N. Alonso-Fagúndeza,
I. Agirrezabal-Telleriab,
P. L. Ariasb,
J. L. G. Fierroa,
R. Mariscala and
M. López Granados*a
aGroup of Sustainable Energy and Chemistry (EQS), Institute of Catalysis and Petrochemistry (ICP-CSIC), C/ Marie Curie 2, Campus de Cantoblanco, 28049 Madrid, Spain
bDepartment of Chemical and Environmental Engineering, Engineering School of The University of The Basque Country (UPV/EHU), Alameda Urquijo s/n, Bilbao 48013, Spain. E-mail: mlgranados@icp.csic.es
First published on 13th October 2014
This investigation explores the selective liquid-phase oxidation of furfural to maleic acid (MA) using hydrogen peroxide as an oxidant and titanium silicalite (TS-1) as a catalyst. The effect of temperature and of the concentration of H2O2, furfural and catalyst on the MA yield was studied. The highest yield, 78 mol%, was obtained under the following reaction conditions: 4.6 wt% of furfural, 4.6 wt% of catalyst, a H2O2/furfural mol ratio of 7.5, corresponding to 12.3 wt% of H2O2, 323 K and 24 hours of reaction. To reduce the amount of H2O2 employed, a two-step sequence of reactions was conducted using TS-1 and Amberlyst 70 consecutively as catalysts in the first and second steps, respectively. In this case, a H2O2/furfural mol ratio = 4.4 was required, which is quite close to the stoichiometric ratio (3.0), and a maleic acid yield close to 80% was obtained under 4.6 wt% of furfural, 4.6 wt% of catalyst and 28 h of reaction at 323 K; after 52 h of reaction, the MA yield reached 92%. Fresh and used catalysts were characterised by X-ray diffraction (XRD), Raman spectroscopy, total reflection X-ray fluorescence (TXRF), X-ray photoelectron spectroscopy (XPS), N2 adsorption–desorption isotherms and thermogravimetric analysis. Ti was largely incorporated within the silicalite framework, but the presence of some TiO2 anatase was also confirmed. Ti leaching was observed, especially during the first run but became much less important in successive cycles. Leaching affects both anatase and Ti species within the silicalite framework. Notwithstanding the leaching, when using pure furfural, TS-1 could be reused for six runs without noticeable deactivation, whereas when using furfural directly derived from biomass, weak but visible deactivation occurred upon reutilisation; this deterioration must be related to the presence of some organic products other than furfural.
Alternative routes based on the oxidation of furfural to MAN and MA, either in gas or liquid phase, have been reported by different research groups. Furfural is a chemical currently obtained from the pentoses contained in lignocellulosic agroresidues; approximately 250–400 ktons of furfural are synthesised annually from this carbohydrate feedstock.4–6 Therefore, these routes from furfural constitute renewable pathways for the manufacture from biomass of MA, MAN and their derived products. Thus, a renewable route for phthalic anhydride formation by Diels–Alder condensation with furan has very recently been demonstrated.7
Gas-phase oxidation of furfural to maleic anhydride is a well-known route, and yields up to 75% can be achieved by using vanadium-oxide-based catalysts; cheap air O2 is used as an oxidising agent.8–12 However, dilute furfural streams (below 1% v/v) are required to achieve high MAN selectivity. The reaction is conducted at high temperatures (higher than 523 K), and the vaporisation of furfural is required. Both of these features have a negative impact on the energy balance and consequently the economic viability of this process.
Liquid oxidation with O2 at milder temperatures has also been explored using homogeneous catalysts like phosphomolybdic acid in a water/tetrachloroethane biphasic system, achieving MA yields not larger than 50%.13,14 Moreover, although milder temperatures are required (383 K), high O2 pressure (2 MPa) is needed. The reusability of these catalysts has not been proved, which is crucial to evaluate the feasibility of possible industrial applications.
Another liquid-phase alternative that has recently been investigated is furfural oxidation with hydrogen peroxide. So far, the best results using this strategy have been achieved by using either a soluble acid catalyst like H2SO4 and p-toluensulphonic acid or by using solid sulphonic-based catalysts such as sulphonic resins or poly-(styrene sulphonic acid).15–19 Oxidation with H2O2 seems attractive for industrial application, first because the reaction proceeds under very mild conditions (low temperatures and atmospheric pressure), and second because aqueous furfural solutions can be processed, which is a key advantage. When pure furfural is produced from lignocellulosic agroresidues, the primary raw product is an aqueous furfural solution that must be further purified by an energy-intensive double distillation. Processing primary raw aqueous furfural solutions would imply that distillation steps are not required, which positively impacts the energy and economic balance of the overall process.
However, the main drawback for oxidation with hydrogen peroxide using acid catalysts is the control of selectivity. A wide distribution of products such as MA, succinic acid (SA), fumaric acid (FumA), β-formylacrylic acid or 2(5H)-furanone is obtained. This lack of selectivity is a consequence of the very complex reaction network that starts with the Baeyer–Villiger oxidation of furfural to the corresponding ester.15,16,19 Large H2O2/furfural ratios (much larger than 7) are required to improve the MA yield, whereas for lower ratios succinic acid is the main product. Maleic acid could be obtained by dehydrogenation of succinic acid,20 but this would mean an additional step. The identification of a robust solid catalyst that can selectively oxidise furfural to MA in one step and that can be easily recovered from the reaction mixture and reutilised for a large number of runs is still a challenge.
