Abstract
Sorghum stem, an agricultural solid waste discarded in large amounts, was effectively fractionated into its chemical components to achieve value-added utilization. The stem was successively extracted using water at 80 °C and alkali aqueous solutions with increased concentrations (1% NaOH; 60% ethanol containing 1% NaOH, 3% NaOH, 5% NaOH, and 8% NaOH) at 50 °C, which yielded hemicellulose and lignin fractions as well as a cellulose-rich residue. The hemicellulose and lignin fractions were characterized in terms of yield, sugar components, alkaline nitrobenzene, and oxidation analysis. In addition, the molecular weights were determined by gel permeation chromatography and the structures were further identified by Fourier transform infrared spectroscopy and nuclear magnetic resonance spectroscopy. The results indicated that the hemicelluloses yielded from the alkali aqueous solution had a linear xylan structure. The alkali lignin had a typical guaiacyl/syringyl/p-hydroxypheny structure and low amounts of contaminating sugars (less than 2%). A high concentration of alkali aqueous solution led to the release of lignin with a large molecular weight, whereas increasing the alkali concentration resulted in lignin degradation. The residual stem after the successive extractions was rich in cellulose and had a low crystallinity. In sum, mild successive extractions are a promising way to fractionate sorghum stem waste for further conversion.
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Successive Fractionations of Hemicelluloses and Lignin from Sorghum Stem by Sodium Hydroxide Aqueous Solutions with Increased Concentrations
Ji-Dong Xu, Ming-Fei Li,* and Run-Cang Sun *
Sorghum stem, an agricultural solid waste discarded in large amounts, was effectively fractionated into its chemical components to achieve value-added utilization. The stem was successively extracted using water at 80 °C and alkali aqueous solutions with increased concentrations (1% NaOH; 60% ethanol containing 1% NaOH, 3% NaOH, 5% NaOH, and 8% NaOH) at 50 °C, which yielded hemicellulose and lignin fractions as well as a cellulose-rich residue. The hemicellulose and lignin fractions were characterized in terms of yield, sugar components, alkaline nitrobenzene, and oxidation analysis. In addition, the molecular weights were determined by gel permeation chromatography and the structures were further identified by Fourier transform infrared spectroscopy and nuclear magnetic resonance spectroscopy. The results indicated that the hemicelluloses yielded from the alkali aqueous solution had a linear xylan structure. The alkali lignin had a typical guaiacyl/syringyl/p-hydroxypheny structure and low amounts of contaminating sugars (less than 2%). A high concentration of alkali aqueous solution led to the release of lignin with a large molecular weight, whereas increasing the alkali concentration resulted in lignin degradation. The residual stem after the successive extractions was rich in cellulose and had a low crystallinity. In sum, mild successive extractions are a promising way to fractionate sorghum stem waste for further conversion.
Keywords: Agricultural solid waste; Extraction; Hemicelluloses; Lignin; Sodium hydroxide; Sorghum stem
Contact information: Beijing Key Laboratory of Lignocellulosic Chemistry, Beijing Forestry University, Beijing 100083, China; *Corresponding authors: limingfei@bjfu.edu.cn; rcsun3@bjfu.edu.cn
INTRODUCTION
Sorghum is a food and energy crop that has a high photosynthetic efficiency and can be planted in drought areas. Among the cereal crops produced globally, sorghum is the fifth most abundant, and its annual production is around 58 million metric tons (Rooney et al.2007). The starches in the grain are good feedstocks for fermentation by amylase. The stem is an agricultural solid waste discarded in large amounts, and it is composed of cellulose, hemicelluloses, and lignin (She et al. 2010). This agricultural waste is a good feedstock for conversion into energy, chemicals, and materials. The cellulose in sorghum bagasse is mainly used for the production of paper (Belayachi and Delmas 1997). Recently, bioethanol and other chemicals such as butanol and acetone have been produced using sorghum bagasse as the feedstock (Jafari et al. 2016; Yu et al. 2016; Banerji et al. 2017).
In contrast to the extensive research on the production of energy from sorghum bagasse, relatively less attention has been paid to the isolation of hemicelluloses and lignin from the feedstock. Hemicelluloses are macromolecules composed of approximately 70-200 structural monomers (mainly D-mannose, D-xylose, D-glucose, L-arabinose, D-galactose, and 4-O-methyl-α-D-glucuronic acid, depending on the species) (Scheller and Ulvskov 2010).
Hemicelluloses have wide applications in chemicals, foods, and pharmaceuticals (Peng and She 2014). Lignin is a natural aromatic polymer consisting of phenylpropanoid units linked by aryl–ether, alkyl–ether, and carbon–carbon covalent bonds into a cross-linked polymer network, in which guaiacyl- (G), syringyl- (S), and p-hydroxyphenyl (H) are the main monomers primarily produced from the dehydrogenative radical polymerization (Dashtban et al. 2009). The composition of lignin varies between species and vascular plants. Lignin is a waste stream in most pulp mills and biorefinery processes, and it is usually burned to generate heat. However, it is a good feedstock for the production of alternative fuels, renewable chemicals, value added materials, and platform compounds ( Upton and Kasko 2016; Wang et al. 2016; Chen and Wan 2017).
