Wuhuan
Li
ab,
Xuesong
Tan
*b,
Changlin
Miao
b,
Zhanying
Zhang
c,
Yunxuan
Wang
d,
Arthur J.
Ragauskas
def and
Xinshu
Zhuang
*ab
aSchool of Energy Science and Engineering, University of Science and Technology of China, Hefei 230026, PR China. E-mail: zhuangxs@ms.giec.ac.cn
bGuangzhou Institute of Energy Conversion, Chinese Academy of Sciences, CAS Key Laboratory of Renewable Energy, Guangdong Provincial Key Laboratory of New and Renewable Energy Research and Development, Guangzhou 510640, PR China. E-mail: tanxs@ms.giec.ac.cn
cSchool of Mechanical, Medical and Process Engineering, Faculty of Engineering; Centre for Agriculture and the Bioeconomy, Faculty of Science, Queensland University of Technology, Brisbane, Queensland 4000, Australia
dDepartment of Chemical and Biomolecular Engineering, University of Tennessee-Knoxville, Knoxville, TN, USA
eJoint Institute for Biological Science, Biosciences Division, Oak Ridge National Laboratory, Oak Ridge, TN, USA
fCenter of Renewable Carbon, Department of Forestry, Wildlife, and Fisheries, University of Tennessee Institute of Agriculture, Knoxville, TN, USA
First published on 4th January 2023
This study conducted mild organosolv pretreatment of sugarcane bagasse with acetone/phenoxyethanol/water (APW) solutions to improve sugar production in the subsequent enzymatic hydrolysis step. The Box–Behnken design was used to optimize pretreatment conditions based on lignin removal. Further examination of the data revealed that lignin removal was positively correlated (R2 > 0.95) with the combined severity factor (CSF). Pretreatment under the optimal conditions (125 °C–120 min, 0.17 M H2SO4, liquid–solid ratio of 15) led to 98.1% lignin removal and 74.5% cellulose digestibility compared to a low digestibility of 9.3% with raw sugarcane bagasse (SCB). Moreover, the APW process showed effective fractionation of pine, corn stalk and bamboo, and lignin removal was over 90%. The recovered lignin was characterized by 2D-HSQC NMR and 31P NMR, suggesting that the pretreatment resulted in breakage of β-O-4, total phenolic OH and H-units increased. However, the enzymatic hydrolysis efficiency (EHE) of samples with a lower lignin content (<4%) varied significantly. Correlations between various substrate-related factors of the pretreated SCB and EHE were analyzed to understand this observation. The results showed that the surface area of cellulose, lateral order index, CrI, and specific surface area were the predominant factors for enzymatic hydrolysis rather than lignin properties.
In the last two decades, various pretreatment methods have been developed, including dilute acid, alkali, ionic liquid, organosolv, deep eutectic solvents, steam explosion, liquid hot water, and combined treatment.6–13 However, not all pretreatment methods can effectively fractionate biomass components, especially lignin, to maximize the value of lignocellulose. Of various pretreatments, organosolv pretreatment is attractive as it can fractionate lignocellulose into carbohydrate polymers and lignin with the selection of solvents and pretreatment conditions.14,15
Organic solvents such as alcohols, esters, phenol, and acetone have been employed in the treatment of biomass.16–18 Islam et al. proposed an acidic pentanol–water biphasic system for the pretreatment of lignocellulose (Acacia Confusa wood) at 170 °C with H2SO4 as the aqueous phase, and over 70% of lignin was removed into the organic phase, leaving a solid residue rich in cellulose.14 The mass transfer efficiency of monophasic systems is obviously higher than that of biphasic systems.9 However, the biphasic system can effectively fractionate lignocellulose biomass, as hemicellulose was decomposed and then dissolved in the aqueous phase. Lignin is distributed in the organic phase with cellulose left as the residue.
