Magdalena
Brzezinska
a,
Johannes
Niemeier
b,
Yannik
Louven
b,
Nicolas
Keller
c,
Regina
Palkovits
b and
Agnieszka M.
Ruppert
*a
aInstitute of General and Ecological Chemistry, Faculty of Chemistry, Łódź University of Technology, ul. Żeromskiego 116, 90-924 Łódź, Poland. E-mail: agnieszka.ruppert@p.lodz.pl; Fax: +48426313128; Tel: +48426313106
bInstitut für Technische und Makromolekulare Chemie, RWTH Aachen University, Worringerweg 2, 52074 Aachen, Germany
cInstitut de Chimie et Procédés pour l'Energie, l'Environnement et la Santé, ICPEES, CNRS, University of Strasbourg, 25 rue Becquerel, 67087 Strasbourg, France
First published on 26th August 2020
Succinic acid is a valuable biomass-derived platform molecule, which can be further catalytically converted into many industrially relevant molecules such as γ-butyrolactone, 1,4-butanediol or tetrahydrofuran. The influence of the support nature on both the activity of Ru/TiO2 catalysts and the selectivity pattern in the hydrogenation of succinic acid was investigated, with focus on the metal–support interaction, the crystallographic structure of the TiO2 support and the supported Ru nanoparticle size features. We showed that the catalyst activity was related to both the Ru particle size and the metal support interaction, those features being induced by the presence of the rutile phase within the TiO2 support and by the preparation method of the supported Ru particles. The rutile phase not only favors the formation of small Ru particles but also promotes stronger metal–support interaction compared with the anatase polymorph. Strong interactions between metal and support can also be formed via thermal reduction in contrast to low-temperature direct chemical reduction. Interestingly, a low temperature solar photon-assisted synthesis method facilitates very high succinic acid conversion, by enabling the stabilization of 1.8 nm small-size Ru nanoparticles in the absence of any rutile phase within the TiO2 support.
Whereas succinic acid has traditionally been produced from petroleum-based feedstock, nowadays it can however be efficiently obtained via a more environmentally friendly pathway, namely through processes based on the fermentation of biomass-derived sugars.2 In those processes, succinic acid is obtained dissolved in aqueous phase. To avoid the energy-intense separation from water and facilitate integration along the chemical value chain, the search for heterogeneous catalysts which are stable in water is highly desired.
In the last decade, different catalysts, mostly based on metals like Pd, Ru, Pt, Re or Cu, were investigated in this process,3,4 and several studies concentrated on Pd-based catalysts. Zhang et al. identified the Pd dispersion as a key factor responsible for high selectivity towards GBL (98%) obtained on Pd/AlOOH catalysts. They combined theoretical investigation and experimental data concluding that single Pd atoms are responsible for the high catalytic performance.5 Uniform, highly dispersed Pd nanoclusters supported on amino-functionalized silica spheres were also considered as active species responsible for the high GBL yield in the work of You et al. The role of the support was mainly related to the improved dispersion which enhanced the activity.6 Similarly, Song's group highlighted dispersion as a key-factor allowing to reach a high selectivity in the case of mesoporous composite Pd-based catalysts.7
Despite the significant focus on other metals, ruthenium was recognized in several works as the most active metal in this reaction. Its high activity was, however, often associated with a poor selectivity towards GBL. By comparing the activity of different metals (Pd, Pt, Rh, Ru) supported on carbon, Luque et al. have found that, although the Ru/C catalyst led to the highest conversion, THF was the main product instead of the highly valuable GBL.3
The selectivity towards GBL obtained with Ru catalysts can be significantly improved when doping by Re. The synergetic effect obtained through the Re–Ru association allowed to increase the selectivity to GBL, and the catalyst strongly outperformed the analogous Pd–Re bimetallic system that requires a much longer reaction time for achieving comparable selectivity.8 A similar effect can also be obtained through the addition of Co to the Ru catalyst, and the existence of new Co–Ru interactions allowed to significantly decrease the time necessary to achieve full succinic acid conversion from 7 h to 2 h for a reaction conducted in a dioxane–rich water solvent (15:
1) at 250 °C under 103.5 bar of H2.9
Despite a significant literature input devoted to the influence of metal dopants, there is only limited information concerning the influence of the support nature and properties on the catalytic activity in the hydrogenation of SA.
