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Article

Functionalized Coal Fly Ash Is an Efficient Catalyst for Synthesizing Furfural from Xylose at a Low Catalyst Load

Department of Chemistry and Chemical Engineering, MOE Engineering Research Center of Forestry Biomass Materials and Bioenergy, Beijing Forestry University, Beijing 100083, China
*
Author to whom correspondence should be addressed.
Catalysts 2023, 13(12), 1492; https://doi.org/10.3390/catal13121492
Submission received: 11 October 2023 / Revised: 27 November 2023 / Accepted: 30 November 2023 / Published: 5 December 2023
(This article belongs to the Section Environmental Catalysis)

Abstract

:
In this study, coal fly ash was functionalized, using a simple one-step process (loading with Al3+ and sulfonation), to yield a solid acid catalyst (S/Al-CFA) with strong acid sites. The catalyst was then used to produce furfural from xylose in a biphasic system (H2O(NaCl)/tetrahydrofuran). The furfural yield reached 82% at 180 °C–60 min with catalyst/xylose ratio of 0.2:1.0 (w/w). With the reaction completed, all of the components could be effectively separated, and the furfural was 97.6% pure. The cycle and regeneration of the catalyst were evaluated, and the catalyst deactivation mechanism was investigated.

1. Introduction

Furfural, a valuable biomass-derived platform chemical, plays a vital role in the seamless transition from the present fossil fuel-centered economy toward a carbon-neutral future [1,2,3]. The use of solid acid catalysts is superior to that of mineral acids in furfural production systems, and the use of biphasic systems is superior to that of single-phase systems; thus, biphasic systems using solid acids have been studied extensively [4,5,6]. However, there are important drawbacks to the currently available biphasic systems, including the following: the catalysts are complicated to prepare, high catalyst doses (sometimes exceeding the xylose dose) are needed, and the components of the system are difficult to separate and recover after the reaction has reached completion [5,7,8,9,10].
Various solid acid catalysts for producing furfural have been synthesized. These include Cr-deAl-Y [11], Sn-Beta [12], γ-Al2O3 [13], Nb2O5 [14], MSPFR [15], Cl0.3 -SR [16], SO42−/Sn-TRP [17], SO42−/SnO2-Al2O3-CFA [9]. In contrast to other solid acid catalysts, coal fly ash (CFA) is a solid waste from coal-burning power plants, and there is great interest in developing CFA-based catalysts because CFA is very thermally stable, cheap, and possible to functionalize [18,19]. However, CFA-based catalysts, like other solid acid catalysts, require relatively high catalyst: xylose ratios (w/w), as shown in Table 1. Moreover, preparing solid acids consumes a lot of energy and comes with safety risks, due to the strongly corrosive acids (e.g., sulfuric acid or chlorosulfonic acid), elevated temperatures (for calcination), and long preparation times used [20,21,22,23]. Many solid acid catalysts are poorly reusable [24]. Therefore, choosing a simple and effective method through which to modify a catalyst for converting xylose into furfural is important.
Modifying a catalyst, by loading it with metal ions that act as Lewis acid sites and sulfonating it to provide Brønsted acid sites, can typically improve catalytic performance [17]. Specifically, Al3+ forms a well-activated metal center as an especially efficient Lewis acid site for facilitating xylose to produce furfural [13,26]. Sulfonation, using sulfamic acid as a sulfonating agent and NaNO2 as a diazotizing agent, is a simple process that produces relatively little hazardous waste [27,28]. Moreover, solid acid catalysts based on sulfonic acid provide a high degree of activity for furfural production, can be reused effectively, and are thermally stable [24,29]. Treating CFA with citric acid before modification can improve CFA activity and remove impurities [30,31].
The chemical stability of furfural is poor, and it is sensitive to solvent environmental changes, so choosing a proper solvent system is crucial for furfural synthesis [32]. Biphasic systems, consisting of water and organic solvents, offer marked advantages over expensive ionic liquids and inefficient pure water systems, including being very efficient and cheap, and allowing for the components to be separated easily when the reaction is complete [33]. Higher furfural yields have been found using polar aprotic solvents than with other solvents [34,35]. A markedly higher furfural yield has been found using tetrahydrofuran (THF) than using other polar aprotic solvents [36]. The boiling point of THF (66 °C) is much lower than the boiling point of furfural (162 °C), so less energy is consumed when separating furfural from THF than from solvents with higher boiling points. NaCl is one of the cheapest and most effective salts for promoting separation of the H2O and THF phases, improving THF extraction, and slowing down furfural degradation [11,12]. NaCl also promotes the dehydration of xylose and, thus, increases the furfural yield [29].
In this work, we prepared a solid acid catalyst (S/Al-CFA) with strong acid sites by subjecting CFA to a simple one-step process through which to simultaneously load the CFA with aluminum ions and sulfonate the CFA. The S/Al-CFA was used to catalyze the preparation of furfural from xylose in an H2O(NaCl)/THF two-phase system. The reaction conditions were optimized, and a furfural yield of 82% was obtained at a low catalyst: xylose ratio (w/w). The components of the reaction system were able to be effectively recovered. The recovered solid acid catalyst maintained excellent performance for five cycles. The furfural obtained after separation was 97.6% pure, and the furfural concentration in the THF was only 0.6%. The fresh and recovered catalysts were characterized to determine why the catalyst became deactivated. Finally, the ability of the catalytic system to produce furfural from corncob hydrolysate, using optimal conditions, was assessed.