The selective oxidation of furan with aqueous H2O2 using TS-1 has been already investigated.21,22 The furan ring possesses a similar chemical structure to furfural, except for the absence of the aldehydic functional group. Maleic dialdehyde and 5-hydroxy-furan-2(5H)-one were obtained selectively by the oxidation of furan using H2O2/furan with approximate mol ratios of 1 and 2, respectively. These products are closely related to maleic acid, as the latter can be obtained from them by further oxidation. Titanium silicalite 1 (TS-1) is frequently used in the epoxidation of numerous alkenes.23–25 The ability of TS-1 to activate hydrogen peroxide is linked to the particular environment of Ti(IV) cations incorporated into the silicalite framework and located within the hydrophobic pores of the zeolite. This allows simultaneous adsorption of the hydrophobic substrate and the oxidant.21,26,27
The latter results using furan encouraged us to explore the utilisation of TS-1 in the selective oxidation of furfural to MA by using H2O2. Because the oxidation of furfural (a C5 aldehyde) to maleic acid (a C4 diacid) implies the loss of a carbon atom, the key question is whether, besides the epoxidation and oxidation steps, the TS-1 catalyst can also promote in practice the removal of a C atom.
In principle the oxidation of furfural with H2O2 is more advantageous than the furan oxidizing route previously demonstrated.21,22 Furan is currently produced by decarbonylation of furfural1,2 and therefore the production of MA from furan would imply two steps: first decarbonylation and subsequently the oxidation of furan. A first drawback of this furan route is that the decarbonylation of furfural is conducted at relatively high temperatures (423–453 K) and in the presence of noble metal catalysts that unavoidably deactivate. Reactivation periods are required to regenerate the initial activity that complicates the viability of the furan route. On the contrary the route here proposed implies the direct conversion of furfural in one-step and at mild temperatures.
In this work, we demonstrate for the first time that TS-1 is an excellent catalyst for the transformation of furfural to MA. We have also conducted the necessary study examining the effect of operating variables like temperature, H2O2/furfural ratio and catalyst and furfural concentration on the catalytic properties of TS-1. Specific attention was paid to the deactivation of catalyst and the reutilisation behaviour of TS-1 under the optimum reaction conditions, using both pure furfural provided by a commercial supplier and aqueous solutions of furfural obtained directly from corncob residues. A commercial TS-1 with a Ti/Si at. ratio above the threshold required to fully saturate the silicalite framework with Ti cations was used in this investigation. This means that a TS-1 with the largest possible incorporation of Ti within silicalite (active sites) was used.
A known amount of reaction mixture (ca. 0.5 g) was sampled at different reaction times and was analysed by HPLC, using a known amount of a 30 mg g−1 aqueous solution of oxalic acid as an internal standard (ca. 15 mg of oxalic acid was added to each aliquot). Subsequently, the aliquot was diluted 10–20 times with water. This diluted aliquot, after being filtered through a 0.22 μm syringe filter, was then analysed in an Agilent 1200 HPLC chromatograph equipped with a refraction index detector and a Bio-Rad Aminex HPX-87H column (300 mm × 7.8 mm). A 0.005 M H2SO4 mobile phase was employed as the eluent at 328 K and a 0.4 mL min−1 flow rate. In addition to oxalic acid and furfural, the following products were detected by HPLC: MA, malic acid, SA, formic acid (FA), fumaric acid (FumA), 5-hydroxy-furan-2(5H)-one (hydroxyfuranone), furan-2(5H)-one (furanone) and furoic acid (FurA). Deeper details of the analyses are given in Fig. SI1 of ESI section.†
Furfural conversion and product yields were calculated according to the following formulas:
The hydrogen peroxide concentration at a given reaction time was determined by iodometric titration. Approximately 0.5 g of reaction sample was diluted 10–20 times with water. Then, 0.5 g of this diluted solution was poured into an Erlenmeyer flask containing 20 mL of water. After adding 2 mL of potassium iodide solution (10%) and 2.5 mL of an acid mixture consisting of a solution of ammonium molybdate and H2SO4, the flask was closed, gently agitated and allowed to rest for five minutes to form triiodide species by oxidation of the iodide with H2O2, which gives a brown colour to the solution. The mixture was then titrated with a ca. 0.1 M sodium thiosulfate solution until the brown triiodide colour was reduced to a light straw colour. A few drops of starch solution (10 g L−1) were added, and the solution became dark blue. Titration was continued until the colour of the solution changed sharply from blue to colourless. A titration of a blank solution (pure water) was also carried out following the same procedure. The actual titer of the sodium thiosulfate solution was determined by titration with potassium iodate solution (0.1 N).
The amount of H2O2 present in solution was calculated as follows:
For the reutilisation tests, catalyst was filtered out of the reaction medium by using a filtration cell and a ceramic membrane. The catalyst was washed twice with water (ca. 200 mL) to remove reaction products that could interfere in successive analysis, carefully removed from the membrane to prevent losses during handling, and dried at 333 K overnight before performing a new reaction run. The filtered solution from the catalyst wash steps (including the filtrate from the reaction medium) was analysed by TXRF for the quantitative determination of Ti and Si.
Nitrogen adsorption–desorption isotherms were recorded at the temperature of liquid nitrogen (77 K) using a Micromeritics TriStar 3000 apparatus. The sample was previously outgassed at 140 °C for several hours. The specific area was calculated by applying the BET method to the range of relative pressures (P/P0) of the isotherms between 0.03 and 0.3 and by assuming a value of 0.162 nm2 for the cross-section of adsorbed nitrogen molecules at 77 K.