A direct effect of the support was reported by Chung et al. for mesoporous structured materials. In comparison to the MCM support, the incorporation of smaller Pd clusters within the SBA channels was proposed to directly result from the intrinsic structure of the SBA material, and to be responsible for the activity boost and the formation of cyclic products like GBL and THF.10 The Corma's group investigated the influence of both the support nature and the metal nanoparticle size on the catalytic activity in biomass-derived dicarboxylic acid hydrogenation. The authors reported that Ru/TiO2 showed better catalytic performance than Ru/C or Ru/CeO2 catalysts. Furthermore, the metal loading was optimized for the applied reaction conditions, a catalyst with a lower Ru content (0.64%) being more active in the carboxylic acid hydrogenation than those with higher metal contents (up to 5%).11
Later on, the group of Pinel demonstrated that both the titania support nature and the preparation method impacted on the activity of Pd/TiO2 catalysts. The authors showed that the deposition–precipitation method provided the most active catalysts independently of the titania support used. The highest conversion was observed for anatase-supported samples and was ascribed mainly to the good dispersion of the metal, whereas far lower conversions were obtained using a mixed phase anatase/rutile TiO2-P25 support. In contrast, no difference was observed in terms of selectivity pattern. Succinic acid was transformed firstly to GBL, which was further hydrogenated to BDO and THF, but only after reaching almost full conversion of SA.12 In another study, the same group evaluated two different titania materials as supports for Pd–Re catalysts, and suggested the enhanced dispersion of the metals as the key-factor responsible for the improved activity obtained for the anatase supported Pd–Re catalysts.8,13,14
We recently showed however that not only the metal dispersion was responsible for reaching high levels of conversion on TiO2 supported Ru catalysts. In the case of the hydrogenation of levulinic acid to γ-valerolactone in water as a solvent, the co-existence of both anatase and rutile polymorphs within the support was crucial. In addition, the interaction of the Ru nanoparticles with the anatase and rutile phases was reported to be of different character, and was proposed to significantly impact the catalytic performance.15
In the current work, we studied the influence of the titania support nature on both the activity of Ru/TiO2 catalysts and the selectivity pattern in the hydrogenation of succinic acid. We especially focused on the metal–support interaction, the crystallographic structure of the TiO2 support and the mean Ru particle size, as well as on the influence of the catalyst preparation method on the its performance.
Pure anatase-phase TiO2, labeled as anatase-P, was prepared via a sol–gel method in basic conditions with a final calcination at 500 °C in static air, using a titanium tetraisopropoxide ethanolic solution as precursor and ammonia as a pH-adjusting agent, as detailed in ref. 16.
Pure rutile-phase TiO2, further denoted as Rutile, was synthesized as described in the literature,17 through the controlled aging at room temperature of an anatase hydrosol derived from the hydrolysis of titanium isopropoxide in a hydrochloric acid aqueous solution in the presence of polyethyleneglycol porogen. After drying, the sample was submitted to a final calcination in flowing air (20 ml min−1) at 500 °C for 2 h (heating rate of 2 °C min−1).
Ru/TiO2 catalyst was also prepared using the UV100 support through the chemical reduction of ruthenium(III) nitrosyl nitrate (Aldrich, 99.99%) using NaBH4 (Sigma-Aldrich, 99%) as a reductive agent. The aqueous suspension of the titania support was stirred for 1 h in presence of Ru(NO)(NO3)3, before a threefold molar excess of NaBH4 was added. After stirring for 15 min, the catalyst was further washed with deionized water and dried at 120 °C for 2 h. This sample was further labeled as UV100-CR.
Furthermore, in the case of the anatase-P support, a Ru/TiO2 catalyst was prepared via a solar light-photoassisted synthesis method using Ru(acac)3 as precursor as described in the literature.18,19 It involved the controlled irradiation with simulated solar light for 3 h of a water–methanol TiO2 suspension in the presence of the Ru precursor, by taking advantage of the solar light-induced properties developed by the TiO2 surface for reducing the Ru precursor adsorbed at the support surface into metallic Ru. After filtration and washing with deionized water, the catalyst was dried at 100 °C before being used as-is without any final reductive treatment.
Surface area and porosimetry measurements were carried out on ASAP2010 Micromeritics using N2 as adsorbent at −196 °C, with a prior outgassing at 200 °C for 3 h in order to desorb the impurities or moisture. BET specific surface area was calculated from the nitrogen adsorption isotherm and the micropore surface area was derived using the t-plot method.
TEM measurements were conducted to measure particle size. TEM JEOL 2010 and JEOL 2100 microscopes operating at 200 kV equipped with an energy dispersive X-ray detector were used. The average Ru nanoparticle size was defined as usually:
TPR measurements were carried out on an AMI1 system from Altamira Instruments, equipped with a thermal conductivity detector, and were performed for investigating the catalyst reducibility. Before the measurement, the calcined catalysts were pre-treated with an O2/Ar (2:
98 v/v) flow for 30 min at 200 °C with heating rate of 10 °C min−1, and further submitted to a H2/Ar (5
:
95 v/v) flow at a weight hourly space velocity of 0.161 h−1.