2. Results and Discussion

2.1. Characterization of Catalysts

SEM images of the CFA and S-CFA-Al are shown in Figure S1. The CFA (A-1 and A-2) consisted of spherical particles of different sizes that were mainly composed of an amorphous glass phase with smooth surfaces. In S/Al-CFA (B-1, B-2), the smooth surface was destroyed to form small spherical particles with relatively rough and wrinkled surfaces. Combined with the BET results (Table 2), the S/Al-CFA surface area (10.805 m2/g) was about eight times higher than the CFA surface area (1.413 m2/g), meaning the S/Al-CFA would have had more adsorption sites [37].
The element contents and distributions were analyzed using an energy-dispersive detector attached to the SEM to verify that loading with Al and sulfonation had been successful during the S/Al-CFA preparation process. As shown in Table S2, the S and Al contents of the CFA were 0.14 wt% and 1.35 wt%, respectively, and the S and Al contents of the S/Al-CFA were 7.85 wt% and 8.96 wt%, respectively, indicating that S and Al were successfully introduced into the CFA. As shown in Figure S1, the energy-dispersive spectroscopy maps of the S/Al-CFA indicated that Al and S were uniformly spread across the CFA surfaces.
The FT-IR and Xps spectra of catalysts are shown in Figure 1a,b. In the FT-IR spectra, the bands at 455, 559, and 1092 cm−1 in CFA and S/Al-CFA were attributed to Si-O-Si, O-Si-O, and Si-O-Al stretching, respectively [38]. The FT-IR spectrum of S/Al-CFA in the 3468 cm−1 band was the Al–OH stretching vibrations peak. This indicates that Al3+ was successfully loaded onto the CFA. The width of the band represented the hydrogen bonding between the hydroxyl groups, indicating that the treatment increased the number of hydroxyl groups and, therefore, the Brønsted acid acidity [23,38]. In S/Al-CFA, the -SO3H group could be identified in the 1037 and 1009 cm−1 bands [39]. In addition, the XPS spectrum of S/Al-CFA contained a single S2p peak, indicating that all of the S was present as SO3H [22].
The XRD pattern of CFA (Figure S2) contained a broad diffraction peak at 15–34°, which was mainly caused by vitreous, SiO2, and SiO2–Al2O3 areas in the CFA. These areas would have given the CFA relatively strong hydrophilicity and surface activity, as well as good sorption ability [9]. The XRD spectrum of C-CFA contained the same peaks as the CFA spectrum, indicating that the citric acid treatment did not affect the crystal structure of the CFA. The citric acid preferentially removed nonstructural aluminum from the CFA to adjust the pore structure [40,41]. No additional characteristic peaks were found after Al loading and sulfonation. The mesopore volume and specific surface area were lower for the S/Al-CFA than for the C-CFA (Table 2). This, and the element map of S/Al-CFA, indicates that the catalyst preparation procedure caused the metal ions and sulfonic acid groups to be uniformly spread across the CFA surfaces.
As shown in Figure S3, the CFA was thermally stable at <400 °C. The modified catalyst remained thermally stable, allowing the S/Al-CFA to perform very well for at least five cycles.
The N2 adsorption–desorption isotherms for the catalysts are shown in Figure S4. According to IUPAC nomenclature, the BET isotherms of catalysts were all of type IV, and the hysteresis loops were type H3 [23]. This suggested that the materials were mesoporous, with slit-shaped or panel-shaped pores [42]. In Table 2, the N2 adsorption–desorption analysis results of the catalysts are summarized. The pore volume and specific surface area were markedly higher for the C-CFA than for the CFA because the citric acid removed some metals and impurities from the CFA. The mesopore volume and specific surface area were lower for the S/Al-CFA than for the C-CFA, indicatin that –SO3H and Al3+ were uniformly distributed through the mesopores. The specific surface area, pore size and mesopore volume for the S/Al-CFA were higher than for the CFA, meaning that more catalytically active sites were exposed on the S/Al-CFA, promoting the production of furfural [23]. The furfural and xylose molecular radii were 0.68 and 0.86 nm, respectively [17]. The mean S/Al-CFA pore diameter was 4.404 nm, indicating that furfural may readily diffuse out of S/Al-CFA pores, and that xylose may readily reach the acidic sites in S/Al-CFA pores.
NH3-TPD was used to evaluate the acid strength and total acid of the catalyst. NH3 desorption at 100–200, 200–400, and 400–800 °C indicated weakly acidic, moderately acidic, and strongly acidic sites, respectively [43]. As shown in Figure 1c, the S/Al-CFA had moderately and strongly acidic sites (at 277 and 585 °C, respectively). The CFA did not contain strongly acidic sites. As shown in Table 2, the total acid content was higher for the S/Al-CFA than for the CFA because of the –SO3H and Al3+ present in the S/Al-CFA. In Table S3, the amounts of weak, moderate, and strong acids were listed for the CFA and S-Al-CFA catalysts, respectively. Py-FTIR was performed to distinguish the acid types. As shown in Figure 1d, the S/Al-CFA contained Brønsted and Lewis acid sites (B and L acid). The bands at 1445, 1490, 1542, 1579, and 1596 cm−1 were attributed to L, B; L, B, L; and L acid sites, respectively [44].

