Abstract
Cellulose is the most abundant source of biomass, which can be converted into monosaccharide or other chemical platform molecules for the sustainable production of chemicals and fuels. Acid catalysts can promote hydrolytic degradation of cellulose into valuable platform molecules, which is of great significance in the development of chemicals and biofuels. However, there are still some shortcomings and limitations of the catalysts for the hydrolytic degradation of cellulosic biomass. Heteropoly acid (HPA), as a green catalyst, seems to be more conducive to the degradation of cellulosic biomass due to its extreme acidity. HPAs can be designed in homogeneous and heterogeneous systems. Moreover, they can be easily separated from the products in both systems by a simple extraction process. According to the unique properties of HPAs (e.g., good solubility, high thermal stability, and strong acidity), using heteropoly acid-based catalysts to depolymerize and convert cellulose into value-added chemicals and biofuels has become one of the most remarkable processes in chemistry for sustainability. In this review, the characteristics, advantages, and applications of HPAs in different categories for cellulose degradation, especially hydrolysis hydrolytic degradation, are summarized. Moreover, the mechanisms of HPAs catalysts in the effective degradation of cellulosic biomass are discussed. This review provides more avenues for the development of renewed and robust HPAs for cellulose degradation in the future.
Introduction
With the continuous exploitation of human beings, the amount of fossil energy that is the most main energy consumed in the world is decreasing gradually. Therefore, developing a sustainable renewable energy source that can provide valuable chemicals and biofuels is of great importance (Zhang et al., 2015). To furnish the desired bioproducts, some resources are needed which can provide us with basic elements such as C, H, and O in luxuriant amounts (Dhepe and Fukuoka, ). Compared with other energy sources (e.g., coal, oil, and natural gas), biomass energy has incomparable advantages as a renewable energy source with little pollution. Moreover, biomass has become the focus of development because of its universality, abundance, and low pollution. In some biorefinery typically using biomass instead of oil, biomass can be converted into energy and relevant bioproducts through multifarious platforms (Chang et al., ; Hu et al., ; Li et al., ; Liu et al., ). Especially, biorefinery combines the key technologies of transforming biological raw materials into industrial intermediates and final products (Scheme 1; Kamm and Kamm, ; Dhepe and Fukuoka, ; Li et al., ; Liu and Zhang, ; Zhang et al., 2018). Therefore, the utilization of biomass is a wonderful choice to develop sustainable and renewable energy.
Scheme 1
As the most abundant source of biomass and one of the most widely distributed and abundant polysaccharides in nature, cellulose provides more possibilities for sustainable chemicals and fuels in the future (Huber et al., ; Climent et al., ; Sheldon, ; To et al., ). Hence, the conversion of cellulose could become a significant part of biomass utilization, which plays an important role in the development of chemicals and fuels in the future. However, cellulose is a homopolymer of D-glucose made up of β-1,4 glycosidic bonds (Scheme 2A). Its intramolecular and intermolecular hydrogen bonds are formed (Scheme 2B), resulting in its water insolubility (Geboers et al., ; Wang et al., ; Harada et al., ; Yabushita et al., ). Therefore, the processes of cellulose conversion are complicated because this biopolymer is insoluble in water, and most organic solvents (Klemm et al., ; Albert et al., ).
Scheme 2
Many homogeneous and heterogeneous acid catalysts were found to be capable of converting cellulose into glucose, a monosaccharide which is an important component for synthesizing different kinds of chemicals and fuels (Scheme 3), such as furans (Li et al., ), ethanol (Chheda et al., ), polyhydric alcohol (Geboers et al., ; de Op Beeck et al., ; Xie et al., ; He et al., ), furfural (Yu et al., 2009b; Feng et al., ; Li et al., ; Pan et al., ), organic acid (Yan et al., 2014; Zhang et al., 2014; Ren et al., ), and so on. Several excellent review literature on the conversion of cellulose have been reported, with focus on the discussion of different solid acid catalysts (e.g., Amberlyst-15, PCPs–SO3H, BC–SO3H, CMK-3-SO3H, Zn–Ca–Fe, CsH2PW12O40, Ru/CMK-3, Fe3O4-SBA–SO3H, CaFe2O4, H3PW12O40, H5BW12O40, H5AlW12O40, H5GaW12O40, and H6CoW12O40) for hydrolysis of cellulose (Table 1; Kobayashi et al., ; Pang et al., ; Rinaldi et al., ; Tian et al., , ; Wu et al., ; Akiyama et al., ; Komanoya et al., ; Lai et al., ; Ogasawara et al., ; Zhang et al., 2011).
Scheme 3
Table 1
| Catalyst | Solvents | Temp (°C) | Time (h) | Glucose/TRS yield TRS yield/% | References |
|---|---|---|---|---|---|
| Amberlyst-15 | [BMIm]Cl/H2O | 100 | 5 | 11.0 | Rinaldi et al., |
| PCPs–SO3H | H2O | 120 | 3 | 5.30 | Akiyama et al., |
| BC–SO3H | H2O | 90 | 1 | 19.8 | Wu et al., |
| CMK-3-SO3H | H2O | 150 | 24 | 74.5 | Pang et al., |
| Zn–Ca–Fe | H2O | 160 | 20 | 29 | Zhang et al., 2011 |
| CsH2PW12O40 | H2O | 160 | 6 | 27.0 | Tian et al., |
| Ru/CMK-3 | H2O | 230 | 24 | 34.2 | Kobayashi et al., |
| Fe3O4-SBA–SO3H | H2O | 150 | 3 | 26.0 | Lai et al., |
| CaFe2O4 | H2O | 150 | 24 | 36.0 | Komanoya et al., |
| H3PW12O40 | H2O | 180 | 2 | 50.5 | Tian et al., |
| H5BW12O40 | H2O | 60 | 6 | 77.0 | Ogasawara et al., |
| H5AlW12O40 | H2O | 60 | 24 | 68.0 | Ogasawara et al., |
| H5GaW12O40 | H2O | 60 | 24 | 62.0 | Ogasawara et al., |
| H6CoW12O40 | H2O | 60 | 24 | 59.0 | Ogasawara et al., |
Cellulose hydrolysis over different solid acid catalysts.
Compared with other solid acids, HPA catalysts are more favorable for hydrolysis of cellulose, considering that they have some unique properties such as stronger acidity compared to other mineral acids (e.g., H2SO4, HCl), high redox properties, good thermal stability, easy separation, good reusability, fewer side products, less waste generation, non-toxicity, and easy handling, as illustrated in Figure 1 (Kozhevnikov, , ; Mizuno and Misono, ; Kaur and Kozhevnikov, ; Yu et al., 2009a; Yang et al., 2011; Deng et al., ; Reddy et al., ; de Op Beeck et al., ). Furthermore, HPA catalysts can be used in both homogeneous and heterogeneous systems. The most significant advantage of the heterogeneous system is that the HPA catalysts can be easily separated from the reaction products, thus improving the catalyst reusability. The most common HPAs are Keggin-type HPAs, which have the anions of [XM12O40]n−, where X is a heteroatom (e.g., P, Si) and M is a metal ion (e.g., W6+, Mo6+). Among them, H3PW12O40 is the most common Keggin-type HPA. Moreover, H3PW12O40 with strong acidity is highly soluble in water and can completely dissociate protons, which facilitates contact with the heterogeneous substrates, thus endowing enhanced reaction rates (Tian et al., ). Besides, the basic structural units of Keggin-type HPAs are oxygen-containing tetrahedron and octahedron anions in good symmetry and low charge density (Figure 2).
Figure 1
Figure 2
Given the unique features and rapid development of HPAs-based catalysts in the preliminary degradation of cellulosic biomass with high efficiency, this review mainly reports the design and structural characterization of different types of HPAs employed for hydrolytic depolymerization of cellulosic biomass. In addition, the properties and preparation methods of HPAs as well as their advantages in the hydrolysis of cellulose are discussed. Also, possible research trends of HPAs in the future are forecasted.
HPAs-Based Catalysts
HPA Properties and Classification
