structural changes of sugar cane bagasse lignin …...technology. the pretreatment conditions were...

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Structural Changes of Sugar Cane Bagasse Lignin during Cellulosic Ethanol Production Process Tana Tana, Zhanying Zhang,* ,Lalehvash Moghaddam, Darryn W. Rackemann, Jorge Rencoret, Ana Gutie ́ rrez, Jose ́ C. del Río, and William O.S. Doherty* ,Centre for Tropical Crops and Biocommodities, Queensland University of Technology, Brisbane, Australia Instituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS), CSIC, Av. Reina Mercedes, 10, E-41012 Seville, Spain * S Supporting Information ABSTRACT: Dilute acid pretreatment is one of the most studied biomass deconstructing technologies due to its relatively low process cost. Typical cellulosic ethanol production process involves three main stages: (1) dilute acid pretreatment, (2) enzymatic hydrolysis, and (3) fermentation/distillation. In this study, three lignins, L1, L2, and L3, were extracted using 1% (w/w) NaOH solution at 80 °C following each stage, respectively. Lignin characterization shows the reduction of aliphatic, guaiacyl, and carboxylic OH groups of the L2 and L3 compared to those of the L1 but increases in both the weight and number molecular weights as well as slight increases in the polydispersity index, probably because, among other reasons, of the removal of a higher molecular weight lignin fraction from the pretreated biomass during enzymatic hydrolysis. While 2D HSQC NMR and Py-GC/ MS did not reveal dierences in the proportions of syringyl and p-hydroxyphenyl units among the lignins, there is a predominance of the phenylcoumaran substructures and guaiacyl lignin units in L1 and the absence of some substructures/ linkages associated with L2 and L3. Lignin extraction following dilute acid pretreatment not only produced the lignin with the highest purity but also resulted in improved glucose yield from 71% to 77%. KEYWORDS: Sugar cane bagasse, Pretreatment, Lignin, Cellulosic ethanol, Enzymatic hydrolysis, Biorenery INTRODUCTION Lignocellulosic biomass is the most abundant renewable bioresource on Earth. 1 The utilization of lignocellulosic biomass for the production of biofuels, chemicals, and polymeric materials will reduce the reliance on fossil resources. 24 Thus, there has been an increasing trend in recent years to cost-eectively produce cellulosic ethanol and other chemicals from agro-industrial residues such as sugar cane bagasse. 5 For every 1 ton of sugar cane processed, approximately 280 kg of bagasse is produced resulting in 1.5 × 10 8 dry tons produced annually throughout the world. 57 Apart from bagasse being available in reasonable quantities, it is deposited in a centralized location in sugar factories, eliminating the cost associated with collection and trans- portation. As sugar cane bagasse contains 4050% cellulose, 2035% hemicelluloses, and 2035% lignin, 5,8,9 only the cellulose and to a lesser extent the hemicelluloses are used to produce ethanol, with the lignin ending up as waste. A typical cellulosic ethanol production process from sugar cane bagasse involves pretreatment, enzymatic hydrolysis of cellulose to glucose, yeast fermentation of the sugars to produce ethanol, and ethanol recovery by distillation. 1,10,11 Dilute acid pretreatment is one of the most promising pretreatment technologies used to produce fermentable sugars because of its relatively low pretreatment cost. 2 Dilute acid pretreatment removes the majority of the hemicellulose component and a small portion of lignin (i.e., acid soluble lignin) from the biomass. 12,13 The presence of lignin in the biomass reduces the eectiveness of the enzymatic hydrolysis process because it forms physical barriers which limit the access of cellulases to cellulose 10,1416 and nonproductively bind to the cellulase enzymes 10,17,18 used in the saccharication process. As lignin is used in neither the enzymatic nor the fermentation processes, it ends up as stillage posing a serious waste disposal issue. Furthermore, a small proportion of monolignol derivatives that are released during enzymatic hydrolysis will act as inhibitors during the fermentation process, negatively impacting ethanol yield. 19 Therefore, some studies have combined dilute acid pretreatment of lignocellulosic biomass with a second alkali pretreatment step, resulting in improved glucose yields. 20,21 Received: May 19, 2016 Revised: September 4, 2016 Published: September 9, 2016 Research Article pubs.acs.org/journal/ascecg © 2016 American Chemical Society 5483 DOI: 10.1021/acssuschemeng.6b01093 ACS Sustainable Chem. Eng. 2016, 4, 54835494

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Page 1: Structural Changes of Sugar Cane Bagasse Lignin …...Technology. The pretreatment conditions were as follows: a liquid/ solid (w/w) ratio of 6, a temperature of 170 C, a reaction

Structural Changes of Sugar Cane Bagasse Lignin during CellulosicEthanol Production ProcessTana Tana,† Zhanying Zhang,*,† Lalehvash Moghaddam,† Darryn W. Rackemann,† Jorge Rencoret,‡

Ana Gutierrez,‡ Jose C. del Río,‡ and William O.S. Doherty*,†

†Centre for Tropical Crops and Biocommodities, Queensland University of Technology, Brisbane, Australia‡Instituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS), CSIC, Av. Reina Mercedes, 10, E-41012 Seville, Spain

*S Supporting Information

ABSTRACT: Dilute acid pretreatment is one of the moststudied biomass deconstructing technologies due to itsrelatively low process cost. Typical cellulosic ethanolproduction process involves three main stages: (1) diluteacid pretreatment, (2) enzymatic hydrolysis, and (3)fermentation/distillation. In this study, three lignins, L1, L2,and L3, were extracted using 1% (w/w) NaOH solution at 80°C following each stage, respectively. Lignin characterizationshows the reduction of aliphatic, guaiacyl, and carboxylic OHgroups of the L2 and L3 compared to those of the L1 butincreases in both the weight and number molecular weights aswell as slight increases in the polydispersity index, probablybecause, among other reasons, of the removal of a highermolecular weight lignin fraction from the pretreated biomass during enzymatic hydrolysis. While 2D HSQC NMR and Py-GC/MS did not reveal differences in the proportions of syringyl and p-hydroxyphenyl units among the lignins, there is apredominance of the phenylcoumaran substructures and guaiacyl lignin units in L1 and the absence of some substructures/linkages associated with L2 and L3. Lignin extraction following dilute acid pretreatment not only produced the lignin with thehighest purity but also resulted in improved glucose yield from 71% to 77%.