2.2. Effects of Using Modified CFA on the Furfural Yield

As shown in Figure 2, furfural yields from xylose when the modified CFA catalysts were used increased in the order CFA < Fe-CFA < Cr-CFA < Al-CFA < S/Fe-CFA < S/Cr-CFA < S/Al-CFA. The actual yields are shown in Table S1. The highest furfural yield (72%) was given by the solid acidic catalyst S/Al-CFA. The solid acid catalysts, with simultaneous Brønsted and Lewis acids, catalyzed furfural production from xylose well, since the Brønsted and Lewis acids could participate synergistically in furfural production [5,21,45,46]. Therefore, co-modifying sulfonation and loaded metal ions markedly improved the catalytic activity. This could be explained by the two-step reaction mechanism proposed by Suzuki et al. [35]. Tests were performed using catalysts prepared using FeCl3, CrCl3, and AlCl3 at various concentrations to assess the effects on the furfural yield. S/Al-CFA had the highest activity when the AlCl3 concentration was 15 mM, which gave a furfural yield of 72%. More oxidation of xylose to CO2 occurred in the presence of Cr3+ and Fe3+ than in the presence of Al3+, resulting in lower furfural yields with the existence of Cr3+ and Fe3+ than with Al3+ [47]. In Scheme S1, a possible reaction pathway for S-Al-CFA catalyzed xylose to furfural is described.

