selective production of diethyl maleate via oxidative cleavage of … · 2019. 9. 18. · article...
TRANSCRIPT
Article
Selective Production of Diethyl Maleate viaOxidative Cleavage of Lignin Aromatic Unit
Zhenping Cai, Jinxing Long,
Yingwen Li, ..., Sijie Liu, Shik Chi
Edman Tsang, Xuehui Li
[email protected] (S.C.E.T.)
[email protected] (X.L.)
HIGHLIGHTS
Selective cleavage of lignin
aromatic unit into diethyl maleate
was achieved
A polyoxometalate ionic liquid
system was provided for lignin-
selective oxidation
556.7 mg g�1 volatiles were
obtained with 72.7% DEM
selectivity at optimized conditions
A five-coordinated Cu+ species is
the active center for lignin
aromatic ring cleavage
A highly efficient process for producing bulk chemical diethyl maleate is achieved
with polyoxometalate ionic liquids from a cleavage lignin aromatic unit with high
yield and selectivity, which is ascribed to the intensive synergistic effect between
the acidic depolymerization, oxidative aromatic ring cleavage, and in situ
esterification. This work offers new insight into the versatile petroleum-based
chemical production from renewable resources.
Cai et al., Chem 5, 2365–2377
September 12, 2019 ª 2019 Elsevier Inc.
https://doi.org/10.1016/j.chempr.2019.05.021
Article
Selective Production of Diethyl Maleatevia Oxidative Cleavageof Lignin Aromatic UnitZhenping Cai,1,5 Jinxing Long,1,5 Yingwen Li,1 Lin Ye,2 Biaolin Yin,1 Liam John France,1 Juncai Dong,3
Lirong Zheng,3 Hongyan He,4 Sijie Liu,1 Shik Chi Edman Tsang,2,* and Xuehui Li1,6,*
The Bigger Picture
As a major component of
biomass, lignin is regarded as an
ideal renewable feedstock for the
production of versatile chemicals.
However, because of its wide
structural diversity, currently
reported chemical conversions of
lignin hardly lead to high yields of
specific products, which
significantly limits the economic
efficiency of biomass process.
Here, we have designed a series of
polyoxometalate ionic liquid
(POM-IL) catalysts that combine
SUMMARY
Green production of bulk chemicals traditionally obtained from fossil resources
is of great importance. One potential route toward realizing this goal is through
the utilization of renewable lignin; however, current techniques generally lead
to low product specificity because of the structural diversity of this recalcitrant
biopolymer. Herein, we devised a new catalytic system to promote selectively
oxidative lignin in air, and diethyl maleate was formed at impressively high yield
of 404.8 mg g�1 and selectivity of 72.7% over the polyoxometalate ionic
liquid of [BSmim]CuPW12O40. This high catalytic activity is ascribed to a five-co-
ordinated Cu+ species, which, through the formation of end-on dioxygen
species in vacant orbitals, facilitates the selective oxidation of basic lignin aro-
matic units (phenylpropane C9 units). Therefore, these results represent signif-
icant progress toward the realization of an industrially applicable and highly
selective lignin oxidation process for the generation of value-added and bulk
chemicals.
the advantages of ionic liquid and
polyoxometalate with the
introduction of acidity, reduction-
oxidation, and miscibility
properties for lignin-selective
depolymerization. The bulk
chemical diethyl maleate is
generated as a single product with
an impressively high yield and
selectivity through controlled
oxidative cleavage of lignin
aromatic ring, suggesting that
lignin-selective oxidation would
be a promising method for diethyl
maleate production via a
sustainable route.
INTRODUCTION
Lignin, as a major component of lignocellulosic biomass (15%–30% by weight), is an
ideal renewable feedstock for the production of platform chemicals;1–4 this natural
polymer is a kind of high-volume ‘‘waste’’ in the pulp and paper industry and in mod-
ern bio-refinery processes.5,6 If converted to useful chemicals traditionally obtained
from fossil resources, it can bring huge benefits to the chemical industry and environ-
ment. However, the efficient utilization of lignin is a major challenge and has long
been recognized as a bottleneck in biomass valorization, mainly because of its com-
plex molecular structure and highly recalcitrant chemical nature.7,8 Typically, less
than 2% of lignin is currently utilized, andmost of it is directly burned for energy gen-
eration.9 To date, bench-scale depolymerization technologies, such as hydrogenol-
ysis, alcoholysis, pyrolysis, liquefaction, and oxidation, have been shown to trans-
form lignin into fine chemicals or biofuel.9,10 Furthermore, carboxylic acids,
including formic acid, acetic acid, and unsaturated dicarboxylic acids, have been ob-
tained from the oxidation of lignin and its model compounds.11 On the other hand,
development of these catalytic methods is severely limited by poor miscibility to
lignin, uncontrolled oxidation leading to a range of products, and the formation of
undesirable interunit C–C bonds, generating more complex intermediates. Shuai
et al. employed formaldehyde as a blocking group in lignin hydrogenolysis, conse-
quently reducing C–C bond formation tendency and resulting in improved mono-
phenol yield.12 Nevertheless, poor catalytic efficiency and product specificity render
the conversion of lignin to useful chemicals very difficult for industrial practice.
