Maray
Ortega
a,
Daviel
Gómez
b,
Raydel
Manrique
a,
Guillermo
Reyes
c,
Julieth Tatiana
García-Sánchez
d,
Victor Gabriel
Baldovino Medrano
de,
Romel
Jiménez
b and
Luis E.
Arteaga-Pérez
*af
aLaboratory of Thermal and Catalytic Processes (LPTC), Wood Engineering Department, Faculty of Engineering, Universidad del Bio-Bio, Concepción, Chile. E-mail: larteaga@ubiobio.cl; Web: https://twitter.com/LptcUbb
bCarbon and Catalysis Laboratory (CarboCat), Department of Chemical Engineering, Universidad de Concepción, Concepción, Chile
cBiobased Colloids and Materials, Department of Bioproducts and Biosystems, School of Chemical Engineering, Aalto University, FI-00076, Espoo, Finland
dCentro de Investigaciones en Catálisis (CICAT), Universidad Industrial de Santander, Colombia
eLaboratorio Central de Ciencia de Superficies (SurfLab), Universidad Industrial de Santander, Colombia
fUniversidad de Concepción, Unidad de Desarrollo Tecnológico, UDT, Coronel, Chile
First published on 21st September 2022
The heterogeneously catalyzed reductive amination of phenolics from lignin is considered an attractive sustainable route for the synthesis of primary or high-order aromatic and aliphatic amines. Here, the reductive amination of phenol with cyclohexylamine was studied, and insights into the role of the catalyst support, metal nanoparticle sizes, and acidic properties were provided. Bulk and surface characterization, IR experiments, and kinetic measurements were performed, and their results were correlated with the catalytic performance and the content of Lewis acid sites (Pd/Al2O3 > Pd/C > Pd/SiO2). The Lewis acid sites in the support and those formed by H2 spillover assisted phenol hydrogenation and CN bond activation, enhancing the formation of secondary amines (selectivity >90%). The Pd coordination in the particles strongly affected the catalytic activity, indicating that phenol amination is a structure-sensitive reaction. The turnover frequency vs. dispersion profiles combined with the site distributions in the Pd particles (edge, corner, and terraces) indicate that low-coordination sites favor phenol amination, which was confirmed via diffuse reflectance infrared spectroscopy with Fourier transform and high-resolution transmission electron microscopy. This study could contribute to the upcycling of fresh and recycled lignin fractions to produce aromatic and aliphatic amines.
The amination of phenol proceeds via a complex mechanism involving several reaction steps, namely, hydrogenation, dehydrogenation, and condensation.10–12 Briefly, the reaction is initiated by the hydrogenation of phenol (PhOH) to cyclohexanone (CyO), which subsequently reacts with the amine (cyclohexylamine, CyA) via nucleophilic attack to form an intermediate imine (N-phenylcyclohexaneimine, imine). The imine then disproportionates to form a secondary amine. In the presence of dehydrogenating catalysts (such as Pd/C), the amine can be dehydrogenated to reduce phenol to cyclohexanone (Fig. 1).
Fig. 1 Summarized reaction pathway for the phenol-to-secondary amine reaction over Pd/C (adapted from ref. 12). |
However, this reaction scheme can vary with the catalyst properties (i.e., nature of the metal, metal–support interactions, support acidity, and metal nanoparticle size), phenolic nature, and reaction conditions. For example, the importance of solvents for these reactions was recently studied by Jameel et al.13 The authors proved that the presence of solvents reduces the activation energy of amination, the condensation step occurs in a stepwise manner rather than a concerted manner. Furthermore, solvent molecules that form hydrogen bonds promote the formation of intermediates in terms of thermodynamics and kinetics by actively participating as proton transfer agents. In addition, the diffusivity of hydrogen into the solvent is critical to facilitate its access to the catalyst's active sites, thus, to complete the catalytic cycle.