2.3. Reaction System Determination

The NaCl concentration affected the furfural yield. As shown in Figure 3a, 22% lower furfural yields were gained without the added NaCl. Increasing the NaCl concentration from 0 to 250 g/L increased the furfural yield, from 22% to 72%. Adding NaCl to an H2O–THF system would have markedly increased the furfural concentration in the THF by affecting the intramolecular binding of the liquid phase constituents and making H2O and THF less miscible [12]. NaCl would also have increased the furfural concentration by increasing the reaction rate [6,48]. The maximum furfural yield was 72% when the NaCl concentration was 250 g/L. Increasing the NaCl concentration further caused the furfural yield to decrease, to 68%, because the high Cl concentration would have inhibited furfural formation [24].
After the optimal NaCl concentration had been determined, the effect of the THF dose on the furfural yield was assessed. The highest furfural yield was 72%, which was achieved at a THF dose of 100 mL (H2O: THF ratio 1:2 (v/v)), as shown in Figure 3b. This indicates that a certain THF dose increased the furfural yield. An excess of the aqueous phase would have weakened the reactivity of the acidic catalyst, and an excess of the organic phase would have led to the formation of unwanted humins [49,50]. THF used as an extractant phase can transfer furfural formed in the aqueous solution in real time and, therefore, shift the reaction equilibrium in the positive direction and prevent secondary loss reactions, meaning that the furfural that is produced is protected in the THF [51].

2.4. Optimizing the Reaction Conditions

The reaction conditions were optimized, and the results are shown in Figure 4a,b. At the beginning of the reaction, the furfural yield and xylose conversion rate grew as the time and temperature increased. Lower temperatures and times did not provide enough energy to facilitate xylose conversion [11,52]. Initially, the furfural yield increased with increasing reaction time or reaction temperature, and the maximum furfural yield, of 82%, was achieved at 180 °C and 60 min. Subsequently, increasing the reaction temperature or extending the reaction time decreased the furfural yield (to 75% at 75 min, or 77% at 190 °C). This was because the intense systemic energy exacerbated unwanted side reactions [25]. Various byproducts could be deposited on the active sites of the catalyst, thus decreasing the catalytic activity and the furfural synthesis efficiency [9].
Figure 4c shows the effect of the S/Al-CFA dose on the furfural yield. When no catalyst was added, only 55% and 26% for xylose conversion and furfural yield were obtained, respectively. Adding S/Al-CFA dramatically improved the xylose conversion rate and furfural yield. A catalyst dose of 0.1 g gave a furfural yield of 76%. Moreover, adding the catalyst gave a xylose conversion rate of >90% in all of the tests, indicating that the S/Al-CFA could fully bond xylose and facilitate xylose conversion. The maximum furfural yield was 82%, and this was achieved at a S/Al-CFA dose of only 0.2 g (catalyst: xylose ratio 0.2 (w/w)). Using a lower catalyst dose will also be cheaper; therefore, the S/Al-CFA catalyst has a clear advantage over most catalysts, which need to be used at high doses. Increasing the S/Al-CFA dose further caused the furfural yield to decrease, to 68%, because the S/Al-CFA provided excess acidic sites that catalyzed side reactions of furfural [28].

2.5. Separation and Recovery of Catalytic System Components

Furfural production can be made more economically efficient if the catalytic system components can be efficiently separated and recovered. The feasibility of recovering all of the components was investigated. As shown in Figure 5, the solvent system and catalyst were first separated through filtration, and then the recovered S/Al-CFA catalyst was used in another reaction. The H2O(NaCl) and THF phases were separated in a separatory funnel. The different boiling points of THF and furfural allowed THF and furfural to be separated through reduced-pressure distillation. The samples were analyzed using HPLC. At 40–60 °C, the furfural concentration in the collected THF was 0.6%. At 60–85 °C, the collected furfural was 97.6% pure. The NaCl in the water was recovered by evaporating the water. All of the components were able to be recovered. The results indicated that the H2O(NaCl)–THF catalytic system containing S/Al-CFA was both efficient and recyclable and has great potential for practical use.