Chem 5, 2365–2377, September 12, 2019 ª 2019 Elsevier Inc. 2365
Polyoxometalate catalysts, known for their high redox activity and satisfactory oper-
ational stability, have been employed previously for delignification and transforma-
tion of lignin by breaking up its corresponding linkage bonds.13,14 For example,
Zhao et al. recently reported a novel polyoxometalate-mediated biomass fuel cell,
which could directly convert lignin to electricity with high power output and faradic
efficiency.15 However, the development of effective catalysts is still important for the
generation of value-added chemicals from lignin. As a novel catalyst, ionic liquid
shows uniform catalytic center and good reusability, and it has also shown impres-
sive performance in lignin conversion.3 Therefore, considering the combined advan-
tages of ionic liquid and polyoxometalate with the introduction of desirable acidity,
reduction-oxidation, and miscibility properties, we designed a series of polyoxome-
talate-ionic liquid catalysts (POM-ILs; Scheme 1) for the selective oxidative cleavage
of lignin basic aromatic units (phenylpropane units [C9 units]; the contents of the
lignin structural units are shown in Table S1) to produce diethyl maleate (DEM) in
ethanol. A typical result over the [BSmim]CuPW12O40 catalyst shows that 94.5% of
wheat stalk lignin is partially converted to 556.7 mg g�1 volatile liquid products,
of which 72.7% is composed of DEM. It is well known that DEM is an industrially
important chemical and widely used in the production of polymers, spices, and
pesticides.16 More importantly, it is a feasible biomass-derived platform chemical
for the production of maleic acid and its derivatives,17 which are high-value com-
modities in the petrochemical industry. DEM has been previously produced via a
two-step process, where benzene (derived from petroleum) is oxidized to maleic
anhydride and maleic acid and then esterified with ethanol (Scheme 1).18 Because
of rigid oxidation conditions and serious pollution, a butane-derived route (from
petroleum refinery) is used as an alternative, accounting for approximately
1.8 million tons/p.a.19 However, the heavy dependence of fossil resources, high
reaction temperature (673–723 K), and low process efficiency (70%–85% conversion
and 65%–70% selectivity of maleic anhydride)20 make this novel renewable
route competitive. Thus, the present process has a great potential in lignin valoriza-
tion and DEM production for replacement of the current petroleum-based
technology.
1School of Chemistry and Chemical Engineering,State Key Laboratory of Pulp & PaperEngineering, South China University ofTechnology, Guangzhou 510640, China
2Wolfson Catalysis, Inorganic ChemistryLaboratory, University of Oxford, Oxford OX13QR, UK
3Beijing Synchrotron Radiation Facility, Instituteof High Energy Physics, Chinese Academy ofSciences, Beijing 100049, China
4Beijing Key Laboratory of Ionic Liquids CleanProcess, Institute of Process Engineering,Chinese Academy of Sciences, Beijing 100190,China
5These authors contributed equally
6Lead Contact
*Correspondence:[email protected] (S.C.E.T.),[email protected] (X.L.)
https://doi.org/10.1016/j.chempr.2019.05.021
RESULTS AND DISCUSSION
Selective Oxidation Cleavage of Lignin Aromatic Unit
We began our study by using an organosolv bagasse lignin, a typical herbaceous
lignin containing all phenylpropane units (C9 unit) of p-coumaryl (H), coniferyl (G),
and sinapyl (S) alcohols. No products attributable to cleavage of the benzene ring
units were detected in the absence of catalyst (Table 1, entry 1). However, 48.2%
lignin was depolymerized, and products such as 4-hydroxybenzaldehyde and
vanillin were formed by aerobic oxidation (Table S9).21 A significant increase in lignin
depolymerization was found for the –SO3H-functionalized acidic ionic liquid,
[BSmim]HSO4, which as an acid is capable of catalyzing cleavage of ether bonds.22
However, only 6.5 and 15.9 mg g�1 DEM and C4 esters, respectively, were detected.
The C4 esters are consistent with cleavage of the benzene ring and were composed
largely of diethyl maleate, diethyl succinate, diethyl fumarate, and diethyl malate
(Table 1, entry 2; Figures S5 and S6; Tables S9 and S10). Lignin depolymerization
and volatile product yields were remarkably enhanced when POM-ILs ([BSmim]
MPW12O40, M=Na+, Mn2+, Co2+, Ni2+, and Cu2+) were used as catalysts (Tables 1
and S9). POM-ILs are composed of [BSmim]+ cations and [MPW12O40]� polyoxome-
talate anions, which form a reversible oxidant that facilitates the transfer of one
electron.23 For example, 81.3% bagasse lignin is depolymerized in the presence
of [BSmim]Na2PW12O40, producing a volatile liquid yield of 69.1 mg g�1, which
2366 Chem 5, 2365–2377, September 12, 2019
Scheme 1. The Novel Renewable Strategy from Lignin Oxidation (Green) versus the Petroleum-Based Process (Red) for DEM Production
POM-ILs: [BSmim]MPW12O40, where BS = –CH2CH2CH2CH2SO3H and M = Na, Mn, Co, Ni, and Cu (Figure S1; the catalyst structure and property
characterization results are shown in Figures S2–S4 and Tables S2–S8); the basic phenylpropane units (C9 units) of lignin are marked accordingly.