Chen et al.11,14 explored the direct cross-coupling of phenols with anilines at temperatures in the range of 80–120 °C. They demonstrated that transition metal complexes (Rh, Pt, Ru, Ni, and Ir) do not produce any aromatic amines, while Pd/C can lead to a 94% yield of arylamines. More recently, Tomkins et al.15 demonstrated that Rh/C can convert 98% of phenol to cycloheyxlamine with a selectivity of 98%, while the dehydrogenation over Pd leads to a 41% yield of N-substituted anilines. In a later study from the same group, Cuypers et al.16 suggested that the acidity of the support plays a major role in the hydrogenation and condensation of cyclohexanone with amino groups. Nonetheless, the nature of the surface acid sites (Lewis or Brønsted) and the role of the metal nanoparticle size in the reaction were not considered. These aspects were studied by Vidal et al.17 using Pt/TiO2 and ethyl levulinate. They concluded that a high Pt dispersion and the Pt–TiO2 interphase favored the spillover of dissociated hydrogen, generating protonic acid sites, thus increasing the rate of imine formation. On the other hand, Corma et al.18 verified that the hydrogenation of imines is sensitive to the Pd nanoparticle structure, and that the activity and selectivity increase with Pd dispersion. They proposed that small metal particles, where step and corner sites are relatively abundant, are more favorable for the cleavage of C–O bonds than large metal particles, which have abundant terrace sites. Similarly, Mazarío et al.19 observed that the average Pd particle size in the catalyst increased slightly after several reaction cycles, leading to a reduced activity. However, an apparent contradiction was proposed by Resende et al.,20 who observed low activities for small Pd metal nanoparticles and attributed this to interactions with reactive substrates. Although these studies focused on the particle size and nature of the catalyst, they suggested that the reaction performance can be significantly affected by the metal–support interactions or support properties. In addition, the nature of the acidic sites plays a key role in the hydrogenation of NC bonds. Hattori and Shishido21 demonstrated that hydrogen can be dissociatively adsorbed on Pt sites to form hydrogen atoms, which migrate to the Lewis acid sites of the support and participate in the hydrogenation. Similar results were reported by Santoro et al.,22 who aimed to simplify the number of steps in the reductive amination of aromatic ketones on Cu catalysts supported on SiO2, Al2O3, and TiO2. They prepared multifunctional catalysts with tailored densities of acidic and hydrogenation-active sites by changing the catalyst support. A Cu/SiO2 catalyst was active as a Lewis acid catalyst in its non-reduced form and very active for the selective hydrogenation in its reduced form, effectively promoting the direct reductive amination of aromatic ketones. Recently, Mazarío et al.19 investigated the role of the support acidity and nanoparticle size using metal oxides (TiO2, Al2O3, ZrO2, and MgO) and their mixtures (TiO2–Al2O3, TiO2–ZrO2, and ZrO2–Al2O3) as supports for Pd nanoparticles. They demonstrated that a high density of acid sites resulted in the formation of undesirable nitrogen-containing sub-products. Furthermore, it was found that the presence of a large number of unsaturated Pd sites on the surface is essential for activating the CN bond and enhancing its hydrogenation. However, the relationship between the nature of the acidic sites and the reaction behavior is yet to be clarified.
Although the previously discussed studies suggest that the quantity and nature of the acid sites in the support and the coordination degree of the metal nanoparticles are key parameters for reductive amination processes, there is no consensus on their specific roles in phenol amination. Moreover, different carbon-containing substrates (phenolic, alcohol, or ketone) and amines (NH3, aniline, or cyclohexylamine) could lead to different surface interactions, as extensively revised by Gomez et al.23
Le Valant et al.24 suggested that a decrease in the catalyst particle size could enhance the effect of the support by modifying the electronic properties of the metal nanoparticles or increasing the contact area between the metal crystallites and the support. These effects have been reported for amination and hydrogenation reactions; thus, it is plausible that the phenol-to-secondary amine reaction is affected by the metal dispersion.17,19,25
In this study, we investigated the role of the metal nanoparticle size and catalyst support in the amination of phenol over supported Pd catalysts. Pd was used as a reference metal because of its proven activity in amination processes. Activated carbon, SiO2, and Al2O3 were selected as supports owing to their abundance, industrial relevance, and different metal–support interactions. All the materials were extensively characterized, and their structural, chemical, and physical properties were correlated with the reaction performance.
According to Van Santen,27 for particle sizes ranging between 2 and 20 nm, three reaction rate behaviors can be observed: (i) reaction rates that increase when the particle size decreases, (ii) reaction rates that decrease with a decrease in particle size, and (iii) reaction rates that are independent of the particle size. This is the basis for classifying reactions as structure-sensitive or structure-insensitive. Different Pd/Al2O3 metal nanoparticle sizes (in the range of 2–10 nm) were obtained by changing the metal loading (1%, 5%, and 10% wt/wt) and the thermal treatment conditions. These samples were denominated Pd/Al2O3-Di, where Di represents the average nanoparticle size (i = 1–4, from lowest to highest nanoparticle size).
The morphology and composition of the catalysts were investigated using scanning electron microscopy (SEM) and energy-dispersive X-ray spectroscopy (EDX), respectively. The analyses were performed using a Hitachi SU3500 device operated at an acceleration voltage of 20 kV and coupled with a Bruker XFlash 610M EDX accessory for semi-quantitative spectral analysis.
The metal content in the samples was inspected by atomic absorption spectrometry (AAS) in a Perkin Elmer 3100 instrument (Perkin Elmer, Manasquan, NJ, USA). Prior to the analyses the samples were subjected to microwave-assisted digestion using 50 mg of the catalyst and 10 mL of concentrated HNO3/HCl (see Table E1†).
