NiCe bimetallic nanoparticles embedded in hexagonal mesoporous silica (HMS) for reverse water gas shift reaction

Hui Dai Siqi Xiong Yongqing Zhu Jian Zheng Lihong Huang Changjian Zhou Jie Deng Xinfeng Zhang

Citation:  Hui Dai, Siqi Xiong, Yongqing Zhu, Jian Zheng, Lihong Huang, Changjian Zhou, Jie Deng, Xinfeng Zhang. NiCe bimetallic nanoparticles embedded in hexagonal mesoporous silica (HMS) for reverse water gas shift reaction[J]. Chinese Chemical Letters, 2022, 33(5): 2590-2594. doi: 10.1016/j.cclet.2021.08.129 shu

NiCe bimetallic nanoparticles embedded in hexagonal mesoporous silica (HMS) for reverse water gas shift reaction

English

  • Since 1950, the concentration of CO2 attributed to human activities has risen by 30% [1]. CO2 emissions directly cause global warming, projecting the global average temperatures to rise by about 1.5-4.5 ℃ by 2050 if left unchecked. Moreover, the burning of fossil fuels and excessive deforestation trigger global warming. The capture, utilization, and transformation of CO2 into other energy sources is a potential approach to addressing the menace. The improvement of chemical processes aimed at reducing CO2 emission is a highly effective strategy. In the past year, many countries have unanimously declared that their economies will be carbon-neutral. The CO2 transformation to other energy sources reduces CO2 emissions and alleviates energy shortages [2].

    CO2 is a thermodynamically and kinetically stable molecule, making it harder to lose electrons and form CO2+, while easier to accept electrons and convert C=O bond into C–O bond. Therefore, addition reactions are more likely to occur [3]. For instance, H2 reacts with CO2 to form hydrocarbons, i.e., CO2 hydrogenation reduction. One useful reaction is reverse water gas shift (RWGS), which produces CO, a main C1 chemical raw material that can be converted into other high-value products [4]. Meanwhile, this process is accompanied by other side reactions, including over hydrogenation to generate methane [5, 6]. RWGS is a major factor influencing CO selectivity in RWGS reaction, where the activation of CO2 requires significant energy. RWGS reaction is typically processed at high temperature (e.g., > 500 ℃), requiring high thermal stability of the used catalyst. For this reaction, noble metals including Pt [7], Pd [8], Rh [9] and Au [10] were applied as catalytic active sites and exhibited excellent performance. Nonetheless, these metals are found in relatively low quantities on earth and at relatively high prices, making them difficult for industrial use. Therefore, research and development of non-precious metals including Cu [11-13] and Ni [14-17] are essential. In recent years, RWGS reactions have widely used Cu-based catalysts, as a substitute for noble metal catalysts. Supported Cu catalysts suffered from low stability in this reaction. For example, the surface area of Cu/SiO2 was significantly reduced after a long-time reaction due to the sintering of the activity components [18]. In contrast with single metal Cu, Ni exhibits better thermal stability for long-term reaction [19-21]. Nevertheless, Ni faces the drawbacks of coke deposition and deactivation. Lu et al. [22] observed different forms of NiO particles for the NiO/SBA-15 catalysts, only separated single NiO particles improved CO selectivity. Methanation seemingly occurs in aggregated NiO species at lower reaction temperature. Therefore, highly dispersed active Ni particles promotes higher CO selectivity.

    Rare earth metal oxide CeO2 as a promoter regulates many reactions due to its redox properties. In the case of dry reforming of methane reaction, the metal support interaction between NiO and ZSM-5 is enhanced by adding Ce as a promoter, which has positive to the catalytic activity [23]. Catalysts prepared with different morphologies of CeO2 as support loaded with Cu have been applied for RWGS, where the amount of surface oxygen vacancies and Cu0 after reduction by H2 increased. The rate of catalytic reaction corresponded with the amount of surface oxygen vacancies for CeO2, participating in CO2 adsorption and activation [24]. The insertion of transition metal like Ni into CeO2 lattice to form Ce–O–Ni solid solution prevents the production of byproduct CH4 [25], however, bulk phase NiO existing in Ni/CeO2 is the active center for synthesis of CH4 [26]. Therefore, the high dispersion of Ni nanoparticles causes higher selectivity of CO [27].