In order to improve the selectivity for different major components of biomass, several ternary organic solvent systems have been developed. For example, a ternary system of acetone/butanol/ethanol was used to fractionate Salix schwerinii at 200 °C,19 achieving 98.5% of hemicellulose removal and 58.2% delignification, while 53.8% xylose and 12.1% of glucose could be recovered from the liquor after pretreatment. NREL proposed a clean fractionation method using a ternary organosolv system composed of acetone/MIBK/H2O to fractionate corn stover. It was found that 77.2% lignin and 74% hemicellulose from the corn stover could be removed using the acetone/MIBK/H2O solvent system at 120 °C for 40 min while avoiding cross-contamination of biopolymers.15,20 However, lower lignin removal limited its application. Recently, our research group developed a ternary solvent system composed of acetone, phenoxyethanol, and water (APW).9 The APW system has the advantages of monophasic deconstruction and biphasic separation and can achieve effective biomass fractionation. With the APW system, Amorpha was effectively fractionated under the optimal conditions of 130 °C, 70 min, 0.15 M sulfuric acid, and 20 LSR (liquid–solid ratio), achieving 95.6% delignification and 98.39% hemicellulose removal, retaining 80.48% of cellulose in the solid fraction. Nonetheless, lignocellulosic biomass pretreated with APW is not widely studied, and its dynamic characteristics of delignification remain unclear.
This study applied APW pretreatment to fractionate sugarcane bagasse (SCB). The effects of temperature, cooking time, liquid–solid ratio, and sulfuric acid concentration were investigated using the Box–Behnken design (BBD). The correlation of lignin removal with a combined severity factor was studied. Then, the APW pretreatment performance of various lignocellulosic biomass (SCB, corn stalk, pine and bamboo) and the characteristics of isolated lignin were also investigated. Subsequently, the cellulose-rich residue was directly hydrolyzed by cellulase. Finally, the interactions between 9 substrate-related factors and enzymatic hydrolysis efficiency(EHE) were comprehensively characterized through correlation analysis to investigate the predominant factors for enzymatic hydrolysis when the lignin content in the residue is low.
Material | Cellulose/% | Hemicellulose/% | Lignin/% |
---|---|---|---|
Sugarcane bagasse | 40.51 | 23.56 | 22.64 |
Corn stalk | 33.50 | 20.04 | 15.72 |
Pine | 43.42 | 18.32 | 28.55 |
Bamboo | 41.83 | 19.47 | 21.17 |
CSF = log![]() |
All the experiments were repeated three times.
Morphological features of the biomass before and after pretreatment were observed using a field emission SEM (S4800, Hitachi) (FESEM) at an accelerating voltage of 2.0 kV. The untreated and pretreated SCB were sprayed with gold before FESEM analysis.
The correlations between 9 substrate-related factors related to different pretreatment conditions and enzymatic hydrolysis were analyzed through statistical analysis by the correlation analysis method. The 9 substrate-related factors included cellulose content, surface area of cellulose (SAC), specific surface area (SA), crystallinity index (CrI), CrI/cellulose, O/C ratio, lateral order index (LOI), surface lignin content (SL) and lignin content.
The cellulose surface area (SAC) was estimated by staining with Congo Red. The measurement procedure was reported by Sipponen et al.24 The Langmuir maximum absorption capacity (Xmc) was determined by fitting the Langmuir isotherm. SAC was calculated based on the following formula:
The specific surface area (SA) was determined by the Barrett–Emmett–Teller (BET) method.
X-ray diffraction (XRD) (PW3040/60, Philips, Holland) was used to detect cellulose crystallinity. The cellulose crystallinity index (CrI) was evaluated as follows:25
CrI/cellulose was introduced to correlate CrI and cellulose content to analyze the actual changes in cellulose crystallinity.
The surface lignin content of SCB was determined by X-ray photoelectron spectroscopy (XPS, ESCALAB 250Xi) using the following equation:
SL = [5 − 6 × (O/C)]/[1.68 + 3.66 × (O/C)], |
Fourier transform infrared (FTIR) spectroscopic analyses of untreated and pretreated SCB were conducted to reveal changes in the functional groups using a Bruker Tensor 27 FTIR spectrometer. The lateral order index (LOI = A1430 cm−1/A898 cm−1) was applied to evaluate structural changes in cellulose.
