cuso4/h2o2-catalyzed lignin depolymerization under the

9
CuSO 4 /H 2 O 2 Catalyzed Lignin Depolymerization under the Irradiation of Microwaves Jinhuo Dai, Gavin N. Styles, Antonio F. Patti,* ,and Kei Saito* ,School of Chemistry, Monash University, Clayton Victoria 3800, Australia * S Supporting Information ABSTRACT: The increasing demand for renewable materials in the world has resulted in sustained eorts to utilize biomass in a better way. Lignin, a natural and abundant polymer in plants, has provided an ongoing challenge for many researchers seeking ways to better utilize this abundant resource. Here, we report a very ecient lignin depolymeriza- tion strategy with the assistant of microwave radiation. Copper sulphate (CuSO 4 ) and hydrogen peroxide (H 2 O 2 ) were used to generate hydroxyl radicals to depolymerize lignin under the irradiation of microwaves. Three dierent types of lignin, organosolv lignin, kraft lignin, and alkali lignin, were all successfully depolymerized using microwave irradiation at a temperature of 110 °C for 7 min. The use of 1 H/ 13 C two-dimensional nuclear magnetic resonance spectroscopy enabled the conrmation of structural changes, comparing before and after depolymerization. Liquid chromatographymass spectrometry was used to characterize the products. Both monomers and oligomers were detected after depolymerization. INTRODUCTION The increasing concern regarding the shortage of energy and the environmental pollution has led to the sustained research eort to investigate abundant, renewable, and cleaner materials to produce energy, fuels, or chemicals. 13 Biomass, a key building block of biofuels and composed largely of oxygen, carbon, and hydrogen, is one of the most competitive candidates. 46 Lignin, a well-known renewable material, is more popular because of the potential to be used as an abundant resource for the production of aromatics and related phenolic ne chemicals. 79 Lignin is a three-dimensional natural polymer with aromatic rings linked by several typical bonds, including β-O-4, α-O-4, 4-O-5, ββ, β-5, and β-1 bond (Scheme 1). 4,7,9,11 Several strategies have been established to isolate lignin from biomass, including the kraft process, sulfur-free alkali (soda) pulping, and organosolv processes, generally associated with paper manufacturing. 1114 Kraft pulping is the dominant pulping process over the world accounting for about 90% of the entire production capacity. 9,15 Paper mills use this method to isolate cellulose bers by dissolving lignin and hemicellulose in a solution of sodium sulte and sodium hydroxide. 7 Sulfur- free alkali (soda) pulping process takes up about 5% of entire pulp production. In this method, 1015% NaOH by weight, based on the raw material, is often used for the isolation of lower lignin content biomass from agricultural wastes. 9,13 The lignin removal rate compared to the kraft process is lower, however the lignin produced is essentially sulfur-free. 8 The presence of sulfur in lignin from the kraft process is potentially a barrier against the application of catalytical lignin depolymerization approaches because of the poisoning of the catalysts. 9,16 The organosolv process commonly involves using organic solvents such as alcohols (e.g., methanol and ethanol) and organic acids (e.g. formic acid and acetic acid). 4,17 Dierent lignin isolation processes normally produce lignin with various structures and also dierent contents of the typical linkages, as previously described. However, numerous papers have been published to establish pathways to degrade dierent Received: August 10, 2018 Accepted: August 17, 2018 Published: September 4, 2018 Scheme 1. Proposed Lignin Structure with Typical Bonds Article http://pubs.acs.org/journal/acsodf Cite This: ACS Omega 2018, 3, 10433-10441 © 2018 American Chemical Society 10433 DOI: 10.1021/acsomega.8b01978 ACS Omega 2018, 3, 1043310441 This is an open access article published under an ACS AuthorChoice License, which permits copying and redistribution of the article or any adaptations for non-commercial purposes. Downloaded via 130.194.146.43 on May 17, 2019 at 00:10:46 (UTC). See https://pubs.acs.org/sharingguidelines for options on how to legitimately share published articles.

Upload: others

Post on 19-Feb-2022

10 views

Category:

Documents


0 download

TRANSCRIPT

CuSO4/H2O2‑Catalyzed Lignin Depolymerization under theIrradiation of MicrowavesJinhuo Dai,‡ Gavin N. Styles,‡ Antonio F. Patti,*,‡ and Kei Saito*,‡

School of Chemistry, Monash University, Clayton Victoria 3800, Australia

*S Supporting Information

ABSTRACT: The increasing demand for renewable materialsin the world has resulted in sustained efforts to utilize biomassin a better way. Lignin, a natural and abundant polymer inplants, has provided an ongoing challenge for manyresearchers seeking ways to better utilize this abundantresource. Here, we report a very efficient lignin depolymeriza-tion strategy with the assistant of microwave radiation.Copper sulphate (CuSO4) and hydrogen peroxide (H2O2)were used to generate hydroxyl radicals to depolymerize ligninunder the irradiation of microwaves. Three different types oflignin, organosolv lignin, kraft lignin, and alkali lignin, were all successfully depolymerized using microwave irradiation at atemperature of 110 °C for 7 min. The use of 1H/13C two-dimensional nuclear magnetic resonance spectroscopy enabled theconfirmation of structural changes, comparing before and after depolymerization. Liquid chromatography−mass spectrometrywas used to characterize the products. Both monomers and oligomers were detected after depolymerization.