    SiO2 mesoporous materials like MCM-41, SBA-15 and hexagonal mesoporous silica (HMS) have drawn significant attention due to their merits including large specific surface area, uniform pore size, and excellent stability, and have been widely used as support in catalysts [28-30]. Among them, HMS with wormhole framework structure incorporates metal into its thick framework wall through neutral amine surfactant and inorganic precursors [31], which is beneficial for the diffusivity of chemical species. Moreover, HMS demonstrated a better thermal stability compared to MCM-41 and SBA-15 [32], also, metals can be uniformly embedded in the HMS skeleton [33-36]. Wang et al. synthesized Ni-HMS catalyst using an in-situ one-step process, which could perform long-term test at 700 ℃ in dry reforming of methane for 100 h without significant reduction due to the high dispersion of Ni active sites on support [37]. Sn-HMS catalyst was prepared by a similar method for propane dehydrogenation reaction and remained stable for 170 h after three times of regeneration [38].

    This study introduced a timesaving, easy-handling, and energy-saving method for the preparation and characterization of nickel-based catalysts and for the first time, described its application in RWGS reaction. The Ni-HMS and NiCe-HMS were prepared using HMS as support to investigate the influence of reaction temperature from 500 ℃ to 750 ℃ for their catalytic performance in RWGS reaction. Further, a series of catalyst characterizations were conducted to better understand the structure and composition of the catalysts as well as explain their catalytic activity. We purposed to prepare a type of RWGS catalyst with effective CO selectivity and better stability using a simple and easy operation method.

    The pore structures of three catalysts were investigated by N2 adsorption-desorption at 77 K (Fig. S1a in Supporting information). For Ni-HMS and Ni/HMS samples, a relative pressure range of 0.3–0.5 suggested a Type Ⅳ isotherm [39]. For Ni-HMS, the hysteresis loops illustrated that it primarily has a 1D cylindrical channel of uniform mesoporous [37]. Nevertheless, after adding Ce into the HMS structure, the hysteresis loop area was reduced and no clear vertical asymptote displayed a Type Ⅰisotherm, which could be attributed to the certain pores of the were loaded by Ce species [40]. Combined with pore size distribution curves (Fig. S1b in Supporting information), the pore diameter was concentrated between 2–5 nm on mesoporous. Among the three catalysts, the Ni/HMS exhibited the largest surface area 782 m2/g, pore-volume 0.87 cm3/g, and diameter 3.5 nm. These physical data were reduced when Ni or Ce nanoparticles were embedded into the structure of HMS, due to the fact that the incorporation of Ni and Ce into the HMS framework occupied a part of the surface structure.

    TEM characterization was conducted on the samples to analyze the nanoparticle distribution of catalysts from the microstructure. The results are shown in Fig. 1. HMS supported presents the wormhole-like framework. Ni-HMS and NiCe-HMS catalysts show the metal oxide particles ordered insert into the hexagonal framework. For Ni/HMS catalyst, the NiO particles were distributed on the surface of HMS by counting the diameter of NiO particles ranging between 3 nm and 12 nm. Combined with the actual content of Ni tested by ICP-OES shown in Table 1, Ni/HMS the content was low while the grain was large. This accounts for the most of NiO particles distributed out of the pore. The average particle size of the three catalysts ranged from large to small, i.e., Ni/HMS (7.1 ± 0.2 nm) > NiCe-HMS (6.7 ± 0.2 nm) > Ni-HMS (6.5 ± 0.2 nm). Ni/HMS unlike the other two had a weak metal-support interaction. As for NiCe-HMS, NiO and CeO2 nanoparticles co-existed on support, while the average particle size was calculated by all the particles. EDX mapping analysis was used to confirm the successful addition of Ce into NiCe-HMS catalyst (Fig. S2 in Supporting information). In NiCe-HMS, Ni and Ce were highly dispersed on the carrier HMS, suggesting that the introduction of Ce enhanced the dispersion of Ni and thus showed a significant structural advantage.

    Figure 1

    Figure 1.  TEM images and nickel particle size distribution of the samples.