2.6. Catalyst Recyclability

Recycling a catalyst can improve the sustainability of the process being performed. The separated S/Al-CFA was washed with deionized water and ethanol, and dried at 110 °C for 5 h before reuse. As shown in Figure 6, the first-cycle yield of furfural was 76%, which was only 6% lower than the yield using the fresh catalyst. After four cycles, the furfural yield still reached 75%.
The catalyst that had been recovered six times (R-S/Al-CFA) was subjected to FT-IR spectroscopy, NH3-TPD, and BET analysis. As shown in Figure 7, the R-S/Al-CFA FT-IR spectrum at 1547 and 1577 cm−1 contained new weak bands, which were attributed to C=C bonds [53]. This may indicate the deposition or adsorption of humins produced during reactions on the S/Al-CFA. As shown in Table 2, the specific surface area, pore size, pore volume, and total acidity were markedly lower for the R-S/Al-CFA than for the S/Al-CFA, and strong acid sites had been lost during use (Figure 7). This loss may have been responsible for the marked decrease in furfural yield.
The regeneration method for R-S/Al-CFA was described in the second paragraph of Section 3.2. Regenerated R-S/Al-CFA was used to catalyze xylose conversion to furfural. The furfural yield was only 2% lower when using regenerated R-S/Al-CFA than when using fresh S/Al-CFA. This indicates that used S/Al-CFA could be reactivated using the regeneration method.

2.7. S/Al-CFA Catalysis of Corncob Hydrolysates

Furfural is usually produced commercially, using corncobs, oat hulls, and cottonseed hulls as raw materials [54,55]. These types of biomass contain more complex components (e.g., cellulose, hemicellulose, lignin, and mineral salts) than xylose. These components may yield complex products (e.g., hydrolyzed cellulose sugars and hydrolyzed lignin phenols) during hydrolysis, and these products may affect furfural production [11,39].
We used the described method in Section 3.4 to prepare a xylose-rich hydrolysate. The xylose concentration in the xylose-rich hydrolysate was 60 g/L. Under optimal conditions, the furfural yield was 80%, and the xylose conversion rate was 100%. Impurities in the corncob hydrolysate slightly decreased the catalytic activity, but ideal catalytic results were still found. This indicates that the S/Al-CFA offers promise for practical use in producing furfural from corncob hydrolysates.

3. Materials and Methods

3.1. Materials

Corncobs from Hebei Province, China, were washed with water, dried at 50 °C to a constant weight, and then crushed to pass through a 60–80 mesh sieve. CFA (5000 mesh) was purchased from Henan Hengyuan New Material Co. (Henan, China). AlCl3·6H2O, citric acid (CA, analytical reagent grade (AR)), CrCl3·6H2O, FeCl3·6H2O, ethanol (AR), maleic acid (AR), NaCl (AR), NaNO2 (AR), sulfanilic acid (AR), THF (AR), and xylose (98%) were all obtained from Shanghai Maclin Biochemical Technology Co. (Shanghai, China). All reagents were used without further purification.

3.2. Preparation of Modified CFA Solid Acid Catalysts

First, 4 g CFA was added to 100 mL of 0.8 M CA solution, and then the mixture was maintained in a water bath at 80 °C for 5 h with stirring. The mixture was then filtered with a reduced pressure filtration operation, the collected solid was washed until the wash water was neutral, and then the solid was dried at 110 °C for 5 h. Activated CFA (C-CFA) was obtained.
Thereafter, 2 g of C-CFA and 8 g of sulfanilic acid were added to 100 mL of a specific concentration (0, 5, 10, 15, 20 mmol/L) of AlCl3 (FeCl3, CrCl3) solution. The mixture was stirred in a water bath at 80 °C for 40 min, then 4 g of NaNO2 was added, and the mixture was stirred for another 10 h at 80 °C in the water bath. Modified CFA (S/Al-CFA, S/Fe-CFA, S/Cr-CFA) was washed with deionized water until the wash water was neutral, and it was dried at 110 °C for 5 h. The solid acid catalyst S/Al-CFA (S/Fe-CFA, S/Cr-CFA) was obtained. Other solid acids were prepared accordingly, including Al-CFA, Fe-CFA, Cr-CFA, and S/CFA.