■ INTRODUCTION

The increasing concern regarding the shortage of energy andthe environmental pollution has led to the sustained researcheffort to investigate abundant, renewable, and cleaner materialsto produce energy, fuels, or chemicals.1−3 Biomass, a keybuilding block of biofuels and composed largely of oxygen,carbon, and hydrogen, is one of the most competitivecandidates.4−6 Lignin, a well-known renewable material, ismore popular because of the potential to be used as anabundant resource for the production of aromatics and relatedphenolic fine chemicals.7−9 Lignin is a three-dimensionalnatural polymer with aromatic rings linked by several typicalbonds, including β-O-4, α-O-4, 4-O-5, β−β, β-5, and β-1 bond(Scheme 1).4,7,9,11

Several strategies have been established to isolate lignin frombiomass, including the kraft process, sulfur-free alkali (soda)pulping, and organosolv processes, generally associated withpaper manufacturing.11−14 Kraft pulping is the dominantpulping process over the world accounting for about 90% ofthe entire production capacity.9,15 Paper mills use this methodto isolate cellulose fibers by dissolving lignin and hemicellulosein a solution of sodium sulfite and sodium hydroxide.7 Sulfur-free alkali (soda) pulping process takes up about 5% of entirepulp production. In this method, 10−15% NaOH by weight,based on the raw material, is often used for the isolation oflower lignin content biomass from agricultural wastes.9,13 Thelignin removal rate compared to the kraft process is lower,however the lignin produced is essentially sulfur-free.8 Thepresence of sulfur in lignin from the kraft process is potentiallya barrier against the application of catalytical lignindepolymerization approaches because of the poisoning of the

catalysts.9,16 The organosolv process commonly involves usingorganic solvents such as alcohols (e.g., methanol and ethanol)and organic acids (e.g. formic acid and acetic acid).4,17

Different lignin isolation processes normally produce ligninwith various structures and also different contents of the typicallinkages, as previously described. However, numerous papershave been published to establish pathways to degrade different

Received: August 10, 2018Accepted: August 17, 2018Published: September 4, 2018

Scheme 1. Proposed Lignin Structure with Typical Bonds

Article

http://pubs.acs.org/journal/acsodfCite This: ACS Omega 2018, 3, 10433−10441

© 2018 American Chemical Society 10433 DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

This is an open access article published under an ACS AuthorChoice License, which permitscopying and redistribution of the article or any adaptations for non-commercial purposes.

Dow

nloa

ded

via

130.

194.

146.

43 o

n M

ay 1

7, 2

019

at 0

0:10

:46

(UT

C).

Se

e ht

tps:

//pub

s.ac

s.or

g/sh

arin

ggui

delin

es f

or o

ptio

ns o

n ho

w to

legi

timat

ely

shar

e pu

blis

hed

artic

les.

types of lignin.7,11 Lignin catalytic cracking, hydrolysis,gasification, lignin reduction, and lignin oxidation are themost popular strategies to depolymerize lignin.7,18 Comparedto other methods, lignin reduction and oxidation methodsutilize milder conditions to degrade lignin, which can thus besuitable for the industry.19,20 Our group has previouslyreported several oxidative lignin depolymerization strat-egies21,22 and also reviewed the recent developments in thechemical degradation of lignin involving catalytic oxidation.23

Lignin catalytic oxidation methods normally show highselectivity in the products formed. It is an approach that isvery promising for generating highly functionalized oligomericand monomeric chemicals via lignin catalytic oxidation.10,23

For most of the lignin oxidation strategies, conventionalheating is required, however, using microwave irradiation isanother option.26 Gedye et al.24 compared oxidation resultsunder conventional heating conditions with those undermicrowave irradiation and concluded several advantages fromusing microwave irradiation. They concluded that microwaveheating is a highly efficient and potentially reaction-selectiveheating method. In some cases, the activation energies ofreactions are more readily achievable under microwaveirradiation. Polar materials can generate more free radicalscompared to conventional heating.24,25 Liu et al.27 developed amethod to depolymerize lignin with the assistance ofmicrowave irradiation in isopropyl alcohol without catalysts.About 45% of low-molecular-weight products were obtainedafter the reaction, which contains ethanone, 1-(4-hydroxy-3-methoxyphenyl) (1), and ethanone, 1-(4-hydroxy-3, 5-dimethoxy phenyl) (2) as the monomeric products (Scheme2).

Zhu et al.28 also reported the depolymerization of lignin withselective Cα−Cβ bond cleavage with a catalyst ferric sulfate andthe application of microwave irradiation. Lignin modelcompounds were utilized in these conditions. Their workdescribed microwave-assisted methylation of benzyl alcohols inthe lignin structure, which leads to lignin degradation andproduction of phenolic compounds from lignin.29 Wang et al.29

showed a pathway to depolymerize lignin using polyoxome-talate as a catalyst in 1-ethyl-3-methylimidazolium acetateunder microwave irradiation. Delignification was confirmedwith the generation of lower-molecular-weight phenolicproducts.It is well-known that copper catalyst is an excellent recipient

of quantitative oxidation.25,30,31 Widespread interest has led tothe development of copper catalyst systems for lignindegradation. Zhu et al.32 proposed a two-step lignindepolymerization strategy using a series of metal chloridesand metal sulphate salts, including CuCl2, CuSO4, FeCl3,MgSO4, and so forth. These salts were used as a catalyst forlignin methylation with methanol under the irradiation ofmicrowave first, and Pd/C was used for methylated lignin

hydrogenolysis for the cleavage of β-O-4 bonds afterward. Inthis case, the microwave and the copper catalysts were onlyused for the methylation step and not for the lignindegradation step. Pan et al.25 reported a microwave-assistedoxidation reaction of lignin model compounds with metal salts,including CuCl2, CrCl3, and MnCl2. In their study, these metalchloride salts were used together with H2O2 to oxidize ligninmodel compounds and not the real lignin. Goni andMontgomery30 presented a microwave digest system, withCuO as a catalyst, to depolymerize lignin at a temperature of150 °C for 90 min, which generated a large quantity ofphenolic compound from geochemical lignin samples.However, this process required 90 min to degrade lignin,where the reaction time was longer than other microwavereactions. A novel microwave-assisted copper catalyzed lignindegradation method which can proceed readily warrantsinvestigation.Compared to other copper complexes, copper salts, such as