    Table 1

    Table 1.  Physicochemical properties of the catalysts
    DownLoad: CSV

    Characterization of the catalyst were performed by XRD (Fig. 2a), and the typical peak at 22.9° was associated with supported HMS crystalline phase (JCPDS No. 49-0623), which exists in three catalysts. In addition, others three peaks were belong to the (111), (200) and (220) crystal face of metal Ni, respectively (JCPDS No. 04-0850) [41]. For Ni-HMS and Ni/HMS, these peaks are relatively sharp, indicating that Ni species are relatively non-uniform and exhibit as larger particles. Combined with the actual content of Ni tested by ICP-OES showed in Table 1, the sharpest diffraction peak of Ni/HMS was found to have the smallest Ni loading of 3.3 wt%, illustrating that Ni nanoparticles are not well dispersed into the supported channel. The peak intensity of Ni-HMS with higher Ni content was obviously lower, indicating that the different preparation methods would directly influence dispersion of the active species. In contrast, NiCe-HMS had the highest loading of 4.43 wt%, while the diffraction peak was not obvious. Only Ni diffraction peak and no diffraction peak ascribed to the Ce metal was found, implying that Ce might increase the dispersion of Ni nanoparticles. All of the above results provide a good support for TEM observation.

    Figure 2

    Figure 2.  XRD partten (a) for the reduced catalysts and H2-TPR (b) profiles of the fresh catalysts.

    H2-TPR test was used to explore the interaction between metal oxides and support (Fig. 2b). By comparing all the three samples, the peak area of Ni/HMS was the highest. Combined with the previous analysis, the metal nanoparticles of the other two catalysts were partially embedded into the wall of support, causing a reduction of only a fraction of metal oxides. The reduction peaks of Ni-HMS and Ni/HMS exhibited similar temperature ranges, but different peak areas. The peak centered around 250 ℃ and 350 ℃ attributed the reduced surface of isolated bulk NiO particles and weak interacted with support, defined as α, β, respectively[41]. The higher reduction peak range was represented as γ, ascribed to the reduction of NiO on the wall subsurface[37]. In contrast with Ni-HMS and NiCe-HMS, the reduction temperature of Ni/HMS was relatively lower and intensity was relatively higher, deducing that the preparation method affects the interaction between the Ni and carrier [42]. For NiCe-HMS catalyst, reduced peak at 344 ℃ peak sharpness, attributed to NiO in close contact with CeO2 and the chemisorbed oxygen in the oxygen vacancies of CeO2 [43]. 500 ℃-600 ℃ had the wide and lower intense reduction peaks, which belong to the simultaneous reduction of NiOx and surface CeO2 [44]. These two types of species were also the active sites of CO2. The high reduced temperature was ascribed to the reduction of metal particles embedded in mesoporous carriers [45]. Therefore, the in-situ preparation method enhances the interaction between the active phase and support. The addition of Ce maintains the dispersibility of active metals, with lots of NiO distributed close to CeO2 existing in the interface between Ni-Ce.

    All the catalysts were applied in the RWGS reaction at the temperature range of between 500 ℃ and 750 ℃. Fig. 3 shows the conversion of CO2, selectivity of CO and CH4 as a function of reaction temperature. Unlike NiCe-HMS, other catalysts revealed relatively poor catalytic performance in CO2 conversion. Chen et al. [46], noted that the bare CeO2 catalyst participates in CO2 transformation in RWGS reaction, meanwhile they produced CO from the surface oxygen vacancies, causing a satisfactory catalytic performance of NiCe-HMS. Ni-HMS exhibits a CO2 conversion of 3.7% in 500 ℃, apparently higher than Ni/HMS. However, with increased temperature, CO2 conversion of Ni/HMS was higher than Ni-HMS, suggesting that Ni/HMS exposed more Ni particles. For Ni-HMS, it had the highest CO selectivity of up to 99.9% among the three catalysts, benefiting from the in-situ preparation method that triggers uniform dispersion of Ni nanoparticles. The RWGS reaction was applied as an endothermic reaction, more favorable to enhance CO selectivity with the increase of reaction temperature. All the catalysts reached CO selectivity of 99.3% at approximately 750 ℃. In contrast, the CO selectivity of Ni/HMS was low because the bulk Ni particles readily produced CH4 [47]. Conclusively, Ni-based catalyst prepared by the in-situ method exhibited a higher CO selectivity than conventional prepared catalyst. Meanwhile, adding Ce increased CO2 conversion. In combination with TPR, higher CO2 conversion was ascribed to the neighboring oxygen vacancies forming the interface of Ni and Ce, active sites for CO2 hydrogenation [48]. A high dispersion of nanoparticles of NiCe-HMS increased the activity oxygen vacancies improving the efficiency in the RWGS reaction [48].