KEYWORDS: Sugar cane bagasse, Pretreatment, Lignin, Cellulosic ethanol, Enzymatic hydrolysis, Biorefinery

■ INTRODUCTION

Lignocellulosic biomass is the most abundant renewablebioresource on Earth.1 The utilization of lignocellulosicbiomass for the production of biofuels, chemicals, andpolymeric materials will reduce the reliance on fossilresources.2−4 Thus, there has been an increasing trend inrecent years to cost-effectively produce cellulosic ethanol andother chemicals from agro-industrial residues such as sugar canebagasse.5 For every 1 ton of sugar cane processed,approximately 280 kg of bagasse is produced resulting in 1.5× 108 dry tons produced annually throughout the world.5−7

Apart from bagasse being available in reasonable quantities, it isdeposited in a centralized location in sugar factories,eliminating the cost associated with collection and trans-portation.As sugar cane bagasse contains 40−50% cellulose, 20−35%

hemicelluloses, and 20−35% lignin,5,8,9 only the cellulose andto a lesser extent the hemicelluloses are used to produceethanol, with the lignin ending up as waste. A typical cellulosicethanol production process from sugar cane bagasse involvespretreatment, enzymatic hydrolysis of cellulose to glucose, yeastfermentation of the sugars to produce ethanol, and ethanolrecovery by distillation.1,10,11 Dilute acid pretreatment is one of

the most promising pretreatment technologies used to producefermentable sugars because of its relatively low pretreatmentcost.2 Dilute acid pretreatment removes the majority of thehemicellulose component and a small portion of lignin (i.e.,acid soluble lignin) from the biomass.12,13 The presence oflignin in the biomass reduces the effectiveness of the enzymatichydrolysis process because it forms physical barriers which limitthe access of cellulases to cellulose10,14−16 and nonproductivelybind to the cellulase enzymes10,17,18 used in the saccharificationprocess. As lignin is used in neither the enzymatic nor thefermentation processes, it ends up as stillage posing a seriouswaste disposal issue. Furthermore, a small proportion ofmonolignol derivatives that are released during enzymatichydrolysis will act as inhibitors during the fermentation process,negatively impacting ethanol yield.19 Therefore, some studieshave combined dilute acid pretreatment of lignocellulosicbiomass with a second alkali pretreatment step, resulting inimproved glucose yields.20,21

Received: May 19, 2016Revised: September 4, 2016Published: September 9, 2016

Research Article

pubs.acs.org/journal/ascecg

© 2016 American Chemical Society 5483 DOI: 10.1021/acssuschemeng.6b01093ACS Sustainable Chem. Eng. 2016, 4, 5483−5494

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Lignin monolignols are connected by a variety of C−O andC−C linkages, with β-O-4′ being the main type. The severity ofthe acid treatment, reaction time and or heat treatment affectthe structure of the lignin as the proportion of β-O-4′ linkagesreduces while the proportion of condensed C−C bonds formedincreases. In one study,22 it was observed that temperature andthe length of time affect the proportion of β-O-4′ linkages andthe proportion of cyclic ethers formed from kraft-derivedlignins. In another study,23 it was found that the biomassprocessing method prior to base-catalyzed depolymerization ofthe lignin-rich solid (obtained after enzymatic hydrolysis)significantly impacted the yield of the water-soluble fractions,with dilute acid pretreatment of the biomass giving the lowestyield. So, it is essential that the structural changes that occur inlignin during biomass processing prior to depolymerization,influence product type and yield. As a consequence,information on the structural changes of sugar cane bagasselignin derived via dilute acid hydrolysis in relation to changesthat occur during subsequent saccharification and fermentationprocesses will dictate at what stage during the ethanolmanufacturing process would be beneficial to recover thelignin for value-added applications.In this study, properties of lignins recovered following dilute

acid pretreatment, enzymatic hydrolysis, and fermentation/

distillation in the cellulosic ethanol production process bydilute NaOH extraction (1% in liquid, w/w) and acidprecipitation were investigated and compared. A number ofanalytical techniques, including elemental analysis, gel per-meation chromatography (GPC), thermogravimetric analysis(TGA), Fourier transforms infrared (FT-IR) spectroscopy,nuclear magnetic resonances (NMRs; proton-, carbon-,phosphorus-, and two-dimensional heteronuclear single quan-tum coherence; 1H, 13C, 31P, and 2D HSQC), and pyrolysiscoupled to gas chromatography−mass spectrometry (Py-GC/MS) were used to determine lignin physical and chemicalproperties, including purity, molecular weights, thermalstability, substructures and linkages, as well as hydroxylfunctional groups. The bagasse lignin recovered after acidpretreatment was also subjected to enzymatic hydrolysis andmonitored using UV−visible spectroscopy to further provideevidence of chemical modification during the process.

■ EXPERIMENTAL SECTIONMaterials. Raw sugar cane bagasse was collected from Racecourse

Sugar Mill (Mackay Sugar Limited, Australia). A total of 20 kg of rawsugar cane bagasse (∼50% moisture) was pretreated with dilute H2SO4in a pilot scale horizontal reactor at the Mackay RenewableBiocommodities Pilot Plant, the facility of Queensland University of

Figure 1. Flowchart of lignin extraction and lignin recovery process.

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Technology. The pretreatment conditions were as follows: a liquid/solid (w/w) ratio of 6, a temperature of 170 °C, a reaction time of 15min, and an acid concentration of 0.4% (w/w in liquid). The detailedprocedure for pretreatment is described elsewhere.24 After pretreat-ment, the solid residue was pressed and collected for furtherprocessing and characterization. The pressed solid residue has awater content of 57%.Sodium hydroxide (NaOH), pyridine, chloroform, chromium

acetylacetonate, cyclohexanol, 2-chloro-4,4,5,5-tetramethyl-1,3,2-diox-aphospholane (TMDP), dimethyl sulfoxide-d6 (DMSO-d6), deuteratedchloroform, and polystyrenesulfonate standards were purchased fromSigma-Aldrich Company (US). Sulfuric acid with a mass fraction of98% and HCl with a mass fraction of 32% were purchased from Chem-Supply Ltd., Australia. All the chemicals used were of analytical gradeor above.Lignin Extraction. Lignin Extraction Prior to Enzymatic

