Mn2O3 + SnO2) systems for oxidation applications are thus getting attention these days [9-14]. A series of catalyst preparations can be seen by impregnation with Cobalt and Lanthanum on to monolith catalysts to improve the redox properties as an attempt in this direction [15].

Catalyzed oxidation of CO is being extensively studied as an environment ‘greening’ process. The Mars van Krevelen mechanism explains the redox pathway where the lattice oxygen of the catalyst is consumed during the oxidation of CO. The change in the redox properties of the metal oxides when new elements are incorporated to them are discussed in literature [16]. Examples like Ni incorporation on to Cu/Zn/Al catalyst and Cu addition to CeO2 systems are studied to show their effect on redox properties as well as the catalytic reaction rates [17,18]. The effect of Palladium loading on the redox properties and the catalytic activities of various ternary compositions of copper, chromium and aluminum are also studied recently [19].

The present work is an attempt for improving the performance of the ferrite spinel catalysts for carbon monoxide oxidation by incorporating metals like palladium, to modify the redox properties of ferrospinels in a beneficial way.

Experimental

Preparation of catalyst samples

Pure ferrite catalysts of Ni, Co and Cu are prepared via co-precipitation method using Ferric chloride, Nickel acetate, Cobalt acetate and Copper acetate as respective metal precursors and NaOH as the precipitating alkali. Calculated amount of NaOH is taken as the base stock and the aqueous solutions of metal precursors at the above mole ratios are added from overhead slowly with thorough mixing. Co-precipitation was done at room temperature at pH 11.5. After the precipitation, the slurry was kept for 10 minutes at autogenous temperature of 40°C, the temperature was then raised to 90°C and kept for 40 minutes with a temperature control of +/- 5o; always maintaining the slurry concentration with hot de-ionized water. The slurry was filtered and warm water washes were given to remove chloride and other impurities. Samples were dried at 100°C for 4 hrs and used for powder X-ray diffraction (PXRD) studies to check the formation of spinel phase. A portion of each sample was calcined at 300°C for 4 hrs and sieved (75 μm). These powders were made into pellets by applying mild compaction and further granulated to ~1mm diameter to use in catalytic performance evaluations.

Incorporation of promoters onto the catalyst samples

A portion of the simple ferrites dried at 100°C were used for the impregnation studies. Nitrate salts of Palladium, Cerium and Lanthanum were dissolved separately in calculated quantity of de-ionized water to get clear solutions. Incipient impregnation method was applied to incorporate the promoter metals on the oxide samples as discussed elsewhere [20]. The targeted concentration of the promoters was 0.3% w/w. Samples were then calcined at 300°C for 6 hrs to complete the calcination process to confirm the removal of nitrates.

Characterization of samples

The prepared samples were characterized by PXRD, N2 adsorption, Temperature programmed desorption using Ammonia (NH3-TPD), Atomic Absorption Spectroscopy (AAS), Thermogravimetry (TG/DTA), TPR, Scanning Electron microscope (SEM) etc. TPD and TPR studies were done using Pulse Chemisorb 2705, Micromeritics. For NH3-TPD, 5 % NH3 in helium gas (Bheruka gases) was used as the adsorbate, where as for TPR, 10% H2 in nitrogen gas (Bheruka gases) was used as the reactive gas mixture. Temperature of the samples was raised to 800°C at a rate of 10°C/min, monitoring the sample outlet at calibrated thermal conductivity detector (TCD). Nitrogen adsorption-desorption measurements were done on a volumetric Micromeritics Tristar apparatus at liquid N2 temperature, 77.3K and BET/BJH methods were used for the calculation of surface area and pore volume respectively. In addition to the gas purification stations for all the input gases, a cold trap was connected during TPR run to remove the moisture formed during the reaction.

Granules of ~1mm diameter were used for the CO oxidation test to avoid pressure build up with powder samples, maintaining the space velocity of ~30000. Calibrated gas mixture of 1%CO and 6%O2 in balance N2 gas (Bheruka gases) was used as the inlet feed. Both inlet and outlet gases were analyzed using gas chromatograph (GC) equipped with flame ionization detector (FID) and methenator. The experimental methods and characterization details are described earlier [21]. For all the dynamic experiments, the sample mass, rate of gas flow, reactive gas composition etc were optimized to agree with the standard criteria to avoid mass transfer limitations and hydrogen thin situations [22,23]. The samples were tested for the CO oxidation under similar conditions of experimental set up and sample preparation explained above.