consists of 77.6% DEM (Table 1, entry 3; the conversion of lignin to model com-
pound, the product yield, and selectivity were calculated according to Supplemental
Equations 1–4 via gas chromatography excluding the oligomer fraction). It can be
seen that selective oxidative cleavage of aromatic units was significantly promoted
by replacement of Na+ with transition-metal ions such as Mn2+, Co2+, Ni2+, and Cu2+
(Table 1, entries 4–7). Overall, [BSmim]CuPW12O40 (Cu-POM-IL) showed the best
activity at 90.7% lignin depolymerization, 259.1 mg g�1 volatile product yield, and
59.3% DEM selectivity (Table 1, entry 7), suggesting that the transition-metal ion
plays a key role in this process. The above results clearly demonstrate the selective
nature of this novel process for DEM production, an observation that stands in
contrast to other lignin depolymerization technologies.10
To obtain the probable reason for this high activity of POM-IL, we conducted several
catalyst characterization techniques. As shown in Figures 1A and S3, X-ray diffraction
(XRD) clearly demonstrated the pattern with a space group of Pcca for the polyoxo-
metalate structure where the Mn+ can substitute into the octahedral W position. Our
synchrotron powder X-ray diffraction (PXRD) study also illustrated the high crystal-
linity and purity of all POM-IL catalysts prepared for this study. For the Cu-POM-IL
([BSmim]CuPW12O40) catalyst, the quality of the Le Bail refinement for synchrotron
PXRD data from Diamond Light Source (UK) was assured with a low goodness-of-
fit factor (gof), a low weighted profile factor, and a well-fitted pattern (Figure S3B).
The Le Bail refinement result clearly depicted that the common space group of
the POM had been altered from Pcca to Pncn (Cu-POM) as a result of the structural
distortion from the M substitution.24–26 The best fitting also suggested that there
were two groups of closely related unit cell parameters, presumably as a result of
a slight difference in the Cu-POM units packing (Tables S2 and S3). The unit cell
volumes were 4,856.1(1) A3 for Cu-POM1 and 3,068.1(1) A3 for Cu-POM2. The
distortion of the POM with the incorporation of Cu2+ ions can be appreciated via
the transformation matrix in WinGX with the input of the Le Bail profile refinement
data as the distorted Cu-POM1 unit (Figure 1A). The presentation of the full struc-
tural details in terms of atomic positions, connectivity, or coordination geometry is
also shown in Tables S2 and S3 by Rietveld refinement according to the initial model
Chem 5, 2365–2377, September 12, 2019 2367
Table 1. Selectively Catalytic Oxidation of Bagasse Lignin to DEM
Entry Catalysts Solventa Conversion (%) Yield of Volatile Product (mg g�1) Selectivity (%)d
DEM C4 Esterb Othersc Total DEM C4 Ester
1 –e 80:20 48.2 – – 14.7 14.7 0 0
2 [BSmim]HSO4 80:20 82.4 6.5 15.9 32.2 48.1 13.5 33.1
3 [BSmim]Na2PW12O40 80:20 81.3 53.6 59.8 9.3 69.1 77.6 86.5
4 [BSmim]MnPW12O40 80:20 80.9 87.7 107.6 22.7 130.3 67.3 82.6
5 [BSmim]CoPW12O40 80:20 80.6 93.3 105.6 40.9 146.5 63.7 72.1
6 [BSmim]NiPW12O40 80:20 84.3 100.4 116.0 50.3 166.3 60.4 69.8
7 [BSmim]CuPW12O40 80:20 90.7 153.6 176.2 82.9 259.1 59.3 68.0
8f [Bmim]CuPW12O40 80:20 80.8 11.0 16.7 29.5 46.2 23.8 36.1
9g H2SO4/CuSO4 80:20 86.8 16.5 20.8 53.7 74.5 22.1 27.9
10h [BSmim]Na2PW12O40/CuSO4
80:20 90.0 100.9 111.2 51.4 162.6 62.1 68.4
11i [BSmim]CuPW12O40 80:20 31.3 – – 78.6 78.6 0 0
12 [BSmim]CuPW12O40 100:0 92.9 274.7 310.9 87.5 398.4 69.0 78.0
13j [BSmim]CuPW12O40 40:60 100.0 152.9 495.7 – 495.7 30.8 100.0
14j [BSmim]CuPW12O40 80:20 100.0 416.3 488.9 – 488.9 85.1 100.0
15j [BSmim]CuPW12O40 100:0 100.0 1,111.5 1,111.5 – 1,111.5 100.0 100.0
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol catalyst, 20 mL ethanol-water mixture, 433 K, 5 h, 0.8 MPa O2.aVolume ratio of ethanol to water (v/v).bIncluding diethyl maleate, diethyl succinate, diethyl fumarate, and diethyl malate.cIn addition to C4 ester of volatile products.dThe selectivity of DEM is based on the volatile product determined by gas chromatography equipped with both a mass spectrometer and a flame ionization
detector.eNot added or detected.fThe yield of volatile product was obtained by esterification of lignin depolymerization product (after removal of original solvent) with ethanol at 373 K for 2.0 h by
adding 0.45 mmol H2SO4.g0.45 mmol H2SO4 with 0.9 mmol CuSO4.hAdding 0.9 mmol CuSO4.iUsing 0.8 MPa N2.j0.25 g maleic acid as substrate.
by Le Bail-WinGX. As seen from the refinement of Cu-POM-IL using the Rietveld
method, after putting the above two groups of the structure and adding some
free waters, we obtained the best fit with an acceptable R-weighted pattern (Rwp)
of 9.975, expected R (Rexp) of 6.605, and goodness of fit (gof) of 1.510. As a result,
the four original six-coordinated (6-CN) W/Cu as Keggin ion units were distorted to
form 5-CN W/Cu units in the general molecular formula (PW12O40)3�, the charge of
which was counter-balanced by [BSmim] cations. In addition, the Cu-POM anions
were inter-connected through the corner sharing of m-oxo ligands of the two 5-CN
W/Cu sites as a result of condensation. Similar m-oxo oligomers and polymers of
W- or V-based POM structures have been reported.27 It is important to establish
the superior activity and selectivity with the Cu incorporation into this new catalyst
system and to anticipate that the two remaining 5-CN Cu sites could be the active
sites that give vacant orbitals to take up the molecular oxygen as end-on species
on Cu sites to approach the distorted near 6-CN sites for this oxidation reaction.