Temperature-programmed reduction (TPR) experiments were performed using a Micromeritics ASAP 2010 device equipped with a TCD cell to quantify the H2 consumption. The total acidity was measured via temperature-programmed desorption of ammonia (NH3-TPD) using a 3FLEX device (Micromeritics) equipped with a TCD and combined with a mass spectrometer (Cirrus 2, MKS Instruments).
The specific surface areas and pore volumes were calculated from N2 adsorption–desorption isotherms at 77 K using the Brunauer–Emmett–Teller (BET) model and Barrett–Joyner–Halenda (BJH) method, respectively. Both isotherms were recorded using a 3FLEX instrument (Micromeritics). Before the analysis, the samples were degassed for 24 h under vacuum at 150 °C.
The bulk crystalline phases were analyzed via X-ray diffraction (XRD) using a Bruker D4 Endeavour diffractometer with Cu Kα radiation (λ = 0.15418 nm). The scanning was performed between 3° and 90° 2θ at a speed of 0.02° s−1 using a signal generated at 40 kV and 20 mA. The crystalline phases were identified via a search–match procedure with the Mercury 3.7 software, using the Crystallography Open Database. The metallic particle sizes were estimated using the Scherrer equation (eqn (1)):28
(1) |
Transmission electron microscopy (TEM) images were obtained using a JEOL JEM 1200 EXII microscope at 120 kV. Transmission electron microscopy (TEM) images were obtained using a JEOL JEM 1200 EXII microscope at 120 kV. For this measurement, the catalysts were dispersed in ethanol in an ultrasound bath for approximately 5 min, deposited on a carbon-coated copper grid, and air-dried before imaging. The images were processed with the software ImageJ and the particle size distribution was estimated from the average of 5 to 10 TEM images using the volume-weighted function recommended by Vannice (eqn (2)):29
(2) |
(3) |
High-resolution transmission electron microscopy (HRTEM) images and electron diffraction patterns were acquired using a JEOL JEM-2200FS (JEOL, Mitaka, Tokyo) microscope with double aberration correction, operated at an acceleration voltage of 200 kV. The samples for the HRTEM studies were drop-cast with acetone onto Cu grids coated with an ultrathin holey carbon film.
The nature of the surface acid sites was investigated via Fourier-transform infrared (FTIR) spectroscopy with pyridine (C5H5N, J. T. Baker, >99.9% purity) in a flow cell equipped with ZnSe windows and a vacuum system (Pfeiffer HiCube Eco Turbo). IR spectra at different desorption temperatures were collected with a Nicolet iS50 device (Thermo Scientific) using an MCT detector and 32 scans with a resolution of 4 cm−1. Diffuse reflectance Fourier transform infrared spectroscopic (DRIFTS) measurements of the CO adsorption on Pd/Al2O3-Di (i = 1 to 4) were performed to relate the degree of surface coordination as a function of particle size. The technique is described in further detail in the ESI.†
The reaction tests were performed in reinforced glass autoclave reactors (4 mL) equipped with a H2 line for pressurization. The reactors were placed in a Reacti-Therm™ system (Thermo Fisher, USA) equipped with an external thermocouple and magnetic stirring. To measure the concentrations over time, the reactant quantities were increased by a factor of 15, and the reaction was performed in an SS316 autoclave reactor (20 mL) equipped with a polytetrafluoroethylene liner and a sampling port.
The conversion of reactants (amine and phenol) and selectivity to products (based on GC-FID measurements) were defined as: (initial moles of reactant − final moles of reactant)/initial moles of reactant × 100, and (moles of product i)/moles of total products × 100, respectively. The turnover frequency (TOF) was defined as: (moles of product i)/(moles of surface metal in the catalyst).
Finally, the basic reaction conditions were: reaction time = 20 h, T = 140 °C, pH2 = 1.5 bar, C0PhOH, C0CyA = 1.4 eq., Pd/C 5% mol mol−1 with respect to phenol, a stirring speed of 900 rpm and tert-amyl alcohol as a solvent.
Catalyst | Particle sizea (nm) | Particle sizeb (nm) | Surface area (m2 g−1) | Dispersion (%) | Pore size (nm) |
---|---|---|---|---|---|
Pd/C | 5.8 | 3.3 ± 1.1 | 832 | 33 | 2.8 |
Pd/SiO2 | 8.6 | 4.6 ± 1.0 | 219 | 24 | 16.4 |
Pd/Al2O3-D3 | 6.6 | 3.6 ± 0.7 | 221 | 30 | 10.8 |
Pd/Al2O3-D4 | 9.6 | 7.7 ± 0.5 | — | 14 | — |
Pd/Al2O3-D2 | 5.6 | 2.3 ± 0.7 | — | 47 | — |
Pd/Al2O3-D1 | 4.5 | 1.7 ± 0.4 | — | 64 | — |
The Pd/C catalyst stands out in terms of its high surface area and narrow pores, whereas the Pd/SiO2 and Pd/Al2O3-D3 catalysts appear to be similar. Therefore, any significant difference in performance between the SiO2 and Al2O3 catalysts can be attributed to the support–Pd interactions. The differences in nature of the supports make their physicochemical study essential, because it can provide relevant information about their role in the phenol amination reaction.