Hydrolysis. Figure 1 shows the flowchart of lignin extraction andrecovery processes. For lignin extraction prior to enzymatic hydrolysis,pretreated bagasse (100 g dry mass) was mixed with the requiredamount of water to a solid/liquid ratio of 1:10 (mass ratio). Themixture was neutralized to pH 5.0 with the addition of 2 M NaOH.After neutralization, 10.0 g of solid NaOH (10% of dry biomass or 1%in liquid) was added and the whole thoroughly mixed. The mixturewas incubated at 80 °C for 1 h in a water bath with swirling every 10min. After incubation, the liquid (black liquor) was separated byfiltration through a Whatman no. 541 filter paper. The solid residuewas washed twice with 5 g L−1 NaOH solution (2 × 250 mL NaOHsolution) to dissolve loosely bound lignin, followed by distilled waterwash twice (2 × 250 mL water per wash) at room temperature (24°C). The washed solution was mixed with the black liquor andcollected for lignin recovery. The solid residue was rinsed with distilledwater twice (2 × 250 mL water) and collected for the determination ofbiomass composition and cellulose digestibility.Lignin Extraction after Enzymatic Hydrolysis. Pretreated bagasse

(100 g dry mass) was mixed with a required amount of water to asolid/liquid ratio of 1:10 (mass ratio). The mixture was neutralized topH 5.0 with 2 M NaOH and sterilized at 121 °C for 15 min. As shownin Figure 1, enzymatic hydrolysis was conducted prior to ligninextraction. Cellulase enzymes (Accellerate 1500, DuPont, US) wereadded to the mixture with a loading of 10 FPU/g biomass. Enzymatichydrolysis was conducted at 50 °C for 72 h. After hydrolysis, analiquot was withdrawn for sugars analysis, and the solid residue wasrecovered by filtration. The wet solid residue (20 g) was vacuum-driedat 45 °C for 48 h and stored for biomass composition analysis. A totalof 2.0 g of the vacuum-dried solid residue was further dried at 105 °Covernight to determine the water content of the wet solid residue. Asubsample of the wet solid residue (50 g dry mass) was mixed with therequired amount of water to obtain a solid/liquid ratio of 1:10 (massratio). A total of 5.0 g of solid NaOH (10% on dry biomass) wasadded to the mixture and was incubated at 80 °C for 1 h in a waterbath. Following incubation, the mixture was processed as described inLignin Extraction Prior to Enzymatic Hydrolysis. The washed solidresidue was collected for biomass compositional analysis.A total of 2.0 g of a subsample of L1 obtained in Lignin Extraction

Prior to Enzymatic Hydrolysis was subjected to enzymatic hydrolysisas described in this section and monitored at various times from 0 to72 h using GBC Cintra 40 UV−visible spectrometer (US).Lignin Extraction after Fermentation and Distillation. Pretreated

bagasse (100 g dry mass) was mixed with the required amount ofwater to a solid/liquid ratio of 1:10 (mass ratio). The mixture wasneutralized and sterilized as described. Simultaneous saccharificationand fermentation were initiated with the addition of cellulase enzymes(10 FPU/g dry biomass), sterilized yeast extract, and peptonesolutions (final concentrations of 5 g/kg media) and Fali yeast(∼0.5 g/kg media, AB Mauri, Australia) and conducted anaerobicallyat a temperature of 30 °C for 72 h. As shown in Figure 1, at the end offermentation, ethanol was distilled by rotary evaporation at 80 °C for 1h. The solid residue was separated after distillation by filtration. Theprocessing of the solid residue for extraction of the lignin was the sameas that described in Lignin Extraction after Enzymatic Hydrolysis. The

extracted and washed solid residue was collected for determination ofbiomass composition.

Lignin Recovery. Lignins in the extraction solutions (LigninExtraction) were recovered by lowering the solution pH as describedpreviously.9,25 Briefly, the pH of a lignin solution was dropped to 5.5by gradually adding 2 M H2SO4 solution with slow stirring, followedby 15 min of stirring at ambient temperature. The solution pH wasfurther dropped to 3.0 by gradually adding 2 M H2SO4 solution withfurther stirred for 30 min in a water bath at 65 °C. The solution wasfiltered, and the lignin residue was washed several times with hot water(70−80 °C) until no foam was observed in the filtered solution. Thewashed lignin was collected and vacuum-dried at 45 °C for 48 h. Thedried lignin was ground manually and was stored in a desiccator forcomposition and structural analysis.26

Lignin Characterization. Compositional Analysis. Composi-tional (cellulose, hemicelluloses, lignin, and ash) analysis of the solidsamples was conducted according to the standard methods developedby National Renewable Energy Laboratory (NREL), US.26 Themaxium standard deviation was no more than 3% using this method.

Elemental Analysis and Methoxyl Group Content. Elementalanalysis of lignin was performed using a Flash EA 1112 OrganicAnalyzer (Thermo Scientific, US). Subsamples of lignins were driedovernight at 105 °C to constant weight prior to analysis. A subsampleof dried lignin (2−4 mg) was encapsulated in a tin container for themeasurement of carbon, hydrogen, and nitrogen while anothersubsample of lignin was encapsulated in a silver container for analysisof oxygen content. The maximum error of analysis for oxygen was3.5%. The maximum error for the other elements was 0.1%.

The methoxyl group (OCH3) content of lignins was determined byusing 1H NMR spectra.27 A quantitative 1H NMR spectrum of ligninsamples was collected with a 90° pulse width before 2D NMR analysis(2D HSQC NMR); the number of scans was 8. The signals ofaromatic protons are registered between 5.98 and 7.74 ppm, while thesignals of the methoxyl group are registered between 3.49 and 4.08ppm. The methoxyl content can be obtained from the followingequation:

= − x%OCH 28.28436 19.7500473 (1)

where x = H (aromatic)/H (methoxyl). The H (aromatic) and H(methoxyl) are integration values of the aromatic and methoxyl signalsin 1H NMR spectra.