Additionally, X-ray absorption spectroscopy (XAS) analysis (Figures 1B and 1C; Ta-
bles S4–S7) indeed showed that the oxidized Cu-POM gave a coordination number
(CN) of around 6. Figure 1D shows that the Cu2+ was in a distorted octahedral
environment with a CN of 5.6. This [BSmim]CuPW12O40 system displayed the
2368 Chem 5, 2365–2377, September 12, 2019
Figure 1. Structural Characterization of POM-IL
(A) The structure of Cu-POM was obtained by transforming the space group Pcca to Pncn with winGX software, which was based on the Le Bail profile
refinement data. The framework of Cu-POM uses the ball-stick mode (unit cell parameters are illustrated in Table S2).
(B) EXAFS and XANES analyses of POM-ILs.
(C) XANES analyses of [BSmim]CuPW12O40.
(D) Cu K-edge and W L3-edge XAS analysis of [BSmim]CuPW12O40.aN, coordination number; R, distance between absorber and backscatter atoms;
s2, Debye-Waller factor to account for both thermal and structural disorders; DE0, inner potential correction; R factor (%), goodness of fit. Error bounds
(accuracies) that characterize the structural parameters obtained by EXAFS spectroscopy were estimated as N G 20%, R G 1%, s2 G 20%, and DE0 G
20%. S02 were determined from CuO and WO3 standard fitting and fixed. Bold numbers indicate fixed N according to the crystal structure. O1, O2, and
O3 represent the first, second, and third nearest neighbor coordination O atoms. bFitting range: 2.5 % k (/A) % 12.5 and 1.6 % R (A) % 2.8.cFitting range: 2.5 % k (/A) % 12.5 and 1.0 % R (A) % 2.0. dCu K-edge fitting range: 2.9 % k (/A) % 12.5 and 1.0 % R (A) % 2.6; W L3-edge fitting
range: 2.5 % k (/A) % 14.5 and 1.0 % R (A) % 2.4.
largest degree of reduction among all POM-IL studied (Tables S4–S7) such that the
Cu CN dropped to 5 in H2 (reduced after H2 pre-treatment at 473 K to mimic the
Cu2+ reduction in organic media) and a characteristic Cu+ pre-edge peak arose
at � 8,984 eV and was attenuated in white line signal at � 8,996 eV in the X-ray
absorption near-edge structure (XANES) analysis (Figures 1A, 1C, and S4). The
reduction can create vacant orbitals to facilitate the formation of dioxygen activation
from oxygen on activated ‘‘Cu’’ in the reduced structure, as previously discussed.
Cu-substituted heteropolyoxometalates havemany similarities to active Cu enzymes
for O2 transport and oxidation developed in biological systems because they
possess coordination sites surrounding an isolated Cu. End-on Cu dioxygen adducts
as ‘‘superoxo’’ complexes have been proposed as reactive but selective intermedi-
ates in the catalytic cycle of mononuclear Cu enzymes, such as peptidylglycine
a-hydroxylating monooxygenase (PHM) or dopamine b-monooxygenase (DbH).28
Indeed, the existence of such a species could be demonstrated by X-ray crystallog-
raphy for a precatalytic PHM complex.29We believe that a similar superoxo is formed
over the reduced Cu+ in polyoxometalate in oxygen, which selectively oxidizes the
specific linkages of lignin to give DEM in the catalytic process.
Chem 5, 2365–2377, September 12, 2019 2369
As shown in Table 1, it is obvious that the lignin transformation remarkably declined
when the ionic liquid [Bmim]CuPW12O40 was used without the sulfonic group (Ta-
ble 1, entry 8), giving lower lignin conversion (80.8%), volatile product yield
(46.2 mg g�1), and DEM selectivity (23.8%) than Cu-POM-IL (Table 1, entry 7), which
demonstrated the importance of acidic functionality for the formation of DEM. Con-
trol experiments employing a H2SO4-CuSO4mixture (Table 1, entry 9) revealed a low
DEM selectivity (22.1%), indicating that polyoxometalate framework and ionic liquid
moiety also play important roles in the process. Interestingly, when CuSO4 and
[BSmim]Na2PW12O40 were combined, the yield of volatile products and DEM was
significantly lower than that of Cu-POM-IL (Table 1, entry 10 versus 7). However,
comparison of the former with [BSmim]Na2PW12O40 revealed an obvious enhance-
ment (Table 1, entry 10 versus 3). It is plausible that this effect may have arisen as
a result of a degree of in situ Cu-POM-IL formation, which is caused by the exchange
of Na+ with Cu2+. It should be noted that in the absence of oxygen, lignin depoly-
merization was notably low (Table 1, entry 11) and exhibited an aromatic product
distribution akin to the acid-catalyzed process (Table S9, entry 11). Moreover,
when POM-IL was added, the weight-average molecular weight (Mw) and number-
average molecular weight (Mn) of regenerated lignin (Table S9) were significantly
smaller than those of bagasse lignin, demonstrating that lignin is depolymerized
via an oxidative process. We can therefore conclude that promoted lignin depoly-
merization, coupled with selective formation of DEM, arises as a result of an efficient
synergistic effect between acidic functionality and transition-metal ions and
improved miscibility between polyoxometalate and lignin rather than any single
factor.