The quantitative 2D HSQC NMR and 31P NMR experiments were carried out according to a previous publication.26,27
No. | A: T (min) | B: Tem. (°C) | C: acid conc. (M) | D: LSR | Glucan retention (%) | Xylan removal (%) | Y: Lignin removal (%) |
---|---|---|---|---|---|---|---|
1 | 75 | 105 | 0.175 | 15 | 86.59 | 69.31 | 84.00 |
2 | 120 | 105 | 0.175 | 20 | 75.29 | 72.42 | 89.46 |
3 | 75 | 105 | 0.175 | 15 | 89.15 | 69.64 | 81.98 |
4 | 75 | 80 | 0.3 | 15 | 91.57 | 47.05 | 34.98 |
5 | 75 | 105 | 0.175 | 15 | 88.38 | 69.57 | 83.58 |
6 | 30 | 105 | 0.175 | 20 | 93.03 | 57.33 | 58.51 |
7 | 30 | 130 | 0.175 | 15 | 90.59 | 82.92 | 84.43 |
8 | 75 | 80 | 0.05 | 15 | 90.99 | 6.27 | 11.46 |
9 | 75 | 105 | 0.05 | 10 | 73.06 | 26.19 | 56.55 |
10 | 75 | 130 | 0.3 | 15 | 75.10 | 100.00 | 93.12 |
11 | 75 | 130 | 0.175 | 10 | 82.77 | 92.96 | 94.91 |
12 | 75 | 80 | 0.175 | 20 | 88.61 | 28.78 | 34.50 |
13 | 75 | 130 | 0.05 | 15 | 85.88 | 82.88 | 95.21 |
14 | 75 | 105 | 0.05 | 20 | 90.26 | 48.09 | 48.90 |
15 | 120 | 105 | 0.05 | 15 | 81.07 | 66.37 | 78.51 |
16 | 120 | 80 | 0.175 | 15 | 85.91 | 36.33 | 49.41 |
17 | 75 | 105 | 0.175 | 15 | 92.51 | 68.84 | 84.17 |
18 | 30 | 105 | 0.05 | 15 | 97.67 | 38.10 | 34.08 |
19 | 30 | 80 | 0.175 | 15 | 90.69 | 11.86 | 26.58 |
20 | 30 | 105 | 0.175 | 10 | 88.18 | 59.54 | 67.43 |
21 | 120 | 105 | 0.3 | 15 | 85.44 | 85.22 | 92.68 |
22 | 75 | 105 | 0.3 | 20 | 77.95 | 80.41 | 91.58 |
23 | 75 | 105 | 0.175 | 15 | 91.61 | 66.61 | 87.14 |
24 | 120 | 105 | 0.175 | 10 | 89.93 | 77.31 | 90.66 |
25 | 120 | 130 | 0.175 | 15 | 77.92 | 93.50 | 93.14 |
26 | 75 | 130 | 0.175 | 20 | 82.45 | 100.00 | 95.07 |
27 | 75 | 105 | 0.3 | 10 | 94.05 | 75.82 | 91.84 |
28 | 75 | 80 | 0.175 | 10 | 92.16 | 25.93 | 24.89 |
29 | 30 | 105 | 0.3 | 15 | 84.53 | 69.59 | 81.80 |
As shown in Table S2,† lignin removal was strongly affected by the temperature (P < 0.0001), sulfuric acid concentration (P < 0.0001), and reaction time (P < 0.0001), while the liquid–solid ratio (P = 0.758 > 0.05) had a lower impact. The value of R2 in the model is 0.9575, indicating great agreement between the experimental value and the expected value. Statistical analysis confirmed that the proposed model is appropriate for the proof of data and offers a comprehensive overview of the relationship between variables and responses. The optimal process parameters for APW pretreatment are as follows: liquid–solid ratio of 15:
1, 125 °C, 120 min, and 0.17 M H2SO4 (reaching complete lignin removal) (SCB-1). The actual lignin removal of SCB pretreated under the optimal condition was 98.12% (Table 3), which was close to the quadratic model prediction, indicating that the model obtained by the surface response design was applicable to the prediction of lignin removal. According to the response surface methodology results, the liquid–solid ratio has little impact on lignin removal, so the solid–liquid ratio is selected as 1
:
10 to improve the pretreatment capacity. Based on the response surface regression equation, at a solid–liquid ratio of 1
:
10, the lowest pretreatment temperature was 110 °C (every 5 °C as an interval) with a target of over 90% lignin removal (shown in Fig. 1). The optimal conditions under this limit were 0.15 M acid for 120 min (SCB-2), which predicted a corresponding lignin removal of 91.51%. The actual lignin removal was 99.03%, slightly higher than the predicted value, indicating that the model obtained using the surface response design was appropriate.