In the plant cell wall, hemicelluloses are covalently linked with lignin and form hydrogen bonds with cellulose, which is a major barrier to valorization. Many approaches, including physical, chemical, physico-chemical, and biological methods, have been developed to treat lignocelluloses to separate their chemical components, in which bioethanol is the major target product (Mutschlechner et al. 2015; Narron et al. 2016; Rabemanolontsoa and Saka 2016; Chng et al.2017). Of these methods, chemical pretreatment is a promising process to achieve industrialization due to its efficiency. Organic solvent pretreatment separates cellulose with a high-purity and minor degradation, as well as its ability to produce lignin with superior properties and convertible hemicelluloses degraded products such as furfural and xylitol. However, the organic solvents used are easy to burn, and the recovery cost of the organic solvents is relatively high (Zhang et al. 2016). The hydrothermal pretreatment is usually operated at a relatively high temperature in a complicated equipment, producing degraded hemicelluloses, as well as a series of inhibitor products such as furfural, phenolic compounds (Gabhane et al. 2014; Rabemanolontsoa and Saka 2016; Shen et al. 2016). The alkali method has outstanding delignification capacity and hemicellulose removal because it causes lignocellulose to swell. Sodium, potassium, calcium, and ammonium hydroxides are commonly used for pretreatment; sodium hydroxide is preferred due to its safety, cost, and reusability. NaOH pretreatment at various temperatures (15 °C, 25 °C, 60 °C, and 121 °C) has been examined by many researchers (Zhao et al. 2008; Park and Kim 2012; Bali et al. 2015; Gabhane et al. 2015), but the major focus of these studies is the production of digestible cellulose for bioethanol. The extraction of hemicelluloses and lignin using NaOH and an appropriate method to achieve effective utilization is worth exploring. Because the swelling capacity of NaOH increases with increased concentration, successive extractions using NaOH aqueous solutions with increased concentrations would yield dissolved fractions having distinct properties; thus it will provide useful feedstock for application.
In the present study, sorghum stem was subjected to successive extractions using water and alkali aqueous solutions with increased concentrations at low temperatures, yielding hemicellulose and lignin fractions and a cellulose-rich residue after a further purification step. The hemicellulose and lignin fractions were characterized in terms of yield, sugar components, alkaline nitrobenzene oxidation analysis, and molecular weights. The structures were further identified by Fourier transform infrared (FTIR) spectroscopy and nuclear magnetic resonance (NMR) spectroscopy. The residual stem was also analyzed chemically and structurally. This study provides comprehensive knowledge on the chemical composition and structure of sorghum stem after a mild separation process, which is meaningful for the valorization of this agricultural waste.
EXPERIMENTAL
Material
The sweet sorghum stems were collected from a firm in Yangling, Shaanxi province, China. They were ground and dried at 60 °C for 16 h. The samples sized at 20- to 60-mesh were extracted with toluene-ethanol (2:1, v/v) for 6 h in a Soxhlet apparatus to remove wax. The de-waxed samples were the raw material for the experiment. The samples contained 42.3% cellulose, 21.8% hemicelluloses, and 18.0% lignin (Sun et al. 2013a), determined according to the procedure proposed by the National Renewable Energy Laboratory.
Fig. 1. Scheme for the fractionation of hemicelluloses and lignin from sweet sorghum stem
The Successive Extraction Process
The procedure for the successive extractions of lignin and hemicelluloses from sweet sorghum stems is illustrated in Fig. 1. The de-waxed sorghum stem was extracted with water at 80 °C for 3 h in a solid-to-liquor ratio of 1:20 (g/mL) and then filtered in a Buchner funnel. The filtrate was concentrated and poured into 3 volumes of 95% ethanol. The pellet was washed with 70% ethanol and then air-dried to obtain water soluble hemicelluloses (H1). The filtrate was evaporated, concentrated, and then precipitated with acid water (pH 1.5 to 2.0, adjusted with HCl). Next, the precipitate was washed with acid water and freeze-dried to obtain water soluble lignin (sample L1). The residue obtained from the water extraction was successively treated with 1% NaOH, 60% ethanol containing 1% NaOH, 3% NaOH, 5% NaOH, and 8% NaOH at 50 °C for 3 h in each step. The filtrate in each step was poured into 3 volumes of 95% ethanol for the extraction of hemicelluloses (H2, H3, H4, H5, and H6), and the supernatants were neutralized with 6 M HCl to isolate the lignin (L2, L3, L4, L5, and L6) according to the method above. The experiments were conducted in triplicate, and the average values are given.