Detailed investigation about the dosage of Cu-POM-IL content, reaction tempera-
ture, and time for oxidative cleavage of lignin to DEM were also evaluated (Figures
S7–S9). The Cu-POM-IL catalyst showed characteristic temperature-controlled parti-
tion and recyclability (Figure S1) such that it was miscible with the reaction mixture at
elevated temperature and precipitated at room temperature,30 and no significant
activity loss was exhibited after six consecutive runs (Figure S10). Furthermore, the
effect of ethanol concentration—whereby the DEM yield and selectivity increased
as ethanol concentrations increased (Table 1, entry 12; Table S11, entries 1–6) until
they reached a maximum of 274.7 mg g�1 and 69.0% selectivity, respectively, in
100% ethanol—seemed to be critical. These findings support the idea that the pri-
mary product, maleic acid, undergoes rapid solvent-mediated reactions to produce
the desired product DEM. To convincingly demonstrate the validity of this effect, we
evaluated the reaction of maleic acid in ethanol-water mixtures. As shown in Tables 1
and S11, DEM selectivity reached 100% only in the presence of pure ethanol.
Lowering the ethanol concentration coincided with the formation of diethyl fumarate
and diethyl malate, which were obviously generated from the isomerization and
hydration of maleic acid, respectively (Table S11, entries 7–9). Therefore, this in
situ esterification process inhibits side reactions during the conversion of the inter-
mediate maleic acid, which could explain the high selectivity of DEM in the volatile
products.
In addition, we measured the carbon balance and the C9 unit utilization efficiency of
the optimized reaction, which are generally key factors for lignin depolymerization
according to elemental analysis (Table S12).9,10 As shown in Figure 2, under the opti-
mized conditions (433 K for 5 h), 18.1% of the lignin carbon, including 12.9% of DEM
(Figure 2B), was converted to volatile products (Figure 2A). However, 56.4 % of lignin
carbon was transformed into phenolic oligomers (Figure 2A), which is still recog-
nized as a big challenge during lignin valorization because of its robust interunit
2370 Chem 5, 2365–2377, September 12, 2019
Figure 2. Process Efficiency of Lignin Oxidation Catalyzed by [BSmim]CuPW12O40
(A) Carbon balance of process (a).
(B) Volatile products from processes (a) and (b). Reaction conditions of process (a): 0.25 g bagasse
lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 100% ethanol, 433 K, 5 h, 0.8 MPa O2. Process (b) was
purged by an extra 0.8 MPa oxygen when reaction (a) was cooled to room temperature and then
heated to 433 K for another 2 h. Detailed calculation procedures can be found in Supplemental
Equations 5–10.
linkage.3,31 Interestingly, DEM production increased notably (from 274.7 to
522.3 mg g�1) when the reaction mixture was refilled with pure oxygen and reheated
for 2 h (Table S13, entries 1 and 4, respectively). Relatively, the carbon yield of DEM
from lignin substantially increased from 12.9% to 24.5% with extra oxygen presence.
The C9-unit-utilization efficiency further illustrates that the converted lignin basic
structure unit for DEM changed from 29.0% to 55.0% with a turnover number
(TON) of 0.84 at the optimized condition and with extra 0.8 MPa oxygen (Figure 2B).
It is noteworthy that both carbon-utilization efficiencies to a single chemical were
much higher than those of other lignin- conversion processes.3,10,31 Furthermore,
the adjustment of oxygen concentration (0.8 and 0.2 MPa for O2 and N2, respec-
tively) still converted 94.2% lignin and yielded 348.6mg g�1 DEM (71.7% selectivity),
showing minor variation from the established result (Table S13, entry 5 versus 1).
Moreover, the gaseous fraction exhibited a corresponding decrease in oxygen con-
tent after the oxidation reaction (Tables S14 and S15). Therefore, lignin carbon is well
utilized in this POM-IL catalytic system, implying that it may have significant poten-
tial in lignin valorization processes.
The adaptability of this POM-IL catalytic systemwas also checkedwith a series of typical
feedstocks, such as rice stalk lignin, pine lignin, corn stalk lignin, wheat stalk lignin, and
dealkaline lignin (Figure 3A; Tables S16 and S17). All types of lignin were efficiently con-
verted, producing both high yield and selectivity of DEM. In particular, the wheat stalk
lignin exhibited the highest yield of volatile products (556.7 mg g�1) with a high DEM
yield (404.8 mg g�1) and selectivity (72.7%), which clearly depicts an alternative to
the current butane-to-DEM technology.32 Moreover, the catalytic efficiency found
with the dealkaline lignin feedstock (Figure 3A) indicates that our technology is also
applicable to byproducts generated by the paper and pulp industry.
The Evolution of Lignin Structure during the Process
We examined the evolution of the lignin structure by comparing heteronuclear
single quantum correlation (HSQC) spectra of the original and regenerated lignin.
As shown in the aromatic regions (Figure 3B), typical basal structure units consisting
of methoxylated phenylpropanoid (syringyl [S] and guaiacyl [G]) subunits linked by
b–O–4 (b-aryl ether) bonds33 in the original lignin disappeared completely after
the reaction, implying that S and G units are more flexible than the H unit for this
lignin oxidative cleavage process catalyzed by POM-ILs. This result is inconsistent
Chem 5, 2365–2377, September 12, 2019 2371
Figure 3. Feedstock Adaptability and Lignin Structural Evolution
(A) Oxidative cleavage of lignin from various resources. Errors bars represent the mean G SEM.