![]() | ||
Fig. 1 Contour plots of time vs acid concentration, lignin removal rate under different temperatures (A:100 °C, B:105 °C, C:110 °C) with LSR is 10. |
Experiment | Tem. (°C) | Time (min) | Acid conc. (M) | LSR | CSF | Solid remaining(%) | Cellulose content (%) | Glucan retention(%) | Xylan removal (%) | Lignin content (%) | Lignin removal (%) |
---|---|---|---|---|---|---|---|---|---|---|---|
SCB-1 | 125 | 120 | 0.17 | 15 | 2.52 | 35.33 | 91.68 | 85.59 | 98.15 | 1.23 | 98.12 |
SCB-2 | 110 | 120 | 0.15 | 10 | 1.98 | 41.29 | 79.58 | 81.10 | 91.83 | 0.53 | 99.03 |
SCB-3 | 110 | 110 | 0.10 | 10 | 1.83 | 49.27 | 70.49 | 78.53 | 81.41 | 0.58 | 96.54 |
SCB-4 | 110 | 80 | 0.20 | 10 | 1.87 | 42.10 | 77.97 | 87.87 | 86.99 | 1.99 | 94.94 |
SCB-5 | 110 | 90 | 0.15 | 10 | 1.86 | 48.62 | 70.01 | 84.77 | 81.52 | 3.90 | 91.55 |
To further evaluate the feasibility of pretreatment optimization using CSF, three process parameters with a CSF of around 1.86 for APW pretreatment were tested as shown in Table 3: (1) 110 °C, 110 min, 0.1 M H2SO4 (SCB-3, CSF = 1.83); (2) 110 °C, 80 min, 0.2 M H2SO4 (SCB-4, CSF = 1.87); and (3) 110 °C, 90 min, 0.15 M H2SO4 (SCB-5, CSF = 1.86). The actual lignin removal of SCB treated under these conditions (CSF with values of 1.83, 1.87, and 1.86) was 95.27%, 94.94%, and 91.55%, respectively. This result suggests that CSF = ∼1.86 can be used as an indicator for effective lignin removal in the APW system and is useful in figuring out a relatively mild condition for the fractionation of lignocellulose biomass, allowing a more straightforward experimental design than using BBD.
In addition, the fractionation effect of various lignocellulosic biomass, including sugarcane bagasse, corn stalk, pine and bamboo, pretreated by APW was also studied to investigate the adaptability of the system, as shown in Table 4. The delignification and hemicellulose removal rates of these biomass were both over 90%, lignin retention in residue was less than 7% and cellulose content in the residue was over 85%. It is worth mentioning that this solvent system can reach over 90% lignin removal of pine. Haykir et al. studied the pine pretreatment with PIL–water (4:
1) at 170 °C for 3 h, and only achieved 52% lignin removal.28 Therefore, APW pretreatment showed excellent fractionation effect on different biomass.