HPA catalysts have attracted people's attention, and are known as effective, environmentally friendly and economically viable acid catalysts (Kozhevnikov, ), which can be used in either homogeneous or heterogeneous state (Izumi et al., ; Nowinska et al., ; Song and Lee, ; Bennardi et al., ; Zhao et al., 2013). Compared with a homogeneous system, the heterogeneous system has the advantage that the catalyst is easy to separate from the reaction products. Due to these special features, HPA catalysts are more beneficial to the degradation of cellulosic biomass than other catalysts.
HPA catalysts can be classified into the following categories: (1) Keggin-type HPAs, the most common HAPs with the anions of [XM12O40]n−, where X is a heteroatom (e.g., P, Si) and M is a metal ion (e.g., W6+, Mo6+). (2) Substituted HPAs, the H+ ions on conventional HPAs are substituted by monovalent cations, such as Cs+ ions. (3) Supported HPAs, the heteropoly compounds are supported on suitable supporters, such as silica. (4) Assembled HPAs, the new catalysts with higher activity are synthesized by self-assembly of HPAs with other substances, such as ionic liquids. (5) Other types, new types of heterogeneous catalysts formed by an effective combination of HPAs with other substances.
Catalyst Preparation Methods
Up to the present, many patents and literature on the preparation of HPAs were published, including e.g., traditional acidification method incorporated with an ether extraction, ion exchange method, impregnation method, and sol-gel method (Bechtold and Square, ; Laferty and John, ; Chiola and Lawrence, ; Chiola et al., ; Izumi et al., ; Vázquez et al., ; Mrowiec-Białoń et al., ; Cardoso et al., ; Yang et al., 2005; Ahmed et al., ). The traditional synthesis method of conventional HPAs is an acidification process coupled with an ether extraction, which is commonly used for the synthesis of phosphotungstate HPA catalysts. In this method, the HPA is prepared by mixing heteroatom oxygen-containing acid and ligand oxide in a certain proportion, heating, refluxing, and then acidifying to obtain HPA. The HPA is dissolved in ether, and the solid HPA is obtained after ether volatilization (Chiola and Lawrence, ; Chiola et al., ). However, the acidification procedure coupled with an ether extraction has the disadvantages of low safety due to the use of toxic substances and low yield of some HPAs. In connection with this, the ion-exchange method has been developed, which first obtains the corresponding ammonium salt, and then obtains HPA through hydrogen ion-exchange resin. This method avoids the use of ether and improves process safety, but the production cycle is relatively long (Bechtold and Square, ; Laferty and John, ). For some supported HPAs, the impregnation method is commonly used. The method is to add the carrier into the solution of HPA with a certain concentration, stir for a long time at a certain temperature, stand still, and then remove the excess solvent to obtain the catalyst. The method is simple and safe, but there are some problems such as the loss of catalyst activity and limited recycling ability. Therefore, the support should be screened and optimized (Vázquez et al., ; Cardoso et al., ; Liu et al., ). The sol-gel method is to add raw materials to the HPA colloid and obtain the HPA catalyst through a series of specific processes, such as drying and heat treatment. This method can be used to prepare catalysts at a low temperature or mild condition, which is widely used in manufacturing nanomaterials catalysts. Likewise, this method has the disadvantages of low security and long cycle (Izumi et al., ; Mrowiec-Białoń et al., ; Yang et al., 2005). Some examples of catalysts for the preparation of HPAs are as follows:
Keggin-type Mo-V-P heteropoly acid catalysts (Scheme 4; Zhizhina and Odyakov, 2008; Odyakov and Zhizhina, ): Firstly, V2O5 was dissolved in cold diluted H2O2 solution to form peroxy complexes, which was gradually decomposed with oxygen to give H6O10V28. Then, by adding excess H3PO4, H6O10V28 acid produced was immediately stabilized to give H9PV14O42, following by addition into the boiling suspension of MoO3 and H3PO4 to form the catalyst.
Substituted heteropoly tungstic acid catalyst CsxH3−xPW12O40 (x = 1–3): It is usually prepared by titration method (Okuhara et al., , , ; Tian et al., ). At room temperature, dropping 0.10 mol dm−3 Cs2CO3 aqueous solution into 0.8 mol dm−3 of H3PW12O40 aqueous solution at a constant rate was stirred continuously. Then the resulting solution was aged overnight at room temperature and heated at 50°C to obtain the catalyst.
The synthesis of catalyst (HOCH2CH2N(CH3)3)x H3−xPW12O40 (abbreviated as ChxH3−xPW12O40) is shown in Scheme 5 (Duan et al., ; Zhang et al., 2016): choline chloride (ChCl, HOCH2CH2N(CH3)3Cl) (3.34 mmol) was added to H3PW12O40 (3.34 mmol) solution and the white precipitate was formed after stirring in 20 mL distilled water for 8 h at room temperature. Then the white precipitate was washed with distilled water, followed by recrystallization twice with CH3CN, drying at 60°C, and finally getting the white product ChH2PW12O40 (HOCH2CH2N(CH3)3H2PW12O40).
The self-assembled HPA ionic liquid catalyst [C4H6N2(CH2)3SO3H]3PW12O40 (Scheme 6; Leng et al., ): 0.11 mol methyl imidazole and 0.10 mol 1,3-propane sulfone were dissolved in 20 mL toluene under nitrogen and stirred for 24 h at 50°C. The resulting white precipitate is filtered and washed three times with ether and then dried in a vacuum. Then it was added to the aqueous solution of H3PW12O40 (0.02 mol) and stirred for 24 h at room temperature. Then water was removed in vacuum to obtain solid products, washed with water and ethanol, and dried at 100°C for 3 h.
Scheme 4
Scheme 5
Scheme 6
Hydrolytic Depolymerization of Biomass With HPAS-Based Catalysts
Keggin-Type HPAs
Keggin-type HPAs are the most common HPA catalysts, which have great application prospects for biomass degradation. The potential of HPAs for catalyzing the hydrolysis of cellulose to glucose has been explored.
Cellulose Conversion to Glucose
Tian et al. developed the heteropoly acid H3PW12O40 for selective conversion of cellulose (Scheme 7). The heteropoly acid catalyst can promote cellulose hydrolysis, achieving the glucose selectivity and yield of 92.3 and 50.5%, respectively at 180°C for 2 h with 0.10 g cellulose amount. The authors also studied and optimized reaction parameters influencing the hydrolysis of cellulose and determined the most optimizing reaction conditions. Compared with HCl, H3PW12O40 had greater catalytic activity and glucose selectivity under identical reaction conditions with the same acid concentration (Table 2: 0.2 mmol HCl is equivalent to 0.06 mmol H3PW12O40, and 0.06 mmol H3PW12O40 had higher catalytic activity). After testing the catalytic activity of H3PW12O40 in six consecutive reaction cycles, the total loss of H3PW12O40 was 8.8% of its initial loss (Figure 3; Tian et al., ). It was found that the acid catalyst H3PW12O40 was generally stable and could be recycled by extraction using diethyl ether. However, there was still a little loss of catalyst activity, which led to a slight decrease in the yield of TRS and glucose.
Scheme 7
Table 2
| Catalyst (mmol) | Conversion (%) | TRS yield (%) | Glucose yield (%) | Selectivity (%) |
|---|---|---|---|---|
| None | 0 | 0 | 0 | 0 |
| HCl (0.20 mmol) | 25.6 | 25.3 | 13.8 | 53.9 |
| H3PW12O40 (0.01 mmol) | 10.4 | 10.4 | 8.2 | 78.8 |
| H3PW12O40 (0.02 mmol) | 17.1 | 16.7 | 13.8 | 80.7 |
| H3PW12O40 (0.03 mmol) | 23.0 | 22.1 | 20.9 | 90.7 |
| H3PW12O40 (0.05 mmol) | 29.7 | 28.4 | 26.5 | 89.2 |
| H3PW12O40 (0.05 mmol) | 33.2 | 32.8 | 30.7 | 92.5 |
| H3PW12O40 (0.06 mmol) | 38.5 | 38.5 | 36.6 | 95.1 |
| H3PW12O40 (0.07 mmol) | 44.0 | 43.8 | 41.8 | 95.0 |
| H3PW12O40 (0.08 mmol) | 54.7 | 54 | 50.5 | 92.3 |
| H3PW12O40 (0.09 mmol) | 57.4 | 56.3 | 51.9 | 90.4 |
Hydrolysis of cellulose with different acid catalysts (Tian et al., ).
TRS, total reducing sugars. Reaction conditions: 0.1 g cellulose, 5 mL water, at 180°C for 2 h.
Figure 3
In 2009, Shimizu et al. studied the effects of Brønsted and Lewis acidities on the activity and selectivity of HPA catalysts for hydrolysis of cellulose (Furukawa et al.,
Figure 4