(B) HSQC spectra of original and regenerated bagasse lignin.
(C) FT-IR spectra of original and regenerated bagasse lignin.
Reaction condition: 0.25 g lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 100% ethanol, 433 K, 5 h, 0.8 MPa O2.
with previous studies showing that H is more active than G and S units in lignin mole-
cule cleavage,22,34 indicating a different pathway for lignin conversion with POM-ILs.
In addition, we also noticed that a small fraction of ketone S0 and G033 was present inthe regenerated lignin. This could also be observed in the aliphatic regions, where
the signals of branched chains disappeared as the ketone structure arose (Figure 3B).
Fourier transform infrared spectroscopy (FT-IR) demonstrated lower band intensity
for the condensed S-G unit (1,327 cm�1) and typical S unit (1,327 and
1,129 cm�1)35 in regenerated lignin than for those in original lignin (Figure 3C; Table
S18). However, two strong modes ca. 1,087 and 988 cm�1 appeared after the reac-
tion and are characteristic of C=O and C–O, respectively,36 verifying the formation
of ketonic G0 and S0 units. Additionally, 13C nuclear magnetic resonance (13C NMR)
analysis showed that the signals of 152.73, 130.74, 115.52, and 56.28 ppm, repre-
senting typical H, G, and S lignin units and –OCH3, respectively,37 were significantly
2372 Chem 5, 2365–2377, September 12, 2019
weakened in the regenerated lignin samples, clearly demonstrating the efficient
lignin depolymerization, and the appearance of peak at 191.64 ppm indicates the
formation of aromatic ketone (such as G0 and S0) during the process. In particular,
the significantly declined signal at 56.28 ppm confirms that regenerated lignin con-
tains fewer G and S units than original lignin, further verifying that the H unit exhibits
the lowest reactivity in this process (Figure S11).
Selective Oxidation of Model Compound from Lignin Depolymerization
To gain further insight into the selectively oxidative cleavage of the lignin aromatic
unit to DEM, we employed a series of phenol, guaiacol, syringol, and their deriva-
tives, the most representative chemicals from lignin depolymerization,3,38 as model
compounds. Interestingly, most model compounds could be efficiently converted
and exhibited relatively high yield and selectivity to DEM (Figure 4; Table S19).
However, the oxidative aromatic ring cleavage performances of these chemicals
were dependent remarkably upon their substituent groups. For instance, phenol
(1) produced 251.8 mg g�1 of volatile products containing 176.7 mg g�1 DEM (Fig-
ure 4); however, the addition of another hydroxyl group in either the ortho or para
position (model compounds 2 and 3) caused a significant increase in DEM yield
(442.4 or 446.5 mg g�1, respectively). This effect can be ascribed to the favorability
of catechol- and hydroquinol-forming benzoquinone, an intermediate of phenol
oxidation and a key startingmaterial for maleic acid generation.39 Figure 4 also dem-
onstrates that oxidative ring cleavage of the phenolic monomer was enhanced when
–OCH3 was substituted at the ortho position (guaiacols 4 and syringols 5). For
example, the yields of total volatile products and DEM increased from 251.8 �1
and 176.7 mg g�1 to 321.6 �1 and 205.2 mg g�1, respectively, when phenol was re-
placed by guaiacol. This improvement was more evident when syringol was used,
which gave yields of 388.1 and 257.3 mg g�1 for volatile products and DEM, respec-
tively. These findings indicate that the depolymerization products from the G and S
lignin units are more likely to produce larger quantities of DEM than H units.
In general, the charge density of the aromatic ring is enhanced by electron-
donating substituents (such as ethyl and methoxyl groups) and weakened by elec-
tron-withdrawing substituents (such as aldehyde and carboxyl groups).40 Hence,
the reactivity of the aromatic ring and the product regioselectivity are influenced
by the nature of the substituents in homogeneous reactions.33,40 Here, higher
charge density facilitated the oxidation of the aromatic ring,41 resulting in higher
DEM yield (6–8). For example, an electron-donating methoxyl group in the ortho
position of 4-ethyl phenol (6) elevated both total product yield (from 336.7 to
502.4 mg g�1) and DEM selectivity (from 67.8% to 73.3%; Table S19, entry 6
versus 7). On the contrary, phenolic monomers with electron-withdrawing substit-
uents weakened the electron density of the aromatic ring, which reduced oxida-
tive ring cleavage activity (9–13). Typically, aldehyde functionalities exhibit a
stronger electron-withdrawing effect than carboxyl groups.11 However, 4-hydrox-
ybenzaldehyde (14), vanillin (15), and syringe aldehyde (16) were more readily
activated than their corresponding acids (Figure 4, model compounds 9–11), es-
ters (Figure 4, model compounds 12 and 13), and monolignols (Figure 4, phenol
1, guaiacol 4, and syringol 5), yielding significantly increased DEM. In this reac-
tion, the aldehyde condensed quickly with ethanol, which was readily catalyzed
by the acidic functionality of the catalyst. Therefore, the electron-withdrawing
group, C=O, was transformed into an electron-donating group, –OC2H5 (this ace-
talization process could be verified in the absence of O2), which resulted in
enhanced C–C bond cleavage of the aromatic ring. These trends were further re-
flected by 4-hydroxylbenzaldehyde (14) and its corresponding acetal (8), such that
Chem 5, 2365–2377, September 12, 2019 2373
Figure 4. Catalytic Oxidation of Lignin Model Compounds into DEM
acetal compound 8 produced a larger DEM yield. Thus, the results about the se-
lective oxidative ring cleavage of model chemicals clearly illustrate that the lignin
structure with more electron-donating groups (such as –OCH3) is much more
2374 Chem 5, 2365–2377, September 12, 2019
easily converted. Namely, G and S, the most predominant structure units in
lignin,10 were more reactive than H, which accords well with the comparative
characterization results of the lignin structure evolution. This result was further
confirmed by the conversion of several H-type dimers with typical linkages,
such as 4–O–5, a–O–4, 5–5, and b–1. Table S19 shows that the cleavages of
C–O bonds, such as 4–O–5 and a–O–4, were effectively carried out but that
less DEM was generated. In comparison with the high reactivity of the C–O
bond, that of C–C bond remained insignificant because of its relatively higher
activation energy.3 On the basis of the discussion above, we proposed a plau-
sible pathway for lignin depolymerization and in situ oxidative ring cleavage (Fig-
ure S12), which we further verified by using controlled reactions with several qui-
nones as model compounds (Table S20).
