Catalysts characterization
The XRD analysis was firstly conducted for the precursors of catalysts, and the patterns are summarized in Fig. 1. All the calcined samples show two diffraction peaks at 2θ = 35.5° and 38.7 °, which are related to CuO species (JCPDS Card no. 74-1230). A series of diffraction peaks can be observed at 2θ = 31.8°, 34.5°, 36.2°, 47.5°, 56.6° for calcined Cu/ZnO samples, which are assigned to ZnO species. There is no obvious characteristic peak of the carrier Al2O3, indicating that Al2O3 is amorphous. The results also suggest that Al2O3 plays a role in dispersing the active component Cu in the sample, and provides skeleton support for Cu species. A new diffraction peak formed at 67ºcorresponds to the spinel CuAl2O4 (JCPDS Card no. 33–0448), which might lead to high reduction temperature, because the structure of spinel is stable and the reduction is difficult. The SiO2 has an obvious "steamed bun" peak at 2θ = 22.5° in the XRD pattern, in line with the previous reports (Hosaka et al. 2023; Yuan et al. 2020). These observations indicate that the influence of these supports on the Cu-based catalysts is different, which should result in different catalytic behaviors.
The N2-adsorption/desorption isotherms and physico-chemical properties for the Cu-based catalysts with various supports are shown in Fig. 2 and Table 1. The ICP analysis demonstrated that all the four samples had the similar content of Cu species. The isotherms of these prepared samples are IV type, which is a typical mesoporous material. The specific surface area was determined by the BET method, and the data in Table 1 show that the BET surface area of these Cu-based samples varied with the supports. Cu/SiO2 demonstrated the highest value of 114.5 m2/g, and the lowest value was observed for Cu/ZnO (34.4 m2/g). The high value of SBET would increase the dispersity of the active sites and improve the catalytic efficiency. The pore volume and pore size changed irregularly, and Cu/ZnO and Cu/MgO show marked larger value than that of Cu/SiO2 and Cu/Al2O3, which should be benefited to the motion of molecules during the reaction.
Table 1
Physico-chemical properties of the Cu-based catalysts.
Catalyst | Cu loading /% | Surface Area /m2∙g− 1 | Pore Volume /mL∙g− 1 | Pore Size /nm |
Cu/SiO2 | 32.9 | 85.2 | 0.152 | 7.151 |
Cu/Al2O3 | 33.6 | 49.5 | 0.087 | 7.001 |
Cu/ZnO | 33.3 | 33.1 | 0.268 | 31.752 |
Cu/MgO | 37.9 | 48.6 | 0.368 | 30.235 |
The surface chemical state of Cu species should play a crucial role in the catalytic dehydrogenation of alcohol. Therefore, XPS analysis of these Cu-based samples was performed to assign the copper species with different supports (Fig. 3). The XPS spectra of the Cu 2p3/2 for all the samples can be fitted by two peaks, and B.E. (Binding Energy) of ca. 934 eV and ca. 932 eV are identified to Cu2+ and Cu+ or Cu0, respectively (Yuan et al. 2020; Prabu et al. 2014; Jiang et al. 2015). In order to accurately distinguish between Cu0 and Cu+, the Cu LMM spectrum was also performed (Fig. 4). Asymmetric peaks for all the four samples can be deconvolved into two peaks centered at ca. 569.9 eV and ca. 573.0 eV, corresponding to Cu0 and Cu+, respectively (Song et al. 2022; Chen et al. 2020). According to the XPS and LMM analysis, the distribution of the surface copper species has been calculated and summarized in Table 2. The content of Cu2+ was found in the order as follows: Cu/MgO > Cu/Al2O3 > Cu/ZnO > Cu/SiO2, which should be related to the varied reduction activities of Cu2+ and the stabilization of Cu+ and Cu0 over different supports. The order of Cu0 contents of these catalysts from high to low was Cu/SiO2, Cu/MgO, Cu/ZnO and Cu/Al2O3, which should be mainly responsible for their catalytic performance. Some research has demonstrated that Cu+ and Cu0 act synergistically to catalyze the dehydrogenation of alcohol (Lu et al. 2023), thus, the molar ratios of Cu+/Cu0 on the surface of these catalysts have also been calculated. And an order can be found as the follows: Cu/ZnO > Cu/SiO2 > Cu/Al2O3 > Cu/MgO.