The TPR profiles for the calcined Pd/C, Pd/Al2O3-D3, and Pd/SiO2 catalysts are shown in Fig. 2c. For Pd/C and Pd/SiO2, a high-intensity reduction peak was observed at low temperatures (approximately 76 °C), which can be attributed to the formation of palladium β hydrides after the reduction of small PdO nanoparticles.33–36 Furthermore, attenuated signals were observed for the three catalysts between 85 and 130 °C. These peaks can be attributed to the reduction of Pd2+ to Pd0 at low temperatures, indicating the presence of small nanoparticles with a narrow distribution.37–40 The similar TPR profiles indicate that the three materials should be reduced under the same conditions to achieve a predominance of Pd0 nanoparticles and similar particle size distributions. This hypothesis was further confirmed via TEM and XRD.
Finally, the total concentrations of acidic sites and their relative strengths on the Pd/C, Pd/Al2O3-D3, and Pd/SiO2 catalysts are shown in Fig. 2d. The strength of the acidic sites was determined according to the temperature of the corresponding ammonia desorption peak: weak, medium, and strong acidic sites correspond to temperatures below 250 °C, between 250 and 450 °C, and above 450 °C, respectively.41 Interestingly, the three catalysts showed desorption peaks at temperatures below 250 °C, indicating the presence of weak acidic sites, which were predominant in Pd/SiO2. The Pd/Al2O3-D3 catalyst showed an additional high-intensity desorption peak located between 250 and 300 °C, indicating that sites with medium acidity were predominant in this material. The evolved gases from these tests were analyzed to confirm the signals attributable to N2 and NH3 (Fig. E2 in the ESI†). For all catalysts, the reduction peaks at low temperatures were correlated with the desorption of molecular ammonia, indicating that it was weakly adsorbed (likely physisorbed) on the weak acidic sites. However, at temperatures above 250 °C, the reduction peaks correlated with the signals of NH3 (m/z = 17) and N2 (m/z = 14, 28). This last result was observed for Pd/C and Pd/Al2O3-D3 and suggests that strongly adsorbed ammonia molecules undergo a redox decomposition with surface O sites, as previously reported.42–44
The TPD-NH3 results indicate that the three catalysts have different concentrations of superficial acidic sites of different nature, which is necessary to investigate their role in the reductive amination of phenol.
The nature of the surface acidic sites of these catalysts was studied via adsorption/desorption of pyridine assisted by FTIR spectroscopy (Fig. 3). The Pd/SiO2 catalyst shows two main peaks at 1446 and 1596 cm−1 associated with coordinated pyridine at Lewis acid sites; this is typically seen in silica-based catalysts.45–48 The Pd/Al2O3-D3 catalyst shows additional peaks at 1493, 1578, 1615, and 1623 cm−1 which can be attributed to the coordination of pyridine at Lewis acid sites.47,49 In the Pd/Al2O3 catalyst, the Lewis sites correspond to exposed Al3+ sites and are classified as medium (1578–1596 cm−1) and strong acidic sites (1615–1623 cm−1).47,50,51 FTIR-PyR confirmed the absence of signals at 1545 cm−1, which indicates that none of the catalysts contains Brønsted acid sites.45,47 The Lewis acidity of Pd on the SiO2 and Al2O3 catalysts can be determined by comparing the intensities of the peaks at 1446 cm−1. The concentrations of acidic sites were calculated from the experiments at 140 °C by applying the molar extinction coefficient for the peak at 1446 cm−1 (2.22 cm μmol−1), determined by Emeis.52 The Pd/Al2O3-D3 catalyst exhibited the highest concentration of Lewis acid sites (371 μmol gcat−1vs. 95 μmol gcat−1 for Pd/SiO2) and abundant strong Lewis acid sites, corresponding to the range of 1615–1623 cm−1. The ratio of intensities at 1446 cm−1 (APd/Al2O-D3/APd/SiO2) indicates that the acidity of the Pd/Al2O3-D3 catalyst is approximately 3.9 times higher than that of Pd/SiO2. On the other hand, the carbon support of the Pd/C catalyst used in this study was identified by Wu et al.53 as an acidic material, with a predominance of Lewis acid sites (151 μmol gcat−1). This is mainly because the carbon support is electrophilic.53–55 In addition, the interactions between Pd and the acid sites form an electron-deficient structure, which can also result in Lewis acidity.