3.3. Catalyst Characterization

Scanning electron microscopy images, energy-dispersive spectra, and relative element maps of the catalysts were acquired using a TESCAN MIRA LMS scanning electron microscope (TESCAN, Brno, Czech Republic) equipped with an Xplore 30 energy-dispersive detector (Oxford Instruments, Abingdon, UK). Fourier transform infrared (FT-IR) spectra of the catalysts were acquired using a Nicolet iS20 instrument (Thermo Fisher Scientific, Waltham, MA, USA) using KBr disks. X-ray photoelectron spectroscopy (XPS) analysis was tested on a Thermo Scientific K-Alpha spectrometer. The crystal structures of the catalysts were determined with X-ray diffractometry (XRD) using a D/MAX-2600 instrument (Rigaku, Tokyo, Japan). Thermogravimetric (TG) analysis was performed using a TG 209 F3 instrument (Netzsch, Selb, Germany). The Brunauer–Emmett–Teller (BET) surface area and pore structure of the samples were analyzed with N2 adsorption–desorption analysis. The acidic sites were identified and the total acidities of the catalysts were determined through temperature-programmed NH3 (NH3-TPD) desorption using a MicrotracBEL Cat II instrument (MicrotracBEL, Osaka, Japan). Pyridine adsorption infrared spectroscopy (Py-FTIR) analysis was performed on a Tensor 27 instrument to detect catalyst Brønsted and Lewis acid types.

3.4. Production of Xylose-Rich Hydrolysate from Corncobs

In a 500 mL Teflon-lined autoclave reactor (China Wuzhou Dingchuang Beijing Technology Co., Beijing, China), 100 mL of 0.15 M maleic acid solution and 5 g of corncob were mixed thoroughly. The reactor was heated to 140 °C for 1 h, and then cooled to 30 °C using circulating cooling water. The hydrolysis solution was obtained through vacuum filtration. The hydrolysate was concentrated with a rotary evaporator to obtain a xylose-rich hydrolysate with which to prepare furfural.
Xylose-oligosaccharides were completely hydrolyzed by subjecting the concentrated hydrolysate to hydrolysis again, using 4% H2SO4 at 121 °C for 60 min. The xylose concentration obtained here was used as the value of the moles for xylose units in the corncob.

3.5. Catalytic Tests

Furfural was produced by treating xylose or xylose-rich hydrolysate in a 500 mL quartz-lined autoclave with mechanical stirring at 300 rpm. In a typical test, xylose or xylose-rich hydrolysate, solid acidic catalysts, NaCl solution or NaCl, and THF were added to the autoclave, which was then sealed, and N2 was introduced to remove the air. The reactor was heated to the desired temperature, which was maintained for a specific duration. Circulating cooling water was then passed through the reactor to cool the contents to 40 °C. The mixture was filtered and the aqueous and THF phases were analyzed using high-performance liquid chromatography (HPLC). To ensure the reliability of the experimental data, each experiment was repeated three times.

3.6. Product Analysis

The furfural concentration was determined with high-performance liquid chromatography using a TC-C18 column (Agilent Technologies, Santa Clara, CA, USA) and a 15/85 (v/v) acetonitrile/water mixture as the mobile phase at a flow rate of 1 mL/min. The xylose concentration was determined with high-performance liquid chromatography using an Aminex HPX-87H column (Bio-Rad Laboratories, Hercules, CA, USA), using 5 mmol/L H2SO4 as the mobile phase at a flow rate of 0.6 mL/min. The detector used was a refractive index detector. The xylose conversion and furfural yield were calculated using the following formulae:
Xylose   conversion =
moles   of   xylose   reacting / moles   of   xylose   staring   × 100 %
Furfural   yield   from   xylose = moles   of   furfural   produced / moles   of   xylose   put   into   the   reactor   × 100 %

4. Conclusions

The solid acid catalyst S/Al-CFA was prepared using a simple one-step process, using AlCl3 and sulfanilic acid/NaNO2. The S/Al-CFA had stronger acid sites, a better developed pore structure, and a markedly higher total acid content than the CFA. The furfural yield at a catalyst: xylose ratio of 0.2 (w/w) was 82%. All components of the catalytic system were able to be separated efficiently. The furfural product was 97.6% pure, and the furfural concentration in the THF was only 0.6%. When the catalyst was used over four cycles, the furfural yield remained >72%. Leaching of acidic sites and pore collapse were important factors in the deterioration of the catalytic properties of the S/Al-CFA. The recycled S/Al-CFA was able to be regenerated, and the furfural yield when the regenerated S/Al-CFA was used was 80%, which was similar to the furfural yield using fresh S/Al-CFA. A furfural yield of 80% was found when the S/Al-CFA was used to catalyze the reaction using corncob hydrolysate. In conclusion, a functional catalyst with strong activity for producing furfural from xylose was synthesized using CFA as a substrate, which provides an attractive avenue for the recycling and high value-added utilization of CFA.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/catal13121492/s1, Scheme S1: Possible reaction pathways for furfural formation from xylose catalyzed by S-Al-CFA; Figure S1: SEM images of the CFA (A-1 and B-1) and the S/Al-CFA (A-2 and B-2). Element maps of Al and S in the S/Al-CFA (C and D); Figure S2: XRD patterns of the CFA, C-CFA, and S/Al-CFA; Figure S3: TG results for the CFA and S/Al-CFA; Figure S4: N2 adsorption–desorption isotherms for CFA, C-CFA, and S/Al-CFA; Table S1: The yield of furfural with different modified CFA catalysts; Table S2: Element compositions of the catalysts determined by EDS; Table S3: Comparison of the catalyst performance before and after the cycle.