Characterization of Hemicelluloses, Lignin, and Residual Stem
The chemical component (cellulose, hemicelluloses, and lignin) analysis of the stem before and after the treatments was conducted according to the National Renewable Energy Laboratory (NREL) standard procedure (Sluiter et al. 2008). Hydrolysis of the stem was achieved using 72% H2SO4 for 60 min at 30 °C followed by a further hydrolysis at 121 °C for 1 h after dilution to 4% H2SO4. The neutral sugar compositions of the hemicellulose and lignin fractions were analyzed by hydrolysis of the specimen with 6% H2SO4 for 2.5 h at 100 °C. The sugars released were characterized by a high-performance anion exchange chromatography (HPAEC) system (Dionex ISC 3000, Sunnyvale, CA, USA) with an ampere detector, an AS50 auto-sample, a Carbopac PA-20 column (4 × 250 mm), and a PA-20 guard column (3 × 30 mm), according to a previous report (Bian et al. 2010). Alkaline nitrobenzene oxidation and the liberated phenolic acids and aldehydes were analyzed by high-performance liquid chromatography (HPLC) following a previously reported procedure (Xu et al. 2006). The molecular-average weights of the hemicellulose fractions were determined by gel permeation chromatograph (GPC) with a differential refractive index detector using a PL aquagel-OH 50 column (300 mm×7.7 mm, Polymer Laboratories Ltd., Shropshire, UK). The data were calibrated with standard PL pullulan polysaccharides with peak average molecular weights of 783, 12200, 100000, and 1600000 (Polymer Laboratories Ltd.). The eluate was 0.02 M NaCl in 0.005 M sodium phosphate buffer (pH 7.5) with a flow rate of 0.5 mL/min. The molecular weights of the lignin samples were determined by the same system on a PL-gel 10 μm mixed-B 7.5 mm i.d. column, calibrated with polystyrene standards with molecular weights of 1320, 9200, 66000, and 435500, (Polymer Laboratories Ltd.). The column was eluted with tetrahydrofuran at a flow rate of 1.0 mL/min.
FTIR spectra of the samples were collected on a Bruker spectrophotometer (Ettlingen, German) in the range of 4000 to 400 cm -1 with a resolution of 4 cm-1 after preparing a KBr disk containing 1% ground samples. The solution-state 1H and 13C NMR spectra of the hemicelluloses and lignin were recorded on a Bruker AVIII 400 MHz spectrometer at 25 °C after dissolving the samples in DMSO-d6 using a previously described procedure (Xu et al. 2008; Wen et al. 2013). A cross polarization/magic angle spinning (CP/MAS) 13C NMR spectrum of the residual stem was acquired on the same NMR spectrometer with a 4 mm magic angle spinning probe. Thermogravimetric (TGA) and differential thermal analysis (DTA) curves of the hemicelluloses were recorded by a thermogravimetric analyzer (SDT Q600, TA Instruments, Leatherhead, UK). A total of 10 mg of the sample was placed in a crucible, and nitrogen was flowed at 100 mL/min during the determination. The sample was heated from 30 °C to 550 °C at a heating rate of 10 °C/min. X-ray diffractograms were recorded by an X-ray diffract meter (XRD-6000, Shimadzu, Kyoto, Japan) with a scanning speed of 5°/min after placing the residual stem in an aluminum holder. All experiments were conducted in triplicate, and the average values are reported.
RESULTS AND DISCUSSION
Extraction Yield of Hemicelluloses and Lignin
The successive extractions with increased alkali concentrations are a promising process to fractionate lignocellulose as well as to obtain hemicellulose specimens with different characteristics and lignin samples with distinct properties. The yields (based on the initial dry sweet sorghum stem) of the hemicellulose and lignin fractions obtained in the present study are given in Tables 1 and 2. The successive extractions of the de-waxed sweet sorghum stem with water at 80 °C for 3 h with 1% NaOH, 60% ethanol containing 1% NaOH, 3% NaOH, 5% NaOH, and 8% NaOH at 50 °C for 3 h yielded 2.0%, 2.3%, 1.3%, 4.0%, 3.9%, and 1.2% hemicelluloses, respectively, together with 0.4%, 1.8%, 2.1%, 0.9%, 0.8%, and 0.8% lignin. The highest yield of hemicelluloses was obtained at the extraction with 3% NaOH solution. Altogether, the yields of the released hemicelluloses and lignin were 14.7% and 6.8%, corresponding to 67.4% and 37.7% of the original hemicelluloses and lignin in the sorghum stem, respectively. Overall, the successive process removed a large proportion of hemicelluloses from the lignocellulose. However, the extraction with water released only small amounts of lignin. The application of alkali caused the lignocellulose to swell and cleaved ester bonds between hydroxycinnamic acids and lignin/hemicelluloses, as well as the α-benzyl ether linkages between lignin and hemicelluloses (Sun et al.2000). The addition of ethanol promoted the extraction of lignin from the lignocelluloses due to the good solubility of the alkaline ethanol aqueous solution.
Structural Characterization of Hemicelluloses
Characterization of the structure of the extracted samples was conductive to the further applications in industry. The hemicellulose samples were subjected to analyses of sugars, alkaline nitrobenzene oxidation products, and molecular weights (Table 1). For H1, glucose was the major sugar generated from starch, which is in agreement with a previous report (Peng et al. 2011). This was attributed to the dissolution of the non-crystalline and hydrophilic starch in hot water. H2 and H3 also exhibited a high glucose content. In H4, H5, and H6, the predominance of xylose together with glucose suggested that these fractions consisted mainly of xylan. In addition, the mass ratio of arabinose to xylose, which is an indicative of the degree of branching, showed a decreasing trend, suggesting that a high concentration of alkali resulted in the release of hemicelluloses with a more liner structure, supporting the previous extractions of hemicelluloses with increased concentrations of KOH (Sun et al.2013b). Lignin is attached to hemicelluloses in the plant cell wall through various linkages. To verify the associated lignin in the hemicellulose fractions, these samples were analyzed using the alkaline nitrobenzene oxidation method to identify the degraded products. The total yields of the products were not higher than 2% and generally decreased from H1 to H6, indicating that the linkages between lignin and hemicelluloses were effectively cleaved. The weight average molecular weight (Mw), number average molecular weight (Mn), and polydispersity index (Mw/Mn) of the samples were calculated. The data were comparable to results reported on hemicelluloses extracted with KOH solution (Mw 22750 to 65290 g/mol) (Sun et al. 2013b).