Average Molecular Weight. Gel permeation chromatography(GPC) was used to determine the molecular weight of recoveredlignins. Next, 10 mg lignin samples were dissolved in 4 g/L NaOH andfiltered through a 0.45 μm syringe membrane filter before GPC. AShodex Asahipak GS-320 HQ column and a Waters 2487 UV detector(280 nm) were used to determine lignin molecular weight distribution.The mobile phase was 4 g/L NaOH (pH 12 adjusted by the additionof dilute HCl) with a flow rate of 0.5 mL/min. The columntemperature was maintained at 30 °C. Sodium polystyrenesulfonateswith a molecular weight range from 1530 g/mol to 34700 g/mol wereused as standards. Average weight molecular weight (Mw) and averagenumber molecular weight (Mn) of lignins were calculated aftercomparison with the standards.

Attenuated Total Reflectance (ATR)-FTIR Spectroscopy. Infraredspectra were collected using a Nicolet Diamond 5700 ATR FTIRspectrometer equipped with a Smart Endurance single bouncediamond ATR accessory (Nicolet Instrument Corp., US). Spectrawere collected in the spectral range 4000−525 cm−1, using 64 scans at4 cm−1 resolution with a mirror velocity of 0.6329 cm/s. Themeasurement time for each spectrum was around 60 s.

TGA. Decomposition studies of lignin samples were carried out in aTA Instruments Q500 in a nitrogen-flowing atmosphere of 15 mL/min. Approximately 15 mg of lignin was heated at a rate of 10 K/minfrom ambient temperature to 1000 °C, and the mass loss was recordedto characterize the various degradation stages.

2D HSQC NMR. Lignin (20 mg) was dissolved in 1 mL of DMSO-d6and transferred to an NMR tube (a diameter of 5 mm). 1H−13Ccorrelation 2D HSQC NMR spectra were recorded on a 400 MRspectrometer (Agilent, US) at room temperature. The spectral widths

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were 5 kHz and 20 kHz for the 1H and 13C dimensions, respectively.The number of the collected complex points was 1024 for the 1Hdimension with a recycle delay of 1.5 s. The number of transients was64, and 256 time increments were recorded in 13C dimension. Thecentral solvent (DMSO-d6) peak was used as an internal chemical shiftreference point (δC/δH 39.5/2.49). The content of aromatic units andS/G ratio of lignins were calculated based on volume integrals(uncorrected) of the HSQC correlation peaks using the ACD/NMRProcessor Academic Edition software.28

31P NMR. A solvent mixture of pyridine/deuterated chloroform (avolume fraction of 1.6:1) was prepared (first solution). Molecularsieves (0.3 nm size) were added to the solvent mixture and the mixturekept in a sealed container under nitrogen to prevent moisture intake.Chromium(III) acetylacetonate (5.0 mg) and cyclohexanol (11.8 mg)were added to 1 mL of the solution mixture to prepare the secondsolution. This mixture served as both a relaxation agent and internalstandard. Dry lignin (30 mg) was mixed with 0.5 mL of the firstsolution mixture. A total of 100 μL of the second solution was mixedwith 100 μL of 2-chloro-4,4,5,5-tetramethyl-1,3,2-dioxaphospholane inorder to tag the hydroxyl groups. After mixing for 5 min, the mixturewas diluted to 1 mL in a glass vial with the addition of the firstsolution. The glass vial was then sealed and the solution wasthoroughly mixed and transferred into an NMR tube. The 31P NMRspectra were obtained on a 400 MR spectrometer (Agilent, US) atroom temperature. 31P NMR acquisition was performed using aninverse gated decoupling pulse sequence with a relaxation delay of 25 sbetween 90° pulses. A total of 1000 transients were recorded, yieldingquantitative spectra. The concentrations of the different hydroxylgroups were calculated based on the internal standard of cyclohexanol(chemical shift 144.5−144.0 ppm).Pyrolysis Coupled to Gas Chromatography and Mass Spectrom-

etry (Py-GC/MS). Pyrolysis of the lignin samples (ca. 0.1 mg) wasperformed at 500 °C in an EGA/PY-3030D microfurnace pyrolyzer(Frontier Laboratories Ltd., Fukushima, Japan) connected to a GC7820A (Agilent Technologies, Inc., Santa Clara, CA) and an Agilent5975 mass-selective detector (EI at 70 eV). The column used was a 30m (length) × 0.25 mm (internal diameter), 0.25 μm film thickness,DB-1701 (J&W Scientific, Folsom, CA). The oven temperature wasprogrammed from 50 °C (1 min) to 100 °C at 20 °C/min and then to280 °C (5 min) at 6 °C/min. Helium was the carrier gas (1 mL/min).Identification of the released compounds was made by comparison oftheir mass spectra with those of the Wiley and NIST libraries and withthose reported in the literature29,30 and, when possible, by comparisonwith the retention times and mass spectra of authentic standards.Molar peak areas were calculated for each lignin degradation productreleased. The summed areas were normalized, and the data for tworeplicates were averaged and expressed as percentages.

■ RESULTS AND DISCUSSIONYields of Sugars and Lignins from Different Pro-

cesses. Table 1 shows the composition of the solid residuesand lignins, as well as the yields of sugars and lignins from thedifferent treatment stages. Lignin extraction from the solid

residue with dilute NaOH solution significantly increased theglucan content. The extraction process enhanced glucandigestibility due to the removal of lignin and hence increasedthe glucose amount from 37.5 to 40.7 g for 100 g of solidresidue processed (Figure 1), corresponding to glucose yieldsfrom 71% to 77%. This increase could potentially lead to arelative ethanol increase of ∼6%.For the enzymatic hydrolysis residue and fermentation/

distillation residue, the amounts of total solid residues reducedsignificantly due to conversion of a large proportion of glucanto soluble glucose by enzymatic hydrolysis (Figure 1). Thehighest amount of lignin (16.4 g) extracted from 100 g ofpretreated solid residue was achieved after enzymatichydrolysis, and this corresponded to a lignin yield (comparedto total lignin in pretreated solid residue) of 57%, 8−9% higherthan the other stages. This is due to the fact that the enzymatichydrolysis process removed glucan, making the substrate moreaccessible to NaOH extraction. L3 yield is lower than L2 yield,possibly because of solubilization of some lignin components atthe relatively high distillation temperature of 80 °C. L3 containsthe highest ash content and so has the least lignin purity.Carbohydrates were not detected in all the recovered lignins.