TXRF (total reflection X-ray fluorescence) analysis was performed in a S2 PICOFOX instrument equipped with two X-ray fine focus lines, Mo and W anodes, and a Co(Li) detector with an active area of 80 mm2 and a resolution of 157 eV at 5.9 keV (Mn Kα). The acquisition time was 300 s and 500 s for qualitative and quantitative analysis, respectively. To carry out the TXRF analysis, a Mo X-ray source was used for Si and Ti determination. For the analysis of solid samples, 10–15 mg of sample was ground in an agate mortar to a powder with a particle size less than 10 μm. Subsequently, 10 mL of high-purity water was added to the powder. The sample was homogenised for 15–20 min by ultrasonic desegregation in order to disperse any possible agglomeration of particles. A 5 μl aliquot of the suspension was removed and placed on a flat carrier of plastic after which the water was evaporated by vacuum.
Raman spectra were recorded on a single-monochromator Renishaw 1000 spectrophotometer equipped with a CCD cool detector (200 K), with an argon laser as the exciting source (λ = 532 nm), a supernotch filter, and an in situ cell that enables sample treatment under a flow of gas. Raman spectra were recorded at room temperature with a laser power of 2 mW after an in situ calcination of the samples in synthetic air with a heating rate of 10 K min−1 up to 833 K for 30 min.
X-ray photoelectron spectra (XPS) were acquired with a VG Escalab 200 R spectrometer equipped with a hemispherical electron analyser and a Mg Kα (1253.6 eV) X-ray source. The solids were outgassed at 393 K for 1 h at 10−5 mbar to remove water before transfer to the ion-pumped analysis chamber. Ti 2p, C 1 s, O 1 s and Si 2p core level were scanned a sufficient number of times to obtain high signal-to-noise ratios. The static charge of the samples was corrected by referencing all binding energies (BEs) to the Si 2p peak (103.4 eV). The accuracy of the BE was ±0.1 eV. The areas of the peaks were computed by fitting the experimental spectra to Gaussian/Lorentzian curves after removing the background (using the Shirley function). Surface atom ratios were calculated from peak area ratios normalised by using the corresponding atomic sensitivity factors.28
Thermogravimetric analysis (TGA) under a controlled atmosphere was carried out on a Mettler Toledo TGA/SDTA 851e, using a heating rate of 10 K min−1 up to a maximum temperature of 973 K under a synthetic air atmosphere.
5-Hydroxy-furan-2(5H)-one (hydroxyfuranone), MA and FA were the main reaction products, malic acid was also detected but with a yield less than 5%. The yield for the remaining possible reaction products (SA, furanones, FumA, furoic acid) was well below 2.4%. The low yield of these products, especially SA and furanones, was rather unexpected: previous results obtained in the liquid phase oxidation of furfural with H2O2 yielded a wider variety of products including SA and furanones.15–19 It is concluded that the reaction mechanism when using TS-1 is different to that of the conventional acid catalysts used previously to conduct this reaction. When acid catalysts are used, the reaction initiates with a Bayer–Villiger step to form 2-hydroxyfuran, which is in equilibrium with furan-2(5H)-one and furan-2(3H)-one (see Scheme SI1†). The eventual oxidation of these furanones gives rise to SA, hydroxyfuranone and MA. Therefore, it appears that when reaction initiates with a Baeyer–Villiger oxidation, a wider distribution of products is obtained.15–19 This is not the case with TS-1. We will return to these points when discussing the reaction mechanism below.
It was also assumed that formic acid arises both from the deep oxidation of the organics and from the loss of formic acid required to convert a C5 chemical into a C4 compound.19 Accordingly, the FA yield was calculated by subtracting the FA supposedly released by the formation of C4 products (1 mol of FA per mol of C4 product) from the total molar quantity of FA detected (the molar quantity of FA formed by deep oxidation was divided by 5 to express the value on a furfural basis). As shown in further figures, the carbon balance can approach 100% under optimum reaction conditions, but for the reaction conditions used in Fig. 1, the carbon balance was always below 100%. In principle, this incomplete carbon balance may be due to the total oxidation to CO2 (not quantifiable by HPLC analysis). However, this is not the only possibility, and the formation of HPLC-silent products can also contribute to the incomplete carbon balance. The carbon balance improved as the reaction progressed, suggesting that these unidentified HPLC products may be (partially oxidised) intermediates of the reaction.
As expected, the rate of furfural conversion increased upon raising the reaction temperature. Thus, at 323 K, full furfural conversion was reached after 6 h, whereas only 3 h was required for 333 K and 1 h was enough at 343 K. A rapid perusal of the figures also indicates that at short reaction times, hydroxyfuranone predominates among the detected products, but for longer periods, MA is the major product. It has been previously suggested that MA is formed at the expense of hydroxyfuranone oxidation; in our experiments at 323, 333 and 343 K, the hydroxyfuranone yield reached a maximum (close to 40%) at 3, 2 and 1 h, respectively, while MA yield continuously rose, indicating that the latter is not a primary product.19 A remarkable result is that the maximum yield of MA (57%) was achieved at 323 K after 24 h of reaction, whereas at higher reaction temperatures, the yield decreased. Thus, the maximum yield at 333 K was 52% (for 24 h), and the maximum at 343 K was 49% (for 6 h). For longer reaction times at 343 K, the MA yield visibly decreased.