CO adsorption/desorption measurements were carried out with a Nicolet 6700 FTIR spectrometer equipped with MCT detector made by Thermo Scientific, using a transmission cell. All spectra were recorded in a wavenumber range of 2300–1700 cm−1, with a scan number of 64 and a spectral resolution set at 4 cm−1. Before the measurement, the samples were first reduced following the same procedure used to prepare the catalysts. After reduction, the samples were cooled down to 40 °C in Ar, before the CO sorption was performed for 20 min and the spectra were collected every 5 min. The CO desorption occurred through a purge with pure Ar for 20 min, and the spectra were collected every 2 min. Gas flow was set at 20 ml min−1.
Considering GBL, THF and BDO as the only detected products from the SA conversion in those conditions, in agreement with the well-established literature reports,20,21 the conversion, selectivity and yield patterns used for characterizing the catalyst behavior were calculated as follows:
Additionally, the activity was defined here as the number of succinic acid molecules converted per number of Ru atoms per hour, as follows:
TiO2 supports | ||||||
---|---|---|---|---|---|---|
P25 | P90 | UV100 | UV100C | Anatase-P | Rutile | |
a The phase composition corresponds to the composition within the crystallized TiO2 phases (without considering the content of amorphous TiO2). b A and R represent the anatase and rutile content in the TiO2 phase composition, respectively. c Determined by using the method developed in ref. 22. d Determined by applying the Scherrer equation to the (101) and (110) peaks of anatase and rutile, at 25.7° and 27.5°, respectively. | ||||||
Composition [%]a,b | R: 20 | R: 10 | A: 100 | A: 100 | A: 100 | R: 100 |
A: 80 | A: 90 | |||||
Amorphous phase [%]c | 7 | 29 | 26 | 30 | 39 | 34 |
Average crystallite size [nm]d | R: 32 | R: 23 | 9 | 14 | 24 | 17 |
A: 22 | A: 13 | |||||
BET surface area (microporous content) [m2 g−1] | 55 (0) | 90 (0) | 330 (243) | 80 (0) | 27 (0) | 26 (0) |
Pore volume [cm3 g−1] | 0.12 | 0.24 | 0.22 | 0.32 | 0.14 | 0.19 |
The impossibility to obtain a high and homogeneous dispersion of Ru particles on the high specific surface area pure anatase TiO2 (UV100) highlighted the importance of using alternative preparation methods in order to obtain small size Ru particles on pure anatase supports. First, the use of NaBH4 as a room temperature chemical reductant allowed to prepare Ru nanoparticles with a mean particle size of 4 nm. Further, the implementation of a one-step solar light photon-assisted synthesis method allowed to prepare highly dispersed Ru nanoparticles in the case of the Ru/anatase-P material. The redox photoactivity developed by the anatase TiO2 support under solar light gave way to a mean Ru particle size of 1.8 nm. The photo-assisted synthesis facilitated the reduction of the adsorbed metallic Ru precursor to metallic nanoparticles with a controlled growth at the support surface, overcoming the need of any further reductive treatment at elevated temperatures.19
FTIR spectra of adsorbed CO recorded for the Ru catalysts show the presence of several bands at 1950, 1990–2000, 2060–2070, 2130 and 2170 cm−1 (Fig. 3). In the case of supported Ru catalysts, there is an ongoing discussion on the interpretation of the FTIR spectra and on band assignment.24–30 However, those bands could be attributed to bridge-bonded CO at 1950 cm−1, linearly bonded CO on steps at 1990–2000 cm−1, linearly bonded CO on faces at 2060–2070 cm−1,30 multicarbonyl species on partially oxidized Ru crystallites at 2130 cm−1,31 and CO adsorbed on the titania surface at 2170 cm−1 (illustration of the differently bonded CO is provided in Fig. S2†).24 The band corresponding to bridge-bonded CO was only observed for the high surface area anatase sample, probably due to the existence of very large Ru crystallites accessible for CO, and coexisted with the low-intensity band assigned to the linearly adsorbed CO. The lowest band intensities were observed in the case of the Ru/UV100 catalyst, what may suggest a location of a part of the Ru nanoparticles in the support micropores, with a resulting lower accessibility for CO molecules. Indeed, the removal of the microporosity by calcination of the support further led to the disappearance of the band assigned to bridge-bonded CO, while the total intensity of the bands corresponding to linearly bonded CO increased. The increase in the rutile phase content in the samples is connected with the increase of the band intensity and with the decrease of the ruthenium particle size.