Table 1. Yield, Sugar Analysis, Alkaline Nitrobenzene Oxidation Products, and Molecular Weight of the Hemicellulose Fractions and the Residual Sorghum Stem a
a The standard errors for yield, sugars, phenolic acids and aldehyde, Mw and Mn were less than 2.2%, 3.5%, 8.2%, 4.5% and 5.6%, respectively.
b GA, glucuronic acid.
The FTIR spectra of the hemicellulose fractions are presented in Fig. 2. The band at 3414 cm-1 is related to an OH group, and the peak at 2920 cm-1 represents CH2 and CH3. H1 revealed a more distinct spectrum than the other fractions. The signal at 1746 cm-1 is due to acetyl and uronic ester groups, and the small signal at 915 cm-1 is due to the α-glycosidic linkages between the sugar units (Huang and Zhang 2009; Li et al. 2011). This result suggested that this fraction contained starch, which is expected due to the higher amount of glucose. A very small signal at 1510 cm-1 indicated the bound lignin in the fraction. For the other fractions, the typical signal for hemicelluloses was observed at 1036 cm-1, corresponding to the glycoside bond stretching (C-O-C) from xylan. The absorption at 895 cm-1 is ascribed to β-glycoside linkages between the sugar units. The signal at 1621 cm-1 is due to the absorbed water in the hemicellulose fractions. The bands due to C–H vibrations of polysaccharides were observed at 1467 and 1380 cm-1.
Table 2. Yield, Sugar Analysis, Alkaline Nitrobenzene Oxidation Products, and Molecular Weight of the Lignin Fractions a
a The standard errors for yield, sugars, phenolic acids and aldehyde, Mw and Mn were less than 2.4%, 3.4%, 8.3%, 4.7%, and 5.2%, respectively.
b based on the total oxidated products.
To investigate the structure of the hemicelluloses in depth, the hemicellulose fraction H6 was further studied with 1H and 13 C NMR after being dissolved in DMSO-d6 (Fig. 3). The signal assignment was conducted according to published data on xylan (Teleman et al.2000). In the 1H NMR spectrum, the signal for β-anomeric protons was observed at 4.4 to 4.6 ppm. The signals at 4.30 (C1H), 3.21 (C2H), 3.57 (C3H), and 3.78 (C4H) ppm were assigned to (1→4) linked β-D-xylan, whereas the signals at 3.35 and 4.10 ppm were due to axial C5-H and equatorial C5-H, respectively. In the 13C NMR spectrum, the strong signals for 1,4-linked β-D-xylan units were observed at 102.2 (C1), 73.2 (C2), 74.4 (C3), 76.6 (C4), and 63.4 ppm (C5).
Fig. 2. FTIR spectra of extracted hemicellulose fractions (a: H1, H2, and H3; b:H4, H5 and H6)
Fig. 3. 1H (a) and 13CNMR (b) spectra of the hemicellulose fraction H6
The thermal behaviors of the extracted hemicellulose samples H2, H4, and H6 were compared using thermogravimetric analysis; the TGA and DTA curves are presented in Fig. 4. The degradation of the hemicelluloses was divided into three stages, i.e., slow (less than 220 °C), rapid (220 to 340 °C), and residual (higher than 340 °C). In the slow stage, the total weight loss was less than 10%, which was mainly due to the loss of absorbed water (at around 100 °C) and pyrolysis of some hemicelluloses with low molecular weights. In the rapid stage, the maximum degradation rates of weight loss were observed at around 270 °C. After this stage, the degradation slowed, and the residual weights of the sample were 42.1%, 34.8%, and 34.9% for H2, H4, and H6, respectively. The residues produced during this stage were mainly due to the pyrolysis of hemicelluloses and the formation of carbonaceous materials under a nitrogen atmosphere (Kirubakaran et al. 2009). In the DTA curves, the thermal degradation of the samples was an exothermal process. In the second stage, all samples exhibited large positive peaks due to rapid degradation. Unlike H2 and H6, H4 had a negative peak at around 220 °C, probably due to its distinct structure.
Fig. 4. TGA/DTA curves of hemicellulose fractions
Structure Characterization of the Lignin Fractions
Because there is a lignin-carbohydrate complex in lignocellulose, the isolated lignin usually contains sugars. Therefore, the lignin fractions were submitted to sugar analysis, and the results are shown in Table 2. The bound sugars included glucose (9.04%) followed by arabinose (0.76%) in L1 and galacturonic acid (0.78%) and disaccharides (0.34%) in L2. The fractions L3, L4, L5, and L6 contained minor amounts of xylose and other mono-saccharides. The data indicated that the lignin had heterogeneous linkages bound to hemicelluloses. Overall, the content of the contaminated sugars was less than 2% for the fractions from L2 to L6, indicating that alkali extraction can produce lignin with a high purity. This result was similar to the case of the extraction of lignin from softwood with 1% NaOH aqueous solutions at 100 °C, in which the lignin obtained contained less than 4% sugars (Xue et al. 2012). The lignin samples were subjected to alkaline nitrobenzene oxidation, and the degraded products were identified. The major products for the lignin samples were vanillin and syringaldehyde for L1 and L2 and p-hydroxybenzoic acid and syringaldehyde for L3, L4, L5, and L6. The presence of high amounts of syringaldehyde and p-hydroxybenzoic acid indicated that the six lignin samples were GSH types. Clearly, L1, L2, and L3 were rich in S units, whereas L4, L5, and L6 had abundant amounts of H units. Minor amounts of p-coumaric and ferulic acids were observed in L1, L2, and L3, supported by the observation that the two hydroxycinnamic acids are strongly bound to lignin in the samples. With increasing alkali concentration, the mass average molecular weight of the lignin first increased from 1270 g/mol in L1 to 2440 g/mol in L4 and then decreased to 1650 g/mol in L6. This result suggested that the alkali solution with a high concentration promoted the release of lignin with a large molecule, while more drastic alkali caused lignin degradation.