The effect of deprotonation enthalpy (DPE) of acid catalysts on catalysts activity (∘, TRS yield; •, cellulose conversion; Δ, TRS selectivity of cellulose hydrolysis). Reaction conditions: 0.58 mmol cellulose, 6 mL H2O, 6 mol catalyst (Mn/3PW12O40) at 150°C for 2 h. Reproduced with permission from Macht et al. (
Figure 5

The effect of Lewis acid on the catalytic rate of catalysts (∘, TRS yield; •, cellulose conversion; Δ, TRS selectivity of cellulose hydrolysis). Reaction conditions: 0.58 mmol cellulose, 6 mL H2O, 6 mol catalyst (Mn/3PW12O40) at 150°C for 2 h. Reproduced with permission from Shimizu and Satsuma (
Ogasawara et al. found that the highly negatively charged HPAs (e.g., H5BW12O40, H5AlW12O40, and H5GaW12O40) could efficiently promote the hydrolysis of crystalline cellulose into glucose in concentrated aqueous solutions (Ogasawara et al.,
Table 3
| No. | Acid catalysts | Concentration | Glucose yield (%) | |
|---|---|---|---|---|
| Anion (mol/L) | Proton (mol/L) | |||
| 1 | H3PW12O40 | 0.70 | 2.1 | 8 |
| 2a | H3PW12O40 | 0.60b | 3.5 | 18 |
| 3 | H4SiW12O40 | 0.70 | 2.8 | 37 |
| 4a | H4SiW12O40 | 0.70 | 3.5 | 61 |
| 5 | H5BW12O40 | 0.70 | 3.5 | 77 |
| 6 | H5BW12O40 | 0.40 | 2.0 | 4 |
| 7 | H5AlW12O40 | 0.70 | 3.5 | 68 |
| 8 | H5GaW12O40 | 0.70 | 3.5 | 62 |
| 9 | H6CoW12O40 | 0.70 | 4.2 | 59 |
| 10 | H2SO4 | 1.75 | 3.5 | <1 |
| 11 | H2SO4 | 4.5c | 9.0 | 5 |
| 12 | HCl | 3.5 | 3.5 | 4 |
| 13 | HCl | 6.0c | 6.0 | 9 |
Hydrolysis of cellulose using different concentrations of aqueous acidic solutions (Ogasawara et al.,
The proton concentration was adjusted using H2SO4.
Saturated concentration.
The same as that of the H5BW12O40 solution (0.7 mol/L).
Reaction conditions: crystalline cellulose (100 mg), aqueous acidic solution (2 mL), 60°C for 48 h.
Scheme 8

Transformation of cellobiose and starch in concentrated H5BW12O40 aqueous solutions (0.70 mol/L, 2 mL).
Figure 6

Recyclability of H5BW12O40 for the conversion of pretreated cellulose. Reaction conditions: 100 mg pretreated cellulose (the cellulose was mercerized and then ball-milled), 0.70 mol/L, 2 mL H5BW12O40 solution, 60°C for 24 h. Reproduced with permission from Ogasawara et al. (
For the conversion pathways, the HPAs can initially hydrolyze cellulose into glucose that can be further converted into other substance in the assistance of their bifunctional properties (i.e., acidity and redox property), such as catalytic oxidation of cellulose to formic acid (Wölfel et al.,
Scheme 9

Conversion of cellulose to other substance with an HPA catalyst (H+, HPA catalyst).
Cellulose Conversion to Formic Acid
Conversion of cellulose to formic acid using HPAs as catalysts is an efficient and environmentally friendly catalytic system (Lu et al.,
Scheme 10

The stages of converting cellulose into formic acid.
In 2014, different Keggin-type HPAs H3+n[PVnMo12−nO40] (n = 0–6) were synthesized, and the optimized HPA catalyst system H8[PV5Mo7O40] could selectively oxidize biomass to formic acid (Albert et al.,
Scheme 11

The redox cycle of the catalyst H5PV2Mo10O40.
Table 4
| Catalyst | Combined yield FA + CO2 (%) | pH before reaction | pH after reaction | Selectivity FA + CO2 (%) |
|---|---|---|---|---|
| HPA-0 | 10 | 3.32 | 1.54 | 40 : 60 |
| HPA-1 | 12 | 3.34 | 1.52 | 50 : 50 |
| HPA-2 | 91 | 3.51 | 1.30 | 52 : 48 |
| HPA-3 | 100 | 3.39 | 1.27 | 56 : 44 |
| HPA-4 | 97 | 3.45 | 1.41 | 54 : 46 |
| HPA-5 | 94 | 3.45 | 1.41 | 61 : 39 |
| HPA-6 | 97 | 3.24 | 1.41 | 58 : 42 |
| H9PV14O42 | 88 | 3.68 | 1.41 | 58 : 42 |
The comparison of the yields of glucose to formic acid with different HPA catalysts (Albert et al.,
Reaction conditions: 5.0 g (27.8 mmol) glucose and 0.8 mmol catalyst, 100.0 mL H2O, 90°C, 8 h, 1,000 rpm. HPA-n, H3+n[PVnMo12−nO40].
In 2016, Lu et al. found that a Keggin-type heteropoly acid catalyst H5PV2Mo10O40 with H2SO4 was efficient for catalytic oxidation of cellulose to formic acid with oxygen as an oxidant (Lu et al.,
Table 5
| Catalyst | Temp/°C | Time/h | pH | FA yield/% |
|---|---|---|---|---|
| HPA | 90 | 66 | 1.79 | 9 |
| HPA + TSA | 90 | 66 | 0.91 | 22 |
| HPA | 170 | 9 | 1.96 | 3 |
| HPA + HCl | 170 | 9 | 1.87 | 34 |
| HPA | 180 | 3 | 1.80 | 45 |
| HPA | 180 | 1/12 | 1.79 | 28 |
| HPA + H2SO4 | 180 | 1/12 | 0.56 | 61 |
Synthesis of formic acid (FA) from cellulose at different pH (Lu et al.,
HPA, H5PV2Mo10O40; TSA, p-toluenesulfonic acid.
Figure 7