Material | Solid remaining/% | Cell./% | Hemi./% | Lign./% | Cellulose retention/% | Hemicellulose removal/% | Delignification/% |
---|---|---|---|---|---|---|---|
ND: not detected. | |||||||
Sugarcane bagasse | 35.33 | 91.68 | 1.23 | 1.45 | 85.59 | 98.15 | 98.12 |
Corn stalk | 29.74 | 87.58 | ND | 0.66 | 68.82 | 100.00 | 98.74 |
Pine | 41.37 | 85.54 | 3.74 | 6.45 | 93.50 | 91.56 | 90.65 |
Bamboo | 28.22 | 92.50 | ND | 2.38 | 68.97 | 100 | 96.83 |
For chemical pretreatment, organic solvents with acid were used, according to Table S3,† chemical pretreatment resulted in a higher delignification rate when compared to the initial concentration in the biomass. Compared to the pretreatment with water/phenoxyethanol,23 adding acetone to water/phenoxyethanol significantly improved delignification from 63.16% to 94.94%. The mixture of 50% ethanol and butylated hydroxytoluene (BHT) was applied to enhance the treatment efficiency of SCB, achieving 45.28% lignin removal at 121 °C.29 Kawamata et. al. employed water/1-buthanol (4.0 mol mol−1) solvent for treatment of SCB at 200 °C and achieved 67% delignification rate.30 Furthermore, 60% pentanol could separate 85% lignin from corn stalk at 160 °C, 60 min.31 Making a comparison with these biphasic solvents or pure solvents, the APW system gave high delignification under mild conditions.
![]() | ||
Fig. 4 Side chain region (δC/δH 54.00–88.00/2.80–5.50) and aromatic region (δC/δH 92.00–147.00/6.10–7.70) in 2D HSQC NMR spectra of MWL (a) and (c) and APWL (b) and (d). |
In the side-chain regions (δC/δH 50–90/2.5–6.0 ppm) of the spectra (Fig. 4a), the xylan backbone at X2 (δC/δH 72.71/3.21 ppm), X3(δC/δH 74.94/3.25 ppm), X4(δC/δH 76.14/3.53 ppm) and C5–H5 in cellulose (Glc5, δC/δH 71.47/3.51 ppm) were indicative of the presence of carbohydrates. However, these signals for polysaccharide cross-peak signals were removed after APW pretreatment, suggesting that the obtained lignin has high purity. As shown in spectra (Fig. 4a and b), the signals of methoxy groups (–OCH3) presented the most prominent signals, implying that these lignin fractions were rich in S- and G-type units. Additionally, the main interunit linkages of MWL were β-O-4 arylethers (A) and β–β resinol (B). Signals corresponding to both β-O-4 and β–β decreased after pretreatment, especially for the β-O-4 linkage which is predominant in MWL but became trace in APWL. β-O-4 linkage is susceptible to breakage under acidic conditions,32 it is speculated that the APW pretreatment facilitated the cleavage of β-O-4. It was found that the Cα–Hα and Cβ–Hβ in β-β (tetrahydrofuran) (B′) with the cross signal at δC/δH 83.57/4.97 ppm and δC/δH 50.49/2.62 ppm, respectively, was detected for MWL and absent for APWL, suggesting that the cleavage of the β–β linkage could take place after APW pretreatment. These results suggest that the proposed APW pretreatment resulted in the cleavage of both C–O bond and C–C bonds.
In the region of aromatic substructures (δC/δH 90–140/6.0–8.0 ppm) of the 2D-NMR spectra (Fig. 4c and d), the correlated peaks of syringyl (S), guaiacyl (G) and p-hydroxypheny (H) can be obviously distinguished. As shown in Fig. 4c, the correlated signals at δC/δH 104.53/6.72 are indicative of the presence of sypringyl(S) unit (S2,6), besides the oxidized S unit (S′2,6) at δC/δH 107.13/7.34. After APW treatment, the signals of main substructure, such as C2,6-H2,6 in syringyl units (S) and the oxidized S unit, were weakened. Interestingly, the H2,6 (δC/δH 129.65/7.16 ppm) correlation of H unit presented a stronger signal in APWL than in WML. Besides, it’s of great importance to note that there is no signal of condensed structure occurred in the APWL even though condensed G2 and S2,6 easily appeared after pretreatment.33 Moreover, given the breakage of β-O-4 linkage and no signal of condensed structure, we hypothesize that the condensation was inhibited by the reaction between solvent and the fractionated lignin during the reaction, but further studies are needed. In addition, the signal of tricin units can only be detected in the spectra of MWL, labeled as T3 and T8 correlation at δC/δH 105.45/7.05, 99.38/6.25, respectively, which was on account of that tricin was easily degraded in acidic organic solvents.23 Additionally, the S/G ratio in lignin was an important implement to evaluate the structural changes during APW pretreatment. The S/G ratio of MWL was 0.59, and that of APWL was 0.13. Previous work has indicated that the decreased S/G ratio of the substrates after the pretreatment was primarily because lignin was depleted in S units and enriched in H units.34 In short, it was found that lignin containing less carbohydrates and enriched in H-units can be obtained after APW pretreatment as compared to that of MWL.