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Table 2
The distribution of the surface copper species
Samples | Content of Cu2+ /mmol∙g− 1 | Content of Cu+ /mmol∙g− 1 | Content of Cu0 /mmol∙g− 1 | Cu2+/ (Cu2++Cu++Cu0) /% | Cu+/Cu0 |
Cu/SiO2 | 0.43 | 1.02 | 1.69 | 13.7 | 0.6 |
Cu/Al2O3 | 0.16 | 0.21 | 0.43 | 20.0 | 0.49 |
Cu/ZnO | 0.29 | 0.79 | 0.45 | 19.0 | 1.75 |
Cu/MgO | 1.10 | 0.38 | 1.02 | 45.0 | 0.37 |
The reducibility and interaction between the copper oxides and supports are studied by H2-TPR, and there have been some studies on the calcined Cu-based catalysts. Most researchers believe that the reduction peak at low temperature is the reduction of copper oxide species or copper oxide microclusters highly dispersed on the surface of carrier, while the reduction peak at high temperature is the reduction of larger CuOx grains (Koppadi et al. 2018). The H2-TPR curves in (Fig. 5) demonstrate that the reduction of CuOx on ZnO and MgO is easier than that on SiO2 and Al2O3, suggestive of the interactions between CuOx and support. The lower reduction temperatures of ZnO and MgO are mainly due to the high dispersion of copper oxide species on the surface of the support. Of note is that an even high reduction temperature peak of about 366°C is found for MgO, which should be related to the reduction of larger CuOx grains. These observations can well explain the high content of Cu2+ in Cu/MgO sample. The different reduction behavior found for the precursor of Cu/SiO2 catalyst with that of Cu/ZnO catalyst may be related to the reduction of highly dispersed CuOx to Cu0 in the later and bulk CuO particles on the calcined Cu/SiO2 sample (Yuan et al. 2020). The reduction temperature of calcined Cu/Al2O3 sample is higher, which should be related to the formation of the stable spinel CuAl2O4 species. The reduction performance of catalyst directly affects the activity of catalyst. The lower the reduction temperature, the better the catalytic activity of catalyst.
Due to the different properties of these supports used, it is expected that they should have different surface properties and affect the catalytic performance. The acidic properties of these catalysts were characterized by NH3-TPD (Fig. 6). The obtained NH3-TPD spectra were deconvoluted by Gaussian fitting, the number and intensity of acid sites were evaluated by the desorption area and temperature of the fitting peak. Acid sites responsible for NH3 desorption below 200°C are classified as weak acid sites, between 200°C and 300°C as medium acid sites, and above 300°C as strong acid sites. Coordination-unsaturated MO6 − x octahedron is used as a site for Lewis acid, thus, the presence of Cu2+ and Cu+ introduce acid sites into the catalyst.
According to the calculated data in Table 3, the amount of strong acid sites in these Cu-based catalysts can be ordered as follows: Cu/MgO > Cu/Al2O3 > Cu/SiO2 > Cu/ZnO. Combined with XPS analysis, coordination-unsaturated Cu2+ species on the surface should be responsible for the results, consistent with the previous reports (Yuan et al. 2020; Nauert et al. 2018). In addition, a large number of weak and medium acid sites in Cu/SiO2 catalyst are observed, which might be ascribed to the coordination-unsaturated Cu+ species. However, Cu/Al2O3 was an exception, which had lowest Cu2+ and Cu+ contents but with high amount of acid sites, suggesting that the acid site should be predominantly ascribed by Al species.
Table 3
The surface acidic properties of the Cu-based catalysts.
Sample | Total acid site /µmol NH3 ∙ g− 1 | Acid sites distribution/µmol NH3 ∙ g− 1 |
50‒200 ℃ | 200‒300 ℃ | 300‒600 ℃ |
Cu/SiO2 | 509.9 | 226.5 | 142.6 | 140.8 |
Cu/Al2O3 | 842.8 | 0 | 0 | 842.8 |
Cu/ZnO | 88.5 | 5.4 | 0 | 83.1 |
Cu/MgO | 6242.0 | 208.4 | 0 | 6033.6 |
CO2-TPD analysis displays (Fig. 7) that the surface basicity also varied with the supports. The CO2 adsorption sites on these catalysts can be generally divided into three types. Strong physical CO2 adsorption sites with desorption temperature between 50–220°C are assigned to the weak basic sites; Weak chemical CO2 adsorption sites (desorption at around 220–360°C) found on these catalysts can be ascribed to the medium basic sites; strong chemical CO2 adsorption sites (CO2 desorption above 360°C) are related to the strong basic sites on the catalyst. According to the calculated data in Table 4, Cu/MgO contained the highest amount of total basic sites, as well as the strong basic sites. By contrast, Cu/ZnO exhibited the lowest surface basicity. Actually, there are a large number of strong physical and chemical CO2 adsorption sites on Cu/Al2O3 and Cu/MgO samples, while moderate amount of physical CO2 adsorption sites is found for Cu/SiO2.