    Figure 3

    Figure 3.  Catalytic activity of three catalysts applied to RWGS: (a) CO2 conversion; (b) CO selectivity; (c) CH4 selectivity.

    The XPS in Fig. 4a demonstrates the chemical states of Ni 2p for NiCe-HMS and Ni-HMS. Three peaks of Ni species were reported and the two lower binding energy represented different environments of surface Ni species. Binding energy around 854 eV consistent Ni(Ⅱ)* species represented the bigger NiO particles. Binding energy at 856.9 eV defined as Ni(Ⅱ), which was the presence of NiO highly dispersed on the support surface, created higher metal-support interaction. The other broad peak was the shakeup satellite peak [49]. Unlike the first two peaks intensity, Ni(Ⅱ)* for Ni-HMS was significantly more than NiCe-HMS catalyst. Combined with the previous characterization analysis, this result once again confirmed that the doped Ce reduced the particle size of the active component. Meanwhile, it had better metal support interaction compared to the intensity of Ni(Ⅱ).

    Figure 4

    Figure 4.  (a) Ni 2p XPS spectra of fresh catalysts NiCe-HMS and Ni-HMS. (b) EPR spectra of reduced catalysts Ni-HMS and NiCe-HMS.

    EPR test was employed to further confirm the existence of oxygen vacancy. As shown in Fig. 4b, at about g = 2.0, sample NiCe-HMS shows a higher EPR signal than sample Ni-HMS, which is a typical signal of oxygen vacancy (OVs) [50]. The existence of oxygen vacancy prevents forming Lewis basic position, which may strongly adsorb and activate gaseous CO2 and enhance the catalytic activity of RWGS. Which results also verified by CO2-TPD (Fig. S3 in Supporting information).

    Effect of feed ratio on the catalytic activity, CO selectivity, and CH4 selectivity were investigated on NiCe-HMS at 500–750 ℃, and the results are shown in Figs. 5a–c. As shown, with the increase of H2/CO2 molar ratio from 1 to 4, CO2 conversion increased, while CO selectivity decreased while CH4 selectivity increased, specifically at lower reaction temperature [51], meanwhile, the CO2 conversion was close to equilibrium. Ni demonstrated a better H2 dissociation activity, when the H2 feed ratio increased, a higher CH4 formed specifically in 500 ℃ [52]. The NiCe-HMS catalyst exhibited a high activity in RWGS with CO yield of up to 35.3% at a ratio of H2/CO2 = 1, with a ratio of H2/CO2 = 4 CO yield rising to 74.4% at 700 ℃. Therefore, higher CO selectivity fed gas H2/CO2 of 1, while, higher CO2 conversion preferred the H2/CO2 of 4. In order to demonstrate the stability of NiCe-HMS catalyst, it was used in reverse water gas shift reaction at 750 ℃ for 28 h. As shown in Fig. 5d, the stability maintains well, albeit with high activity and stability for a long time. The conversion of CO2 and selectivity of CO maintains stable, which can be attributed to the good thermal stability and resistance to carbon deposition of NiCe-HMS catalyst. Therefore, the NiCe-HMS catalyst may be a promising candidate for industrial application in the future.

    Figure 5

    Figure 5.  Catalytic activity of catalyst NiCe-HMS applied to RWGS at different inlet ratios: (a) CO2 conversion; (b) CO selectivity; (c) CH4 selectivity; (d) The catalytic activity of NiCe-HMS for 28 h at 750 ℃.