In summary, we have achieved a highly efficient and selective process for the pro-
duction of DEM, an important, versatile, and widely used bulk chemical currently
derived from fossil fuel, by using POM-IL catalysts. Under optimized conditions,
94.5% wheat stalk lignin was oxidized, producing 556.7 mg g�1 of volatile products
and a DEM selectivity of 72.7% over [BSmim]CuPW12O40. The presence of a syner-
gistic effect attributable to acidic functionality and selective superoxo species (the
latter of which was formed by the Cu-containing polyoxometalate) could explain
the observed improvement. Furthermore, the solvent of ethanol also showed an
intensification effect on DEM production via the in situ esterification with the formed
maleic acid. Moreover, this process is highly feedstock adaptable for the depolymer-
ization of many typical lignin sources and has the substantial advantage of facile
catalyst separation and recycling. Therefore, we have demonstrated that the present
process has great potential in lignin valorization and sustainable DEM production
because of its high process efficiency and DEM selectivity.
EXPERIMENTAL PROCEDURES
Full experimental procedures are provided in the Supplemental Information.
SUPPLEMENTAL INFORMATION
Supplemental Information can be found online at https://doi.org/10.1016/j.chempr.
2019.05.021.
ACKNOWLEDGMENTS
The financial support of the Natural Science Foundation of China (21736003,
21336002, 21690083, 21878111, 21676108, and 11605225), the Science and Tech-
nology Program of Guangzhou, China (201804020014), and the Fundamental
Research Funds for the Central Universities (SCUT) is gratefully acknowledged. Ac-
cess to beamline I11 of Diamond Light Source (UK) for the SXRD characterization
is also acknowledged. The authors would like to thank Wenxing Chen of Tsinghua
University (China) for helping with sample preparation.
AUTHOR CONTRIBUTIONS
C.Z.P., L.J.X., and L.X.H. designed the catalysts and experiments; C.Z.P., L.Y.W.,
L.J.F., and L.S.J. synthesized and characterized the catalysts and conducted the ex-
periments; S.C.E.T. performed the PXRD and XAS characterization and analysis with
help from Y.L, D.J.C., and Z.L.R.; C.Z.P., L.J.X., L.J.F., and L.X.H. analyzed the data
and wrote the manuscript with help from S.C.E.T.; Y.L., D.J.C., Z.L.R., Y.B.L., and
H.H.Y. contributed to catalyst characterization and product determination; and all
authors participated in data analyses and discussions.
Chem 5, 2365–2377, September 12, 2019 2375
DECLARATION OF INTERESTS
The authors declare no competing interests.
Received: November 20, 2018
Revised: February 19, 2019
Accepted: May 28, 2019
Published: June 17, 2019
REFERENCES AND NOTES
1. Ragauskas, A.J., Beckham, G.T., Biddy, M.J.,Chandra, R., Chen, F., Davis, M.F., Davison,B.H., Dixon, R.A., Gilna, P., Keller, M., et al.(2014). Lignin valorization: improving ligninprocessing in the biorefinery. Science 344,1246843.
2. Rahimi, A., Ulbrich, A., Coon, J.J., and Stahl,S.S. (2014). Formic-acid-induceddepolymerization of oxidized lignin toaromatics. Nature 515, 249–252.
3. Sun, Z., Fridrich, B., de Santi, A.d., Elangovan,S., and Barta, K. (2018). Bright side of lignindepolymerization: toward new plattformchemicals. Chem. Rev. 118, 614–678.
4. Wu, L., Moteki, T., Gokhale, A.A., Flaherty,D.W., and Toste, F.D. (2016). Production offuels and chemicals from biomass:condensation reactions and beyond. Chem 1,32–58.
5. Son, S., and Toste, F.D. (2010). Non-oxidativevanadium-catalyzed C-O bond cleavage:application to degradation of lignin modelcompounds. Angew. Chem. Int. Ed. 49, 3791–3794.
6. Lan, W., Amiri, M.T., Hunston, C.M., andLuterbacher, J.S. (2018). Protection groupeffects during a, g-diol lignin stabilizationpromote high selectivity monomer production.Angew. Chem. Int. Ed. 57, 1356–1360.