![]() | ||
Fig. 3 FTIR absorbance spectra of adsorbed CO obtained for the Ru catalysts on the rutile (red); TiO2 P25 (black); TiO2 UV100C (green) and TiO2 UV100 (blue). |
Fig. 4a shows the influence of the rutile phase content in the TiO2 support on the maximum temperature of complete reduction of the supported phase. It can be observed that the maximum temperature of complete reduction first strongly increases with the increase in the rutile phase content until it reaches a 20% content, and further increases only moderately for a higher rutile content. The lowest value of 100 °C is observed for the catalyst supported on high surface area anatase (UV100), while this temperature further increases to 150 °C, 165–185 °C and finally 200 °C for medium surface area anatase (UV100C), mixed-phase supports containing rutile, and the pure rutile support, respectively. It may suggest that the rutile phase interacts more strongly with the ruthenium particles, so that a higher temperature is needed for complete reduction. This indicates that the crystalline phase of the TiO2 support strongly and directly impacts the full reduction of the supported Ru species, and consequently the strength of the interaction with the support.
The group of Crossley showed that the presence of rutile in the support stabilizes the Ru particles and consequently prevents the sintering phenomena.32 The group of Weckhuysen have further reported the absence of any sintering when Ru was supported on a mixed phase as well as on pure rutile supports, while Ru sintering was observed on pure anatase phase.33 Further, Sassoye et al. indicated that the migration of RuO2 can be observed from the anatase to the rutile phase when the TiO2 support contains both polymorphs.34 This confirmed the existence of weaker interactions of the supported Ru species with the anatase phase than with the rutile phase.
Taking into account that the rutile content in the support may also influence on the Ru crystallite size, in Fig. 4b we show the relationship between the mean Ru particle size and the maximum temperature of complete reduction that characterizes the strength of the Ru–TiO2 interactions. Generally, stronger interactions are related to the presence of smaller particles. However, the Ru particle size is not a predominant factor affecting the temperature of complete reduction of the supported phase, except for the UV100C-based catalyst. Indeed, the complete reduction temperature varies from 160 °C up to 200 °C in the case of the P90, P25 and rutile supports, although they exhibit a rather similar Ru nanoparticle mean size.
Ru catalyst | Activity [mol molRu−1 h−1] | SA conversion [%] | GBL selectivity [%] | THF selectivity [%] | BDO selectivity [%] |
---|---|---|---|---|---|
a Result obtained after reaction at 180 °C and under 80 bar H2. | |||||
Rutile | 8.1 | 51 | 40 | 2 | 58 |
P25 | 6.4 | 40 | 93 | 2 | 5 |
P25a | 6.7 | 43 | 67 | 6 | 27 |
P90 | 6.7 | 43 | 51 | 11 | 38 |
UV100C | 3.2 | 20 | 54 | 46 | 0 |
UV100 | 0.5 | 3 | 0 | 100 | 0 |
UV100-CR | 1.0 | 7 | 100 | 0 | 0 |
Anatase-P | 9.1 | 58 | 58 | 13 | 29 |
![]() | ||
Fig. 5 Catalytic efficiency of the Ru catalysts in terms of activity and selectivity to GBL, THF and BDO. Reaction time of 18 h at 180 °C under 50 bar H2. |
High succinic acid conversion was achieved using pure rutile as support for Ru catalyst, with an activity of 8.1 mol molRu−1 h−1, and selectivities to GBL and BDO of 40% and 58%, respectively. The presence of anatase within the mixed-phase supports was detrimental for the catalytic activity, which dropped down to 6.4–6.7 mol molRu−1 h−1 on both Ru/P25 and Ru/P90 catalysts, and also lower conversions of 40–43% were achieved. However, mainly GBL was observed on Ru/P25, with a selectivity of 93%, while the reaction was less selective on Ru/P90, with a broad product distribution of 51% for GBL, 38% for BDO and a relatively large THF contribution of 11%.
In the case of the Ru catalysts prepared on pure anatase by wet impregnation, far lower activities and SA conversions were obtained, whether the micropore content of the support has been suppressed by calcination or not. The reaction pathway proceeds towards THF through the transformation of the GBL intermediate, and a THF selectivity of 46% at a SA conversion of 20% (activity of 3.2 mol molRu−1 h−1) was observed with UV100C. Using high surface area UV100 with a high microporous content as a support, a further drop in activity to 0.5 mol molRu−1 h−1 was observed, with a full THF selectivity.