CuSO4 and CuCl2, turn out to be an excellent competitorbecause of their good solubility in water, enabling water to beused as a reaction solvent.32−34 Additionally, these catalystscan be separated from the low molecular products and can bereused by a simple extraction after the depolymerizationreaction. Herein, we report the use of CuSO4 in combinationwith H2O2 as a catalyst to depolymerize lignin undermicrowave irradiation. The whole process was completedwithin 7 min at a temperature of 110 °C. Lignin wasdepolymerized with the production of oligomeric andmonomeric products. The method was shown to be widelyapplicable with three different types of lignin, includingorganosolv lignin, alkali lignin, and kraft lignin, all beingsuccessfully depolymerized. Two-dimensional nuclear mag-netic resonance (2D-NMR) spectroscopy was used to confirmthe cleavage of β-O-4 bonds, β−β bonds, and β-5 bonds afterthe reaction. Monomeric products, including vanillic acid, 4-hydroxybenzaldehyde, vanillin, syringaldehyde, 2-hydroxy-3-(4-hydroxyphenyl)propanal, 4-hydroxybenzoic acid, and 2-hydroxy-3-(4-hydroxy-3-methoxyphenyl)propanal were de-tected and characterized by the liquid chromatography−massspectrometry (LC−MS) technique.

■ RESULTS AND DISCUSSIONModel Microwave-Assisted Reactions with 1-Phenyl-

ethanol. In the beginning, 1-phenylethanol was used as amodel compound for this reaction to test the oxidation abilityof this microwave system. CuSO4 and H2O2 were chosen asthe catalyst in this system. The percentage conversion of thesecondary alcohol of 1-phenylethanol to a ketone wascalculated based on the 1H NMR results, which indicatedthe ratio of acetophenone to the products. The signal of theterminal methyl group was used as a reference and comparison,which appears as a doublet at 1.41 ppm for 1-phenylethanoland as a singlet at 2.59 ppm for acetophenone.35 From theresult, it was shown that the oxidation reaction only occurred ifH2O2 was present, and the conversion was enhanced by thepresence of CuSO4 (Supporting Information Table S1). Theconversion was only 10%, when an autoclave with heat wasused instead of microwave (Table S1, entry 5 in theSupporting Information). This also indicated that microwaveis necessary for accelerating the reaction (Figure 1).The optimization of reaction conditions was carried out at

the same time. For each part, only one parameter was changedcompared to the initial conditions. First, the effect of the

Scheme 2. Two Phenolic Products from LigninDepolymerization under Microwave Irradiation

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10434

dosages of CuSO4 and H2O2 were investigated. Figure 2 showsthe results of oxidation with different amounts of CuSO4 andH2O2. Figure 2a shows that with the increase of CuSO4 dosage,the conversion increased from about 26 to 66%. When theamount of CuSO4 increased beyond 13% of the molar amountof 1-phenylethanol, the conversion remained steady at around65%. This indicated that the dosage of CuSO4 could positivelypromote the oxidation reaction to generate more acetophe-none.The effect of the quantity of H2O2 used in the reaction was

also investigated. As the results show in Figure 2b, with theincrease of H2O2 dosage, the conversion increased from about13 to 66%. When the amount of H2O2 increased beyond 2.0 ×10−3 mL/mg to 1-phenylethanol, the conversion slightlydecreased to 60%. This indicated that the dosage of H2O2could also positively promote the oxidation reaction togenerate more acetophenone.In addition, the temperature and the reaction time were also

investigated. However, the temperature did not significantlyaffect the oxidation conversion. When the temperature wasincreased from 80 to 110 °C with other conditions keptconstant, the conversion showed no great difference (about 56and 58%, respectively). Similarly, the conversion to theproduct did not show a significant shift when the reactiontime was increased from 10 to 30 min.Microwave Reaction with Lignin. The optimized

reaction conditions established with the model compoundwere then applied to lignin. In this study, organosolv lignin,kraft lignin, and alkali lignin were selected to perform the lignindegradation reaction under microwave irradiation. These threelignin samples were treated with methanol to obtain amethanol-soluble part and a methanol-insoluble part to formthe lignin with narrow polydispersity to follow the depolyme-rization easily and effectively. Six lignin samples includingmethanol-insoluble organosolv lignin, methanol-soluble orga-nosolv lignin, methanol-insoluble kraft lignin, methanol-solublekraft lignin, methanol-insoluble alkali lignin, and methanol-soluble alkali lignin were obtained; the molecular weights andpolydispersity (D) of the six lignin samples are listed in Table1, entry 1.

All six types of lignin samples were subjected to microwavetreatments to effect depolymerization. For each reaction, theinitial reaction condition, 0.1 mass ratio of CuSO4 to lignin (5mg of CuSO4 to 50 mg of lignin) and 1 × 10−3 mL/mg ofH2O2 to lignin (0.5 mL of H2O2 to 50 mg of lignin) were usedto depolymerize lignin under microwave irradiation at thetemperature of 80 °C for 10 min. After reactions, the solventswere removed to give the depolymerized lignin products,which were characterized by size exclusion chromatography(SEC) to give the molecular weights (Figure S1−S3 in theSupporting Information).The results in Table 1, entry 2 suggest that this method can

apply and degrade different lignin types with ranges of differentmolecular weights and that the methanol pretreatment is notnecessary and does not require narrow polydispersity samplesas in other depolymerization techniques. Consequently,organosolv lignin, kraft lignin, and alkali lignin were subjecteddirectly without any pretreatment to the microwavedepolymerization method to investigate the depolymerizationability of the microwave system to original lignin samples.These three original lignin samples were analyzed by SEC andalso by 2D-NMR spectroscopy to show the differences in thestructure before and after microwave treatment (2D-NMRresults in Figure S7 in the Supporting Information). Thesethree types of lignin have overall molecular weights around Mn= 1500 with quite a high polydispersity.Table 2, entries 1 and 2, summarizes the molecular weight