Fig. 5. FTIR spectra of extracted lignin fractions (a: L1, L2 and L3; b: L4, L5 and L6)
Fig. 6. 1H (a) and 13C NMR (b) spectra of the lignin fraction L6
The FTIR spectra of the isolated lignin fractions are presented in Fig. 5. A broad brand at around 3400 cm-1 was due to the -OH groups in the phenolic and aliphatic structures. The signals at 2920 and 2855 cm-1 were assigned to C-H stretching in CH3 and CH2. The main signals of lignin were detected in the range of 1880 to 820 cm-1. The signals at 1740 to 1680 cm-1 are related to C=O stretching in unconjugated ketone, carbonyl, and ester groups, while those at 1670 to 1640 cm-1 correspond to C=O stretching in conjugated p-substituted aryl ketones. Typical signals for aromatic skeleton vibrations were found at 1590, 1508, and 1458 cm-1. The absorption at 1470 to 1450 cm-1 is related to C-H deformation, and those at 1370 to 1350 cm-1 are due to aliphatic C-H stretching in CH3 (not -OCH3) and phenolic –OH. The band at 1287 cm-1 is due to the C-H stretching of G units. The absorption at 1230 to 1210 cm-1 is related to C-C plus C-O plus C=O stretching. The signal at 1191 cm-1 is typical for H, G, and S units of lignin. The signals at 1120 to 1115 cm-1 and 1044 cm-1 are related to C-H in plane deformation. The peak at around 840 cm-1 indicated the p-substituted phenolic group. The intensity of the signal at 1738 cm-1 in L1 was relatively strong, suggesting C=O stretching in unconjugated ketones and carbonyl groups in lignin (Yan et al. 2009). The signal was weaker from L2 to L6, which can be attributed to the cleavage of the linkages in following alkali extraction processes.
The NMR spectra of the lignin fraction L6 obtained by extraction with 8% NaOH at 50 °C for 3 h are presented in Fig. 6. In the 1H NMR spectrum, typical resonances for lignin were observed. The signals at 6.7 to 6.8 and 7.0 ppm are due to aromatic protons in S and G units in lignin (Faix 1991; An et al. 2017). The presence of H units, Cα=O groups, and hydroxycinnamic acids in the lignin fraction was confirmed by the signals at 7.2 and 7.5 ppm (Seca et al. 2000). Hβ in β-O-4 exhibits a signal at 4.8 ppm. The methoxyl proton (–OCH3) exhibits a sharp signal at 3.7 ppm. The signal at 3.4 ppm is due to the protons in water dissolved in DMSO, and the strong signals at 2.5 ppm correspond to protons in DMSO. Methyl and methylene in saturated aliphatic side chains give signals at 0.8 to 1.2 ppm. With respect to the 13C NMR spectrum, signals at 57 to 103 ppm have relatively low intensity (Xu et al. 2008), revealing that the lignin obtained had a low content of contaminated sugars, which is in agreement with the aforementioned sugar analysis. Aromatic signals of lignin were observed in the range of 104 to 168 ppm. The S units exhibit signals at 151.8 (C-3/C-5, S etherified), 146.7 (C-3/C-5, S non-etherified), 137.7 (C-4, S etherified), 133.9 (C-1, S etherified), and 104.7 and 104.1 ppm (C-2/C-6, S non-etherified). The signals at 149.0 (C-3, G etherified), 146.9 (C-4, G etherified), 145.0 (C-4, G non-etherified), 133.9 (C-1, G etherified), 119.0 (C-6, G), and 110.8 ppm (C-2, G) are related to the G units. The signals for H units were observed at 129.2 ppm (C-2/C-6, H). The above results indicated that the lignin fraction had a GSH structure. More intense signals were observed at 151.8 ppm than at 146.9 ppm, implying that S units were more involved in ether linkages than G units. In addition, small signals for etherified ferulic acid were found at 122.5 ppm (C-6, etherified), and those for esterified p-coumaric acid at 115.0 ppm (C-3/C-5). These findings were in accordance with the results of alkaline nitrobenzene oxidation of the sample. β-O-aryl ether linkages of the sample was observed at 85.6, 72.8, and 60.4 ppm, corresponding to C-β, C-α, and C-γ in β-O-4, respectively. The intense signals of resonance indicate that the extraction with strong alkali did not break the β-aryl ether linkages of lignin to a significant extent. The signal at 55.6 ppm arises from –OCH3. The signals at 14-29 ppm are related to γ-methyl and α- and β-methylene groups inside chains of lignin.