Conversion of cellulose to formic acid (FA) and acetic acid (AA) under different concentration of H2SO4. Reaction conditions: 0.16 g cellulose, 0.10 g catalyst, 6 mL H2O, 3 MPa O2, 180°C for 0.25 h. Reproduced with permission from Lu et al. (
Likewise, Gromov et al. reported the one-pot catalytic process which was applied to hydrolytic oxidation of cellulose to formic acid (Gromov et al.,
Scheme 12

The overall scheme of the hydrolysis-oxidation of cellulose.
The Keggin-type (Mo-V-P)-HPAs were used to catalyze the hydrolysis of hemicellulose in a diluted aqueous solution that was reported by Shatalov (
Cellulose Conversion to Other Substances
In the oxygen environment, HPAs can also catalyze cellulose being converted to glycolic acid. In 2019, Zhang et al. reported the conversion of cellulose to glycolic acid by phosphomolybdic acid catalyst (Zhang et al., 2012). In this reaction system, the heteromolybdic acid acted as multifunctional catalysts that first hydrolyzed cellulose to glucose, followed by oxidation to glycolic acid in a water medium, which combines the advantages of homogeneous and heterogeneous catalysts. The proposed reaction pathways for the conversion of cellulose to glycolic acid are shown in Scheme 13. Cellulose was hydrolyzed to glucose, which was converted to glycolaldehyde by the continuous retro-aldol reaction, and then to glyoxal by oxidation. Simultaneously, the isomerization of glucose produced fructose, which was converted to glycolaldehyde and formaldehyde via the retro-aldol reaction, which was then oxidized to glycolic acid and formic acid, respectively. In addition, the authors investigated the reusability of the phosphomolybdic acid catalyst in cellulose conversion (Figure 8). The results indicated that the catalyst exhibited constant catalytic performance. X-ray photoelectron spectroscopy (XPS) showed that the oxidation state of Mo in the heteromolybdic acid catalyst was unchanged after successive reactions (Figure 9). It can be concluded that Mo-containing HPAs can effectively promote the conversion of various kinds of cellulosic biomass materials to glycolic acid.
Scheme 13

The proposed reaction pathways for the conversion of cellulose to glycolic acid.
Figure 8

The yield of glycolic acid in the continuous reaction of cellulose conversion with HPM (H3PMo12O40) as the catalyst. Reproduced with permission from Zhang et al. (2012). Reaction conditions: 200 mg cellulose, 0.025 mmol catalyst, 20 mL H2O, 0.6 MPa O2, 180°C for 1 h. Reproduced with permission from Zhang et al. (2012).
Figure 9

XPS spectra of Mo 3d in the fresh (A) and used (B) HPM (H3PMo12O40) catalyst. Reproduced with permission from Zhang et al. (2012).
The effective alcoholysis of cellulose to monosaccharide is of great significance for fuel production. The H3PW12O40 catalyst can promote cellulose transformation into methyl glucosides after pretreatment of microcrystalline cellulose by the ionic liquid 1-allyl-3-methylimidazolium chloride, as reported by Zheng et al. (2018). In their work, cellulose was firstly obtained by pretreatment with the ionic liquid 1-allyl-3-methylimidazolium chloride, followed by cellulose alcoholysis using H3PW12O40 as the bifunctional catalyst. It was found that cellulose was easier to be saccharified after pretreatment by the ionic liquid. Meanwhile, prolonging the pretreatment time with the increased temperature is beneficial to the succedent alcoholysis reaction. Whereafter, the authors investigated the effects of various parameters on the alcoholysis reaction, including the alcoholizing time, the alcoholizing temperature, and different concentrations of H3PW12O40 catalyst. It was observed that under the optimum conditions (110°C, 60 min), the yield of methyl glucosides could be up to 70.2% with this system. Therefore, using some processes such as pretreatment of cellulose with ionic liquid can make it easier to saccharify, thus better-promoting HPA catalytic conversion of cellulose into the desired products. However, the reusability of the catalyst is not satisfactory. As shown in Figure 10, the activity of the H3PW12O40 catalyst decreased gradually in the repeated experiment, indicating the low catalyst stability.
Figure 10

Recyclability of H3PW12O40 in alcoholysis of cellulose to methyl α-D-glucoside (M-α-G) and methyl β-D-glucoside (M-β-G). Reaction conditions: 0.3 g cellulose, 8.7 mmol/L catalyst H3PW12O40, 170°C for 2.75 h. Reproduced with permission from Zheng et al. (2018).
In addition, the HPA is also an important catalyst for the formation of glucose from other saccharides. In 2015, Klein et al. found that HPA can catalyze the hydrolysis of glycogen to glucose (Klein et al.,
Table 6
| Method | Reactant | Reaction products | ||
|---|---|---|---|---|
| Glycogen | Glucose | LAa | FAb | |
| Autoclavec | –f | +g | – | – |
| Microwaved | – | + | + | + |
| Sonicatione | – | + | – | – |
Effect of H4SiW12O40 on glycogen hydrolysis using different methods (Klein et al.,
LA, levulinic acid.
FA, formic acid.
Glycogen: 50 mg, HSiW: 50 mg, water: 2 mL, 2 h, 100°C.
Glycogen: 200 mg, HSiW: 1.2 g, water: 10 mL, 0.25 h.
Glycogen: 250 mg, HSiW: 1.5 g, water: 10 mL, 3 h.
-, absent.
+, present.
Substituted HPAs
Substituted HPAs are formed when H+ ions on conventional HPSs are substituted by monovalent cations, such as Cs+ ions. One of the typical substitutional HPAs, CsxH3−xPW12O40 has the advantages of super acidity, microporous structure, shape selectivity, and hydrophobicity, which is conducive to the hydrolysis of cellulose (Okuhara,
Cellulose Conversion to Glucose
In 2010, Tian et al. reported hydrolysis of cellulose over the CsxH3−xPW12O40 (x = 1–3) catalysts, which were active in the hydrolysis of cellulose into glucose. Notably, cellulose can be hydrolyzed to glucose in the presence of CsxH3−xPW12O40 catalysts due to the breaking of β-1,4-glycoside bond (Scheme 14).
Scheme 14

The pathways of cellulose hydrolysis into glucose over CsxH3−xPW12O40.
After a series of catalyst tests, it was found that Cs1H2PW12O40 showed the best catalytic performance in terms of cellulose conversion (54.0%) and glucose yield (27.2%), while Cs2.2H0.8PW12O40 showed the highest selectivity toward glucose (83.9%). The test results are shown in Figures 11A–C. In the meantime, they also studied the effect of CsxH3−xPW12O40's properties on cellulose hydrolysis. Cs1H2PW12O40 with the strongest protonic acid site was found to have the best catalytic performance for the hydrolysis and transformation of cellulose. However, the catalyst surface area and porous structure have little effect on the conversion of cellulose (Tian et al.,
Figure 11