Elemental Analysis. The elemental analysis results of thelignins are shown in Table 2. The data show that the nitrogen

contents of L2 and L3 are much higher than that of L1. Thehigher nitrogen contents obtained for L2 and L3 are very likelyfrom nitrogen sources (cellulases, yeast extract, and peptone)used in enzymatic hydrolysis and fermentation stage andnitrogen-rich biomass (i.e., yeast) produced during ethanolproduction. Assuming that all the nitrogen is from protein, witha protein conversion factor of 6.25, the L1 sample has thelowest protein content of 4.4%. Therefore, the purity of L1 isabout 93% (97.8% − 4.4%).Atomic ratios were calculated using values in Table 2,

neglecting the nitrogen contents, to give the empirical formulasof the different lignins (Table 2). The empirical formula,C9HxOy(OMe)z, is used to represent the lignin structural unit.There is no noticeable difference in the empirical formulaamong the samples.

Table 1. Biomass Composition and Yields of Glucose and Lignins

component (%)

sample typesoda

extraction glucan xylan lignin ashglucose yield (g/100 g glucose in pretreated

solid residue)lignin yield (g/100 g lignin in pretreated

solid residue)

pretreatedbagasse

no 47.7 1.4 28.7 12.7 71yes 63.8 0.9 13.0 14.0 77

hydrolysis residue no 30.9 0.9 41.2 19.0yes 48.1 1.0 23.8 17.8

fermentationresidue

no 31.9 1.3 42.8 13.8yes 54.0 1.2 21.7 14.5

L1 0.0 0.0 97.8 1.3 48L2 0.0 0.0 97.1 1.4 57L3 0.0 0.0 95.3 2.0 49

Table 2. Elemental Analysis Results and Formulae of Lignins

lignin type N% C% H% O% formulas

L1 0.7 59.9 5.8 31.7 C9H10.64O2.92(OCH3)1.11L2 1.4 50.0 5.9 31.3 C9H10.94O2.83(OCH3)1.23L3 1.7 58.7 6.0 30.2 C9H11.18O2.67(OCH3)1.33

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Lignin Average Molecular Weights. Table 3 showsaverage molecular weights, Mw and Mn, and polydispersity

index (Mw/Mn). The average molecular weight of ligninrecovered prior to enzymatic hydrolysis, i.e., L1 wassignificantly lower than L2 and L3. From the molecular weightdistribution curves (Figure S1, Supporting Information), it maybe due to the formation of a new fraction of higher molarmass.22 It is likely, though, that the higher average molecularweight of the lignin obtained after enzymatic hydrolysis (L2)and fermentation (L3) is due to a loss of soluble lowermolecular weight lignin fractions and functional groups duringprocessing. It may also be due to increased degree of branchingand condensation, as a consequence of incubation for 72 h inthe matrix during enzymatic hydrolysis.31 While these areplausible explanations, it is more than likely that the lignin thatwas retained in the biomass after pretreatment, which is of ahigher molecular weight than L1 as it is less exposed to acidpretreatment, was made available after enzymatic pretreatment.

As shown in Figure 1, the amount of lignin recovered increasedby ∼18%, indicating that some of the residual lignin notremoved during acid pretreatment was removed aftersaccharification of the cellulose component of the biomass.

ATR-FTIR Spectra. FTIR spectroscopy is a useful tool todetermine the functional groups and the changes of chemicalstructural features of the lignins.32−35 In this study, the spectraof L2 and L3 were subtracted from the spectrum of L1,following normalization of the spectra with the band at 1116.6cm−1. The spectral subtraction results show that there are cleardifferences between these lignins (Figure 2). The wide peak at3030−3690 cm−1 is attributed to O−H stretching vibrationsand hydrogen bonding in phenolic and aliphatic structures inlignins.9,36,37 The L1 lignin has the highest O−H stretchingvibrations, and the intensities in the 3000−2800 cm−1 region,which are assigned to the C−H stretching of the aromaticmethoxyl and methyl and methylene groups of the lignin sidechains,32,35 are also the highest with this lignin sample. L2 hasthe least proportion of these groups.The unconjugated ketones or carboxyl stretching vibration at

1699 cm−137 is present in the highest proportion in L1 (Figure2). The peaks at 1591, 1506, and 1456 cm−1, which correspondto the characteristic vibrations of core aromatic structures inlignin,36,38,39 were observed in all lignin samples. However,Figure 2 shows that L2 and L3 lignins have higher proportionsof these aromatic units than L1. The peak at 1423 cm−1 isrelated to C−H deformation in lignin, and the peaks at 1324and 1261 cm−1 are attributed to syringyl ring breathing with

Table 3. Weight-Average (Mw) and Number-Average (Mn)Molecular Weights and Polydispersity (Mw/Mn) of theDifferent Lignin Samples

lignin type Mw (g mol−1) Mn (g mol−1) Mw/Mn

L1 8327 4454 1.87L2 9303 4876 1.91L3 9272 4854 1.91

Figure 2. ATR-FTIR subtraction spectra of lignins.

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C−O stretching36 and guaiacyl ring breathing with COstretching, respectively.40

The peak area ratio of the ester bonds associated with p-hydroxyphenyl (1169 cm−1) to the syrinyl units (1119 cm−1)was found to be 0.26, 0.20, and 0.10 for L1, L2, and L3 in thatorder.The peak at 1219 cm−1 is related to ring breathing with C−O

stretching of both the syringyl and guaiacyl structures. In the1117−833 cm−1 region, there is a significant difference amongthe three lignins. The absorption band at 835 cm−1 is indicativeof the presence of p-hydroxyphenyl units41 and is present in allthree samples.TGA Results. TG curves reveal the weight loss of substances

in relation to the temperature of thermal degradation, whileDTG curves show the corresponding rate of weight loss.39,42

Similar weight loss trends were observed in the TG/DTGcurves for all the lignins (Figure 3). The thermal curves showthe first stage of weight losses at 40−150 °C due to theevaporation of residual moisture.