and polydispersity of organosolv lignin, kraft lignin, and alkalilignin before and after the reactions using the initial reactioncondition as described above. The SEC chromatograms of themolecular weights of organosolv lignin, kraft lignin, and alkalilignin before and after the initial reactions are shown in FigureS4 in the Supporting Information.As the results show in Table 2, in entries 1 and 2, compared

to the original lignin samples, there was a significant molecularweight decrease and polydispersity increase of the threeoriginal lignin samples observed after the initial reaction. Afterthe reaction, ethyl acetate was used to extract the low-molecular-weight fractions from the product. Table 3summarizes the yield of ethyl acetate-soluble fraction beforeand after the initial reactions. The yield of the ethyl acetate-soluble fraction of the three samples all increased from lessthan 16% to more than 30% (Table 3, entries 1 and 2). Thisindicated that the all these three lignin samples weredepolymerized with the generation of low-molecular-weightfractions.

Figure 1. Oxidation reaction of 1-phenylethanol.

Figure 2. Effect of CuSO4 dosage on the oxidation of 1-phenylethanol.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10435

Condition Optimization of Lignin Depolymerization.Following the confirmation of lignin depolymerization, furtherwork to optimize the reaction conditions was undertaken tomaximize the yields of lower-molecular-weight fractions. In thiscase, alkali lignin, with higher molecular weight than the othertwo lignin samples, was used for optimizing the reactionconditions. As the reaction with 1-phenylethanol demon-strated, the dosages of CuSO4 and H2O2 can positively affect

the microwave reaction. On this basis, different dosages ofCuSO4 and H2O2 were used to degrade alkali lignin. After thereaction, ethyl acetate was used to extract the low-molecular-weight fractions from the reaction mixture. The SECchromatograms are listed in Figure 3.The effect of different levels of CuSO4 and H2O2 were

investigated separately. For each part, only one parameter wasinvestigated, compared to initial conditions. The dosage ofCuSO4 was calculated based on the mass ratio with lignin(Figure 3a). With the increasing dosage of CuSO4, the signalfrom SEC shown by the red dash line at lower retention timedecreased in intensity. This indicated that a higher molecularweight fraction was depolymerized with the increasing massratio of CuSO4 to lignin in the reaction mixture. Meanwhile,the intensity at a high retention time, which is marked by ablack dash line at 17−19 min, only shifted slightly. When themass ratio of CuSO4 increased from 0.14 to 0.18, the SECintensity marked by the red dash line decreased. When themass ratio of CuSO4 was increased more than 0.18, similarresults were obtained; hence the mass ratio of 0.18 CuSO4 tolignin was considered as the most efficient mass ratio for lignindegradation, for the conditions that were tested.The effect of varying the amount of H2O2 was also

investigated, with the results shown in Figure 3b. All reactionswere carried out with 0.1 mass ratio of CuSO4 to lignin at 80°C for 10 min. The dosage of H2O2 was calculated based onthe mass ratio with lignin. When the ratio of H2O2 (30 wt %)

Table 1. Molecular Weights of Lignin Samples (Methanol-Soluble and Methanol-Insoluble) before and after the Reaction

entry MIO MSO MIK MSK MIA MSA

1 Mn//D before the reaction 5600/3.6 1000/3.7 9000/5.2 5300/5.3 12 000/5.3 1000/3.82 Mn/D after the reaction 400/34.6 400/4.3 600/5.6 400/5.5 600/6.2 500/4.4

Table 2. Molecular Weights and Polydispersity of Ligninunder Different Conditions

entry conditionalkali lignin(Mn/D)

organosolv lignin(Mn/D)

kraft lignin(Mn/D)

1 original lignin 1500/5.9 1400/12.9 1500/7.72 after initial

condition600/2.6 600/2.6 650/2.4

3 after optimizedcondition

120/3.2 150/2.8 180/3.6

Table 3. Yield of Ethyl Acetate-Soluble Fraction for LigninSamples

entry conditionalkali lignin

(%)organosolvlignin (%)

kraft lignin(%)

1 original lignin 16 6.7 152 after initial condition 38 31 373 after optimised

condition52 54 48

Figure 3. SEC chromatograms of microwave degradation of alkali lignin under different conditions: (a) different CuSO4 dosages; (b) differentH2O2 dosages; and (c) different reaction times.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10436

to lignin was increased from 1.0 × 10−3 to 1.4 × 10−3 mL/mg,a shift in the molecular-weight distribution was observed,evidenced by the decrease in the intensity of the SEC signal inthe retention time region of 12.5−15 min. This provides strongevidence of the loss of high-molecular-weight material, and thecorresponding increase in the intensity of the signal in the 16−19 min region of the chromatogram was consistent with this.However, when the ratio of H2O2 to lignin increased from 1.4× 10−3 to 1.8 × 10−3 mL/mg, a shift in the molecular-weightdistribution to higher molecular weights was observed. Theintensity of the signal at the retention times marked by the reddash line increased while the signal intensity at the retentiontime marked by the black dash line increased. Interestingly, thepeak that appeared at 17.5−18 min with the ratio of 1.0 × 10−3

mL/mg H2O2 (marked with the black dashed line) shifted tolower retention times at higher H2O2 dosage. This indicatedthat the increasing ratio of H2O2 could certainly promote thedegradation reaction, however, when an excess amount ofH2O2 was added into the reaction, repolymerization of thesmaller fractions could occur. The reason can be that with theincreasing dosage of H2O2, more hydroxide radicals can begenerated, which could lead to repolymerization. Competitionbetween depolymerization and repolymerization has beenpreviously reported when radical reaction mechanisms areinvolved.21