To further determine the changes of different OH groups in lignin before and after APW pretreatment, the quantitative 31P NMR technology was used. The spectra of the lignin fractions were recorded based on the previous methods,27 and the results are listed in Fig. S4 and Table S5.† The content of aliphatic OH was reduced after APW pretreatment as compared with that (8.60 mmol g−1) of MWL, indicating that the aliphatic OH groups in SCB carbohydrate fractions were removed after the pretreatment process, which is in agreement with the 2D-HSQC NMR of the MWL sample (Fig. 4). In addition, the content of S and G-type phenolic hydroxyl groups significantly increased after APW pretreatment, which was ascribed to the cleavage of β-O-4 linkages and free phenolic hydroxyl groups released. Phenolic OH is the main factor affecting the redox activity of lignin because of its strong ability to capture and neutralize free radicals.35 The total phenolic OH content of MWL was 2.41 mmol g−1. In comparison with MWL, APWL exhibited higher total phenolic OH contents, which was calculated to be 3.04 mmol g−1, resulting from the dissociation of β-O-4 ether linkages. In short, the lignin induced by APW pretreatment contained higher total phenolic OH contents and less aliphatic OH compared with MWL.
In our study, after APW pretreatment, with the lignin content being 1.23%, 0.53%, 0.58%, 1.99%, and 3.90% in SCB-1, SCB-2, SCB-3, SCB-4, and SCB-5, the EHE values were 74.52%, 63.67%, 68.62%, 74.15%, and 67.76%, respectively. Therefore, it indicated that the enzymatic hydrolysis efficiency varied greatly even when most of the lignin was removed. Since many substrate-related factors could affect enzymatic hydrolysis efficiency,37,38 we conducted a correlation analysis to understand the properties of substrates that affect enzymatic hydrolysis with 9 participatory hydrolysis-related factors including the cellulose content, surface area of cellulose (SAC), specific surface area (SA), crystallinity index (CrI), CrI/cellulose, O/C ratio, lateral order index (LOI), surface lignin content (SL) and lignin content, as shown in Table.5.
As illustrated in Table 5, the cellulose content of untreated and pretreated SCB varied from 70.01% to 91.68%. FTIR spectra (Fig. S2†) showed that the intensity of the characteristic peaks of cellulose increased significantly after pretreatment under different conditions, such as bands at 898 cm−1 and 1165 cm−1, which were attributed to β-(1–4)-glycosidic bond (C–O–C), and the wide band at 3423 cm−1 which was associated with O–H stretching of the hydrogen bonds of cellulose. However, the cellulose content implicitly correlated with EHE (r = 0.49, p > 0.05). Since the absorbance at 1430 cm−1 and 897 cm−1 are assigned to the crystal structure of cellulose, the absorbance ratio A1430/A897 or lateral order index (LOI) has been used to reflect the cellulose I fraction in the cellulose structure. The higher value of LOI indicates that it contains a higher fraction of cellulose I. The correlation between LOI and EHE was positive (r = 0.94, p < 0.05), indicating that higher cellulose I content is favorable for enzymatic hydrolysis. At the same time, delignification and hemicellulose removal of the APW pretreatment increased the content of cellulose I.39 For SAC, the increase in exposed SAC is supposed to improve EHE due to the effective contact between cellulase and the cellulose surface.24 This study found a significant positive correlation between EHE and SAC (r = 0.98, p < 0.05). Many studies have reported that biomass porosity increased after pretreatment. In contrast, in the present study, the specific surface area (SA) of the treated substrates was lower than that of the raw material, as indicated by BET tests. This can be attributed to the fractionation of the cell wall and the separation of the major biopolymers, leading to the blockage of the fiber cell cavities and pits