    In conclusion, NiCe-HMS and Ni-HMS were prepared by one-pot in-situ route and applied in RWGS reaction at the temperature range of 500-750 ℃. The selectivity to CO on these samples was significantly enhanced compared to conventionally impregnated Ni-HMS. This benefited from the highly dispersed Ni nanoparticles formed on the surface of the support, inhibiting the generation of CH4. In contrast with Ni-HMS, after adding Ce, the conversion of CO2 increased due to the large amount of NiO nanoparticles existing close to CeO2. And a high dispersed Ni and Ce nanoparticles interface formed more active oxygen vacancies and efficient reaction sites for CO2 hydrogenation. The catalysts prepared by the one-pot in-situ method outperformed those prepared by the traditional impregnation method. When the ratio of H2/CO2 = 4, the conversion of CO2 was close to the equilibrium. Our findings provide a promising strategy for the development of a bimetal catalyst system in RWGS.

    There are no conflicts to declare.

    The authors thank to the Chengdu University of Technology Teachers Development Research Fund (No. 10912-2019KYQD07266) and National Natural Science Foundation of China (No. 21806015) for financial support.

    Supplementary material associated with this article can be found, in the online version, at doi:10.1016/j.cclet.2021.08.129.


    1. [1]

      N. Charisiou, G. Siakavelas, L. Tzounis, et al., Int. J. Hydrogen Energy 43 (2018) 18955-18976 doi: 10.1016/j.ijhydene.2018.08.074

    2. [2]

      Y.H. Wu, Q. Chen, S. Liu, et al., Chin. Chem. Lett. 30 (2019) 2186-2190 doi: 10.1016/j.cclet.2019.08.014

    3. [3]

      G. Zhou, B. Dai, H. Xie, et al., J. CO2 Utilization 21 (2017) 292-301 doi: 10.1016/j.jcou.2017.07.004

    4. [4]

      H. Yang, C. Zhang, P. Gao, et al., Catal. Sci. Technol. 7 (2017) 4580-4598 doi: 10.1039/C7CY01403A

    5. [5]

      Y. Wang, H. Arandiyan, S.A. Bartlett, et al., Appl. Catal. B: Environ. 277 (2020) 119029 doi: 10.1016/j.apcatb.2020.119029

    6. [6]

      Y.H. Dai, M. Xu, Q.J. Wang, et al., Appl. Catal. B: Environ. 277 (2020) 119271 doi: 10.1016/j.apcatb.2020.119271

    7. [7]

      S.M. Lee, H. Eom, S.S. Kim, Environ. Technol. 40 (2019) 182–192. doi: 10.1080/09593330.2017.1384070

    8. [8]

      F.C. Meunier, D. Tibiletti, A. Goguet, D. Reid, R. Burch, Appl. Catal. A: Gen. 289 (2005) 104-112 doi: 10.1016/j.apcata.2005.04.018

    9. [9]

      M. Maestri, K. Reuter, Chem. Eng. Sci. 74 (2012) 296-299 doi: 10.1016/j.ces.2012.02.043

    10. [10]

      A.A. Upadhye, I. Ro, X. Zeng, et al., Catal. Sci. Technol. 5 (2015) 2590-2601 doi: 10.1039/C4CY01183J

    11. [11]

      X. Hu, X.S. Hu, Q.X. Guan, et al., Sustain. Energy Fuels 4 (2020) 2937-2949 doi: 10.1039/d0se00147c

    12. [12]

      C.A. Galvan, J. Schumann, M. Behrens, et al., Appl. Catal. B: Environ. 195 (2016) 104-111 doi: 10.1016/j.apcatb.2016.05.007

    13. [13]

      Q. Zhang, L. Pastor-Perez, W. Jin, et al., Appl. Catal. B: Environ. 244 (2019) 889-898 doi: 10.1016/j.apcatb.2018.12.023

    14. [14]

      J.X. Chen, Q.W. Long, K. Xiao, et al., Sci. Bull. 66 (2021) 1063-1072 doi: 10.1109/tcpmt.2021.3084966

    15. [15]

      B. Dong, J.Y. Xie, Z. Tong, et al., Chin. J. Catal. 41 (2020) 1782-1789 doi: 10.1016/S1872-2067(20)63621-X

    16. [16]