In a reaction pathway compatible with the results of Fig. 1, furfural is rapidly oxidised through unknown intermediates to hydroxyfuranone: a C1 species (formic acid) is released to form the C4 product. Hydroxyfuranone is subsequently oxidised to MA. In addition, furfural and all the other organic products can undergo deep oxidation to formic acid and to CO2.
In summary, for the reaction temperatures tested, 323 K results in the maximum MA yield. This was the reaction temperature selected for further studies. We discarded lower temperatures because the reaction rates would be very slow. Similar conclusions can be reached by working at lower H2O2 concentrations at the three different temperatures tested (results included in Fig. SI2 of the ESI†).
As regards the transformation to oxidised C4 compounds, the major detected products were hydroxyfuranone and maleic acid; the combined yield of FA and malic acid was smaller than 9%. The yields of the remaining products was smaller than 2%. For H2O2/furfural mol ratio = 4, the MA formation rate was slower than that at 7.5; thus, after 24 h of reaction, only a 28% MA yield was reached, whereas for a ratio of 7.5, the yield was 57%. In principle, one might assume that a H2O2/furfural mol ratio > 7.5 would result in a better MA yield, and at short reaction times (time < 7.5 h) in these conditions, the formation rate of MA is substantially faster (at the expense of a faster disappearance of hydroxyfuranone). However, the MA yield attains a maximum yield of 44% at 7.5 h of reaction, and after 24 h of reaction it decreases to 36%. The high hydrogen peroxide concentration results in an overoxidation of MA.
In summary, an excess of H2O2 with respect to the stoichiometric amount for furfural oxidation to MA is needed to improve the MA yield. The optimum H2O2/furfural mol ratio is approximately 7.5; lower ratios result in lower reaction rate, and larger ratios result in overoxidation. Similar conclusions were obtained when conducting similar experiments to those presented in Fig. 2, but with a larger catalyst concentration (4.6 wt%). The results are presented in Fig. SI3 of the ESI section.†
The incorporation of more catalyst intensifies this effect, and thus, for a catalyst concentration of 4.6 wt% (TS-1/furfural wt. ratio = 1), a MA selectivity close to 80% was attained for 24 h of reaction, with residual formation of malic and formic acids. It must be stressed that, for the latter specific reaction conditions, the carbon balance was close to 100% for all aliquots analysed throughout the kinetic experiments. The latter suggests that for a catalyst concentration lower than 4.6% a carbon balance smaller than 100% would be very likely due to the formation of undetectable intermediates. On the other hand, a larger catalyst concentration (9.2 wt%) resulted in the overoxidation of MA, very likely to CO2, as can be deduced from the lower MA yield, larger FA yield and incomplete carbon balance.
H2O2 consumption is very selective at the beginning of the reaction when hydroxyfuranone predominates. However, as the reaction proceeds, selectivity worsens, indicating that a large fraction of H2O2 is consumed in unselective transformations. Thus, when 4.6 wt% of furfural is used (Fig. 4b), for 1 h of reaction, the selectivity of the H2O2 devoted to produce C4 compounds is close to 80%, and as the reaction progresses, the selectivity continuously decreases down to a value of 40% after 24 h of reaction. Similar trends can be observed for the remaining experiments in Fig. 4. Formic acid formation partly explains the unselective transformation of H2O2, but there are other unselective routes; we will address this point in Section 3.3.
Regarding MA selectivity, a very remarkable result is that for reaction times shorter than 7.5 h, the furfural concentration clearly has a very positive effect on the MA yield. Thus, the MA yield after 7.5 h of reaction is 25, 53, 68 and 69% for 2, 4.6, 7.5 and 9.2 wt% of furfural, respectively. The intrinsic MA formation rate was calculated after 1 h of reaction to take into account the fact that the catalyst concentration also increases throughout the series of experiments (furfural/TS-1 ratio was kept constant). The intrinsic rate was found to be 0.14, 0.44, 0.82 and 0.87 μmol of furfural gcat−1 s−1 for 2, 4.6, 7.5 and 9.2 wt% of catalyst, respectively. Therefore, the intrinsic MA reaction rate also rises with furfural concentration, which means that the effect is due to the increase of furfural concentration. An explanation could be that as the furfural concentration rises, so does the relative surface furfural coverage with respect to other reactants. In any case, the increase in both the MA yield and formation rate levels off for furfural concentrations larger than 7.5 wt%. Moreover, when 9.2 wt% of furfural is used, overoxidation of MA is evident for longer reaction times; thus, for 24 h of reaction, the MA yield (71% yield) is smaller than that for the 4.6 and 7.5 wt% experiments (78 and 80% yields, respectively). The overoxidation of products in the 9.2 wt% experiment is also evident by the stronger deviation of the carbon balance, to a value notably lower than 100%.
In summary, we can conclude that among all the reaction conditions tested, the optimum reaction conditions to obtain the highest MA yield (80%) are those used in Fig. 4b and c: 323 K, between 4.6–7.5 wt% of TS-1, TS-1/furfural wt ratio = 1; H2O2/furfural mol ratio = 7.5 and 24 h of reaction.