by the cell wall fragments, subsequently reducing the pore volume.40 It is also worth noting that drying the substrate could lead to a partial collapse of biomass pores. For instance, the pore diameter of native hardwoods decreased considerably due to thermal drying at 200 °C for 4 h.41 To avoid this collapse, organic solvent exchange drying was used in surface area measurements.42 EHE was significantly positively correlated with SA (r = 0.97, p > 0.05). XRD quantified the CrI of pretreated SCB (Fig. S3†), and the results ranged from 54.62% to 61.82%. The correlation between cellulose CrI and EHE was positive (r = 0.92, p < 0.05). It was confirmed from the results that a lower value of CrI has high resistance to enzymatic hydrolysis.39,43 These results show that there is no increase in the trend of enzymatic hydrolysis with a decrease in crystallinity. This effect is probably due to only the relative CrI cannot illustrate the correlation between crystallinity and enzymatic hydrolysis. Since it was observed that cellulose CrI always increases with cellulose content increasing, a parameter (CrI/cellulose value) was adopted to associate cellulose CrI and cellulose content to analyze the actual changes in cellulose crystallinity.44 The CrI/cellulose value of the residue decreased significantly after pretreatment. This observation could be ascribed to the fact that a stronger pretreatment condition facilitates the degradation of amorphous cellulose, leaving cellulose with a more crystalline region. However, the correlation between CrI/cellulose and EHE was indefinite (r = 0.23, p > 0.05).
EHE (%) | Cellulose content (%) | LOI | SAC (m2 g−1) | SA (m2 g−1) | CrI | CrI/cellulose value | Lignin content (%) | O/C | SL | |
---|---|---|---|---|---|---|---|---|---|---|
SCB | 9.25 | 40.51 | 1.24 | 151.81 | 6.139 | 41.39 | 1.02 | 22.64 | 0.32 | 1.08 |
SCB-1 | 74.52 | 91.68 | 1.04 | 220.01 | 5.79 | 66.7 | 0.73 | 1.23 | 0.72 | 0.16 |
SCB-2 | 63.67 | 79.58 | 0.98 | 174.07 | 3.63 | 54.62 | 0.69 | 0.53 | 0.58 | 0.40 |
SCB-3 | 68.62 | 70.49 | 1.01 | 192.27 | 4.16 | 56.97 | 0.81 | 0.58 | 1.69 | 0.40 |
SCB-4 | 74.15 | 77.97 | 1.07 | 213.54 | 5.94 | 61.82 | 0.79 | 1.99 | 0.54 | 0.48 |
SCB-5 | 67.76 | 70.01 | 1.01 | 181.29 | 4.63 | 58.18 | 0.83 | 3.90 | 0.59 | 0.38 |
![]() | ||
Fig. 5 Metrix of correlation coefficients among all factors. Larger redder (bluer) plots display strong positive (negative) correlations. |
The results showed that the correlation between EHE and the residual lignin content was indefinite (r = 0.12, p > 0.05). After different runs of APW pretreatment, the lignin content ranged from 0.53% to 3.90% (Table 3). Previous studies found that the residual lignin on the surface of the substrate had more impact on cellulose conversion than the bulk lignin.37 Mooney et al. reported that the decreased surface distribution of lignin on biomass materials positively influenced the enzymatic hydrolysis of woody biomass.48 Therefore, it was imperative to investigate the surface compositions and lignin coverage of pretreated SCB and their relationship with cellulose conversion. The surface carbon (C1s) and oxygen (O1s) of pretreated SCB were determined by XPS, and then the surface-lignin content (SL) was identified by the O/C ratio. The theoretical O/C ratios of lignin and cellulose were 0.33 and 0.83, respectively.38,49 Therefore, a higher O/C ratio indicated that lignin was less distributed than cellulose on the surface. However, the O/C ratio exhibited a poor correlation with EHE (r = −0.086, p > 0.05), while the correlation between EHE and SL was also indefinite (r = −0.34, p > 0.05). These results suggest that the surface coverage of lignin on SCB was not an essential factor affecting fermentable sugar yield when the lignin content was low in the substrate.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d2gc04404h |
This journal is © The Royal Society of Chemistry 2023 |