Qiang Fang‡
a,
Hailian Li‡a,
Qingquan Lin*a,
Kuo Liu*b,
Yang Suc,
Guodong Huoa,
Xuhua Zoua,
Xiufeng Xua,
Haisheng Weia and
Shixue Qi*a
aInstitute of Applied Catalysis, College of Chemistry and Chemical Engineering, Yantai University, Yantai 264005, China. E-mail: Tsqlin@ytu.edu.cn; Qishixue@ytu.edu.cn
bResearch Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China. E-mail: kuoliu@rcees.ac.cn
cDalian National Laboratory for Clean Energy, Dalian Institute of Chemical Physics, Chinese Academy of Sciences, Dalian 116023, China
First published on 16th June 2020
Gold nanoparticles have a high activity for CO oxidation, making them suitable to be used in a CO2 laser which maintains its efficiency and stability via the recombination of CO and O2 produced by the CO2 decomposition. However, the high concentration of CO2 in the working environment greatly reduces the activity of the catalyst and makes the already unstable gold nanoparticles even more so. A novel Au/Ce-Co-Ox/Al2O3 gold catalyst, prepared by a deposition precipitation method in this study, displays high activity and good stability for CO oxidation in a simulated atmosphere of a CO2 laser with the feed gases containing a high concentration of CO2 up to 60 vol% but a low concentration of O2 for the stoichiometric reaction with CO. An excellent performance for CO oxidation under CO2-rich conditions could be achieved by decorating the surface of the Al2O3 support with Ce–Co composite oxides. The strong interaction between gold and the composite support, accompanied by the increase of labile lattice oxygen species and the decrease of surface basicity, led to a high CO oxidation rate and resistance towards CO2 poisoning.
Over the past decades, various platinum group metal (PGM) catalysts for CO oxidation have been widely developed.5,13 In particular, because gold (Au) nanoparticles (NPs) were discovered, showing excellent catalytic performance towards CO oxidation even at very low temperatures, Au-based catalysts have been extensively and systematically investigated.14,15 When compared with PGM catalysts, Au catalysts have the advantages of a higher catalytic activity for CO oxidation, a wider working temperature range, abundant reserves and less price fluctuation, and thus, Au catalysts became promising catalysts for CO oxidation.9,16 Many researchers investigated the effect of a small amount of CO2 on the performance of the used Au catalysts and found the prepared catalysts had some resistance to CO2 poisoning in the CO-PROX catalysts.17–20 However, little attention has been paid to the effect of high concentration of CO2 and few Au catalysts can be utilized well in atmospheres with high concentrations of CO2.21 Therefore, it is necessary to study the characteristics and behaviour of Au catalysts in the feed gases containing a high concentration of CO2.7,21 Also, investigation of the behaviour and characteristics of the Au-based catalysts under CO2-rich conditions can help with the fundamental understanding of the Au catalysts.
In order to design a stable Au catalyst under a high concentration of CO2, acidic supports were firstly considered because less carbonate species may be formed on the surface of them22,23 and alumina is a suitable material for this. However, alumina supported Au NPs (Au/Al2O3) have long been considered to have a relatively low catalytic activity, because Al2O3 is an inert carrier, unlike TiO2 and other reducible carriers which are active, despite its large specific surface area and high thermal stability.24 Fortunately, a series of active Au catalysts has been prepared by doping metal oxides on the surface of the alumina to increase the surface oxygen species on the catalyst surface and thus significantly improving the catalytic activity for the CO oxidation in an O2-rich atmosphere.7,22,23 Hedge and co-workers found that the oxygen storage materials (OSM) could be good dopants which they applied for Pd catalysts and highly improved the reaction rates of CO oxidation.25,26
Based on the reasons discussed previously, in order to improve catalytic activities and stability of the alumina supported Au catalysts for CO oxidation in the simulated CO2-rich atmosphere of the CO2 laser, firstly the surface of the alumina was decorated with the Ce–Co composite oxygen storage oxides, and a novel Au/Ce-Co-Ox/Al2O3 catalyst was designed using a deposition precipitation method, which improved the strong interaction between the Au and the support, and meanwhile the labile oxygen species increased and the basicity on the surface of the support decreased. Finally, after being decorated, the prepared Au/Ce-Co-Ox/Al2O3 catalyst showed a much superior performance for the reaction of CO oxidation in the simulated atmospheres of the CO2 laser containing a low concentration of O2 (0.5 vol%) and a high concentration of CO2 (as high as 60 vol%). Experimental and characterization results showed that the added lattice oxygen species and less strongly alkaline site of the decorated Au/Ce-Co-Ox/Al2O3 catalyst both played a crucial role in achieving high activity and good stability.
An Au/Al2O3 catalyst was also prepared using the same procedure, but the pH value was adjusted to 10, in order to obtain slightly larger Au NPs.