The effect of time on the reaction of this system was alsostudied. All reactions were carried out with a 0.1 mass ratio ofCuSO4 to lignin and 1.0 × 10−3 mL/mg of H2O2 to lignin at80 °C. The depolymerized lignin products were extracted byethyl acetate to give about 40−50 wt % of products and wereanalyzed by SEC to give the results shown in Figure 3c. As thecurves showed, the SEC signal intensity marked by the reddash line, which is the depolymerized oligomer, increased withthe increase in the reaction time. Again, the strikingappearance of a signal intensity at ∼18 min retention timeand after 1 min of reaction time suggests rapid formation of alow-molecular-weight material. This steadily increased inintensity up to 7 min, but at 9 min, repolymerization wasagain evident as the intensity of this peak decreasedsignificantly. Thus, it was decided to stop the reaction at 7min to have the best depolymerization.The effect of temperature was also tested with 0.1 mass ratio

of CuSO4 to lignin and 1.0 × 10−3 mL/mg of H2O2 to ligninfor 10 min. The results show that higher temperature is betterfor depolymerization (Supporting Information, Figure S5),however, to keep the reaction mild, a reaction temperature of110 °C was set.In conclusion, the optimum conditions based on these

investigations for microwave-assisted lignin degradation werechosen as 0.18 mass ratio of CuSO4 to lignin and 1.4 × 10−3

mL/mg of H2O2 to lignin at the temperature of 110 °C for 7min. This condition was then applied for all three originallignin samples (Table 2). The SEC results of ethyl acetate-extracted products were compared with the initial conditions,which is shown in the Supporting Information (Figure S6).As the results show in Table 2, entry 3, all these three lignin

samples showed better depolymerization under the optimizedconditions chosen, compared to the initial conditions. Theoverall molecular weight of the ethyl acetate-extracted fractiondecreased from 600 g/mol to less than 200 g/mol. Moreover,the low-molecular-weight peak, which appeared at higherretention time, increased in intensity with the peaks at lowerretention time decreasing (Figure S6 in the SupportingInformation).The percentage of ethyl acetate-soluble fractions in different

lignin samples is listed in Table 3. After reaction, the yield ofethyl acetate-soluble fractions increased by more than 2 times.The reason is that the amount of small-molecular-weightfractions increased after microwave treatment because of thedepolymerization of lignin.Control reactions of this catalyst system for lignin

degradation were carried out with alkali lignin as the startingmaterial (summarized in Table S3 in the SupportingInformation). The yield of ethyl acetate fractions from thereaction without CuSO4 and H2O2 and also with only CuSO4or H2O2 was 15−18%, and there were no significant increasefrom the original lignin (15%). This indicated that both CuSO4and H2O2 are necessary for this reaction, which is alsoconsistent with our optimization condition results. A reactionusing an autoclave with heat was also used for this reactioninstead of the microwave, which only gave 20% yield of theethyl acetate-soluble fraction that was significant lower thanthe yield (52%) using microwave irradiation. The hypothesis isthat CuSO4 plays an important role as a catalyst to generatehydroxyl radicals from H2O2, and the irradiation of microwaveaccelerated the reaction, and these radicals degrade the ligninas previously reported.32

The ethyl acetate-soluble fractions, which yield about 50%,were analyzed by 2D-NMR spectroscopy to characterize themonomeric and oligomeric products. Figure 4 shows threetypical bonds detected by 2D-NMR spectroscopy. The 2D-NMR spectra of the alkali lignin and depolymerized alkalilignin are shown in Figure 5.Comparing Figure 5a,b, the 2D-NMR spectra after micro-

wave-assisted lignin depolymerization indicate that the β-O-4bonds, β−β bonds, and β-5 bonds were cleaved. The signalsfrom each bond, which existed in alkali lignin, disappearedafter depolymerization (the dash circle in Figure 5b). Thisindicated that this microwave-assisted strategy could efficientlydegrade lignin via cleaving these particular three bond types,

Figure 4. Different bonds in lignin detected by 2D-NMR spectroscopy.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10437

which leads to the generation of oligomeric and monomericproducts. Similar results were also obtained from kraft ligninand organosolv lignin (Supporting Information, Figure S7).LC−MS was used to analyze the extracted low molecular

products. The compounds detected are shown in Figure 6 and

the LC−MS chromatogram results are shown in Figure 7.From the LC−MS results, seven monomers have beendetected. These are vanillic acid (compound 1), 4-hydrox-ybenzaldehyde (compound 2), vanillin (compound 3),sy r inga ldehyde (compound 4) , 2 -hydroxy -3 -(4 -hydroxyphenyl)propanal (compound 5), 4-hydroxybenzoicacid (compound 6), and 2-hydroxy-3-(4-hydroxy-3-methoxyphenyl)propanal (compound 7).Figure 7 shows the LC chromatograms of three depoly-

merized lignin products. From these three lignin samples,vanillic acid (compound 1), 4-hydroxybenzaldehyde (com-pound 2), and vanillin (compound 3) were all generated incommon. This demonstrated that microwave irradiation wasvery effective in the production of these three monomers withmultiple types of lignin as feedstock. Moreover, depolymerizedkraft lignin and depolymerized organosolv lignin also showedthe presence of other aromatic monomers compared to thedepolymerized alkali lignin. These observations are consistentwith differences in the original structures of each lignin samplewith different contents of G units and S units. The wide broadpeaks after 36 min in all these three LC chromatograms wereassigned to dimeric or oligomeric products. The mass spectraare shown in the Supporting Information (Figures S8−S10).This one-pot catalyst system can degrade lignin into

monomeric and oligomeric products in 7 min with CuSO4/H2O2 as catalysts. MnCl2 and CuO, which have beenreported28,30 for lignin model compound degradation underthe irradiation of microwave, have been attempted and

compared with our catalyst under this condition. The yieldof the ethyl acetate-soluble fraction from alkali lignin usingMnCl2 and CuO were 41 and 43%, respectively, which wereless than our yield of 52%. These results indicate that ouroptimized condition has a potential to be used for othercatalyst systems. In addition, a milder reaction condition wasused in our system compared to other lignin degradationsystems reported using different copper catalysts.30,36