Amberlyst 70 displayed an oxidation activity pattern typically catalysed by strong acids and a wide number of products can be obtained.15,16,19 Succinic acid, furan-2(5H)-one and maleic acid are mainly formed, hydroxyfuranone, and malic, fumaric and formic acids are also detected at non-negligible yields, especially at shorter reaction times. After 24 h of reaction, the yield of SA, furan-2(5H)-one and MA was approximately 50, 30 and 20%, respectively. Although the ZSM-5 zeolite presents acid sites on its surface, these sites are not as active as those of TS-1 or as the sulphonic sites of Amberlyst 70. The latter presents a comparatively large strong-acid-site concentration (2.55 mmol gcat−1),19 which explains its relatively high activity. ZSM-5 displays an activity pattern resembling that of a catalyst-free run (see Fig. 3a). After 24 h of reaction, an MA yield of 15% and SA yield of 30% was observed for ZSM-5. Accordingly, the catalytic activity of TS-1 cannot be associated to acid sites present in the MFI-framework of TS-1, but rather to the presence of Ti(IV) sites in the TS-1. Anatase presents very active sites, but the Ti sites in anatase are not as selective as framework Ti in TS-1: the H2O2 efficiency is lower, the carbon balance is incomplete and the MA yield is lower (MA yield of 31% was observed after 24 h of reaction). These latter results suggest that Ti sites in anatase are not responsible for the good behavior of TS-1. In summary, among the family of catalysts tested, TS-1 features a high activity and selectivity to MA.
It has been reported that furan can be oxidised very selectively with hydrogen peroxide to maleic dialdehyde21 or to hydroxyfuranone22 by using a H2O2/furfural mol ratio of 1 and 2, respectively. The latter can eventually be oxidised to MA. Therefore, if furan could be formed from furfural, the oxidation of furan would yield MA, provided that a H2O2/furfural ratio > 2 is used.
One possibility is that the reaction starts with the oxidation of furfural to furoic acid, which can subsequently be transformed to furan by releasing formic acid (see Scheme SI2 in the ESI† for a description of this mechanism proposal). However, this possibility can be discarded because when the oxidation of furoic acid with H2O2 was conducted by using TS-1 (at 323 K, 4.6 wt% of furoic acid, 4.6 wt% of TS-1 and a H2O2/furoic acid mol ratio of 7.5, equivalent to 12.3 wt%) the MA yield was much lower than that obtained with furfural (see Fig. SI7 in the ESI† for further details).
Another plausible possibility is that furan can be formed by the decarbonylation of furfural. However, the decarbonylation of furfural requires different catalysts and reaction conditions to proceed,30–32 and therefore this route can also be discarded.
We propose a different mechanism based on the results and on the proposal of Jacobs et al. when oxidising furan to maleic dialdehyde.21 They proposed that one of the double bonds in the furan ring is epoxidised and the thus-formed epoxide then rapidly rearranges, yielding unsaturated 1,4-dicarbonyl compounds. The same epoxidation and rearrangement steps can be applied to furfural (see Scheme 1): the double bond with less steric hindrance is selectively epoxidised, and the furfural-epoxide rapidly undergoes a rearrangement to yield the Z-4-oxopent-2-enedial. The loss of a carbon atom is still needed for the formation of the corresponding C4 derivative. We propose that the formation of a C4 intermediate occurs via Baeyer–Villiger oxidation of the aldehyde functionality at 1-position of the Z-4-oxopent-2-enedial. An ester is formed, which is rapidly hydrolysed to form β-formylacrylic acid ((Z)-4-oxobuten-2-enoic acid), releasing formic acid. The electron withdrawing nature of the acyl group directly bonded to the reacting aldehyde at C1 strongly increases its electrophilicity favoring the Baeyer–Villiger reaction and justifying the regioselecctivity of the process. Formylacrylic acid is in equilibrium with the hydroxyfuranone. Experimentally, the formation of MA parallels the consumption of hydroxyfuranone. This suggests that hydroxyfuranone can be directly oxidised to MA. However, it cannot be excluded that MA is formed by the oxidation of β-formylacrylic, in equilibrium with hydroxyfuranone. We could not identify any HPLC peak as β-formylacrylic, very likely because the equilibrium is strongly shifted to hydroxyfuranone. It is also possible that the former is present at very low concentration, and therefore difficult to detect by HPLC, but still involved as an intermediate of the reaction. If so, whereas β-formylacrylic is consumed by oxidation to MA, so must be hydroxyfuranone.
The stoichiometric H2O2/furfural mol ratio required to selectively oxidise furfural to MA is 3. The maximum yield to MA was achieved by using a mol ratio = 7.5, which is more than double the stoichiometric ratio. The unselective utilisation of H2O2 comes from thermal and catalytic decomposition. Interestingly, the results presented in Fig. SI5† indicate that the catalytic decomposition is seriously inhibited by the presence of furfural. At the beginning of the reaction, decomposition is practically negligible: only after 5 hours is the catalytic decomposition detectable.