From the analysis above, the hemicelluloses and lignin extracted showed typical structures, which can be used in many fields. The application of hemicelluloses includes the possibilities such as films, hydrogels, additives for food, and fillers for drug. Lignin may be used for the preparation of dispersants, polyurethane foams, epoxy resins, and antioxidants, etc.
Fig. 7. Structure characterization of the residue after the successive extractions. (a) FTIR spectrum, (b) CP/MAS 13C NMR spectrum, and (c) X-ray diffractogram
Analysis of the Residue
After the successive extractions with water and alkali solutions, the chemical components of the residual sorghum stem changed. Chemical component analysis showed that the residue had a high proportion of cellulose (73.0%) and lower contents of hemicelluloses (15.2%) and lignin (11.0%). The residue produced a very low yield of oxidized products during the alkaline nitrobenzene oxidation, supporting the low content of lignin (Table 1). The structure of the residue was characterized by FTIR, NMR, and X-ray diffraction (Fig. 7). In the FTIR spectrum, the signals corresponding to lignin at 1597, 1510, and 1420 cm-1 were rather weak, indicating effective lignin removal. Strong signals for β-glycoside linkages between sugar units were observed at 897 cm-1. The disappearance of the signal at 1740 cm-1 indicated the removal of acetyl groups after alkali treatments. In the CP/MAS 13C NMR spectrum, the signal at 106 ppm was assigned to the C-1 of cellulose and xylan (from hemicelluloses). The resonances at 65 and 89 ppm are due to the C-6 and C-4 of crystalline cellulose, respectively. The overlapped intense peaks at 73 to 75 ppm result from the C-2, C-3, and C-5 of cellulose and xylan. The signal at 62 ppm and the resonance at 84 ppm were related to the C-6 and C-4 of mixed amorphous cellulose together with xylan. X-ray analysis of the residue indicated that it was a mixture of crystal cellulose and amorphous compounds. The calculated crystallinity index was 23.8%, revealing the low crystallinity of the sample. Residue with a relatively low crystallinity index is considered a promising feedstock for further conversion to bioethanol (Li et al. 2010; Nitsos et al.2013) .
CONCLUSIONS
- Successive extractions with water and NaOH aqueous solutions with increased concentrations enabled the effective removal of hemicelluloses (67.4%) and lignin (37.7 %) from sorghum stem at relatively low temperatures.
- The hemicelluloses obtained from the alkali aqueous solution showed a linear xylan structure, had medium molecular weights (Mw 31700 to 217,000 g/mol), and had minor amounts of bound lignin as evidenced by the low alkaline nitrobenzene oxidation products (less than 2%).
- The lignin obtained from the alkali solution extractions showed a typical GSH structure and had low amounts of contaminated sugars (less than 2%). The alkali solution with a high concentration led to the release of lignin with a large molecule, while more drastic alkali resulted in the degradation of lignin.
- The residual stem after the successive extraction was rich in cellulose (73.0%) and had less hemicelluloses and lignin and a low crystallinity, making it an ideal feedstock for further conversion into biofuels.
ACKNOWLEDGMENTS
This work was supported by National Natural Science Foundation of China for a Key Project (31430092), Beijing Key Lab Project (Z161100005016041) and the Fundamental Research Funds for the Central Universities (2015ZCQ-CL-02).
REFERENCES CITED
An, L., Wang, G., Jia, H., Liu, C., Sui, W., and Si, C. (2017). “Fractionation of enzymatic hydrolysis lignin by sequential extraction for enhancing antioxidant performance,” Int. J. Biol. Macromol. 99, 674-681. DO1: 10.1016/j.ijbiomac.2017.03.015
Bali, G., Meng, X. Z., Deneff, J. I., Sun, Q. N., and Ragauskas, A. J. (2015). “The effect of alkaline pretreatment methods on cellulose structure and accessibility,” Chemsuschem 8(2), 275-279. DOI: 10.1002/cssc.201402752
Banerji, A., Kishore, V., and Balakrishnan, M. (2017). “A comparison of pretreatments on release of sugars from sweet sorghum bagasse for bioethanol production,” Int. J. Green Energy 14(6), 522-527. DOI: 10.1080/15435075.2014.888658
Belayachi, L., and Delmas, M. (1997). “Sweet sorghum bagasse: A raw material for the production of chemical paper pulp: Effect of depithing,” Ind. Crop. Prod. 6(3), 229-232. DOI: 10.1016/S0926-6690(97)00012-5
Bian, J., Peng, F., Peng, P., Xu, F., and Sun, R. C. (2010). “Isolation and fractionation of hemicelluloses by graded ethanol precipitation from Caragana korshinskii,” Carbohydr. Res. 345(6), 802-809. DOI: 10.1016/j.carres.2010.01.014
Chen, Z., and Wan, C. (2017). “Biological valorization strategies for converting lignin into fuels and chemicals,” Renew. Sust. Energ. Rev.73, 610-621. DOI: 10.1016/j.rser.2017.01.166
Chng, L. M., Lee, K. T., and Chan, D. J. C. (2017). “Synergistic effect of pretreatment and fermentation process on carbohydrate-rich Scenedesmus dimorphus for bioethanol production,” Energ. Convers. Manage. 141, 410-419. DOI: 10.1016/j.enconman.2016.10.026