■ CONCLUSIONS

In this work, we presented a very efficient approach todepolymerize lignin with CuSO4 and H2O2 as catalysts undermicrowave irradiation conditions. These conditions candepolymerize different lignin samples into low-molecular-weight monomeric and oligomeric products at a temperatureof 110 °C for only 7 min with power of 80 W. Monomers, suchas vanillin, 4-hydroxybenzaldehyde, and vanillic acid weredetected and characterized in the products. The high efficiencyof this method showed the potential to utilize lignin for theproduction of valuable low-molecular-weight aromatics inindustrial applications.

■ EXPERIMENTAL SECTION (MATERIALS ANDMETHODS)

Materials. Organosolv lignin was purchased from ChemicalPoint. Kraft lignin was isolated from black liquor supplied byMaryvale Paper mill, by the method reported previously.22

Alkali lignin, CuSO4, and 30 wt % H2O2 solution werepurchased from Sigma-Aldrich Australia. Ethyl acetate,acetonitrile (ACN), dimethyl formamide (DMF), chloroform(CDCl3), dimethyl sulfoxide (DMSO-d6), and methanol werepurchased from Merck Australia. All reagents were used aspurchased from the supplier without any further purification.

Instruments and Measurements. CEM Discover SP-microwave synthesizer was used to perform all microwavereactions. 1H NMR spectra were recorded on a Bruker DRK-600 spectrometer operating at 600 MHz for solutions inCDCl3 and DMSO-d6. The molecular weight of isolated ligninand depolymerized samples were measured by SEC performedon a Tosoh EcosHLC-8320 system equipped with bothrefractive index and ultraviolet (UV) detectors (UV detection,λ = 280 nm) using Tosoh alpha 4000 and 2000 columns. DMF(with 10 mM LiBr) was used as a solvent to dissolve all ligninsamples as well as the mobile phase with a flow rate of 1.0 mL/min. UV detector in SEC chromatograms set at 280 nm wasused to analyze all depolymerized samples and isolated lignin.Calibration curves were obtained using polystyrene standards.LC−UV/MS was performed using an Agilent 1260 Infinityliquid chromatograph system coupled with a 6120 seriesquadrupole mass spectrometer. A column of Kinetex 5 μm C18100 Å Column (250 mm × 4.6 mm i.d.; particle size 5 μm)with two mobile phases A and B was applied. Mobile phase Aconsisted of water with 0.2% formic acid and mobile phase Bconsisted of 0.2% formic acid in ACN. The gradient programselected used a flow rate of 0.8 mL/min and an ambienttemperature. The gradient for analysis was as follows: 0 min,0% ACN; 30 min, 30% ACN; 45 min, 100% ACN; 51 min,100% ACN; 52 min, 0% ACN; and 56 min, 0% ACN. UVwavelengths: 210, 254, 260, 280, 320, and 378 nm; dataacquisition rate, 5 Hz. Data acquisition and processing wereperformed using Mass IQ (PerkinElmer), MS parameters:drying gas flow of 9.8 L/min, nebulizer pressure of 28 psi,

Figure 5. 2D-NMR spectra of alkali lignin and depolymerized alkalilignin.

Figure 6. LC−MS detected monomers from depolymerized ligninproducts.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10438

drying gas temperature of 300 °C, capillary voltage of 3000 V,and mass scan range of 100−900 Da with a cycle time of 1.57 sper cycle.Isolation of kraft lignin from black liquor was undertaken

according to the method we have previously reported.22

Elemental analysis of carbon, hydrogen, nitrogen, and sulfurgave the following result (average over three measurements):carbon 65.30%, hydrogen 6.07%, nitrogen <0.3% (detectionlimit), and sulfur 2.57%.Microwave-mediated oxidation of 1-phenylethanol with

copper sulfate involved using a 10 mL microwave reactorvial charged with 1-phenylethanol (0.05 mL, d = 1.013 g/mL,50 mg, 0.41 mmol), 2.5 mL of water, 2.5 mL of ACN, 5 mg(0.03 mmol) of copper sulfate, and 0.5 mL (30 wt % in H2O,0.15 g, 4.41 mmol) of H2O2, which was placed in themicrowave reactor and heated to 80 °C for 10 min with amaximum microwave power of 80 W. The resulting mixturewas then partitioned between water (30 mL) and ethyl acetate(2 × 20 mL). The combined organic layers were washed withsaturated brine (1 × 30 mL) and dried over anhydrousmagnesium sulfate. The solvent was removed in vacuo, and theproduct was then analyzed by 1H NMR spectroscopy todetermine the percentage conversion of secondary alcohol toketone.Isolation of the high-molecular-weight fraction of lignin was

undertaken using a solubility method reported before.21 Themolecular-weight distribution of the methanol-insolublefraction of lignin (M-lignin) was determined by SEC.