The beneficial input of the rutile polymorph on the activity of Ru catalysts was highlighted by Hernandez-Meija et al. for the xylose hydrogenation, with 98% yield to xylitol vs. 10% on pure anatase.23 Kim et al. reported that the presence of rutile increased the catalyst activity in CO2 methanation, thanks to a higher Ru dispersion originating from the RuO2 migration towards the rutile phase and the subsequent stabilization of Ru particles by epitaxy.34 The group of Weckhuysen also evidenced that the Ru catalyst stability depended on the crystallographic nature of the titania support, strong sintering being observed on pure anatase, while an irreversible reduction of the anatase support caused by strong levulinic acid adsorption induced the SMSI effect.33
A closer look reveals that both P25- and P90-supported Ru catalysts have almost similar activities, while they differ in terms of mean Ru particle size (2.1 nm vs. 2.9 nm), indicating that the particle size is not the only factor affecting the activity. Also, a negligible activity was observed for the catalyst prepared via the room temperature chemical reduction with NaBH4, despite an intermediate mean Ru particle size of 3.9 nm, suggesting that the absence of any reductive thermal treatment was detrimental to the activity, probably due to the impossibility to create proper interaction with the support. Interestingly, although here the catalyst was not submitted to any reductive thermal treatment and the support did not contain any rutile phase, the highest activity was observed for the Ru catalyst prepared via room-temperature solar light photon-assisted synthesis (Ana-P). This can be explained by the room temperature charge-driven mechanism of the photon-assisted method that does not require the presence of any rutile phase for stabilizing size-controlled Ru nanoparticles at the TiO2 surface.16,19 Further, we also suggest that the photogenerated electron and hole charges are subsequently transferred to the Ru–TiO2 interface during the Ru nanocluster growth and the formation of the metallic particles, favoring the establishment of the necessary interaction between the Ru species and the TiO2 support.
We cannot rule out that the differences observed in Ru nanoparticle sizes might affect the electronic character of the catalysts, especially for the very small sizes. This might be considered as an additional factor contributing to the effect of the Ru nanoparticle size on the behavior of the catalysts.
![]() | ||
Fig. 8 Influence of the activity of the catalyst on a) the GBL yield and b) the BDO yield in the SA hydrogenation. |
In the case of the BDO yield, a volcano-shaped pattern can be seen as a function of the catalyst activity. No BDO was observed for the catalysts supported on anatase reduced in H2 flow or with NaBH4, while a maximum yield of 30% was achieved for the catalyst supported on pure rutile. Interestingly, the catalyst supported on anatase prepared via the photoassisted method showed a certain yield to BDO (17%).
As far as the THF yield was concerned, no dependence on the catalyst activity was observed. In contrast, a clear relationship could be drawn between the mean Ru nanoparticle size and the THF yield in the case of the catalysts prepared via the standard wet impregnation method (Fig. 9), while no clear trend was observed for both GBL and BDO yield (not reported). Interestingly, the THF yield significantly dropped with the decrease in the mean Ru crystallite size, from 9% on the Ru/UV100C catalyst with a large average Ru particle size of 10 nm, down to ca. 1% for the catalysts with the average Ru particle size of about 2 nm, i.e. those with TiO2 P25 and pure rutile TiO2 supports. While this trend was well visible for the samples that were submitted to the final thermal treatment in order to obtain metallic Ru nanoparticles, the two other samples (for which no thermal treatment was applied) did not follow this trend. Indeed, a THF yield of 8% (i.e. close to that obtained using UV100C with large Ru crystallites) was achieved on the Ru/anatase-P catalyst prepared via the photon-assisted synthesis crystallites, which had a small mean Ru particle size of 1.8 nm. In contrast, the catalyst prepared by chemical reduction with NaBH4 displayed inversely a very low THF yield, while it exhibited a moderate (intermediate) mean Ru particle size of 3.9 nm.
To summarize, we showed that the behavior of Ru/TiO2 catalysts depends on both the Ru particle size and the metal–support interaction. Those features are induced by the presence of different crystallographic phases in the support and by the preparation method. The rutile phase in the support favors the presence of small metallic Ru particles. This induces different interactions between the supported metal and the respective TiO2 phases, the Ru–TiO2 interaction being reported to be stronger for rutile than for anatase.37 Stronger metal–support interaction can be also induced by using a thermal reduction method, in comparison to the low-temperature direct chemical reduction, while the solar photon-assisted method is a way to stabilize small-size Ru nanoparticles in the absence of any rutile phase within the support.
Footnote |
† Electronic supplementary information (ESI) available: XRD and TPR characterization, illustration of the bonded CO molecules in FTIR. See DOI: 10.1039/d0cy01446j |
This journal is © The Royal Society of Chemistry 2020 |