The second weight losses occur at 200−500 °C, and themaximum weight loss rates are observed at 335−350 °C, similarto those reported by previous workers.39,43 The peaktemperatures (Tm) corresponding to the maximum degradationrate for L2 and L3 are 335 °C, about 15 °C lower than that ofL1. This is unexpected as L1 has a lower molecular weight thanL2 or L3, while the thermal stability of lignins is known toincrease with increasing molecular weight.44 The higher ash(Table 1) and protein (as indicted by nitrogen content in Table2) contents in L2 and L3 may have contributed to the lower Tmvalues obtained by influencing the rate of degradation throughweakening of the C−O bond in the β-O-4 unit of the lignins.31

Also, the lower Tm for L2 and L3 may be because the inherentsubstructures and linkages possibly changed during theenzymatic hydrolysis and the fermentation process. The ligninmacromolecule mainly contains β-ether linkages which maybreak during incubation at pH 5 and 50 °C for 72 h during theenzymatic hydrolysis process. The differential increase of theUV band at 325 nm of the lignin solution exposed to 72 h ofenzymatic hydrolysis (Figure S2) is associated with increasedformation of the ferulic acid moiety45 and is thereforesuggestive of increased lignin breakdown. The lignin break-down could be the effect of incubation at that pH or thepresence of a ligninolytic enzyme in the cellulase cocktail thatbreaks down lignin.46

The weight losses of the lignins in TG curves become lesssignificant above 500 °C. The final residue yields for L1, L2,and L3 lignin were 25.7, 28.8, and 30.1% in that order,mirroring their ash and protein contents.

NMR Spectra. 2D HSQC NMR. The aromatic units anddifferent interunit linkages present in the lignins were analyzedby 2D HSQC NMR. It is a powerful technique for ligninstructure determination compared to 1D NMR (1H NMR or13C NMR), which suffers from signal overlapping.47 Figure 4shows the side chain (δC/δH 50.0−90.0/2.50−6.00) andaromatic regions (δC/δH 100.0−135.0/5.50−8.50) of the 2DHSQC NMR spectra of the lignins. The assignments of thecorrelation signals in the spectra (Table 4) were based onprevious publications.9,48−50 The main lignin substructuresfound are depicted in Figure 4.The aliphatic-oxygenated 1H−13C correlations of the spectra

of the lignin side chain interunit linkages are shown in Figure4I. In this region, correlation signals from methoxyl groups andside chains in β-O-4′ substructures (A) were the commonlyobserved signals in the lignins. The signals of methoxyl groupobserved at δC/δH 55.4/3.72 were the most prominent signalsat the side chain region for all lignins. In addition to themethoxyl group, the aliphatic side-chain region of the spectraalso showed other commonly observed signals correspondingto the Cα/Hα and Cβ/Hβ correlations of β-O-4′ substructures(A). Signals for phenylcoumaran substructures (B) were alsoobserved in the HSQC spectra, being more evident in the L1sample (Figure 5). However, signals due to γ-acylated ligninstructures (arising from p-coumarates acylating the γ-positionof the lignin side chain), and which are present in significantamounts in the HSQC spectra of the native lignin frombagasse,52 could not be detected in the spectra of L1, L2, andL3, suggesting that p-coumarate groups have been hydrolyzedduring dilute acid pretreatment and/or during lignin extractionwith NaOH.In the aromatic/unsaturated region of the HSQC spectra, the

main correlation signals correspond to aromatic rings of the p-hydroxyphenyl (H), guaiacyl (G), and syringyl (S) lignin units,respectively (Figure 4II). Prominent signals at δC/δH 103.8/6.69 due to C2,6−H2,6 correlations in S units were present in allsamples. Weak signals at δC/δH 106.4/7.31 associated withC2,6−H2,6 correlations in Cα-oxidized S (S′) units were presentin all the lignins except in L3 (Figure 5, structure 2). Thestrong signals at δC/δH 115.1/6.72 are due to C5−H5correlations in G units that is superimposed with the C3,5−H3,5 correlations of p-coumarates (pCA) and were present in allthe samples. Weak signals at δC/δH 111.0/7.02 correspondingto C2−H2 correlations in G units were observed in all thelignins, while a relatively strong signal at δC/δH 119.0/6.77related to C6−H6 in G units was only observed for the L1

Figure 3. (a) TGA and (b) DTG curves of lignins.

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(Figure 5, substructure 3). The Cβ−Hβ correlations for p-coumarates (pCA) and ferulates (FA) at δC/δH 116.3/6.40were observed in all spectra, although they were weaker in L3(Figure 5, structure 4). As the UV data showed a higherproportion of ferulic acid was formed in the sample after 72 hof enzymatic hydrolysis, it must have been removed duringrecovery of L3. The signals for H-lignin units at δC/δH 127.9/7.01 associated with C2,6−H2,6 correlations were observed invery low intensities for all three lignins. Signals at δC/δH 130.0/7.50 related to C2,6−H2,6 correlation in p-coumaric acid (pCA)were present in the samples. A strong Cα−Hα correlation signal

in pCA at δC/δH 144.1/7.50 is also present in all samples.Finally, and as said above, it is important to note that theHSQC indicates that both ferulic acid and p-coumaric acid,which in bagasse occurs acylating the γ-carbon of the ligninside-chains, have been completely hydrolyzed and are presentin free form in the alkaline lignins (as indicated by thecharacteristic signals from the Cβ-Hβ correlations at δC/δH116.3/6.40).It was not possible to calculate the S/G ratios because of

overlapping between G5/G6 and pCAβ/FAβ signals (Figure 4).However, the S/G2 ratios are 8.3, 87, and 57.2 for L1, L2, and

Figure 4. Spectra map of lignin substructures.

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L3 in that order, showing in a very qualitative way subtledifferences among the lignin samples. In summary, however,

the predominance of phenylcoumaran substructures and theC6−H6 in G units in the L1 sample and the absence of thelinkages associated with the substructures of C2,6−H2,6 inoxidized (CαO) S (S′) units and pCAβ/FAβ clearly indicatechanges in lignin substructures during enzymatic hydrolysis andfermentation/distillation of pretreated bagasse.

31P NMR. 31P NMR is now routinely used to quantifydifferent hydroxyl groups in the lignin molecular structure.Figure S3 shows a typical 31P NMR spectrum of the ligninswith the detailed signal assignments of hydroxyl groups basedon previous studies.51,52 The integration data of various OHgroups for all the lignins are summarized in Table 5.