Microwave-Assisted Reaction with 1-Phenylethanol.Several reactions have been tested to optimize the reactionconditions. The typical reaction procedure is as follows: 1-phenylethanol (0.05 mL, d = 1.013 g/mL, 50 mg, 0.41 mmol),2.5 mL of water, 2.5 mL of ACN, 5 mg (0.03 mmol) of coppersulfate, and 0.5 mL (30 wt % in H2O, 0.15 g, 4.41 mmol) ofH2O2 were placed in the 10 mL vessel of a microwave reactorand heated to 80 °C for 10 min with a maximum microwavepower of 80 W. For each reaction, 0.41 mmol (50 mg, 0.05mL) 1-phenylethanol was used as the substrate, and the yieldof total recovered material was always around 90−95%.

Procedure for Microwave Oxidation of Lignin withCopper Sulfate. Several reactions have been tested tooptimize the reaction conditions. The typical reactionprocedure is as follows: A 10 mL microwave reactor vial wascharged with 50 mg of lignin, 2.5 mL of water, 2.5 mL of ACN,5 mg (0.03 mmol) of copper sulfate, and 0.5 mL (30 wt % inH2O, 0.15 g, 4.41 mmol) of H2O2. The vial was then placed inthe microwave reactor and heated to 80 °C for 10 min with amaximum microwave power of 80 W. The solvent was thenremoved; the remaining solid was dissolved in a 10 mmol/Lsolution of LiBr in DMF to give a concentration of 2 mg/mLof oxidation products; and the solution was analyzed by SEC.

■ ASSOCIATED CONTENT*S Supporting InformationThe Supporting Information is available free of charge on theACS Publications website at DOI: 10.1021/acsome-ga.8b01978.

Figure 7. Liquid chromatogram spectra of the extracted low-molecular-weight products from (a) depolymerized alkali lignin, (b) depolymerizedkraft lignin, and (c) depolymerized organosolv lignin.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10439

Results from the control reaction of 1-phenylethanol,ethyl acetate-soluble fraction yields of different ligninsamples, SEC and 2D-NMR analysis of original lignins,and LC−MS mass spectra of depolymerized products(PDF)

■ AUTHOR INFORMATIONCorresponding Authors*E-mail: [email protected]. Phone: +61(0)399051620(A.F.P.).*E-mail: [email protected]. Phone: +61(0)399054600(K.S.).ORCIDKei Saito: 0000-0002-5726-8775Author Contributions‡These authors contributed equally. The manuscript waswritten through contributions of all authors. All authors havegiven approval to the final version of the manuscript.NotesThe authors declare no competing financial interest.

■ ACKNOWLEDGMENTSThe financial support of the ARC Industrial TransformationResearch HubBioprocessing Advanced Manufacturing Ini-tiative (BAMI), Monash University, PRESTO JST,JPMJPR1515, Japan, and the China Scholarship Council(CSC) is gratefully acknowledged.

■ ABBREVIATIONSSEC, Size exclusion chromatography; LC−MS, liquidchromatography−mass spectrometry; 2D-NMR, two-dimen-sional nuclear magnetic resonance spectroscopy; MIA,methanol-insoluble alkali lignin; MSA, methanol-soluble alkalilignin; MIO, methanol-insoluble organosolv lignin; MSO,methanol-soluble organosolv lignin; MIK, methanol-insolublekraft lignin; MSK, methanol-soluble kraft lignin

■ REFERENCES(1) Pleßmann, G.; Erdmann, M.; Hlusiak, M.; Breyer, C. Globalenergy storage demand for a 100% renewable electricity supply.Energy Procedia 2014, 46, 22−31.(2) Edenhofer, O.; Pichs-Madruga, R.; Sokona, Y.; Seyboth, K.;Matschoss, P.; Kadner, S.; Zwickel, T.; Eickemeier, P.; Hansen, G.;Schlomer, S. IPCC Special Report on Renewable Energy Sources andClimate Change Mitigation. Prepared By Working Group III of theIntergovernmental Panel on Climate Change; Cambridge UniversityPress: Cambridge, UK, 2011 http://rael.berkeley.edu/old_drupal/node/762 (accessed Aug 2018).(3) Larcher, D.; Tarascon, J.-M. Towards greener and moresustainable batteries for electrical energy storage. Nat. Chem. 2015,7, 19−29.(4) Zakzeski, J.; Bruijnincx, P. C. A.; Jongerius, A. L.; Weckhuysen,B. M. The catalytic valorization of lignin for the production ofrenewable chemicals. Chem. Rev. 2010, 110, 3552−3599.(5) Sarkanen, K. V.; Ludwig, C. H. Lignins: Occurrence, Formation,Structure and Reactions; Sarkanen, K. V., Ludwig, C. H., Ed.; Wiley-Interscience: New York, 1971; Chapter xxv, pp 870−895.(6) Ma, R.; Xu, Y.; Zhang, X. Catalytic Oxidation of BiorefineryLignin to Value-added Chemicals to Support Sustainable BiofuelProduction. ChemSusChem 2015, 8, 24−51.(7) Pandey, M. P.; Kim, C. S. Lignin depolymerization andconversion: a review of thermochemical methods. Chem. Eng. Technol.2011, 34, 29−41.