(A) The relationship between cellulose conversion and cesium content in CsxH3−xPW12O40, (B) the relationship between the yield of TRS and glucose and cesium content in CsxH3−xPW12O40, and (C) the relationship between the selectivity of TRS and glucose and cesium content in CsxH3−xPW12O40. Reaction conditions: 0.1 g microcrystalline cellulose, 0.06 mmol CsxH3−−xPW12O40, 5 mL distilled water, at 160°C for 6 h (stirring 30 rpm). Reproduced with permission from (Okuhara,
Cellulose Conversion to Other Products
In 2011, Geboers et al. studied the hydrotreated cesium salts of HPAs in combination with Ru/C which can be used to degrade cellulose for the synthesis of hexitol (Geboers et al.,
Table 7
| Entry | Acid catalyst | Reaction time/h | Conversion (%) | Hexitol yield |
|---|---|---|---|---|
| 1 | Cs3.5SiW | 24 | 100 | 55 |
| 2 | Cs3.5SiW | 13 | 100 | 56 |
| 3 | Cs2.5PW | 8 | 91 | 45 |
| 4 | Cs2.5PW | 8 | 95 | 59 |
| 5 | Cs2.5 | 11 | 93 | 46 |
| 6 | H4SiWc | 24 | 100 | 18 |
| 7 | H3PWc | 24 | 81 | 41 |
Hydrolysis and hydrogenation of cellulose with Ru/C and different HPAs at 190°C and 5 MPa H2 (Geboers et al.,
1 g cellulose, 0.5 g CsHPA ([H+] = 1.5 mM), 0.25 g Ru/C, 50 m water.
5 g cellulose, 2.5 g CsHPA ([H+] = 7.5 mM), Ru/C = 1.25 g, water 50 mL.
Adjust the HPA amount to make the proton concentration consistent with CsHPA.
As compared with their fully protonated counterparts (Cs2.5PW and Ru/C or Cs3.5SiW and Ru/C), the cesium HPAs have higher proton activity due to their higher surface acidity and hydrophobicity. After a hydrotreatment of cesium HPAs catalysts in water at 190°C was performed, the activity and selectivity of the catalysts were improved obviously due to the increase of crystallinity and hydrophobicity of samples. Finally, they found that these cesium HPAs could be completely recovered under certain conditions by a simple recrystallization method (Geboers et al.,
In 2014, Zhang et al. synthesized a series of HPA catalysts (HOCH2CH2N(CH3)3)xH3xPW12O40 (HOCH2CH2N(CH3)3 abbreviated as Ch), which could be used as heterogeneous catalysts for degradation of cellulose to 5-hydroxymethylfurfural (HMF) (Zhang et al., 2016). By comparing several different types of acid catalysts (Figure 12), they found that the conversion of cellulose with Brønsted acid in HCl and H3PW12O40 was 41.5 and 89.2%, respectively, while that of ChCl and Ch3PW12O40 without Brønsted acid was 2.0 and 12.2%, respectively. So the strong Brønsted acidity of the catalyst was the necessary condition for cellulose hydrolysis. And (HOCH2CH2N(CH3)2)H2PW12O40 had the highest catalytic activity among the previous catalysts. The yield of HMF can reach 75% when cellulose was catalyzed by (HOCH2CH2N(CH3)2)H2PW12O40 within 8 h at 140°C. Besides, the temperature-responsive property and high stability of the catalyst made the recovery and reuse benefit reach 10 times without obvious activity loss (Figure 13).
Figure 12

Hydrolysis of cellulose under different catalysts. Reaction conditions: 0.1 g cellulose, 0.11 mmol catalyst, 0.5 ml water, 5 mL methyl isobutyl ketone, 140°C for 8 h. Reproduced with permission from Zhang et al. (2016).
Figure 13

The recycle reaction test of catalyst. Reaction conditions: 0.1 g cellulose, 0.11 mmol ChH2PW12O40, 0.5 mL water, 5 ml methyl isobutyl ketone, 140°C for 8 h. Reproduced with permission from Zhang et al. (2016).
Overall, it can be seen that the substituted HPA catalysts showed high activity in the conversion of cellulose and they were stable and reusable. Therefore, the substituted HPA catalysts have good application prospects in cellulose degradation. However, the substituted HPA catalysts still suffer the disadvantage of low target product yield or selectivity, possibly due to the resistance of mass transfer.
Supported HPAs
So far, more and more attention has been paid to the supported acid catalysts, especially the supported HPAs. The dispersion of these catalysts on the support material increases the specific surface area, thus improving the catalytic activity. Some supported HPAs have been used in the degradation of cellulose. In 1981, Yusuke and Urabe found that activated carbon can encapsulate a certain amount of HPA, thus producing solid acid catalysts, which provided a convenient method for liquid phase etherification and gas-phase selective esterification of alcohols (Yusuke and Urabe, 1981). In 1989, the nuclear magnetic resonance (NMR) technology had been used in the structural research of HPAs and H3PW12O40 supported on SiO2 (Mastikhin et al.,
HPAs are usually used as soluble catalysts in the liquid phase and as supported catalysts in the gas phase. From a practical point of view, it is useful to develop those supported HPA catalysts, which can be applied to a variety of reactions through fixed catalysts without leakage of HPA in the liquid, such as acylation of anisole with acetic anhydride (Bachillerbaeza and Anderson,
Scheme 15

Dehydration of aldehydes to nitriles catalyzed by HPA-SiO2.
In 2007, Guo et al. studied a sol-gel co-condensation technology that can be used to prepare the green supported heteropoly acid catalysts (H3PW12O40-silica), which was an efficient and reusable solid acid catalyst for the catalytic esterification of levulinic acid (LA) with phenol (Guo et al.,
Table 8
| Catalyst | 2θ/o | SBET/m2 g−1 | D/nm | Porosityb | LA conversion (%) | TOF |
|---|---|---|---|---|---|---|
| H3PW12O40/SBA-15-E-4.0 | 0.95 | 691.6 | 7.1 | 1.20 | 23.6 | 6.9 |
| H3PW12O40/SBA-15-E-14.8 | 0.92 | 683.0 | 7.4 | 0.95 | 74.8 | 46.4 |
| H3PW12O40/SBA-15-E-17.5 | 0.90 | 630.4 | 8.6 | 0.91 | 80.1 | 51.0 |
| H3PW12O4/SBA-15-C-7.5 | 0.95 | 753.0 | 6.0 | 1.10 | 19.2 | 3.5 |
| H3PW12O4/SBA-15-C-11.3 | 0.91 | 713.2 | 6.4 | 0.85 | 72.3 | 48.5 |
| H3PW12O4/SBA-15-C-15.7 | 0.96 | 604.5 | 6.6 | 0.75 | 80.3 | 53.9 |
| H3PW12O40/SiO2-D-15.4 | – | 317.6 | 1.2 | 0.34 | 5.3 | 0.65 |
| H3PW12O40 | – | 5.5 | – | – | 60.1 | 1.04 |
| HCl | – | – | – | – | 65.4 | 0.73 |
| SBA-15-E | 0.99 | 858.2 | 5.2 | 0.71 | 0 | 0 |
| SBA-15-C | 0.96 | 750.1 | 5.3 | 0.51 | 0 | 0 |
Comparison of surface properties and catalytic activities of different catalysts in the esterification of levulinic acid (LA) with phenol (Guo et al.,
aPore diameters are estimated from BJH desorption determination.
bThe porosity is estimated from the pore volume determined using the adsorption branch of the N2 isotherm curve.
Reaction conditions: 3.4 mmol LA, 13.6 mmol phenol, 0.05 g catalyst, 100°C for 8 h.
Figure 14