The reaction rate was tested with a gas flow of 200 mL min−1, and the gas compositions and reaction temperature were exactly the same as those shown previously. A portion (0.01 g) of catalyst and 0.09 g of diluent (Al2O3) were loaded into the reaction tube. The CO content was determined by a gas chromatography.
A Thermo Scientific IRIS Intrepid II ICP was used to determine the content of Au in the catalyst. A portion (0.1 g) of sample was put into a beaker, and the Au on the surface of the catalyst was soaked with aqua regia solution. Then the Au was washed with deionized water, and the eluent was transferred into a volumetric flask.
Transmission electron microscopy (TEM) images were recorded using a Hitachi 7700 microscope operated at 120 kV. Prior to making the observations, the catalysts were pretreated with H2 or air at 300 °C for 1 h and then suspended in ethanol with ultrasonic dispersion for >10 min. One or two droplets of the dispersed solution were dropped on a microgrid carbon polymer supported on a copper grid. By measuring 300 particles from randomly selected areas, the particle size distribution was acquired.
High-angle annular dark-field scanning transmission electron microscopy (HAADF-STEM) was be used to determine the particle size of the Au. A FEI Tecnai G2 F30 S-Twin field emission transmission electron microscope with an acceleration voltage of 300 kV was also used. Prior to the observations, the powder catalysts were collected after peeling off the outside of the samples (a physical method that does not change the nanoparticle size of Au but could increase the content of it in order to easily observe more Au particles). Then, the samples were finely ground in an agate mortar and subsequently dispersed ultrasonically in ethanol for 5 min. After a period of time, 1–2 drops of the supernatant were dropped on to the micro grid, followed by drying.
Oxygen temperature programming desorption (O2-TPD) was evaluated using an automatic PCA-1200 chemisorption analyzer. A portion (100 mg) of the dried sample was reduced with H2 (30 mL min−1) at 300 °C for 1 h. After cooling to room temperature, the catalyst was purged with He (20 mL min−1) for 20 min, and then with O2 (20 mL min−1) for 30 min to absorb the O2. The heating rate was 10 °C min−1.
Hydrogen temperature-programmed reduction (H2-TPR) was conducted using an automatic PCA-1200 Chemisorption analyzer. The catalysts were firstly purged with N2 (30 mL min−1) at 120 °C for 30 min. After cooling to room temperature, 10 vol% H2/Ar (20 mL min−1) was introduced onto the surface of the catalysts, and the temperature was increased to 900 °C at 10 °C min−1. The H2 consumption was monitored by a TCD detector.
Carbon dioxide temperature programming desorption (CO2-TPD) was evaluated using an automatic PCA-1200 chemisorption analyzer. At first, 100 mg of dried sample was reduced with H2 (30 mL min−1) at 300 °C for 1 h. After cooling to room temperature, the catalyst was purged with He (20 mL min−1) for 20 min, and then with CO2 (20 mL min−1) for 30 min to absorb the CO2. The heating rate was 10 °C min−1.
Fig. 1a shows the profiles of CO conversions as a function of reaction time over the Au/Al2O3 and Au/Ce-Co-Ox/Al2O3 catalysts in a simulated CO2-rich atmosphere of a high-frequency CO2 laser at the usual working temperature of 220 °C and a high space velocity of 120000 mL gcat−1 h−1 in order to accelerate the deactivation of catalyst and compare their performances. Considering the big changes of the two curves, a significant effect of the type of support used is easily observed. As shown in Fig. 1a, the Au/Al2O3 catalyst had a very low activity for this reaction which was reflected by the following phenomenon. The Au/Al2O3 catalyst only gave a CO conversion of approximately 35% at the start of reaction and the CO conversion decreased slowly as the reaction time was extended, and the remaining CO conversion was maintained at only 15%, about half of the original activity after nearly 1500 min of testing. However, on the Au/Ce-Co-Ox/Al2O3 catalyst, at the beginning of CO oxidation, the CO conversion reached as high as 78%, 2.2 times that of the unmodified Au/Al2O3 catalyst. After a long time of activity test, a conversion of approximately 55% over Au/Ce-Co-Ox/Al2O3 was maintained, corresponding to a retention of 70% of the original activity and 3.7 times higher than that of the Au/Al2O3 catalyst. In addition, a well-known active and stable reducible oxide supported Au catalyst (1 wt% Au/Fe2O3–HgI) synthesized by Haruta's laboratory and obtained from Haruta Gold Inc., was compared with our Au catalyst. As shown in Fig. 1a (inset), the Au/Fe2O3–HgI catalyst had a very high initial activity, but suffered from a faster deactivation. Under the same conditions, although the initial activity of our Au/Ce-Co-Ox/Al2O3 catalyst was slightly lower than that of Au/Fe2O3–HgI, the Au/Ce-Co-Ox/Al2O3 catalyst obviously lost its activity much more slowly. After 50 min, the CO conversion over Au/Ce-Co-Ox/Al2O3 became higher than that over 1 wt% Au/Fe2O3–HgI, demonstrating that a much better stability was found on Au/Ce-Co-Ox/Al2O3.