Fig. 4 (a) X-ray diffraction (XRD) patterns for Pd on different supports (Pd/C, Pd/Al2O3-D3, and Pd/SiO2). (b) XRD patterns for Pd with different metal nanoparticle sizes (D1, D2, D4) supported on Al2O3. Standards from the Crystallography Open Database are shown:60 Pd (1011105) and Al2O3 (2107301). Note: analysis was performed after catalyst reduction. |
Fig. 4b shows the XRD spectra of the three other Pd/Al2O3 catalysts with different particle sizes (Pd/Al2O3-D1, Pd/Al2O3-D2, and Pd/Al2O3-D4). These patterns and that of Pd/Al2O3-D3 show different intensities of the diffraction peaks at 40.0°, 82.2°, and 86.7° which correspond to Pd0, while the Pd peaks at 46.7° and 68.1° overlapped with the signals at 45.8° and 66.9° of the (400) and (440) planes of Al2O3. The Pd/Al2O3-D1 catalyst was the most complex to analyze because of its low Pd content (approximately 1% wt/wt) and the peaks of Pd and Al2O3 overlapping, which hinders Pd quantification.
The Pd crystallite sizes were calculated using the Scherrer equation applied to the reflection at 40°. The results are listed in Table 1.
Fig. 5a–c show the TEM images and the corresponding particle size distribution histograms of Pd/C, Pd/Al2O3-D3, and Pd/SiO2. Fig. 5d–f show the results for the three additional Pd/Al2O3 catalysts prepared with different metal nanoparticle sizes (Pd/Al2O3-D1, Pd/Al2O3-D2, and Pd/Al2O3-D4).
The TEM images show particles with well-defined contours that are dispersed on the supports. This suggests that the use of TEA during the incipient wetness impregnation effectively contributed to the formation of uniformly distributed Pd nanoparticles with unimodal size distributions, with standard deviations of less than 1.1 nm. The similar dispersions found for Pd/C (33%), Pd/Al2O3-D3 (30%), and Pd/SiO2 (24%) are suitable for studying the effect of the support on the catalytic amination of phenols without significant interference from the previously reported structural sensitivity.17 Finally, the TEM images shown in Fig. 5d–f confirm the effectiveness of the synthesis method used to produce different particle sizes in Pd/Al2O3-D1 (1.7 nm), Pd/Al2O3-D2 (2.3 nm), and Pd/Al2O3-D4 (7.7 nm). According to Van Santen,27 the reactivity of metal particles can be correlated to their orbital structure, which is strongly affected by the number of atoms. For particles between 1 and 3 nm, the number of surface atoms is higher than the number of bulk atoms; at 3 nm, the number of surface atoms becomes lower than the number of bulk atoms. Therefore, the particle sizes shown here (1–10 nm) are in a range which allows us to investigate the relevance of the structural sensitivity in the phenol amination process.
The particle size overestimation by the Scherrer equation (with respect to the particle size measured via TEM) can be attributed to any type of lattice imperfection that causes additional diffraction line broadening. Therefore, the metal particle size measured using X-ray diffraction is rarely equivalent to that measured via microscopic methods.63–65 Although the TEM technique could also imply some deviations from actual size values, it is more accurate than XRD; thus, the dispersions calculated via TEM were used here for the quantification of the reaction rates expressed as turnover frequency (TOF).
HRTEM and selective area diffraction measurements were used to characterize the Pd with different particle sizes on Al2O3 surfaces (Fig. 6). The electron diffraction patterns shown in the lower left corner of each image exhibit three diffuse rings, which can be assigned to the (111), (200), and (311) planes of fcc palladium. The interplanar distances calculated from the (111) rings are consistent with those reported by other authors.66–68
The HRTEM images show that the synthesized Pd nanocrystals mainly display octahedral geometries. The octahedral particles exhibit the expected (111) facet67 with multiple dislocations on this plane. The lattice spacing of the measured fringes was larger for the Pd/Al2O3-D1 catalyst (d = 0.35 nm) than for the other catalysts. In general, the Pd nanoparticle surface analyses show that the differences are mainly attributed to surface facets.