Dashtban, M., Schraft, H., and Qin, W. S. (2009). “Fungal bioconversion of lignocellulosic residues: Opportunities & perspectives,” Int. J. Biol. Sci. 5(6), 578-595. DOI: 10.7150/ijbs.5.578
Faix, O. (1991). “Classification of lignins from different botanical origins by FT-IR spectroscopy,” Holzforschung 45(s1), 21-27. DOI: 10.1515/hfsg.1991.45.s1.21
Gabhane, J., William, S., Gadhe, A., Rath, R., Vaidya, A. N., and Wate, S. (2014). “Pretreatment of banana agricultural waste for bio-ethanol production: Individual and interactive effects of acid and alkali pretreatments with autoclaving, microwave heating and ultrasonication,” Waste Manage. 34(2), 498-503. DOI: 10.1016/j.wasman.2013.10.013
Gabhane, J., William, S., Vaidya, A. N., Das, S., and Wate, S. R. (2015). “Solar assisted alkali pretreatment of garden biomass: Effects on lignocellulose degradation, enzymatic hydrolysis, crystallinity and ultra-structural changes in lignocellulose,” Waste Manage. 40, 92-99. DOI: 10.1016/j.wasman.2015.03.002
Huang, Z., and Zhang, L. (2009). “Chemical structures of water-soluble polysaccharides from Rhizoma Panacis Japonici,” Carbohydr. Res. 344(9), 1136-1140. DOI: 10.1016/j.carres.2009.02.014
Jafari, Y., Amiri, H., and Karimi, K. (2016). “Acetone pretreatment for improvement of acetone, butanol, and ethanol production from sweet sorghum bagasse,” Appl. Energ. 168, 216-225. DOI: 10.1016/j.apenergy.2016.01.090
Kirubakaran, V., Sivaramakrishnan, V., Nalini, R., Sekar, T., Premalatha, M., and Subramanian, P. (2009). “A review on gasification of biomass,” Renew. Sust. Energ. Rev 13(1), 179-186. DOI: 10.1016/j.rser.2007.07.001
Li, M. F., Fan, Y. M., Xu, F., and Sun, R. C. (2011). “Structure and thermal stability of polysaccharide fractions extracted from the ultrasonic irradiated and cold alkali pretreated bamboo,” J. Appl. Polym. Sci. 121(1), 176-185. DOI: 10.1002/App.33491
Li, M. F., Fan, Y. M., Xu, F., Sun, R. C., and Zhang, X. L. (2010). “Cold sodium hydroxide/urea based pretreatment of bamboo for bioethanol production: Characterization of the cellulose rich fraction,” Ind. Crop. Prod. 32(3), 551-559. DOI: 10.1016/j.indcrop.2010.07.004
Mutschlechner, M., Illmer, P., and Wagner, A. O. (2015). “Biological pre-treatment: enhancing biogas production using the highly cellulolytic fungus Trichoderma viride,” Waste Manage. 43, 98-107. DOI: 10.1016/j.wasman.2015.05.011
Narron, R. H., Kim, H., Chang, H. M., Jameel, H., and Park, S. (2016). “Biomass pretreatments capable of enabling lignin valorization in a biorefinery process,” Curr. Opin. Biotechnol. 38, 39-46. DOI: 10.1016/j.copbio.2015.12.018
Nitsos, C. K., Matis, K. A., and Triantafyllidis, K. S. (2013). “Optimization of hydrothermal pretreatment of lignocellulosic biomass in the bioethanol production process,” Chemsuschem 6(1), 110-122. DOI: 10.1002/cssc.201200546
Park, Y. C., and Kim, J. S. (2012). “Comparison of various alkaline pretreatment methods of lignocellulosic biomass,” Energy 47(1), 31-35. DOI: 10.1016/j.energy.2012.08.010
Peng, P., Peng, F., Bian, J., Xu, F., Sun, R., and Kennedy, J. F. (2011). “Isolation and structural characterization of hemicelluloses from the bamboo species Phyllostachys incarnata Wen,” Carbohydr. Polym.86(2), 883-890. DOI: 10.1016/j.carbpol.2011.05.038
Peng, P., and She, D. (2014). “Isolation, structural characterization, and potential applications of hemicelluloses from bamboo: A review,” Carbohydr. Polym. 112, 701-720. DOI: 10.1016/j.carbpol.2014.06.068.
Rabemanolontsoa, H., and Saka, S. (2016). “Various pretreatments of lignocellulosics,” Bioresource Technol. 199, 83-91. DOI: 10.1016/j.biortech.2015.08.029
Rooney, W. L., Blumenthal, J., Bean, B., and Mullet, J. E. (2007). “Designing sorghum as a dedicated bioenergy feedstock,” Biofuel. Bioprod. Bior. 1(2), 147-157. DOI: 10.1002/bbb.15
Scheller, H. V., and Ulvskov, P. (2010). “Hemicelluloses,” Annual Review of Plant Biology 61(1), 263-289. DOI: 10.1146/annurev-arplant-042809-112315
Seca, A. M., Cavaleiro, J. A., Domingues, F. M., Silvestre, A. J., Evtuguin, D., and Neto, C. P. (2000). “Structural characterization of the lignin from the nodes and internodes of Arundo donax reed,” J. Agric. Food Chem. 48(3), 817-824. DOI: 10.1021/jf9910988
She, D. A., Xu, F., Geng, Z. C., Sun, R. C., Jones, G. L., and Baird, M. S. (2010). “Physicochemical characterization of extracted lignin from sweet sorghum stem,” Ind. Crop. Prod. 32(1), 21-28. DOI: 10.1016/j.indcrop.2010.02.008
Shen, D. S., Wang, K., Yin, J., Chen, T., and Yu, X. Q. (2016). “Effect of phosphoric acid as a catalyst on the hydrothermal pretreatment and acidogenic fermentation of food waste,” Waste Manage. 51, 65-71. DOI: 10.1016/j.wasman.2016.02.027
Sluiter, A., Hames, B., Ruiz, R., Scarlata, C., Sluiter, J., Templeton, D., and Crocker, D. (2008). Determination of Structural Carbohydrates and Lignin in Biomass (NREL/TP-510-42618), National Renewable Energy Laboratory, Golden, CO, USA, (http://www.nrel.gov/docs/gen/fy13/42618.pdf).