Nitrogen adsorption-desorption isotherms and pore size distribution profiles (inset) of H3PW12O40/SBA-15 materials. (A) Removal of H3PW12O40/SBA-15 by extraction with acidic ethanol, and (B) removal of H3PW12O40/SBA-15 by calcination at 400°C. Reproduced with permission from Guo et al. (
In 2011, silica-supported HPA, a heterogeneous and environmentally benign catalyst was found by Parghi et al. (
Table 9
| Entry | Catalyst | Benzonitrile yield/% |
|---|---|---|
| 1 | SiO2 | 10 |
| 2 | HPW | 51 |
| 3 | HPW | 40 |
| 4 | HPW-SiO2 | 85 |
| 5 | HPW-SiO2 | 72 |
| 6 | – | – |
Aldosterone dehydration with different catalysts (Parghi et al.,
Reaction condition: 2 mmol benzaldehyde oxime, catalyst (20 wt%); 3 mL toluene, 100°C for 4.5 h.
In 2012, An et al. reported on the conversion of cellulose and cellobiose by polyoxometalate-supported gold nanoparticles (An et al.,
Scheme 16

Catalytic conversion of cellulose to gluconic acid with Au/CsxH3xPW12O40.
Table 10
| Catalyst | Conversion (%) | GAa selectivity (%) | GA yield (%) |
|---|---|---|---|
| Au/Cs1.2H1.8PW12O40 | 97 | >99 | 97 |
| Au/Cs1.7H1.3PW12O40 | 98 | 96 | 94 |
| Au/Cs2.2H0.8PW12O40 | 96 | 95 | 91 |
| Au/Cs2.6H0.4PW12O40 | 97 | 90 | 87 |
| Au/Cs3.0PW12O40 | 95 | 85 | 81 |
| Au/SiO2 | 67 | 61 | 41 |
| Au/Al2O3 | 95 | 31 | 29 |
| Au/TiO2 | 96 | 63 | 60 |
| Au/H-ZSM-5 | 45 | 76 | 34 |
| Au/HY | 64 | 62 | 40 |
| Au/CNT | 84 | 86 | 72 |
Transformation of cellobiose with different supported catalysts (An et al.,
aGA, GLUCONIC acid. Reaction conditions: 12 mmol/L cellobiose, 0.050 g catalyst (Au loading: 1.0 wt%), 25 mL H2O, 0.5 MPa O2, 145°C for 3 h. Reproduced with permission from An et al. (
Figure 15

The effect of Au/Cs2.2H0.8PW12O40 catalysts with different average particle sizes of Au on TOFs of glucose oxidation to gluconic acid. Reaction conditions: 24 mmol/L glucose, 25 mL H2O, 0.5 MPa O2, 145°C for 3 h. Reproduced with permission from An et al. (
In 2012, Lanzafame et al. reported that some solid acid catalysts can convert cellulose into glucose, HMF, and other soluble by-products in 190°C aqueous solution for 5 h or <5 h (Lanzafame et al.,
Figure 16

Activity comparison of different solid acid catalysts for cellulose conversion. Reaction conditions: 2 g cellulose, 0.2 g catalyst, 55 mL distilled water, 190°C for 5 h. Reproduced with permission from Lanzafame et al. (
In 2014, Hafizi et al. found a unique heterogeneous silica-supported Preyssler heteropoly acid catalyst (H14NaP5W30O120), which can be used for alkylation of benzene (Hafizi et al.,
Table 11
| Sample | Compressive strength (MPa) | Specific surface area (m2 g−1) | Pore volume (cm3 g−1) | Mean pore size (nm) |
|---|---|---|---|---|
| CF0 | – | 201.2 | 0.208 | 9.72 |
| CF10 | 0.096 | 225.6 | 0.221 | 7.95 |
| CF20 | 0.126 | 253.9 | 0.232 | 4.36 |
| CF30 | 0.147 | 302.5 | 0.259 | 4.03 |
| CF40 | 0.146 | 255.2 | 0.242 | 3.65 |
| Original HPW/CF30 | 0.148 | 200.9 | 0.222 | 3.73 |
| Reused HPW/CF30 | 0.140 | 221.9 | 0.223 | 2.01 |
Selected properties of different catalysts (Zhang et al., 2019).
Figure 17

Reusability test of the HPW/CF30 catalyst for cellulose hydrolysis. Reaction conditions: 0.1 g MAMCC (mechanical activation microcrystalline cellulose), 1.0 g HPW/CF30, 10 mL H2O, 170°C for 9 h. Reproduced with permission from Zhang et al. (2019).
Based on the studies of these supported HPA catalysts, it can be seen that the supported HPAs have a higher specific surface area than conventional HPAs. Also, the supported HPAs can be used in the heterogeneous reaction, which is more convenient for product separation and can be reused. It is worth noting that there are still some shortcomings of the catalysts, such as low selectivity of the target product and gradual decline of stability of the catalysts in recycles.
Assembled HPAs
In recent years, people began to explore new efficient catalysts for cellulose conversion. The assembled HPA catalysts have also become one of the research directions. It is noteworthy that the assembled HPA catalysts were studied for the degradation of cellulose in biomass and other valuable catalytic reactions. For example, in 2010, Wee et al. proposed a simple and highly repetitive synthesis method for the assembly of nanomaterial catalyst H3PW12O40/Cu3(BTC)2 (BTC = benzene tricarboxylic acid). Cu3(BTC)2 was encapsulated into Keggin HPA H3PW12O40 for application in catalysis (Wee et al.,
Figure 18

Effect of catalysts on conversion of acetic acid in esterification. Catalysts: (A) without catalyst, (B) micron-sized HPW/Cu3(BTC)2, (C) ultrastable Y zeolite (CBV 720), (D) 65 nm HPW/Cu3(BTC)2, and (E) 50 nm HPW/Cu3(BTC)2. Reaction conditions: 1 mol acetic acid, 40 mol 1-propanol, 2.23 wt% catalyst, 60°C. Reproduced with permission from Wee et al. (
In 2011, Cheng et al. reported that a micellar HPA catalyst [C16H33N(CH3)3]H2PW12O40 (C16H2PW) was designed to hydrolyze cellulose and starch into glucose. The micellar HPA catalyst can allow cellulose molecules to enter into the catalytic sites, so as to improve the reaction rate and cellulose conversion rate (Dwars et al.,
Table 12
| Catalyst (mmol) | Reaction time (h) | Amount of water (mL) | Cellulose conversion (%) | TRS yield (%) | Glucose yield (%) | Glucose selectivity (%) | TOF (g mmol−1 h−1) |
|---|---|---|---|---|---|---|---|
| CTAB (0.07) | 8 | 7 | 0 | 0 | 0 | 0 | 0 |
| H3PW12O40 (0.07) | 5 | 5 | 70.4 | 68.1 | 59.9 | 85.1 | 0.201 |
| Cs2.5H0.5PW (0.07) | 6 | 5 | 23.7 | 22.2 | 21.3 | 89.9 | 0.056 |
| C16 H2PW (0.08) | 8 | 7 | 45.7 | 36.3 | 35.1 | 76.8 | 0.071 |
| C16 H2PW (0.07) | 8 | 8 | 43.7 | 35.7 | 34.2 | 78.3 | 0.078 |
| C16 H2PW (0.07) | 8 | 7 | 44.1 | 40.2 | 39.3 | 89.1 | 0.079 |
| C16 H2PW (0.07) | 8 | 6 | 42.6 | 40.5 | 37.0 | 86.9 | 0.076 |
| C16 H2PW (0.07) | 8 | 5 | 39.3 | 34.4 | 33.5 | 85.2 | 0.070 |
| C16 H2PW (0.07) | 8 | 4 | 34.7 | 30.7 | 29.3 | 84.4 | 0.062 |
| C16 H2PW (0.06) | 8 | 7 | 42.8 | 38.5 | 37.6 | 87.9 | 0.089 |
| C16 H2PW (0.05) | 8 | 7 | 37.4 | 31.3 | 30.2 | 80.7 | 0.093 |
Hydrolysis of cellulose over different catalysts (Cheng et al.,
Reaction conditions: 0.1 g cellulose, 170°C. Reproduced with permission from Cheng et al. (
Figure 19