On the other hand, when TS-1 is used as catalyst and at short reaction times, hydroxyfuranone is primarily produced, with a relatively selective utilisation of H2O2. Kinetic data show that furfural oxidation to hydroxyfuranone is very rapid and selective, even when lower H2O2/furfural mol ratios are used (see Fig. SI3a†). Therefore, a good strategy would be to conduct the oxidation in two steps; in the first step, to oxidise rapidly furfural to hydroxyfuranone using TS-1 and a H2O2/furfural mol ratio close to stoichiometry. For short reaction times, the unselective catalytic decomposition of H2O2 is prevented. In a subsequent step, the oxidation of hydroxyfuranone to MA will be conducted with another catalyst because TS-1 unselectively decomposes H2O2. Sulphonic-based catalysts have demonstrated a capacity to transform hydroxyfuranone to MA.15,16,19
In practice, we proceeded as follows: first, the oxidation of furfural to hydroxyfuranone was conducted by using TS-1 as catalyst with a H2O2/furfural mol ratio of 2.4 (2 mol of H2O2 are needed for the stoichiometric oxidation of furfural to hydroxyfuranone). Previous reactions with a low H2O2 concentration (Fig. SI3a† (H2O2/F mol ratio = 2.15)) showed that after 4 hours of reaction, the hydroxyfuranone concentration did not increase, most likely because of the total consumption of the H2O2. For that reason, this first reaction step was carried out for 4 h. After that, the TS-1 catalyst was filtered off and the second oxidation step was conducted by using an Amberlyst 70 sulphonic resin as a catalyst. Further addition of H2O2 was performed to obtain a H2O2/furfural mol ratio of 2 with respect to the initial furfural concentration. One mol of H2O2 is needed for the stoichiometric oxidation of hydroxyfuranone to maleic acid, so a small excess of H2O2 was incorporated to account for non-selective decomposition. To prevent the dilution of the reaction media, a 70 wt% H2O2 solution was used to incorporate H2O2 in this second step. Fig. 6 displays the results obtained by taking samples at different reaction times. Products yields are calculated with respect to the initially loaded furfural.
After 4 h, the oxidation of furfural with TS-1 resulted in a 70% hydroxyfuranone yield, while the yield of maleic acid was less than 10%. However, once the TS-1 was filtered off and Amberlyst 70 and further H2O2 were incorporated, the selective oxidation of hydroxyfuranone to maleic proceeded continuously, and after 24 h of reaction with Amberlyst (equivalent to 28 h of total reaction time), the MA yield was close to 76%, very close to that obtained after 24 h with TS-1 (78%). The MA yield reached almost 90% after 2 days with Amberlyst. These results therefore demonstrate that MA can be produced from furfural by a two-step catalyst process with high selective utilisation of both furfural and H2O2. The overall H2O2/furfural mol ratio was 4.4.
Regarding the aqueous solution of pure furfural, successive reutilisation runs were carried out after 7 h of reaction, with a catalyst and furfural content of 4.6 wt% and a H2O2/furfural molar ratio of 7.5, corresponding to 12.3 wt% H2O2. The catalyst was filtered off and dried before each new run (see Experimental section for details). Medium-term reaction times (7 h) are more sensitive to detect the deactivation processes. Longer reaction times may miss the deactivation if the deactivation is not very intense. Fig. 7 shows the results obtained after 6 reutilisation cycles. The conversion and the yields of the main products are represented (MA, 5-hydroxyfuranone and FA). The results of a blank experiment without TS-1 catalyst are also included (first column): much lower values for the conversion and yields to selective oxidation products were obtained in this blank test.
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Fig. 7 TS-1 catalyst reutilisation tests for aqueous solution of furfural (4.6 wt%), 323 K, H2O2/F mol ratio = 7.5, corresponding to 6.6 wt% of H2O2, 4.6 wt% catalyst and 7 h reaction. |
When TS-1 was reused, the conversion values remained at 100% throughout all the runs. Moreover, the yields of MA, hydroxyfuranone and formic acid remained quite similar for all the runs investigated; MA yields were between 43–48% and hydroxyfuranone between 40–50%. Attending to these results, we can conclude that when commercial furfural is used, TS-1 is quite stable, and no sign of deactivation could be observed for at least 6 cycles.
Reutilisation runs were also conducted by using aqueous furfural solutions obtained from lignocellulosic biomass. Briefly, furfural was obtained from corncobs by using Amberlyst 70 as catalyst, at 453 K, 19 bar and by using a N2 flow of 150 mL min−1 (STP) to strip the water-furfural vapour stream. Stripping of furfural by N2 results in the rapid extraction of furfural from the reaction mixture, which prevents furfural from being consumed in further secondary reactions in the liquid phase. This furfural stream is condensed to separate gases from the aqueous furfural solution. Further details of the procedure can be found elsewhere.33,34 The furfural concentration of this aqueous solution was determined to be 2.5% (GC analysis). Other impurities like acetic acid and 5-methyl-furfural were also detected by GC-MS. The results obtained after successive reutilisation runs at 323 K, 24 h of reaction, H2O2/furfural mol. ratio = 7.5 and catalyst/furfural wt ratio = 1 are displayed in Fig. 8. The actual furfural concentration in the reaction media was 2 wt%, and at this relatively low concentration of furfural, the rates of furfural conversion and MA formation are lower than those found when the optimum reaction conditions are set (see Fig. SI8 in the ESI† for the kinetics of oxidation when this biomass furfural solution was used, and see also Fig. 4a for the kinetic curve of commercial furfural at similar reaction conditions to those in Fig. 8). To obtain a measurable and relatively high MA yield (larger than 30%), a long reaction time is needed (24 h).
When aqueous furfural obtained directly from biomass is used, a slight but continuous deactivation of TS-1 can be observed. The deactivation is more visible in the MA yield, as the hydroxyfuranone yield remained above 40% for the first six runs (in the seventh run the yield dropped to 31%). It is also noteworthy that the formic acid yield slightly but inexorably increased upon reutilisation runs, which confirms that the selective oxidation sites of TS-1 are being deteriorated by the utilisation of real furfural. All these results strongly suggest that the impurities present in the real aqueous furfural derived from biomass have a detrimental effect on the deterioration of TS-1. The removal of these impurities from biomass-derived furfural aqueous solutions is recommended to prevent the deterioration of TS-1.