Further investigation of the intrinsic catalytic activity was made by means of the specific reaction rates of the two catalysts (Fig. 1b). The specific reaction rate over Au/Ce-Co-Ox/Al2O3 was more superior to that on the Au/Al2O3 catalyst and this was consistent with the results of the CO conversion method mentioned previously. The reaction rate over Au/Ce-Co-Ox/Al2O3 catalyst was calculated to be 0.22 molCO molAu−1 s−1 when the test was started, and it was 3.8 times that of Au/Al2O3 catalyst (0.057 molCO molAu−1 s−1). When the reaction had proceeded for 150 min, a more striking observation was that the reaction rate of the Au/Ce-Co-Ox/Al2O3 catalyst had reached 0.16 molCO molAu−1 s−1, which was nearly 6 times that of the Au/Al2O3 catalyst (0.025 molCO molAu−1 s−1). Thus, it was further confirmed that co-decoration of Al2O3 by CeOx and CoOx had a significant promotional effect on the catalytic performance of the alumina-based Au catalysts.
The activity of CO oxidation on the Au/Ce-Co-Ox/Al2O3 and Au/Al2O3 catalysts in the feed gases with or without CO2 was studied (Fig. S1, ESI†). At a very high space velocity of 120000 mL gcat−1 h−1, the CO conversion over the Au/Al2O3 catalyst decreased from 48% (no CO2 in the feed gases) to 36% (60 vol% CO2 in the feed gases) at the start of reaction, and then the CO conversion quickly decreased by nearly half to 20% as the reaction time progressed. However, on the Au/Ce-Co-Ox/Al2O3 catalyst, it is interesting that the CO conversions were both very high, reaching as high as 82% (no CO2 in the feed gases) and 78% (60 vol% CO2 in the gas feed) at the beginning of the CO oxidation. In order to show the promotional effect of CeCoOx on the stability in a CO2-rich atmosphere, ratios of CO conversion in the CO2 rich atmosphere (60 vol% CO2) to that in the atmosphere without CO2 (0 vol% CO2) over Au/Ce-Co-Ox/Al2O3 and Au/Al2O3 were calculated (Fig. 2). Compared with Au/Al2O3, Au/Ce-Co-Ox/Al2O3 had a higher ratio, indicating that Au/Ce-Co-Ox/Al2O3 exhibited a better tolerance to high concentrations of CO2. Similarly, the reaction rates over the Au/Al2O3 and Au/Ce-Co-Ox/Al2O3 catalysts almost showed the same trend, as shown in Fig. S2 (ESI).† Meanwhile, compared with the reaction rate obtained in the atmosphere without CO2, the reaction rate of CO oxidation over Au/Ce-Co-Ox/Al2O3 maintained one-half or more (0.22 vs. 0.42 molCO molAu−1 s−1) when reacted in a CO2-rich atmosphere, which further indicated that the decoration of CeOx and CoOx had indeed improved the catalytic activity of CO oxidation.
Fig. 2 Ratios of CO conversion in the CO2 rich atmosphere to that in the atmosphere without CO2 on the Au/Ce-Co-Ox/Al2O3 and Au/Al2O3 catalysts. |
In addition, the CO conversions on Au/Ce-Co-Ox/Al2O3, Au/CeOx/Al2O3 and Au/CoOx/Al2O3 were also obtained at a space velocity of 120000 mL gcat−1 h−1, and the results are shown in Fig. 3. The Au/CeOx/Al2O3 catalysts had a higher original activity, which was about twice that on the Au/CoOx/Al2O3 catalyst, which may be due to the lower Au loading of Au/CoOx/Al2O3. Furthermore, the Au/Ce-Co-Ox/Al2O3 catalyst not only had a high original activity, but also possessed better reaction stability than that on Au/CeOx/Al2O3 during CO oxidation. Therefore, co-decoration with CeOx and CoOx could promote the stability of CO oxidation in a CO2-rich atmosphere and it is important to clarify the promotional principle.