Recycling test of the [C16H33N(CH3)3]H2PW12O40 catalyst. Reaction conditions: 0.1 g cellulose, 0.07 mmol catalyst, 7 mL water, 170°C for 8 h. Reproduced with permission from Cheng et al. (
In 2012, Sun et al. investigated a kind of HPA-ionic liquid catalysts [C4H6N2(CH2)3SO3H]3−nHnPW12O40 (n = 1, 2, 3) (abbreviated as [MIMPSH]nH32nPW), which can be used to degrade cellulose into water-soluble products such as glucose and levulinic acid (Sun et al.,
Table 13
| Catalyst | Conversion/% | TRS yield/% | Glucose yield (%) | TOF/g mmol−1 |
|---|---|---|---|---|
| MIMPSH | 0 | 0 | 0 | 0 |
| H3PW12O40 | 54.1 | 31.6 | 27.0 | 0.12 |
| H3PW12O40 + ILb | 57.3 | 33.8 | 27.1 | 0.12 |
| [MIMPSH]H2PW | 55.1 + 1.7 | 40.2 + 1.7 | 36.0 + 2.6 | 0.17 |
| [MIMPSH]H2PWc | 13.1 + 1.6 | 9.6 + 2.0 | 8.4 + 2.3 | 0.14 |
| [MIMPSH]2HPW | 42.7 + 1.3 | 35.9 + 1.9 | 27.3 + 1.8 | 0.13 |
| [MIMPSH]3PW | 28.4 + 1.4 | 25.2 + 1.5 | 23.2 + 2.5 | 0.11 |
| Cs2.5H0.5PW12O40 | 12.3 | 10.0 | 8.1 |
Hydrolysis of cellulose with different catalystsa (Sun et al.,
Reaction conditions: 0.1 g cellulose, 0.07 mmol catalyst, 0.5 mL water and 5 mL MIBK (methyl isobutyl ketone) at 140°C for 5 h.
0.07 mmol H3PW12O40 and 0.07 mmol IL as the catalyst.
No MIBK, just 5.5 mL water. Reproduced with permission from Sun et al. (
Scheme 17

Conversion of other polysaccharides over the [MIMPSH]H2PW catalyst. Reaction conditions: 0.077 mmol catalyst, 0.5 mL water, and 5.0 mL MIBK.
Figure 20

Reusability test of the [MIMPSH]H2PW catalyst. Reaction conditions: 0.1 g cellulose, 0.07 mmol catalyst, 0.5 mL H2O, 5 mL MIBK, 140°C for 5 h. Reproduced with permission from Sun et al. (
In 2013, Chen et al. synthesized the polyvinylpyrrolidone-stabilized heteropolyacids (PVP–HPAs), a kind of reusable self-assembling catalysts for conversion of cellulose (Chen et al.,
Scheme 18

Synthetic routes to PVP-HPAs model.
Scheme 19

The conversion pathways and mechanism for the alcoholysis of cellulose.
Figure 21

(A) The FT-IR spectra of PVP, HPAs, and PVP–HPAs, and (B) solid MAS 1H-NMR spectra of PVP–HPW catalysts. Reproduced with permission from Chen et al. (
In 2015, Sun et al. synthesized an assembled HPA catalyst [C16H33N(CH3)3]xH6−xP2W18O62 (abbreviated as (C16TA)nH6−nP2W18O62). Wells–Dawson heteropolyacid H6P2W18O62 was used to synthesize the micellar assembly catalyst, which can catalyze the hydrolysis of cellulose to glucose (Sun et al.,
Scheme 20

The mechanism of cellulose conversion by (C16TA)nH6−nP2W18O62 catalyst.
Table 14
| Catalyst | Conversion/% | TRS yield/% | Glucose yield (%) | TOF/g mmol−1 |
|---|---|---|---|---|
| H6P2W18O62 | 93.5 | 52.6 | 45.6 | 12.9 × 10−2 |
| (C16TA)H5P2W18O62 | 87.2 | 72.4 | 69.1 | 12.1 × 10−2 |
| (C16TA)2H4P2W18O62 | 75.5 | 64.4 | 61.7 | 10.5 × 10−2 |
| (C16TA)3H3P2W18O62 | 63.8 | 58.7 | 53.4 | 8.9 × 10−2 |
| (C16TA)4H2P2W18O62 | 58.3 | 53.0 | 49.4 | 8.1 × 10−2 |
| (C16TA)5HP2W18O62 | 43.5 | 40.3 | 37.8 | 6.0 × 10−2 |
| (C16TA)6P2W18O62 | 30.6 | 28.5 | 25.7 | 4.3 × 10−2 |
| (C16TA)H2PW12O40 | 81.6 | 75.3 | 63.3 | 11.3 × 10−2 |
| H3PW12O40 | 55.7 | 46.3 | 44.2 | 7.7 × 10−2 |
Conversion of cellulose over different catalysts (Sun et al.,
Reaction conditions: 100 mg cellulose, 0.08 mmol catalyst, 5 mL H2O, 160°C, 9 h. Reproduced with permission from Sun et al. (
Sun et al. found that the high catalytic activity of the catalyst was due to the interaction of a high concentration of acid sites, which provided more opportunities for the substrate to enter the catalytic sites and the oxidation ability of (C16TA)nH6−nP2W18O62 (Sun et al.,
Figure 22

The circulation reaction test of the [C16H33N(CH3)3]H5P2W18O62 catalyst in conversion of cellulose to glucose. Reaction conditions: 100 mg cellulose, 0.08 mmol catalyst, 5 mL H2O, 160°C for 9 h. Reproduced with permission from Sun et al. (
Lu et al. prepared heterogeneous catalysts (CnH2n+1N(CH3)3)H4PW11TiO40 (n = 4, 8, 12, 14, 16, and 18) composed of HPAs and amphiphilic quaternary ammonium salt by self-assembly method (Lu et al.,
Figure 23

The efficiency of different catalysts for fructose transformation. Reaction conditions: 0.6 g fructose, 0.01 mmol catalyst, 2 mL H2O, 130°C for 1.5 h. Reproduced with permission from Lu et al. (
Figure 24