Table 4
The surface basic properties of the Cu-based catalysts.
Sample | Total basic sites /µmol CO2 ∙ g− 1 | Basic sites distribution /µmol CO2 ∙ g− 1 |
50–220 ℃ | 220–360 ℃ | 360–600 ℃ |
Cu/SiO2 | 80.5 | 44.4 | 13.4 | 22.7 |
Cu/Al2O3 | 257.9 | 103.6 | 29.1 | 125.2 |
Cu/ZnO | 34.1 | 4.6 | 14.4 | 15.1 |
Cu/MgO | 465.1 | 102.6 | 101.3 | 261.2 |
Catalytic performance of Cu-based catalysts in the dehydrogenation of dodecanol
The catalytic performace of these prepared Cu-based catalysts were studied in the anaerobic dehydrogenation of dodecanol (Table 3). The conversion varied in the order as follows: Cu/Al2O3 < Cu/SiO2 < Cu/MgO < Cu/ZnO, albeit the difference was not marked. Of note is that ester, olefin and ketone were also detected in the reaction besides the objective product aldehyde. We speculated that the reactivity should be influenced by multiple properties of the catalysts. Concerning on the distribution of products, Cu/SiO2 gave the highest aldehyde selectivity of 98.9% with a satisfactory 82.3% conversion, significantly superior to the reported catalytic system based on Cu/La2O2CO3 (Wang et al. 2013). Cu0 species has been generally believed as the active site for the dehydrogenation, therefore, the excellent selectivity obtained over Cu/SiO2 should be due to its highest amount of Cu0. The high value of SBET might be also partly responsible for the high catalytic performance, because more active sites can be exposed on Cu/SiO2 with similar Cu contents (Chen et al. 2020).
In contrast, although the highest conversion was obtained for Cu/ZnO, only a 35.6% selectivity was observed with the formation of ester as the main byproducts. Under the anaerobic conditions, we speculated that the ester was generated from dodecanol and dodecanal via a coupling reaction (Miura et al. 2017; Sato et al. 2012). It can also explain the highest conversion, because a proportion of dodecanol transformed via coupling reaction instead of dehydrogenation. The results also suggest that the surface properties had little effect on the coupling reaction, because highest selectivity of ester was observed for Cu/ZnO but with lowest acidity and basicity. Under the catalysis of Cu/MgO, a 32.9% selectivity to ketone was observed, which might be produced via ketonisation of ester for its high amount of surface acidic sites ( Prabu et al. 2014; Gaertner et al. 2009; Shen et al. 2012). Similar phenomenon can be observed for Cu/Al2O3 catalyst but with relatively lower level, probably due to its reduced surface acidity. Of note is that the pore property of these catalysts should also has effect on the product distribution. Cu/SiO2 and Cu/Al2O3 with small pore size (~ 7.0 nm) offered high selectivities toward aldehyde, while Cu/ZnO and Cu/MgO with larger value (~ 31.0 nm) gave more products of ester or ketone. These results suggest that larger pore size is benefitial to the entrance and exit of the large molecules, namely ester and ketone. Consequently, the excellent selectivity with satisfied conversion observed for Cu/SiO2 catalyst should be related to its proper surface acidity and basicity, and its small pore size.