Fig. 4 XRD diffraction patterns of Al2O3 (a), Au/Al2O3 (b), Ce-Co-Ox/Al2O3 (c) and Au/Ce-Co-Ox/Al2O3 (d). |
In order to confirm the conclusions given previously, TEM was conducted. As shown in Fig. 5, the Au NPs were both well dispersed on the surface of Au/Al2O3 and Au/Ce-Co-Ox/Al2O3 catalysts with a mean particle size of (3.0 ± 0.5) nm and (3.3 ± 0.5) nm, respectively. It has been reported by many researchers that the diameter of the Au particle could affect the CO oxidation activity, and the optimum particle size of Au might be in the range of 0.5–5 nm.28 The Au particle size in this study was within this range, guaranteeing a high CO oxidation rate. In order to further verify the dispersion of Au particles in the Au/Ce-Co-Ox/Al2O3 catalyst, HADDF-STEM was also conducted. As shown in Fig. 5e, the bright spot represents Au NPs, whereas the large pale white patch is Ce-Co-Ox, indicating that most of the Au NPs were attached to the surface of Ce-Co-Ox. A uniform special distribution of the Au, Ce and Co elements can also be observed from the results of the energy dispersive spectrometry (EDS) mapping of the HAADF-STEM image (Fig. 6). The spectra of energy dispersive X-ray spectroscopy (EDX) line scan demonstrated a similar distribution of the Au, Ce and Co elements along one particle (Fig. S3, ESI†), indicative of their close contact. The close contact between Au NPs and Ce-Co-Ox can lead to a strong interaction between Au and Ce-Co-Ox,29,30 thus benefiting the CO oxidation.
Fig. 5 The TEM images of the Au/Al2O3 (a) and Au/Ce-Co-Ox/Al2O3 catalysts (b) with their Au particle size distributions (c and d) and HADDF-STEM image of the Au/Ce-Co-Ox/Al2O3 catalyst (e). |
The difference in the mean particle sizes of the two catalysts was insignificant, which might not be the main reason for the different CO oxidation activity and stability. Thus, it can be proposed that the Au/Ce-Co-Ox/Al2O3 had a much higher reactivity for the SMSI between Au and the Ce-Co-Ox/Al2O3 composite support, and the chemical properties of Ce-Co-Ox composite oxides were likely to benefit the CO oxidation reaction.
It has been reported previously by many researchers that the adsorbed oxygen can directly combine with CO on the catalyst to produce CO2 over Au/Al2O3, and its lattice oxygen cannot participate in this reaction.33,34 However, Widmann and Behm35,36 reported that the lattice oxygen on the reducible support surface could participate in CO oxidation and oxygen vacancies could be formed. Then, the adsorbed oxygen will replace the oxygen vacancy and form a new cycle.35–38 The conclusion that the lattice oxygen species of CeOx and CoOx can participate in CO oxidation was also confirmed by the 18O isotope labelling experiment conducted by Madier et al.39 and Amin et al.40 Therefore, it could be inferred that both the adsorbed and lattice oxygen species contributed to CO oxidation in this study.
The previous results were verified by the H2-TPR. As shown in Fig. 8, two H2 consumption peaks at 196 °C and 792 °C were observed over Au/Al2O3, and ascribed to the reduction of Au species and the lattice oxygen of Al2O3, respectively. When Al2O3 was decorated with CeOx and CoOx, three peaks were observed, which can be assigned to the reduction of CoOx (283–483 °C), CeOx (483–572 °C),1,2 and lattice oxygen of Al2O3 (675 °C) possibly due to the H2 spill over from CoOx or CeOx, respectively. After Au was deposited on the Co-Ox/Al2O3 composite support, the reduction peaks of the Au species, CoOx, CeOx and Al2O3 all shifted to lower temperatures (98 °C, or 98–165 °C for the overlap of the reduction peak of partial Au species), demonstrating that the SMSI between Au and the composite support was increased. It was clearly observed that after co-decoration and Au loading, more labile oxygen species were generated. The labile oxygen species were important for improving the reaction rate on catalysts for CO oxidation, for example, on Ce-Co-O.35–40 A synergistic effect in the CeO2 and Co3O4 compound was found by Luo et al.37 in the Ce-Co-O catalyst, resulting in a better activity of the CO oxidation. Thus, it can be inferred that the synergistic effect was also present in our catalyst, increasing the amount of labile oxygen species. In general, the more oxygen species adsorbed by the Au NPs, the more labile lattice oxygen species there were on the surface of the support, jointly promoting the catalytic activity on the Au/Ce-Co-Ox/Al2O3 catalyst. Therefore, the Au/Ce-Co-Ox/Al2O3 catalyst was greatly improved due to the increase of the number of labile oxygen species.
Fig. 10 The CO oxidation specific rates (a) and the mechanism on Au/Ce-Co-Ox/Al2O3 (b) and Au/Al2O3 (c). |
Footnotes |
† Electronic supplementary information (ESI) available: The equation for calculating the reaction rate, and the characterization data of physical properties, HADDF-STEM & EDX. See DOI: 10.1039/d0ra03558k |
‡ These authors contributed equally to this work. |
This journal is © The Royal Society of Chemistry 2020 |