Author Contributions

Conceptualization, M.L.; Methodology, M.L.; Software, M.L. and Y.G.; Validation, Y.W., L.L. and Y.G.; Formal analysis, M.L. and Z.G.; Investigation, M.L. and Y.W.; Data curation, L.L.; Writing—original draft, M.L.; Writing—review & editing, M.L., Z.G. and L.Z.; Supervision, L.Z.; Funding acquisition, L.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by Ministry of Science and Technology of the People’s Republic of China (2019YFB1503803-01-05).

Data Availability Statement

Data is contained within the article or supplementary material.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Characterization of catalysts. (a) FT−IR, (b) Xps, (c) NH3−TPD, and (d) Py−FTIR.
Figure 1. Characterization of catalysts. (a) FT−IR, (b) Xps, (c) NH3−TPD, and (d) Py−FTIR.
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Figure 2. The effects of different metal ion concentrations during catalyst preparation on the catalyst performance under the same reaction conditions (180 °C, 30 min, catalyst: xylose ratio 0.2:1.0 (w/w), THF: H2O(NaCl) ratio 2:1 (v/v), 250 (g NaCl)/L). (a) Effect of the AlCl3 concentration on the modified CFA performance. (b) Effect of the CrCl3 concentration on the modified CFA performance. (c) Effect of the FeCl3 concentration on the modified CFA performance.
Figure 2. The effects of different metal ion concentrations during catalyst preparation on the catalyst performance under the same reaction conditions (180 °C, 30 min, catalyst: xylose ratio 0.2:1.0 (w/w), THF: H2O(NaCl) ratio 2:1 (v/v), 250 (g NaCl)/L). (a) Effect of the AlCl3 concentration on the modified CFA performance. (b) Effect of the CrCl3 concentration on the modified CFA performance. (c) Effect of the FeCl3 concentration on the modified CFA performance.
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Figure 3. Effects of NaCl concentration and THF dose on the xylose conversion rate and furfural yield. Reaction conditions: (a) 30 min, 180 °C, catalyst: xylose ratio 0.2:1.0 (w/w), H2O: THF ratio 1:2 (v/v) and (b) catalyst: xylose ratio 0.2:1.0 (w/w), 50 mL of 250 g/L NaCl.
Figure 3. Effects of NaCl concentration and THF dose on the xylose conversion rate and furfural yield. Reaction conditions: (a) 30 min, 180 °C, catalyst: xylose ratio 0.2:1.0 (w/w), H2O: THF ratio 1:2 (v/v) and (b) catalyst: xylose ratio 0.2:1.0 (w/w), 50 mL of 250 g/L NaCl.
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Figure 4. Effects of reaction time, reaction temperature, and S/Al-CFA dose on the xylose conversion rate and furfural yield. Reaction conditions: (a) 180 °C, H2O: THF ratio 1:2 (v/v), catalyst: xylose ratio 0.2:1.0 (w/w), 250 g/L NaCl; (b) 60 min, H2O: THF ratio 1:2 (v/v), catalyst: xylose ratio 0.2:1.0 (w/w), 250 g/L NaCl; and (c) 60 min, 180 °C, H2O: THF ratio 1:2 (v/v), xylose dose 1.0 g, 250 g/L NaCl.
Figure 4. Effects of reaction time, reaction temperature, and S/Al-CFA dose on the xylose conversion rate and furfural yield. Reaction conditions: (a) 180 °C, H2O: THF ratio 1:2 (v/v), catalyst: xylose ratio 0.2:1.0 (w/w), 250 g/L NaCl; (b) 60 min, H2O: THF ratio 1:2 (v/v), catalyst: xylose ratio 0.2:1.0 (w/w), 250 g/L NaCl; and (c) 60 min, 180 °C, H2O: THF ratio 1:2 (v/v), xylose dose 1.0 g, 250 g/L NaCl.