After the 7th run, the used TS-1 was filtered off, dried at 323 K overnight and finally calcined at 823 K in an oven under air for 3 hours. This calcined catalyst was again used for an additional 8th run, and the MA yield was partially restored. This indicates that the deactivation of TS-1 is partially due to the deposition of organic products derived from these impurities, which are removed by calcination. Other sources of deactivation will be discussed below.
These contaminants must be removed when considering an industrial application. As indicated in the Introduction, a double distillation is required to purify furfural.1 The first distillation removes impurities and an azeotrope with 35% of furfural is yielded. The second distillation column further removes water and results in pure and very concentrated furfural.
The double distillation may compromise seriously the economic viability of the process here described. Possible solutions to reduce the cost and energy consumption can be the following. The azeotrope free of contaminants can be used for the oxidation to MA, preventing the use of the second distillation column. In practice the furfural–water azeotrope is condensed before entering the second vacuum distillation column and two phases are formed: a rich furfural phase (which is that readily further distilled) and a poorer aqueous furfural stream. Another solution could be that the latter diluted stream, free of contaminants, could be withdrawn and used in the oxidation to MA, leaving the concentrated furfural for processes requiring very concentrated and free of contaminants furfural.
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Fig. 9 Visible laser Raman spectra of fresh (dashed) and used (continuous) catalysts after in situ calcination at 823 K for 30 min in synthetic air. A denotes Raman bands from the anatase phase. |
Raman bands at 290, 380, 437, 469, 815, 837, 960 and 1125 cm−1 that have been previously reported for TS-1 are clearly observed in the Raman spectra of Fig. 9; the features at 960 and 1125 cm−1 demonstrate the substitutional Ti(IV) insertion within the silica framework: they have been assigned to the stretching Ti–O–Si vibrations of inserted TiO4 tetrahedra (respectively, in-phase and out of phase antisymmetric stretching of the four connected Ti–O–Si bridges).35–38 The bands detected at 144, 515 and 637 cm−1 correspond to Raman features of anatase (TiO2); there must be another anatase-derived band at 390 cm−1, but it is overshadowed by the most intense band of TS-1 at 380 cm−1. Visible Raman spectroscopy is very sensitive to extraframework titanium oxide species and therefore is an excellent probe for the detection of very small TiO2 domains. Therefore, these bands demonstrate the presence of extraframework Ti and that not all the Ti cations are inserted within the zeolite framework.
No large differences can be detected between the spectra from fresh and used catalysts, which suggests that TS-1 is essentially unaltered by the utilisation of the catalyst in the reaction medium. Nevertheless, a closer examination (see inset in the figure) indicates that the TiO2 band at 144 cm−1 is apparently less intense, which could suggest that there may be some leaching during the utilisation as catalyst.
Chemical analyses by TXRF were conducted to confirm the leaching. Ti and Si were analysed in both the fresh and used solids and in the liquid phase after each reaction run, the latter case for runs conducted with commercial and biomass-derived furfural. Table 1 summarises the results of TXRF.
Catalyst | Si/Ti at. ratio in solid | Amount of metal leached to the reaction mixture (mg) | |||||||
---|---|---|---|---|---|---|---|---|---|
Run 1b | Run 2b | Run 3b | Run 4b | Run 5b | Run 6b | Run 7b | |||
a Si/Ti at. ratio of fresh sample.b Values between brackets represent the metal leached during the run cycle with respect to the total amount of metal initially present in the solid (expressed as wt%). | |||||||||
Used with comm. furfural | 31 (25.5)a | Ti | 3.51 (11.2%) | 0.96 (3%) | 0.41 (1.3%) | 0.47 (1.5%) | 0.56 (1.8%) | 0.36 (1.1%) | — |
Si | 0.31 (0.03%) | 0 | 0 | 0 | 0 | 0.27 (0.03%) | — | ||
Used with biomass-derived furfural | 29.4 (25.5)a | Ti | 2.29 (15.4%) | 0.46 (3.1%) | 0.28 (1.9%) | 0.28 (1.9%) | 0.21 (1.4%) | 0.24 (1.6%) | 0.20 (1.3%) |
Si | 0.48 (0.13%) | 0.52 (0.14%) | 0 | 0.31 (0.81%) | 0.16 (0.04%) | 0 | 0 |
The Si/Ti at. ratio of the catalyst used with the commercial furfural is clearly higher than that of fresh catalyst, which indicates that Ti was leached during the six utilisation runs. The same conclusion may be reached by examining the Ti concentration in the liquid reaction mixture. Most of the Ti is leached during the first run (ca. 56% of the total Ti leached), and the impact of lixiviation seems to decline upon reutilisation. Si leaching also takes place, although to a much smaller degree, and in some cases below the detection limit of the technique: Ti leaching represents ca. 20% of the initial Ti content, whereas Si leaching accounts for less than 0.1% of the initial Si.
The former TXRF analyses also suggest that the contribution of the leached species to the overall activity is not relevant. In the first run 3.5 mg of Ti was leached to the reaction medium, whereas for the 3rd and successive runs the amount of Ti leached was much smaller (around 0.4–0.6 mg). If the leached homogeneous Ti species would have a significant contribution to the overall activity, the total activity of the latter runs would have been appreciably smaller than that of the first run, and not similar.