Run | Catalyst | Phenol (mol L−1) | Cyclohexylamine (eq.) | H2 (bar) |
---|---|---|---|---|
1 | n.n. | 0.20 | 1.40 | 1.5 |
2 | Al2O3 | 0.20 | 1.40 | 1.5 |
3 | C | 0.20 | 1.40 | 1.5 |
4 | SiO2 | 0.20 | 1.40 | 1.5 |
5 | Pd/C | 0.0 | 1.40 | 1.5 |
6 | Pd/C | 0.20 | 0.0 | 1.5 |
7 | Pd/C | 0.20 | 1.40 | 0.0 |
8 | Pd/C | 0.20 | 1.40 | 1.5 |
Resultsa | |||||
---|---|---|---|---|---|
Run | X PhOH/XCyA (%/%) | S DCyA (%) | S CyPhA (%) | S CyO (%) | S Imine (%) |
X i = 100 × ((ni,o − ni,t)/ni,o), i = reactants, t = reaction time. , i = reactants, n = products, t = reaction time.a Quantities for conversion and selectivity were determined by GC-FID analysis. | |||||
1 | 3/5 | n.d. | n.d. | n.d. | 100 |
2 | 3/3 | n.d. | n.d. | n.d. | 100 |
3 | 6/8 | n.d. | n.d. | 10 | 90 |
4 | 0/9 | n.d. | n.d. | n.d. | 100 |
5 | 24 | 77 | 23 | n.d. | n.d. |
6 | 100 | n.d. | n.d. | 100 | n.d. |
7 | 15/76 | 36 | 61 | n.d. | 3 |
8 | 87/78 | 57 | 18 | 24 | 1 |
The experiments under non-catalytic conditions (run-1) and with the Al2O3 support (run-2) confirmed that the homogeneous condensation between phenol and cyclohexylamine occurs at a very low reaction rate (0.0008 mmol h−1) and yields the intermediate imine as a product.17,23,69 When the carbon support was used (run-3), the phenol conversion was similar to that of run-1, but cyclohexanone was detected in the products, which suggests the occurrence of phenol hydrogenation with this support. Finally, the phenol conversion with SiO2 (run-4) was zero; however, the cyclohexylamine conversion with SiO2 was 9%, and the imine was the only product (run-4), which suggests that the amine underwent self-condensation with this support. The phenol conversion values obtained for the homogeneous reaction conditions and with the three supports, that is, run-1 to run-4 (<6% after 20 h), demonstrate that the substrate–surface interactions and the presence of a metal catalyst are critical for achieving a reasonable activity level for this reaction system. The effectiveness of Pd0 for hydrogenation and amination was confirmed by the results of run-5 to run-7. The results from run-6 confirmed the total conversion of phenol (XPhOH = 100%) via its partial hydrogenation to cyclohexanone on Pd/C. However, the reduction of the produced cyclohexanone to cyclohexanol over Pd0 was hindered, presumably due to the keto–enol equilibrium between cyclohexanone and a surface intermediary, which is the kinetically relevant step in this reaction.70,71 This is a remarkable result because the over-hydrogenation of phenol would reduce the effectiveness of the amination cycle. Self-condensation of the amine (run-6) to form dicyclohexylamine (DCyA) and cyclohexylaniline (CyPhA) was observed. This confirmed the capacity of Pd0 to promote the hydrogenation/dehydrogenation of the intermediate imine. This capacity was further studied via a reaction experiment in the absence of H2 (run-7). The selectivity to the dehydrogenated secondary amine (CyPhA) was 1.7 times that to dicyclohexylamine. These results suggest that the Pd0 sites can promote the dehydrogenation of the imine, providing the necessary H2 equivalents to complete the catalytic cycle, as has been previously reported for a similar reaction.72 Finally, the Pd/C catalyst demonstrated remarkable activity in the amination of phenol with cyclohexylamine (run-8), mainly producing dicyclohexylamine, cyclohexylaniline, and cyclohexanone. Based on these results, we proposed a reaction pathway for the amination of phenol with cyclohexylamine (Fig. 7).
The reaction begins with the hydrogenation of phenol to cyclohexanone, which subsequently reacts with the amine (cyclohexylamine, CyA) via nucleophilic attack to form an intermediate imine (cyclohexaneimine, CyNCyA). The imine then disproportionates to form secondary amines (dicyclohexylamine, DCyA, and/or cyclohexylaniline, CyPhA). In addition to this main reaction cycle, we propose that parallel self-condensation of CyA via a hemi-aminal intermediate could occur, producing DCyA and NH3. DCyA can then be dehydrogenated to produce CyPhA. The species involved in this cycle and reported in Table 2 were identified via gas chromatography coupled to mass spectrometry, and their analytical standards were used for quantification (see ESI_2.xls and ESI_3.xls†). Despite several authors having proposed the hemi-aminal as an intermediary for these reactions, it is very reactive and unstable under the reaction conditions used here; thus, it was not detected by GC-MS.15,73–76
Finally, time-dependent compositional profiles were used to analyze the presented reaction pathway using the first- and second-rank Delplot approach.77 The initial rates of cyclohexylamine and phenol conversion (r0i, mmol h−1 mmol−1 Pd) were obtained via polynomial regression and differentiation of the Civs. time curves (Fig. 8a), extrapolated to zero time. The results indicate that the amine is converted more rapidly (r0CyA = 7.5 h−1) than phenol (r0CyA = 6.7 h−1), presumably due to its participation in the cyclohexanone condensation and its self-condensation. In addition, the concentration profile of the imine shows an intermediate-like behavior, with a maximum at 310 min. The eventual formation of the secondary amines (dicyclohexylamine and cyclohexylaniline) suggests their role as secondary products. However, the dicyclohexylamine profile should be carefully analyzed, as it could also suggest its role as an intermediary for the formation of cyclohexylaniline. This last point is discussed here based on the Delplot rank curves.