31P NMR spectra of phosphitylated lignin give a goodquantification of aliphatic hydroxyl groups, syringyl, guaiacyl, p-hydroxyphenyl, condensed phenol units, and carboxyl acids. Ascan be seen from Table 5, the L1 extracted before enzymatichydrolysis has the highest content of aliphatic OH groupsamong all the OH groups (a confirmation of the FTIR data)and the lowest content of condensed phenolic OH group (5-5′). Notably, the content of the aliphatic hydroxyl, condensedphenolic OH (4-O-5′), guaiacyl OH, and carboxylic acid OHgroups decreased significantly after enzymatic hydrolysis. Thenthe contents of the aliphatic OH group and guaiacyl OH groupfurther drop to 0.15 and 0.04 mmol/g, respectively, afterfermentation/distillation while condensed phenolic OH (4-O-5′) and carboxylic acid OH groups’ proportions did not change.The low content of the guaiacyl OH group is possibly due tothe formation of catechol and condensed phenols betweenguaiacyl and syringyl units (4-O-5′). The decreasing content ofthe guaiacyl OH group may be due to increased formation ofcondensed phenols between guaiacyl and syringyl units (4-O-5′).

Py-GC/MS. The pyrograms of the selected lignin samplesare shown in Figure 6. The identities and relative molarabundances of the lignin-derived compounds released are listedin Table 6. Pyrolysis released phenolic compounds derivedfrom lignin and from p-hydroxycinnamic acids (p-coumaric andferulic acids). The pyrograms showed the phenolic compoundsderived from the p-hydroxyphenyl (H), guaiacyl (G), andsyringyl (S) lignin units, such as phenol (1), guaiacol (2), 4-methylphenol (4), 4-methylguaiacol (5), syringol (14), 4-methylsyringol (19), 4-vinylsyringol (26), and trans-4-prope-nylsyringol (32), among others. High amounts of 4-vinylphenol(8) and 4-vinylguaiacol (9) were also released but, as usuallyoccurs in the pyrolysis of grasses, they mostly arise from p-coumaric and ferulic acid, respectively, after decarboxylationupon pyrolysis.47,52The Py-GC/MS analysis revealed subtledifferences (phenol, 4-vinylphenol, syringol, and 4-methylsyr-ingol) in the lignins. Similar S/G ratios of ∼1.5−1.6 (Table 7)and ∼30−33% of “H units” mostly derived from p-coumaratesthat are attached to the lignin γ-OH28 were obtained for thethree lignins. However, some minor amounts of intact p-coumaric acid methyl ester (44) and ferulic acid methyl ester(42) were also detected from L2 and L3 recovered afterenzymatic hydrolysis and fermentation/distillation.

Table 4. Assignment of Lignin Signals in the 1H−13C 2DHSQC NMR Spectra

labelregion (δC/

δH) assignments

−OCH3 55.4/3.72 C−H in methoxyl groupsAγ 59.2/3.69 Cγ−Hγ in β-O-4′ substructures (A)Bγ 62.4/3.73 Cγ−Hγ in β-5′ phenylcoumaran substructures (B)Aα 71.7/4.84 Cα−Hα in β-O-4′ substructures (A)Aβ(S)1 85.8/4.09 Cβ−Hβ in β-O-4′ substructures (A, erythro form)Aβ(S)2 86.3/4.00 Cβ−Hβ in β-O-4′ substructures (A, threo form)S2,6 103.8/6.69 C2,6−H2,6 in syringyl units (S)S′2,6 106.4/7.31 C2,6−H2,6 in oxidized (CαO) syringyl units (S′)G2 111.0/7.02 C2−H2 in guaiacyl units (G)FA2 111.0/7.34 C2−H2 in ferulates (FA)G5 115.1/6.72 C5−H5 in guaiacyl units (G)pCAβ/FAβ

116.3/6.40 Cβ−Hβ in free p-coumaric (pCA) and ferulic (FA)acids

G6 119.0/6.77 C6−H6 in guaiacyl units (G)H2,6 127.9/7.01 C2,6−H2,6 in p-hydroxyphenyl units (H)pCA2,6 130.0/7.50 C2,6−H2,6 in free p-coumaric acid (pCA)pCAα/FAα

144.1/7.50 Cα−Hα in free p-coumaric acid (pCA) and ferulic(FA) acids

Figure 5. Lignin substructures affected during processing.

Table 5. Contents of Lignin Hydroxyl Groups Calculated by 31P NMR Spectra (mmol g−1 lignin)

lignin aliphatic OH condensed phenolic OH (4-O-5′) condensed phenolic OH (5−5′) guaiacyl OH p-hydroxylic phenyl carboxylic acid OH total OH

L1 1.62 0.45 0.00 0.23 0.42 0.40 3.11L2 1.04 0.24 0.01 0.11 0.48 0.23 2.12L3 0.15 0.22 0.01 0.04 0.42 0.19 1.04

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In summary, the extraction of lignin from the pretreatedbagasse by dilute NaOH solution enhanced sugar yield andproduced a lignin with higher purity and higher thermalstability but lower molecular weights than the lignins obtainedafter enzymatic hydrolysis and the fermentation/distillationprocess. Lignins recovered by sodium hydroxide treatmentfollowing enzymatic hydrolysis and fermentation/distillationhave lower contents of aliphatic hydroxyl, methoxyl, andketone/carbonyl, groups probably as a consequence ofdehydration. While there were no obvious differences in theproportions of monolignols, differences were observed in the

proportion of lignin substructures and linkages. The sodiumhydroxide treatment influences lignin composition (by theremoval of polysaccharides), but not its structure. All the solidresidues have been exposed to the same sodium hydroxidetreatment. Therefore, the differences in lignin structure aremore likely related to the effects of the enzymatic hydrolysisand the fermentation-distillation stages on the strength of thevarious lignin linkages. The weakening of the linkages by thetwo processing stages may have allowed the sodium hydroxidetreatment to be able to remove some of condensed phenolicOH (4-O-5′) groups. The slight increase in condensed

Figure 6. Pyrograms of the lignins.

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phenolic OH (5-5′) likely arose from the long-time exposure ofthe pretreated biomass to lower pH rather than the sodium

hydroxide lignin recovery process, as the latter process does notcause lignin condensation under the conditions used in thepresent study.Lignin recovered prior to enzymatic hydrolysis and

fermentation/distillation will be better suited for making resinsand coatings because of higher proportions of functionalgroups, which provide sites for avenues for improved chemicalreactivity. The pyrolysis data, and to a lesser extent the TGAdata, showed that the decomposition profiles of the lignins aresimilar, and bio-oils that will be derived by pyrolysis of thelignins will have similar compositions. What is not known iswhether the stability of these oils will be similar.