(8) Upton, B. M.; Kasko, A. M. Strategies for the conversion oflignin to high-value polymeric materials: Review and perspective.Chem. Rev. 2015, 116, 2275−2306.(9) Chakar, F. S.; Ragauskas, A. J. Review of current and futuresoftwood kraft lignin process chemistry. Ind. Crops Prod. 2004, 20,131−141.(10) Grabber, J. H. How do lignin composition, structure, and cross-linking affect degradability? A review of cell wall model studies. CropSci. 2005, 45, 820−831.(11) Azadi, P.; Inderwildi, O. R.; Farnood, R.; King, D. A. Liquidfuels, hydrogen and chemicals from lignin: A critical review. RenewableSustainable Energy Rev. 2013, 21, 506−523.(12) Xu, C.; Arancon, R. A. D.; Labidi, J.; Luque, R. Lignindepolymerisation strategies: towards valuable chemicals and fuels.Chem. Soc. Rev. 2014, 43, 7485−7500.(13) Guerra, A.; Filpponen, I.; Lucia, L. A.; Saquing, C.;Baumberger, S.; Argyropoulos, D. S. Toward a better understandingof the lignin isolation process from wood. J. Agric. Food Chem. 2006,54, 5939−5947.(14) Guerra, A.; Filpponen, I.; Lucia, L. A.; Argyropoulos, D. S.Comparative evaluation of three lignin isolation protocols for variouswood species. J. Agric. Food Chem. 2006, 54, 9696−9705.(15) Obst, J. R.; Kirk, T. K. Isolation of lignin. Methods Enzymol.1988, 161, 3−12.(16) Sun, Y.-C.; Lin, Z.; Peng, W.-X.; Yuan, T.-Q.; Xu, F.; Wu, Y.-Q.;Yang, J.; Wang, Y.-S.; Sun, R.-C. Chemical changes of raw materialsand manufactured binderless boards during hot pressing: ligninisolation and characterization. BioResources 2014, 9, 1055−1071.(17) Thakur, V. K.; Thakur, M. K. Recent advances in greenhydrogels from lignin: a review. Int. J. Biol. Macromol. 2015, 72, 834−847.(18) Thakur, V. K.; Thakur, M. K.; Raghavan, P.; Kessler, M. R.Progress in green polymer composites from lignin for multifunctionalapplications: a review. ACS Sustainable Chem. Eng. 2014, 2, 1072−1092.(19) Amen-Chen, C.; Pakdel, H.; Roy, C. Production of monomericphenols by thermochemical conversion of biomass: a review.Bioresour. Technol. 2001, 79, 277−299.(20) Stark, K.; Taccardi, N.; Bosmann, A.; Wasserscheid, P.Oxidative depolymerization of lignin in ionic liquids. ChemSusChem2010, 3, 719−723.(21) Dai, J.; Nanayakkara, S.; Lamb, T. C.; Clark, A. J.; Guo, S.-X.;Zhang, J.; Patti, A. F.; Saito, K. Effect of the N-based ligands in coppercomplexes for depolymerisation of lignin. New J. Chem. 2016, 40,3511−3519.(22) Dai, J.; Patti, A. F.; Longe, L.; Garnier, G.; Saito, K. OxidizedLignin Depolymerization using Formate Ionic Liquid as Catalyst andSolvent. ChemCatChem 2017, 9, 2684−2690.(23) Dai, J.; Patti, A. F.; Saito, K. Recent developments in chemicaldegradation of lignin: catalytic oxidation and ionic liquids.Tetrahedron Lett. 2016, 57, 4945−4951.(24) Gedye, R. N.; Smith, F. E.; Westaway, K. C. The rapid synthesisof organic compounds in microwave ovens. Can. J. Chem. 1988, 66,17−26.(25) Pan, J.; Fu, J.; Lu, X. Microwave-assisted oxidative degradationof lignin model compounds with metal salts. Energy Fuels 2015, 29,4503−4509.(26) Badamali, S.; Luque, R.; Clark, J.; Breeden, S. Microwaveassisted oxidation of a lignin model phenolic monomer usingCo(salen)/SBA-15. Catal. Commun. 2009, 10, 1010−1013.(27) Liu, Q.; Li, P.; Liu, N.; Shen, D. Lignin depolymerization toaromatic monomers and oligomers in isopropanol assisted bymicrowave heating. Polym. Degrad. Stab. 2017, 135, 54−60.(28) Zhu, G.; Jin, D.; Zhao, L.; Ouyang, X.; Chen, C.; Qiu, X.Microwave-assisted selective cleavage of C α C β bond for lignindepolymerization. Fuel Process. Technol. 2017, 161, 155−161.(29) Wang, H.; Maxim, M. L.; Gurau, G.; Rogers, R. D. Microwave-assisted dissolution and delignification of wood in 1-ethyl-3-methylimidazolium acetate. Bioresour. Technol. 2013, 136, 739−742.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10440

(30) Goni, M. A.; Montgomery, S. Alkaline CuO oxidation with amicrowave digestion system: Lignin analyses of geochemical samples.Anal. Chem. 2000, 72, 3116−3121.(31) Gamez, P.; Arends, I. W. C. E.; Reedijk, J.; Sheldon, R. A.Copper(II)-catalysed aerobic oxidation of primary alcohols toaldehydes. Chem. Commun. 2003, 2414−2415.(32) Zhu, G.; Qiu, X.; Zhao, Y.; Qian, Y.; Pang, Y.; Ouyang, X.Depolymerization of lignin by microwave-assisted methylation ofbenzylic alcohols. Bioresour. Technol. 2016, 218, 718−722.(33) Villar, J. C.; Caperos, A.; García-Ochoa, F. Oxidation ofhardwood kraft-lignin to phenolic derivatives with oxygen as oxidant.Wood Sci. Technol. 2001, 35, 245−255.(34) Chaudhuri, P.; Hess, M.; Weyhermuller, T.; Wieghardt, K.Aerobic Oxidation of Primary Alcohols by a New Mononuclear CuII-Radical Catalyst. Angew. Chem., Int. Ed. 1999, 38, 1095−1098.(35) Abraham, R. J.; Mobli, M.; Smith, R. J. 1H chemical shifts inNMR: Part 19. Carbonyl anisotropies and steric effects in aromaticaldehydes and ketones. Magn. Reson. Chem. 2003, 41, 26−36.(36) Barta, K.; Ford, P. C. Catalytic Conversion of Nonfood WoodyBiomass Solids to Organic Liquids. Acc. Chem. Res. 2014, 47, 1503−1512.

ACS Omega Article

DOI: 10.1021/acsomega.8b01978ACS Omega 2018, 3, 10433−10441

10441