According to the first-rank Delplot profiles for the reaction products (Fig. 8b), the imine and dicyclohexylamine have finite Y-intercepts at zero time that correspond to primary products formed via parallel reactions taking place at different rates,77 while cyclohexylaniline has a zero intercept that represents a high-order product. This indicates that dicyclohexylamine can be formed as a primary product via the reactions of self-condensation and with phenol (as previously discussed), while cyclohexylaniline is formed in a second reaction step. For the second-rank Delplots (Fig. 8b), the profiles for the imine and dicyclohexylamine are similar and show a tendency to diverge on the Y-axis when X → 0, which is characteristic of primary products. The curve for cyclohexylaniline confirms its role as a second-order product with a zero intercept on the Y-axis. The consistency between the product composition results, individual reactions for hydrogenation and self-condensation, and Delplot analysis validates the reaction pathway proposed here. In the following sections, the effects of the catalyst support and metal nanoparticle size are assessed considering this reaction pathway.
The results of conversion, selectivity, and yields of secondary amines, as well as the acidic site densities of Pd/Al2O3-D3, Pd/C, and Pd/SiO2 demonstrated that phenol conversion and yield of secondary amines were strongly favored by highly acidic catalysts (Fig. 8a and b). Moreover, the imine is formed regardless of the nature of the support, which is consistent with previous findings.19,79 The conversion values for Pd/Al2O3-D3 and Pd/C were 5 times higher than that for Pd/SiO2, and the yield of secondary amines increased from 13% for Pd/SiO2 to 64 and 82% for Pd/C and Pd/Al2O3-D3, respectively. In addition, different product distributions were observed among these catalysts, which could be related to the promotion or suppression of different reaction steps in the catalytic cycle owing to the density and/or nature of the acidic sites. These differences can be explained by the mechanistic divergences created over different types of acidic sites. Neri et al.80 proposed that phenol adsorption is sensitive to the number of strong acidic and basic sites around the metal sites. In general, a support with a high phenol adsorption capacity will enhance phenol conversion, and cyclohexanone selectivity is increased owing to the weak interaction with the support.
Additional dynamic experiments were performed to estimate the initial reactant conversion and product formation rates. The rates (r0i, mmoli h−1 mmolPd−1) were calculated via polynomial regression and differentiation of the Civs. time curves extrapolated to zero time:
(4) |
Reaction | Pd/Al2O3-D3 TOF (h−1) | Pd/C TOF (h−1) | Pd/SiO2 TOF (h−1) |
---|---|---|---|
PhOH + CyA + 2H2 → PhNCyA + H2O | 8.25 | 6.75 | 2.25 |
2CyA → DCyA + NH3 | 11.25 | 6.75 | 4.5 |
The hydrogenation reactions on Pd-based catalysts proceed via a metal hydride (HPdH) formed by the dissociation of H2 on the Pd nanoparticles, which is a key step in the catalytic cycle.18 However, because all the catalysts discussed in this section have the same metal loadings and similar dispersions, the rates of HPdH formation on their surfaces under a constant H2 pressure are expected to be similar. Therefore, this step cannot explain the different conversions and product distributions. A theory that could explain this was proposed by Hattori and Shishido21 and further confirmed by Vidal et al.,17 who proposed the formation of protonic acidic sites via H spillover from HPdH to the Lewis acid sites of the support. Furthermore, Lewis acid sites can activate aromatic rings to become highly nucleophilic through electrophilic aromatic substitution reactions,81 which induces the aromatic ring to accept electrophilic groups, such as H+. The synergy of the metallic hydrogen activation82 and Lewis acid sites can thus increase phenol conversion.
The high conversions and yields of secondary amines obtained for Pd/C and Pd/Al2O3-D3 suggest that the imine is formed and further hydrogenated preferentially on highly acidic materials. The enhanced imine hydrogenation can be attributed to the promotion of the condensation reaction on Lewis acid sites17,19 and to the dragging effect of the hydrogenation/dehydrogenation reaction on imine formation.22 The latter is a plausible explanation for the presence of cyclohexanone in the Pd/C products, whereas the cyclohexanone was completely condensed when Pd/Al2O3-D3 was used. Moreover, the two-fold increment in cyclohexylaniline selectivity found in Pd/Al2O3-D3 with respect to Pd/C suggests that the imine is adsorbed with different strengths, leading to a higher rate of hydrogenation/dehydrogenation on Pd/Al2O3-D3 than on Pd/C.