Results and Discussion

Elemental compositions of the samples were in agreement with the targeted figures showing the absence of leaching of metallic ions during the preparation and washing stages. The formation of the spinel phase is confirmed by the X-ray diffraction experiments. The typical peak value corresponding to 2Θ= 35.5 represents the characteristic 311 plane for spinels. The XRD patterns are quite similar for the pure and mixture samples and this trend is expected due to the similarities among the +2 valence state of metal ions present in the mixed samples [21]. TG patterns of the ferrites showed good thermal stability of the samples even above 700°C during air oxidation. The low temperature weight losses up to 300°C are related to free moisture as well as bound water of crystallization. The BET surface areas of all the samples are given in Table-I. The surface area of CoFe2O4 is 138m2/g and that of CuFe2O4 is 116m2/g. These samples have higher surface area values if we compare with similar samples prepared through nitrate route [21], matching to the relatively higher pore volume and lower APD values. The average particle size from SEM is 5 μm for the NiFe2O4, CoFe2O4 and CuFe2O4; their porous and aggregate nature is clear from the SEM images given in Figure-1.

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Figure 1: SEM images of pure (a) NiFe2O4 (b) CoFe2O4 and (c) CuFe2O4 ferrite samples calcined at 300°C

material-sciences-Physico-Chemical-properties-Pure

Table 1: Physico-Chemical properties of Pure NiFe2O4 (a) CoFe2O4 (b) CuFe2O4 (c) and their Pd/Ce/La doped samples.

Average pore diameter values obtained from the BJH N2 adsorption experiments are plotted in Figure-2. All the samples have pores in the meso-porous range, with well-defined step and Type IV hysteresis loop due to capillary condensation, originate from the secondary inter particle voids between their aggregates. These observations are in line with the observations from the SEM analysis. The IR spectra showed two absorption bands at 500 and 700 cm-1 each arising from inter atomic vibrations which are the characteristics of spinel ferrites.

material-sciences-Average-Pore-diameter-distribution

Figure 2: Average Pore diameter distribution of pure and Pd/Ce/La doped NiFe2O4, CoFe2O4 and CuFe2O4 calcined at 300°C

AAS analysis to estimate the impregnated trace metals showed matching results to the expected composition of 0.3% w/w within ± 3% variation, confirmed the proper incorporation of promoters into the samples. All the samples gave similar patterns in thermogravimetric experiments and showed that the promoters do not alter the catalyst pore structure significantly during calcination due to heat changes. However, the presence of the different metal ions on the surface of the spinel samples affect surface area, porosity etc. The BET surface areas of the samples showed variations after impregnation and calcination at 300°C (Table-I). Surface area of the Pd impregnated samples got reduced and the Ce impregnated samples did not exhibit any change. The La impregnated samples showed increase of surface area. The mean pore diameter of the samples also shifted slightly towards micro pore size in this case as shown in Figure-2.

The TPR studies of the pure ferrite samples calcined at 300°C were done and the results are given in Figure-3(a), Figure-3(b) and Figure-3(c); the profiles of pure ferrites are shown magnified for easy read-out. The respective reduction peaks of metal ions present and their peak positions are well matching with the earlier data [21,24]. It is interesting that all the three simple ferrite samples got exactly similar TPR pattern in comparison with those prepared through nitrate routes. The low temperature peak profile in each sample not only represents the reduction of divalent metal ions but also includes the initial reduction stages of Iron oxides [25,26].

material-sciences-TPR-profiles-pure-NiFe2O4

Figure 3a: TPR profiles of pure and Pd/Ce/La doped NiFe2O4 calcined at 300°C

material-sciences-TPR-profiles-pure-CoFe2O4

Figure 3b: TPR profiles of pure and Pd/Ce/La doped CoFe2O4 calcined at 300°C

material-sciences-TPR-profiles-pure-CuFe2O4

Figure 3c: TPR profiles of pure and Pd/Ce/La CuFe2O4 calcined at 300°C

Carbon monoxide oxidation profiles of the samples are given in Figure-4(a), Figure-4(b) and Figure-4(c). CuFe2O4 showed the maximum CO conversion activity at low temperatures compared to CoFe2O4 and NiFe2O4. The performance of the samples follow same trends of conversion compared to similar samples prepared via nitrate route and it validate the influence of the inherent activities by the divalent ion in the octahedral positions. However, the former possess relatively lower conversion values only, might be due to retention of small amounts of chloride ions on the surface of the catalyst samples even after thorough washing. The presence of relatively bigger chloride ions on the catalyst surface might deter the adsorption of CO molecules for oxidation. This is in line with the operation of the Mars van Krevelen mechanism probable for the CO oxidation on spinels [16].

material-sciences-CO-oxidation-profiles-NiFe2O4

Figure 4a: CO oxidation profiles of pure and Pd/Ce/La doped NiFe2O4 calcined at 300°C

material-sciences-CO-oxidation-profiles-CoFe2O4

Figure 4b: CO oxidation profiles of pure and Pd/Ce/La doped CoFe2O4 calcined at 300°C

material-sciences-CO-oxidation-profiles-CuFe2O4

Figure 4c: CO oxidation profiles of pure and Pd/Ce/La doped CuFe2O4 calcined at 300°C.