      L.L. Zeng, L.J. Yang, J. Lu, et al., Chin. Chem. Lett. 29 (2018) 1875-1878 doi: 10.1016/j.cclet.2018.10.026

    17. [17]

      X.D. Zhang, K. Liu, J.W. Fu, et al., Front. Phys. Beijing 16 (2021) 63500 doi: 10.1007/s11467-021-1079-4

    18. [18]

      C.S. Chen, W.H. Cheng, S.S. Lin, Chem. Commun. (2001) 1770-1771

    19. [19]

      A. Ranjbar, A. Irankhah, S.F. Aghamiri, Res. Chem. Int. 45 (2019) 5125-5141 doi: 10.1007/s11164-019-03905-1

    20. [20]

      F.M. Sun, C.F. Yan, Z.D. Wang, C.Q. Guo, S.L. Huang, Int. J. Hydrogen Energy 40 (2015) 15985-15993 doi: 10.1016/j.ijhydene.2015.10.004

    21. [21]

      L. Yang, L. Pastor-Perez, S. Gu, A. Sepulveda-Escribano, T.R. Reina, Appl. Catal. B: Environ. 232 (2018) 464-471 doi: 10.1016/j.apcatb.2018.03.091

    22. [22]

      B.W. Lu, K. Kawamoto, RSC Adv. 2 (2012) 6800-6805 doi: 10.1039/c2ra20344h

    23. [23]

      N.B. Gao, M.X. Cheng, C. Quan, Y.P. Zheng, Fuel 273 (2020) 117702 doi: 10.1016/j.fuel.2020.117702

    24. [24]

      G.L. Zhou, F.Q. Xie, L.D. Deng, G.Z. Zhang, H.M. Xie, Int. J. Hydrogen Energy 45 (2020) 11380-11393 doi: 10.1016/j.ijhydene.2020.02.058

    25. [25]

      B.C. Dai, G.L. Zhou, S.B. Ge, et al., Can. J. Chem. Eng. 95 (2017) 634-642 doi: 10.1002/cjce.22730

    26. [26]

      L.H. Wang, H. Liu, Y. Liu, Y. Chen, S.Q. Yang, J. Rare Earth 31 (2013) 969-974 doi: 10.1016/S1002-0721(13)60014-9

    27. [27]

      B.W. Lu, K. Kawamoto, Mater. Res. Bull. 53 (2014) 70-78 doi: 10.1016/j.materresbull.2014.01.043

    28. [28]

      V. Parvulescu, C. Dascalescu, B.L. Su, Nanotechnol. Mesostruct. Mater. 146 (2003) 629-632

    29. [29]

      R. Wojcieszak, S. Monteverdi, M. Mercy, et al., Appl. Catal. A: Gen. 268 (2004) 241-253 doi: 10.1016/j.apcata.2004.03.047

    30. [30]

      T. Kang, Y. Park, J. Yi, J. Mol. Catal. A: Chem. 244 (2006) 151-159 doi: 10.1016/j.molcata.2005.09.003

    31. [31]

      T.R. Pauly, Y. Liu, T.J. Pinnavaia, S.J.L. Billinge, T.P. Rieker, J. Am. Chem. Soc. 121 (1999) 8835-8842 doi: 10.1021/ja991400t

    32. [32]

      P.T. Tanev, T.J. Pinnavaia, Chem. Mater. 8 (1996) 2068-2079 doi: 10.1021/cm950549a

    33. [33]

      Y.Y. Liu, K. Murata, M. Inaba, N. Mimura, Appl. Catal. A: Gen. 309 (2006) 91-105 doi: 10.1016/j.apcata.2006.04.042

    34. [34]

      S.S. Bhoware, S. Shylesh, K.R. Kamble, A.P. Singh, J. Mol. Catal. A: Chem. 255 (2006) 123-130 doi: 10.1016/j.molcata.2006.03.072

    35. [35]

      E. Lira, C.M. Lopez, F. Oropeza, et al., J. Mol. Catal. A: Chem. 281 (2008) 146-153 doi: 10.1016/j.molcata.2007.11.014

    36. [36]