■ ASSOCIATED CONTENT*S Supporting InformationThe Supporting Information is available free of charge on theACS Publications website at DOI: 10.1021/acssusche-meng.6b01093.

Figures S1−S3 (PDF)

■ AUTHOR INFORMATIONCorresponding Authors*Postal address: GPO Box 2432, 2 George St, Brisbane, QLD4001, Australia. Tel.: +61 7 31387792. Fax: +61 7 3138 4132.E-mail: [email protected].*Postal address: GPO Box 2432, 2 George St, Brisbane, QLD4001, Australia. Tel.: +61 7 31381245. Fax: +61 7 3138 4132.E-mail: [email protected] authors declare no competing financial interest.

■ ACKNOWLEDGMENTSThis study was partly funded by the Australian Indian StrategicResearch Fund (AISRF) Grand Challenge Project(GCF020010). Jose Rio, Jorge Rencoret, and Ana Gutierrezwho conducted the analytical pyrolysis work were partiallyfunded by the Spanish projects AGL2014-53730-R andCTQ2014-60764-JIN (cofinanced by FEDER funds).

■ REFERENCES(1) O’Hara, I. M.; Zhang, Z.; Doherty, W. O.; Fellows, C. M.Lignocellulosics as a renewable feedstock for chemical industry:Chemical hydrolysis and pretreatment processes. Green Chemistry forEnvironmental Remediation 2012, 505−560.(2) Wettstein, S. G.; Alonso, D. M.; Gurbuz, E. I.; Dumesic, J. A. Aroadmap for conversion of lignocellulosic biomass to chemicals andfuels. Curr. Opin. Chem. Eng. 2012, 1 (3), 218−224.(3) Zhou, C. H.; Xia, X.; Lin, C. X.; Tong, D. S.; Beltramini, J.Catalytic conversion of lignocellulosic biomass to fine chemicals andfuels. Chem. Soc. Rev. 2011, 40 (11), 5588−5617.(4) Binder, J. B.; Raines, R. T. Simple Chemical Transformation ofLignocellulosic Biomass into Furans for Fuels and Chemicals. J. Am.Chem. Soc. 2009, 131 (5), 1979−1985.(5) Sun, J. X.; Sun, X. F.; Sun, R. C.; Fowler, P.; Baird, M. S.Inhomogeneities in the chemical structure of sugarcane bagasse lignin.J. Agric. Food Chem. 2003, 51 (23), 6719−6725.(6) Cardona, C. A.; Quintero, J. A.; Paz, I. C. Production ofbioethanol from sugarcane bagasse: Status and perspectives. Bioresour.Technol. 2010, 101 (13), 4754−4766.(7) Cerqueira, D. A.; Filho, G. R.; Meireles, C. D. Optimization ofsugarcane bagasse cellulose acetylation. Carbohydr. Polym. 2007, 69(3), 579−582.(8) Ferreira-Leitao, V.; Perrone, C. C.; Rodrigues, J.; Franke, A. P.M.; Macrelli, S.; Zacchi, G. An approach to the utilisation of CO2 as

Table 6. Phenolic Compounds of Lignins Obtained by Py-GC-MS

main compounds L1 L2 L3

1 phenol 2.6 3.2 3.12 guaiacol 5.7 6.2 6.13 3-methylphenol 0.5 0.5 0.54 4-methylphenol 2.6 2.85 2.85 4-methylguaiacol 6 5.1 5.26 4-ethyl phenol 2.4 2.2 2.37 4-ethylguaiacol 2 1.9 1.98 4-vinylphenol 20.5 22.7 22.39 4-vinylguaiacol 5.4 5.6 610 3-methoxycatechol 1.4 0.6 1.111 eugenol 0.5 0.5 0.512 4-propylguaiacol 0.2 0.2 0.213 4-allylphenol 0.2 0.3 0.214 syringol 10.5 10.9 11.515 cis-4-propenylphenol 0.2 0.2 0.216 cis-isoeugenol 0.6 0.7 0.617 trans-4-propenylphenol 0.6 0.7 0.718 trans-isoeugenol 2.4 2.4 2.319 4-methylsyringol 9.2 7.9 8.420 vanillin 1.4 1.3 1.121 homovanillin 0 0 022 4-ethylsyringol 2.5 2.6 2.723 vanillic acid methyl ester 0.4 0.5 0.424 acetovanillone 0.9 1 0.825 4-hydroxybenzaldehyde 0.4 0.4 0.426 4-vinylsyringol 4.6 4.6 4.227 guaiacylacetone 0.4 0.4 0.428 4-allylsyringol 0.9 0.9 0.929 4-propylsyringol 0.9 0.9 0.930 4-hydroxyacetophenone 0.2 0.2 0.231 cis-propenylsyringol 1.3 1.4 1.332 trans-propenylsyringol 4.4 4.4 4.533 syringaldehyde 2.1 1.5 134 dihydroconiferyl alcohol 0.1 0 0.135 homosyringaldehyde 0 0 036 syringic acid methyl ester 0.4 0.5 0.437 acetosyringone 2.5 2.3 2.138 trans-coniferyl alcohol 0.3 0.3 0.339 coniferaldehyde 0 0 040 syringylacetone 0.8 0.7 0.641 propiosyringone 0.4 0.3 0.342 ferulic acid methyl ester 0.3 0.3 0.343 syringyl vinyl ketone 0.3 0.2 0.244 p-coumaric acid methyl ester 0.3 0.5 0.445 syringic acid 0.6 0.2 0.346 dihydrosinapyl alcohol 0.2 0.1 0.247 trans-sinapyl alcohol 0.1 0.1 0.248 trans-sinapaldehyde 0 0 0

Table 7. Lignin Aromatic Units and S/G Ratio CalculatedBased on the Py-GC/MS Results

lignin aromatic units L1 L2 L3

S (%) 41.7 39.4 39.6G (%) 26.2 26.0 26.0H (%) 30.1 33.1 32.7S/G ratio 1.6 1.5 1.5

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