The previously discussed results allow us to conclude that the Lewis acidity of the catalysts followed the order Pd/Al2O3-D3 > Pd/C > Pd/SiO2 and played an important role in the activity of the catalysts (Fig. 9), promoting the conversion of phenol and leading to high selectivity values for secondary amines. These results demonstrate that Pd offers hydrogenation sites, whereas the supports provide Lewis acid sites, which could enable H2 spillover and enhance the hydrogenation of surface intermediates such as the imine.
Fig. 10 a) Effect of the metal dispersion on the turnover frequency (TOF). b) Fractions of different metal sites as a function of the metal dispersion.83 The reaction experiments were carried out at T = 140 °C and with 0.2 Mol L−1 phenol (PhOH), 1.4 eq. cyclohexylamine (CyA), 1.5 bar H2, and 5% mol mol−1 Pd. |
For structure-sensitive reactions, the nature of the activated chemical bond determines the arrangement of surface atoms that provides the lowest activation energy. However, the structural sensitivities of some reactions can be complementary depending on whether a bond is broken or formed. In fact, the TOF vs. D profiles shown here are similar to those reported by Van Santen27 for reactions with complimentary dissociative bond cleavage and associative bond formation (type I and type III). The implications of the metal nanoparticle size for the elementary hydrogenation and amination steps in the phenol-to-secondary amine catalytic cycle are discussed next.
The first step in the phenol amination (PhOH → CyO) involves the partial hydrogenation of phenol via the conversion of –OH to CO (Fig. 11). Mortensen et al.84 measured an increase in the reaction rate upon increasing the metal particle size, presumably because benzene ring hydrogenation is fast on large facets, while phenol is adsorbed on the support. However, the effect of the support (especially for metal oxides) on phenol hydrogenation was several orders of magnitude greater than that of the particle size, which could explain the apparent contradiction with our results. Accordingly, our results can be explained by the high availability of HPdH sites for small particle sizes, which increases the probability of H spillover to the support, generating extra Lewis acid sites. These sites are necessary for the conversion of phenol into a keto–enol intermediate and further isomerization to cyclohexanone, which explains the increase in the phenol conversion TOF for low particle sizes.
Fig. 11 Reaction scheme for phenol hydrogenation on Pd/Al2O3.85 |
In the second step (imine → secondary amines), the CN bond must be activated to facilitate imine hydrogenation/dehydrogenation. In this case, the activity increases with the fraction of low-coordination sites (steps and corners), which are reported to be chemoselective for CN conversion.17,19
The previously discussed results indicate that high proportions of low-coordination sites in the Pd/Al2O3 catalysts increase their effectiveness in phenol amination. Therefore, direct characterization of the surface was performed via CO adsorption experiments on Pd/Al2O3-D1, Pd/Al2O3-D2, Pd/Al2O3-D3, and Pd/Al2O3-D4. The experiments were conducted using diffuse reflectance infrared spectroscopy with Fourier transform (DRIFTS) on a Nicolet iS50 infrared spectrometer (Thermo Scientific) interfaced with a mass spectrometer (Pfeiffer QMG 220).
Fig. 12 shows the IR spectra at 30 °C after performing the CO adsorption experiments for the reduced Pd/Al2O3 catalysts (D1 to D4). The IR band at 2082 cm−1 was detected for all the catalyst samples and was attributed to CO molecules linearly adsorbed on metallic Pd.19,86 This linear adsorption is characteristic of Pd particles with (111) facets and low-coordination Pd atoms (edges and corners), which is consistent with the low range of particle sizes obtained here (<10 nm).87,88 In addition, the intense signals at 1976 and 1926 cm−1 (more pronounced on catalysts with large nanoparticles) correspond to the bridge CO and three-fold CO configurations, which are commonly located at terrace sites in Pd (100), (110), and (111).19,87,89,90 Accordingly, the intensity ratios of these signals (a2082/(a1976 + a1926)) are proportional to the fractions of uncoordinated sites in the catalysts, which follow the order Pd/Al2O3-D1 (0.184) > Pd/Al2O3-D2 (0.151) > Pd/Al2O3-D3 (0.136) > Pd/Al2O3-D4 (0.106) (see insert in Fig. 12). Therefore, based on the CO IR and HRTEM results and the catalytic data gathered here, we confirmed that catalysts with a high proportion of uncoordinated Pd sites, such as Pd/Al2O3-D1, are likely to favor phenol amination.
Fig. 12 Diffuse reflectance infrared spectroscopy with Fourier transform spectra of adsorbed CO on supported Pd catalysts at 200 °C. Note: analysis was performed after catalyst reduction. |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d2re00259k |
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