      I.S. Ke, S.T. Liu, Appl. Catal. A: Gen. 317 (2007) 91-96 doi: 10.1016/j.apcata.2006.10.007

    37. [37]

      M. Wang, Q. Zhang, T. Zhang, et al., Chem. Engin. J. 313 (2017) 1370-1381 doi: 10.1016/j.cej.2016.11.055

    38. [38]

      G.W. Wang, H.L. Zhang, Q.Q. Zhu, et al., J. Catal. 351 (2017) 90-94 doi: 10.1016/j.jcat.2017.04.018

    39. [39]

      M. Thommes, K. Kaneko, A.V. Neimark, et al., Pure Appl. Chem. 87 (2015) 1051-1069 doi: 10.1515/pac-2014-1117

    40. [40]

      D.Y. Zhao, J.L. Feng, Q.S. Huo, et al., Science 279 (1998) 548-552 doi: 10.1126/science.279.5350.548

    41. [41]

      J.X. Chen, J.J. Zhou, R.J. Wang, J.Y. Zhang, Ind. Eng. Chem. Res. 48 (2009) 3802-3811 doi: 10.1021/ie801792h

    42. [42]

      J.E. Spanier, R.D. Robinson, F. Zheng, S.W. Chan, I.P. Herman, Phys. Rev. B64 (2001) 245407 doi: 10.1103/PhysRevB.64.245407

    43. [43]

      M. Peymani, S.M. Alavi, M. Rezaei, Int. J. Hydrogen Energy 41 (2016) 6316-6325 doi: 10.1016/j.ijhydene.2016.03.033

    44. [44]

      C. Alvarez-Galvan, J.L. Martinez, M. Capel-Sanchez, L. Pascual, J.A. Alonso, Adv. Sustain. Syst. (2021) 2100029 doi: 10.1002/adsu.202100029

    45. [45]

      Z.Y. Zakaria, J. Linnekoski, N.A.S. Amin, Chem. Engin. J. 207 (2012) 803-813

    46. [46]

      X. Chen, X. Su, B. Liang, et al., J. Energy Chem. 25 (2016) 1051-1057 doi: 10.1016/j.jechem.2016.11.011

    47. [47]

      G. Zhou, H. Liu, K. Cui, et al., Int. J. Hydrogen Energy 42 (2017) 16108-16117 doi: 10.1016/j.ijhydene.2017.05.154

    48. [48]

      Y. Liu, Z. Li, H. Xu, Y. Han, Catal. Commun. 76 (2016) 1-6 doi: 10.1016/j.catcom.2015.12.011

    49. [49]

      C. Italiano, J. Llorca, L. Pino, et al., Appl. Catal. B: Environ. 264 (2020) 118494 doi: 10.1016/j.apcatb.2019.118494

    50. [50]

      Y.C. Huang, H.B. Li, M.S. Balogun, et al., ACS Appl. Mater. Int. 6 (2014) 22920-22927 doi: 10.1021/am507641k

    51. [51]

      A. Ranjbar, A. Irankhah, S.F. Aghamiri, J. f Environ. Chem. Engin. 6 (2018) 4945-4952 doi: 10.1016/j.jece.2018.07.032

    52. [52]

      S. Choi, B.I. Sang, J. Hong, et al., Sci. Reports 7 (2017) 41207

  • Figure 1  TEM images and nickel particle size distribution of the samples.

    Figure 2  XRD partten (a) for the reduced catalysts and H2-TPR (b) profiles of the fresh catalysts.

    Figure 3  Catalytic activity of three catalysts applied to RWGS: (a) CO2 conversion; (b) CO selectivity; (c) CH4 selectivity.

    Figure 4  (a) Ni 2p XPS spectra of fresh catalysts NiCe-HMS and Ni-HMS. (b) EPR spectra of reduced catalysts Ni-HMS and NiCe-HMS.

    Figure 5  Catalytic activity of catalyst NiCe-HMS applied to RWGS at different inlet ratios: (a) CO2 conversion; (b) CO selectivity; (c) CH4 selectivity; (d) The catalytic activity of NiCe-HMS for 28 h at 750 ℃.

    Table 1.  Physicochemical properties of the catalysts

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  • 发布日期:  2022-05-15
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