Sun, R. C., Tomkinson, J., Ma, P., and Liang, S. F. (2000). “Comparative study of hemicelluloses from rice straw by alkali and hydrogen peroxide treatments,” Carbohydr. Polym. 42(2), 111-122. DOI: 10.1016/S0144-8617(99)00136-8
Sun, S. L., Wen, J. L., Ma, M. G., Li, M. F., and Sun, R. C. (2013a). “Revealing the structural inhomogeneity of lignins from sweet sorghum stem by successive alkali extractions,” J. Agr. Food Chem.61(18), 4226-4235. DOI: 10.1021/jf400824p
Sun, S. L., Wen, J. L., Ma, M. G., and Sun, R. C. (2013b). “Successive alkali extraction and structural characterization of hemicelluloses from sweet sorghum stem,” Carbohydr. Polym. 92(2), 2224-2231. DOI: 10.1016/j.carbpol.2012.11.098
Teleman, A., Lundqvist, J., Tjerneld, F., Stalbrand, H., and Dahlman, O. (2000). “Characterization of acetylated 4-O-methylglucuronoxylan isolated from aspen employing 1H and 13C NMR spectroscopy,” Carbohydr. Res. 329(4), 807-815. DOI: 10.1016/S0008-6215(00)00249-4
Upton, B. M., and Kasko, A. M. (2016). “Strategies for the conversion of lignin to high-value polymeric materials: Review and perspective,” Chem. Rev. 116(4), 2275-2306. DOI: 10.1021/acs.chemrev.5b00345
Wang, C., Kelley, S. S., and Venditti, R. A. (2016). “Lignin-based thermoplastic materials,” Chemsuschem 9(8), 770-783. DOI: 10.1002/cssc.201501531.
Wen, J. L., Sun, S. L., Xue, B. L., and Sun, R. C. (2013). “Quantitative structures and thermal properties of birch lignins after ionic liquid pretreatment,” J. Agric. Food Chem. 61(3), 635-645. DOI: 10.1021/jf3051939
Xu, F., Sun, J., Sun, R., Fowler, P., and Baird, M. S. (2006). “Comparative study of organosolv lignins from wheat straw,” Ind. Crop. Prod. 23(2), 180-193. DOI: 10.1016/j.indcrop.2005.05.008
Xu, F., Sun, R. C., Zhai, M. Z., Sun, J. X., She, D., Geng, Z. C., and Lu, Q. (2008). “Fractional separation of hemicelluloses and lignin in high yield and purity from mild ball-milled Periploca sepium,” Separ. Sci. Technol. 43(11-12), 3351-3375. DOI: 10.1080/01496390802063721
Xue, B. L., Li, M. F., Xu, F., Sun, R. C., and Jones, G. (2012). “Microwave-enhanced alkali treatment of Pinus yunnanensis: Physiochemical characterization of the dissolved lignins,” Ind. Crop. Prod. 36(1), 209-216. DOI: 10.1016/j.indcrop.2011.09.008
Yan, T. T., Xu, Y. Q., and Yu, C. W. (2009). “The isolation and characterization of lignin of kenaf fiber,” J. Appl. Polym. Sci. 114(3), 1896-1901. DOI: 10.1002/app.29881.
Yu, M. H., Li, J. H., Chang, S., Zhang, L., Mao, Y. Y., Cui, T., Yan, Z. P., Luo, C. L., and Li, S. Z. (2016). “Bioethanol production using the sodium hydroxide pretreated sweet sorghum bagasse without washing,” Fuel 175, 20-25. DOI: 10.1016/j.fuel.2016.02.012
Zhang, K., Pei, Z. J., and Wang, D. H. (2016). “Organic solvent pretreatment of lignocellulosic biomass for biofuels and biochemicals: A review,” Bioresource Technol. 199, 21-33. DOI: 10.1016/j.biortech.2015.08.102
Zhao, Y. L., Wang, Y., Zhu, J. Y., Ragauskas, A., and Deng, Y. L. (2008). “Enhanced enzymatic hydrolysis of spruce by alkaline pretreatment at low temperature,” Biotechnol. Bioeng. 99(6), 1320-1328. DOI: 10.1002/Bit.21712
Article submitted: July 28, 2017; Peer review completed: October 14, 2017; Revised version received: January 9, 2018; Accepted: January 20, 2018; Published: February 7, 2018.
DOI: 10.15376/biores.13.2.2356-2373