Recycling test of the (C16H33N(CH3)3)H4PW11TiO40 catalyst in the conversion of fructose to HMF. Reaction conditions: 0.6 g fructose, 0.01 mmol catalyst, 2 mL H2O, 130°C for 1.5 h. Reproduced with permission from Lu et al. (
It can be seen that the assembled HPA catalysts can convert cellulose into glucose or other substances. Their unique structure can make cellulose aggregate to the catalytic sites, thus improving the catalytic efficiency. And almost all of them can be recycled by simple instruments. These advantages make their research more meaningful. However, it can not be ignored that some supported catalysts have low selectivity and yield for glucose, such as (C16TA)H5P2W18O62 and [MIMPSH]H2PW. Moreover, the stability of some HPA catalysts decreased after reuse, which should be improved by the exploration of novel preparation methods.
Other HPA Catalysts
In addition to the HPA catalysts mentioned above, many other HPAcatalysts have also been developed and utilized for cellulose degradation. For example, HPAs can be combined with other catalysts to facilitate cellulose conversion. Palkovits et al. proved that the combination of HPAs and supported Ru catalysts can directly convert cellulose into glycols with a yield of 81% (Palkovits et al.,
phosphotungstic acid catalyst. They used several characterization instruments to characterize the catalyst and found that the modified heteropoly acid was still the Keggin structure (Wu et al.,
Comparison of Different HPA-Based Catalysts
As discussed above, it can be concluded that the Keggin HPA-based catalysts are one of the most common cellulose degradation catalysts. Due to their dual functional properties, the HPA-based catalysts can further promote the oxidation of hydrolysates into valuable compounds. However, their specific surface areas are relatively low, which is not conducive to the catalytic activity. To solve this deficiency, some substituted and supported heteropoly acid catalysts were developed, which are demonstrated to have higher specific surface areas, higher reactivity, and better thermal stability, and are more conducive to the separation because they are commonly used in the heterogeneous systems. It is worth noting that the preparation of these catalysts is complicated and the synthesis cycle is long. In order to further improve the catalytic activity of HPAs, the assembled HPAs and other modified HPA catalysts have been developed. With unique structures, these catalysts exhibit high catalytic performance in cellulose conversion. More importantly, they are all heterogeneous catalysts, providing convenience for the catalyst separation and recycling processes. Therefore, different HPA catalysts have their own characteristics, advantages and disadvantages, and the catalytic upgrading of cellulosic biomass can be effectively enabled with these HPA-based catalysts as long as their properties are properly switched.
Conclusions and Outlook
With the rapid development and utilization of chemical fuels, depolymerization of cellulosic biomass has become one of the ways to provide organic carbon sources. It is reported that cellulose can be converted into a variety of useful platform molecules that can be applied in various fields. In this review, the focus is placed on finding homogeneous and heterogeneous HPA catalysts for cellulose degradation.
HPAs, as a king of efficient, environmentally friendly, and safe catalysts, show high catalytic activity for cellulose degradation. HPA catalysts have higher catalytic activity than conventional solid acid catalysts, which are more conducive to the degradation of cellulose into valuable platform molecules, such as glucose. Meanwhile, due to its unique physical and chemical properties, HPAs can be used in homogeneous and heterogeneous systems. And they can all be reused after separation in the reactor with almost no loss of catalytic activity.
Several methods have been developed to synthesize HPA catalysts. (1) The acidification process coupled with an ether extraction is the most commonly used method, which is mainly used for the synthesis of common HPAs (e.g., H3PW12O40, H3SiW12O40), but its safety is low due to the use of some toxic substances. (2) The ion-exchange method has high safety, but it has the disadvantage of a long production cycle. (3) The impregnation method is simple and safe but suffers the disadvantage of the loss of catalyst activity and limited recycling ability. (4) The sol-gel method can prepare HPA catalysts at low temperatures or mild conditions, which is widely used in the synthesis of HPA-based nanomaterial catalysts. However, this method has the disadvantages of low security and long cycle. Therefore, it is very important and urgent to develop more efficient methods for the preparation of HPA-based catalysts.
As depicted in previous studies, typical Keggin-type HPA catalysts are the most common ones for cellulose degradation, and they can further catalyze the oxidation of the hydrolysates to valuable substances due to their dual functional properties. Then, the supported and substituted HPA catalysts always exist in heterogeneous form. After supporting and substituting disposal, the acid site number, the acid strength, and the specific surface area of the HPA catalysts increase, which improves the catalytic properties of the catalysts. In addition, the assembled HPA catalysts and other modified HPA catalysts show good catalytic performance in cellulose conversion because of their unique structure. Therefore, HPA-based catalysts provide convenience for cellulose degradation and more possibilities for the development of chemical fuels in the future. But it cannot be neglected that some of HPAs have the disadvantages of high catalyst dosage and relatively low catalytic activity with respect to the reaction conversion, product selectivity, and catalyst stability. For example, the selectivity of substituted and supported HPAs toward target products is lower than that of Keggin-type HPAs. Also, the stability of the supported HPAs is lower than that of common HPAs.
Although HPAs-based catalysts in either homogeneous or heterogeneous state have made great progress in the degradation of biomass cellulose, there are still many deficiencies to be improved:
(1) Study on the relationship between the properties of HPA catalysts and the degradation of cellulose to further improve the catalytic activity.
(2) Design of a cleaner, safer, and more effective HPA catalyst with simple preparation methods to promote cellulose degradation.
(3) Development of more new HPA catalysts with special structure, and ensure no or fewer side reactions in the reaction process, with the focus on the improvement of the HPA catalyst disadvantages especially unsatisfactory conversion, selectivity, and stability.
(4) Further understanding the structural characteristics of HPAs, study of the reaction mechanism catalyzed by HPAs, and promotional completion of the target reaction by linking the relationship between them.
(5) Extension of HPA catalysts to other biomass feedstocks, providing more help for the future development of fuels and HPAs in the field of catalysis.
In summary, this review mainly summarizes some examples of the degradation of cellulose by some kinds of HPA catalysts. The HPA catalysts are considered to have great application prospects in the degradation of cellulose and the conversion of other relevant research fields.
Statements
Author contributions
XL and HL initiated the project. XL, HW, CL, ZL, HL, HZ, YL, YS, and SY searched the data and wrote, revised, and completed the manuscript. All authors contributed to the article and approved the submitted version.
Funding
The authors thank the financial support from the National Natural Science Foundation of China (21666008, 21908033, and 21576059), Fok Ying-Tong Education Foundation (161030), Guizhou Science & Technology Foundation ([2018]1037), and Program of Introducing Talents of Discipline to Universities of China (111 Program, D20023).
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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Summary
Keywords
cellulose hydrolysis, heteropoly acid, biomass conversion, green chemistry, sustainable catalysis
Citation
Luo X, Wu H, Li C, Li Z, Li H, Zhang H, Li Y, Su Y and Yang S (2020) Heteropoly Acid-Based Catalysts for Hydrolytic Depolymerization of Cellulosic Biomass. Front. Chem. 8:580146. doi: 10.3389/fchem.2020.580146
Received
04 July 2020
Accepted
17 August 2020
Published
25 September 2020
Volume
8 - 2020
Edited by
Svetlana Ivanova, University of Seville, Spain
Reviewed by
Sara Navarro-Jaén, Université de Lille, France; Fabien Drault, Centrale Lille, France
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© 2020 Luo, Wu, Li, Li, Li, Zhang, Li, Su and Yang.
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*Correspondence: Song Yang jhzx.msm@gmail.comHu Li hli13@gzu.edu.cn
This article was submitted to Green and Sustainable Chemistry, a section of the journal Frontiers in Chemistry
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