All Palladium impregnated samples showed significant improvement in their performance. Even though La incorporation facilitated the shifting of pore diameter towards the lower pore size region thereby causing an increase in surface area, the catalytic effect on oxidation was not pronounced. Ceria containing samples showed practically no improvement on the oxidation rates. The reduction profiles of most of the Ce and La doped samples are very similar to their parent ferrite samples; a few exceptions are there as in the case of CoFe2O4 up on Ce impregnation.

The Pd doped samples showed abrupt difference in their reduction pathway. In the case of NiFe2O4 impregnated with 0.3% Pd, the first Tmax got shifted to 307°C from 429°C. The shifting of the temperature to the lower side by about 120°C is quite significant. For pure CoFe2O4, the first Tmax is at 554°C, whereas it is at 284°C, 513°C and 511°C for Pd, La and Ce doped CoFe2O4 respectively. CuFe2O4 showed first Tmax at 229°C, while the Pd, La and Ce analogues have Tmax points at 135°C, 215°C and 217°C respectively.

In the case of NiFe2O4, Pd doped sample showed significant improvement in CO oxidation conversion, where as Ce and La samples showed a mixed response. On an average, La and Ce samples have similar conversion trends as that of the un-doped NiFe2O4 sample over the entire range of temperatures. For example, at 100°C NiFe2O4 had only 4.5 % conversion, where as Pd impregnated samples had 32.9 % conversion. In the meantime, Ce and La impregnated NiFe2O4 samples have only 10.2 and 6.8 % conversions respectively. Among CoFe2O4 series at T100, the un-doped CoFe2O4 has 28.5 % conversion; Ce and La had 10.7 and 30.9 % conversions respectively. For Pd-CoFe2O4 sample, T100 conversion increased to 53.0 % and is correlated to the shift of reduction peaks in the TPR profile. Pure CuFe2O4 is having the best conversion compared to pure Ni and Co samples and exhibits almost full conversion at around 180°C. Upon Pd doping, the conversion at T100 came up to 37.5 % from 17.4% of the un-doped samples. Generally in all the cases, Pd doping enhanced the low temperature oxidation in the case of NiFe2O4, CoFe2O4 and CuFe2O4 samples which would help in the modification of kick-off temperatures of the catalyst samples for exhaust treatment applications.

Doping with Pd gave a prominent enhancement for the reduction of the divalent metals as well as the hematite to magnetite reduction part as observed in the H2-TPR pattern. The hydrogen spillover from palladium to the base metal oxide is also likely [12,14]. It is well known that palladium oxide can be easily reduced to metallic Pd by H2. Metallic Pd, as a noble metal shows intrinsically high capability for hydrogen dissociation, which serve as a catalyst triggering the reduction of the other surrounding oxides by dissociating hydrogen molecule with a decrease of activation energy. This amounts to auto catalysis of the gas–solid reaction attributed to hydrogen spillover effect. The H2 consumption values calculated from the peak area upon calibrated TCD exceeded that required for the Pd or the divalent metal alone or its combination, showing also the occurrence of hematite to magnetite reduction along with.

It is established that CO preferentially gets adsorbed on to noble metals like Pd compared to pure base metal oxides. The spillover of CO from Pd to base metal oxides to consume lattice oxygen is the potential reason for their enhanced catalytic properties. The redox properties of the base metal oxides are also significant. The modification by promoter addition facilitates enhancement in their catalytic activity because the redox properties of the base metal oxides are improved that ease the supply of lattice oxygen for CO oxidation.

The TPR results of Pd containing samples show exactly the kind of reduction pathway that begin at lower temperatures with extension to high temperatures [18,20]. Even CuFe2O4, the catalyst with best reducibility got enhanced in their reducibility and activity upon introduction of small amounts of palladium. These results support Mars van Krevelen mechanism that considers redox nature of the catalyst surface as the key parameter for CO oxidation reactions. CO and O2 compete to get adsorbed on pure base metal oxides at least during the rejuvenation step as discussed in Mars van Krevelen mechanism. Once a CO molecule is adsorbed on a surface, it suppresses the adsorption of O2 to complete the reaction cycle by filling up the lattice oxygen vacancy. In Pd promoted surfaces, CO preferentially gets adsorbed on Pd allowing O2 to easily interact with reduced base metal surfaces that enhances the reaction rate even at low temperature. Thus the noble metal incorporated ferrites have very important applications as CO oxidation catalysts.

Ferrite catalyst samples are synthesized through methods involving hydrothermal step that directly gives spinel phase. Samples were characterized and the carbon monoxide oxidation activities were evaluated. Promoters like Pd, Ce and La were incorporated via pore filling impregnation method, characterized, and tested for CO oxidation activity. The effect of reducibility of the catalyst precursor and its relation to the CO oxidation especially when Pd is loaded has been investigated. Preferential adsorption of CO compared to oxygen is believed to occur on Pd centers and the lattice oxygen from the base metal oxides steer the formation CO2. These noble metal loaded catalysts exhibit a strong synergy between the different metal components and thereby acquire enhanced catalytic properties.

References