Concerning on the side-reactions and the paths for the generation of these byproducts mentioned above, the exact dehydrogenation yields over different catalyst have been estimated in term of aldehyde (Table 5). The results demonstrate an order of dehydrogenation activity as follows: Cu/ZnO < Cu/MgO < Cu/Al2O3 < Cu/SiO2, not exactly in line with the amount of Cu0. Although Cu/MgO has markedly higher amount of Cu0 than Cu/Al2O3, but lower yield of dehydrogenation was obtained. These results suggest that the Cu+ species might also play a role in the dehydrogenation (Lu et al. 2023), and synergistic effect between Cu+ and Cu0 species might exist. Concerning on the varied ratios for these catalysts (Table 2), proper ratio of Cu+/Cu0 is beneficial to the catalytic performance of Cu-based catalysts.
Table 5. The results for the catalytic dehydrogenation of dodecanol over different Cu-based catalysts.
Effect of reaction conditions on the catalytic dehydrogenation of dodecanol
The effects of reaction conditions on the catalytic dehydrogenation of dodecanol were subsequently studied using Cu/SiO2 as the catalyst. The reaction temperature was initially investigated. When the reaction temperature was elevated from 200 ℃ to 260 ℃, the conversion of dodecanol increased gradually from 67% to 82% (Fig. 8). In contrast, the selectivity remained basically constant when the temperature was set above 240 ℃. Further increasing the reaction temperature led to a slight decreasement of the conversion, which might be due to the reversible hydrogenation of aldehyde.
We then focused on the reaction pressure. With a reaction pressure increasing from normal pressure to 0.8 MPa, the conversion of dodecanol decreased from 83.6% to 61.2%, and the selectivity of dodecanal dropped sharply from 98.3% to below 60% (Fig. 9). The anaerobic dehydrogenation of dodecanol to dodecanal is a reversible reaction, associated by the release of H2. With the increase of pressure, the reaction is promoted in the reverse direction, and the dehydrogenation of alcohol is suppressed, in line with the obtained results. Therefore, normal pressure was determined as the optimal condition.
As can be seen from Fig. 10, when the (gas hourly space velocity) of carrier gas increases from 300 h-1 to 600 h-1, the conversion of dodecanol gradually increases. However, when the GHSV continues to increase, the conversion decreases significantly. For the selectivity of dodecanal, it increases slightly as the increase of GHSV. Therefore, the optimal GHSV value was set as 600 h-1.
The effect of LHSV (liquid hourly space velocity) on the catalytic dehydrogenation of dodecanol was finally studied. With the increasement of LHSV of dodecanol, the conversion of dodecanol decreases gradually, whilst the selectivity of dodecanal increases slightly (Fig. 11). The conversion remains around 85% when the LHSV is lower than 0.3 h-1, which is mainly due to the fact that excessive raw material shortens the residence time of the raw material.
In summary, Cu/SiO2 presents excellent catalytic activity for the dehydrogenation of dodecanol to dodecanal in vapor-phase fixed bed reactor. Under the optimized conditions, the conversion and the selectivity reach 82.3% and 98.9%, respectively. And the catalytic dehydrogenation process probably provides a continuous process for the production of dodecanal.
The catalytic stability of Cu/SiO2 in the dehydrogenation of dodecanol
The catalytic stability of the Cu/SiO2 catalyst was also investigated in a continuous vapor-phase fixed bed reactor. The results in Fig. 12 demonstrate that the conversion of dodecanol decreased slightly in the reaction period of 125 h, and then remained basically unchanged. On the other hand, the selectivity of dodecanal showed an upward trend and tended to remain constant above 97.5% as the reaction proceeding. These results suggest that the prepared Cu/SiO2 catalyst had good stability in the continuous dehydrogenation of dodecanol.
XRD analysis of the used Cu/SiO2 catalysts was carried out to gain insight into the evolution of the catalytic structure during the dehydrogenation process. The XRD pattern (Fig. 13) show that the main diffraction peaks for Cu0 species at 2θ = 43.3°, 50.9° and 73.6° (JCPDS Card no. 04-0836) generally remained after continuous reaction for 200 h. An enhanced diffraction peak of 2θ = 36.2°, 42.3° and 61.3° (JCPDS Card no. 47-1230) generally assigned to the Cu2O phase is observed, (Yuan et al. 2020) indicating the agglomeration of copper ions due to the destruction of the Cu2O-like phase, which might be responsible for the slight reduction of the catalytic activity. However, it was difficult to absolutely eliminate the presence of the CuO phase (2θ = 35.6°, 38.7°, 41.2° and 61.5°, JCPDS Card no. 72-0629) in the catalysts because both exhibited the close position of the characteristic diffraction peaks.