The same analyses were carried out with furfural from biomass. As with commercial furfural, Ti is leached in all reaction cycles, especially after the first one. When considering the relative amount of Ti losses in successive runs, we have to take into account that the loading of catalyst for the experiments with biomass-derived furfural was smaller (2 wt%) than that used with commercial furfural (4.6 wt%). In this case, the aggregate loss of Ti represents ca. 27% of the total Ti. This slight increase in the leached Ti may be due either to the longer contact time between the furfural and catalyst (when using furfural from biomass, each run takes 24 hours) or to some of the products detected with the furfural from biomass (dihydroxyacetone, acetic acid, and 5-methyl-2-furancarboxaldehyde) that could promote Ti leaching. As for pure furfural, most of the Ti is leached (ca. 58%) during the first run. Si leaching also takes place to a slightly higher extent than with “commercial” furfural: Ti leaching represents ca. 27% of the initial Ti content, whereas the leached Si accounts for less than 0.4% of the initial Si.
The leaching of Ti is also evidenced by the comparison of the XPS spectra of fresh and used TS-1 catalyst. Fig. 10 compares the Ti 2p core level of both samples, and Table 2 summarises the main chemical parameters deduced from the XPS analyses. The Ti 2p core level was deconvoluted into two contributions; one is represented by the Ti 2p3/2 peak at 459.8 ± 0.1 eV, and other is represented by the Ti 2p3/2 contribution at 458.6 ± 0.2 eV (the corresponding Ti 2p1/2 levels are at located at 5.7 eV higher BE). The first contribution was assigned to tetrahedral Ti(IV) incorporated in the silicalite framework (Tit), whereas that represented by the peak at 458.6 was assigned to octahedral Ti(IV) in anatase TiO2 (Tio).39–41 For very good fitting, a small contribution represented by the Ti 2p3/2 contribution at ca. 457.2 eV was required; this has been assigned to Ti(III) produced by the photoreduction of Ti(IV) within the XPS chamber, driven by the X-ray impact and the ultrahigh vacuum required to record the spectra.40,41
The first evidence of leaching arises from the comparison between the XPS Ti/Si ratios of fresh and used samples. The XPS Ti/Si ratio of used samples is 0.027, half the value of the fresh samples (0.052). Moreover, a comparison between the XPS and TXRF Ti/Si ratios of fresh and used samples indicates that the leaching process is very intense at the surface of the TS-1 crystallites. Thus, the XPS value of the fresh sample (0.052) is larger than that determined by TXRF analysis (0.039), perhaps because anatase-like domains are present at the external surface of TS-1. However, the XPS Ti/Si value of the used sample (0.027) is smaller than that determined by TXRF (0.032), indicating the surface is no longer enriched in Ti and therefore that Ti leaching at the surface is very intense. Finally, the Ti leaching process affects both anatase Ti (Tio) and Ti inserted in the silicalite (Tit). Thus, the XPS Tio/Si ratio of the used sample is 0.008, vs. 0.015 for the fresh sample, and the XPS Tit/Si ratio of the used sample is 0.015, vs. 0.035 for the fresh sample.
Taking into account that 20% of Ti was leached upon reutilization, it is quite remarkable that no deactivation was observed when pure furfural is used for the reutilization experiments. A likely hypothesis is that outermost Ti is being leached and innermost active Ti sites remain to conduct the reaction. In this sense, the decrease observed upon reutilization of the surface at. Ti/Si by XPS (from 0.052 to 0.027, ca. 50% decrease) is larger than that observed for the bulk TXRF ratio (from 0.039 to 0.032, 18% decrease) indicating that leaching affects mainly to Ti cations located at the surface.
The leaching of Ti also seems to result in slight modifications of the long range order in the framework and in the textural properties of the TS-1: slight but visible modifications of the XRD reflections and of N2 isotherms are evident when comparing the patterns of the fresh and used samples (see Fig. S10 and SI11 in the ESI† and the discussion therein for further details).
All the characterisation data confirm the existence of Ti leaching, which is also associated with a slight leaching of Si. This leaching is very intense during the first run but much less important in successive cycles and affects Ti both in anatase and within the silicalite framework.
Notwithstanding the leaching, when using pure commercial furfural, TS-1 could be reused for six runs without noticeable deactivation. When using furfural directly derived from biomass, weak but visible deactivation occurs upon reutilisation; this deterioration must be related to the presence of other organic products than furfural.
The amount of H2O2 required when using TS-1 is 2.5 times the value that is stoichiometrically needed. A very selective two-step process has also been demonstrated, which needs a H2O2/furfural mol ratio of 4.4, an amount of H2O2 much closer to the stoichiometric value (which is 3). This process involves the consecutive utilisation of TS-1 to selectively oxidise furfural to hydroxyfuranone, and consequently, once TS-1 is removed, Amberlyst 70 to catalyse the selective oxidation of hydroxyfuranone to MA.
FA | Formic acid |
FumA | Fumaric acid |
Hydroxyfuranone | 5-Hydroxy-furan-2(5H)-one |
MA | Maleic acid |
MAN | Maleic anhydride |
SA | Succinic acid |
Footnote |
† Electronic supplementary information (ESI) available: Additional information on experimental details, catalytic activity, other proposals of mechanism of reaction and characterisation of catalysts by TG analyses, XRD, and N2 adsorption. See DOI: 10.1039/c4ra11563e |
This journal is © The Royal Society of Chemistry 2014 |