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Figure 5. Separation and recovery of the catalytic system components.
Figure 5. Separation and recovery of the catalytic system components.
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Figure 6. Xylose conversion rates and furfural yields for recycled S/Al-CFA. Reaction conditions: 180 °C, 60 min, catalyst: xylose ratio 0.2:1.0 (w/w), H2O: THF ratio 1:2 (v/v), 250 g/L NaCl.
Figure 6. Xylose conversion rates and furfural yields for recycled S/Al-CFA. Reaction conditions: 180 °C, 60 min, catalyst: xylose ratio 0.2:1.0 (w/w), H2O: THF ratio 1:2 (v/v), 250 g/L NaCl.
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Figure 7. Characterization of the catalyst before and after cycling. (a) FT−IR and (b) NH3−TPD.
Figure 7. Characterization of the catalyst before and after cycling. (a) FT−IR and (b) NH3−TPD.
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Table 1. Solid acid catalysts for converting xylose into furfural.
Table 1. Solid acid catalysts for converting xylose into furfural.
CatalystReaction ConditionYield
(Furfural)
Ref
SolventTemperature—TimeXylose:Catalyst Ratio
SO42−/SnO2-Al2O3
-CFA
Water/
toluene
180 °C–30 min1.0684.7[9]
Sulfuric acid-treated
CFA
Water/
toluene
170 °C–210 min0.6768[23]
S-IRCCWater/
MIBK
190 °C–60 min173.64[24]
SO42−/Sn-TRPWater
/toluene
170 °C–180 min282.79[17]
SO42−/SnO2
-SSXR
ChCl-MAA/
toluene
180 °C–15 min0.5382.6[5]
Sn-MMTSBP/
NaCl-DMSO
180 °C–30 min576.79[25]
γ-Al2O3Water/
toluene
150 °C–60 min0.7123[13]
Nb2O5Water/
toluene
120 °C–180 min1.3453.23[14]
Cl0.3-S-Rwater/
1,4-dioxane
190 °C–80 min138.1[16]
S/Al-CFAWater/
THF
180 °C–60 min0.282This work
Table 2. Characteristics of the catalysts.
Table 2. Characteristics of the catalysts.
CatalystSBET
(m2/g)
D
(nm)
VMeso
(cm3/g)
Total Acid
μmol/g
CFA1.4133.8230.012356
C-CFA13.2294.8260.037-
S/Al-CFA10.8054.4040.0352390
R-S/Al-CFA7.2443.9050.0231849
SBET: The specific surface area, measured using the BET method. D: The pore sizes, measured using the BJH adsorption method. VMeso: The mesopore volumes, measured using the BJH adsorption method.
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Li, M.; Wang, Y.; Liu, L.; Gao, Y.; Gao, Z.; Zhang, L. Functionalized Coal Fly Ash Is an Efficient Catalyst for Synthesizing Furfural from Xylose at a Low Catalyst Load. Catalysts 2023, 13, 1492. https://doi.org/10.3390/catal13121492

AMA Style

Li M, Wang Y, Liu L, Gao Y, Gao Z, Zhang L. Functionalized Coal Fly Ash Is an Efficient Catalyst for Synthesizing Furfural from Xylose at a Low Catalyst Load. Catalysts. 2023; 13(12):1492. https://doi.org/10.3390/catal13121492

Chicago/Turabian Style

Li, Mengling, Ye Wang, Lin Liu, Yanan Gao, Zhanyun Gao, and Liping Zhang. 2023. "Functionalized Coal Fly Ash Is an Efficient Catalyst for Synthesizing Furfural from Xylose at a Low Catalyst Load" Catalysts 13, no. 12: 1492. https://doi.org/10.3390/catal13121492

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