7. Corma, A., Iborra, S., and Velty, A. (2007).Chemicals routes for the transformation ofbiomass into chemicals. Chem. Rev. 107, 2411–2502.
8. Guo, H., Zhang, B., Qi, Z., Li, C., Ji, J., Dai, T.,Wang, A., and Zhang, T. (2017). Valorization oflignin to simple phenolic compounds overtungsten carbide: impact of lignin structure.ChemSusChem 10, 523–532.
9. Sun, Z., Fridrich, B., de Santi, A., Elangovan,S., and Barta, K. (2018). Bright side oflignin depolymerization: toward newplatform chemicals. Chem. Rev. 118,614–678.
10. Li, C., Zhao, X., Wang, A., Huber, G.W., andZhang, T. (2015). Catalytic transformation oflignin for the production of chemicals and fuels.Chem. Rev. 115, 11559–11624.
11. Suzuki, H., Cao, J., Jin, F., Kishita, A.,Enomoto, H., and Moriya, T. (2006). Wetoxidation of lignin model compounds andacetic acid production. J. Mater. Sci. 41,1591–1597.
12. Shuai, L., Amiri, M.T., Questell-Santiago,Y.M., Heroguel, F., Li, Y., Kim, H., Meilan, R.,Chapple, C., Ralph, J., and Luterbacher, J.S.
2376 Chem 5, 2365–2377, September 12, 2019
(2016). Formaldehyde stabilizationfacilitates lignin monomer production duringbiomass depolymerization. Science 354,329–333.
13. Sun, N., Jiang, X., Maxim, M.L., Metlen, A.,and Rogers, R.D. (2011). Use ofpolyoxometalate catalysts in ionic liquidsto enhance the dissolution anddelignification of woody biomass.ChemSusChem 4, 65–73.
14. Wang, M., Ma, J., Liu, H., Luo, N., Zhao, Z., andWang, F. (2018). Sustainable productions oforganic acids and their derivatives frombiomass via selective oxidative cleavage of C-Cbond. ACS Catal 8, 2129–2165.
15. Zhao, X.B., and Zhu, J.Y. (2016). Efficientconversion of lignin to electricity using a noveldirect biomass fuel cell mediated bypolyoxometalates at low temperatures.ChemSusChem 9, 197–207.
16. Yadav, G.D., and Thathagar, M.B. (2002).Esterification of maleic acid with ethanol overcation-exchange resin catalysts. React. Funct.Polym 52, 99–110.
17. Bernasconi, M., Muller, M.A., and Pfaltz, A.(2014). Asymmetric hydrogenation of maleicacid diesters and anhydrides. Angew. Chem.Int. Ed. 53, 5385–5388.
18. Coulston, G.W., Bare, S.R., Kung, H., Birkeland,K., Bethke, G.K., Harlow, R., Herron, N., andLee, P.L. (1997). The kinetic significance of V5+
in n-butane oxidation catalyzed by vanadiumphosphates. Science 275, 191–193.
19. Dodds, D.R., and Gross, R.A. (2007). Chemistry.Chemicals from biomass. Science 318, 1250–1251.
20. Centi, G., Trifiro, F., Ebner, J.R., and Franchetti,V.M. (1988). Methanistic aspects of maleicanhydride synthesis fromC4 hydrocarbons overphosphorus vanadium oxide. Chem. Rev. 88,55–80.
21. Ma, R., Xu, Y., and Zhang, X. (2015). Catalyticoxidation of biorefinery lignin to value-addedchemicals to support sustainable biofuelproduction. ChemSusChem 8, 24–51.
22. Cai, Z., Li, Y., He, H., Zeng, Q., Long, J., Wang,L., and Li, X. (2015). Catalyticdepolymerization of organosolv lignin in anovel water/oil emulsion reactor: lignin as theself-surfactant. Ind. Eng. Chem. Res. 54,11501–11510.
23. Wang, S.S., and Yang, G.Y. (2015). Recentadvances in polyoxometalate-catalyzedreactions. Chem. Rev. 115, 4893–4962.
24. Kozhevnikov, I.V. (1995). Heteropoly acids andrelated compounds as catalysts for finechemical synthesis. Catal. Rev. 37, 311–352.
25. Tadesse, H., and Luque, R. (2011). Advances onbiomass pretreatment using ionic liquids: anoverview. Energy Environ. Sci. 4, 3913–3929.
26. Spirlet, M.-R., and Busing, W.R. (1978).Dodecatungstophosphoric acid-21-water byneutron diffraction. Acta Crystallogr. B 34,907–910.
27. Long, D.L., Burkholder, E., and Cronin, L.(2007). Polyoxometalate clusters,nanostructures and materials: Fromselfassembly to designer materials anddevices. Chem. Soc. Rev. 36, 105–121.
28. Mirica, L.M., Ottenwaelder, X., and Stack,T.D.P. (2004). Structure and spectroscopy ofcopper-dioxygen complexes. Chem. Rev. 104,1013–1045.
29. Prigge, S.T., Eipper, B.A., Mains, R.E., andAmzel, L.M. (2004). Dioxygen binds end-on tomononuclear copper in a precatalytic enzymecomplex. Science 304, 864–867.
30. Leng, Y., Wang, J., Zhu, D., Ren, X., Ge, H., andShen, L. (2009). Heteropolyanion-based ionicliquids: Reaction-induced self-separationcatalysts for esterification. Angew. Chem. Int.Ed. 48, 168–171.
31. Schutyser, W., Renders, T., Van den Bosch,S.V.d., Koelewijn, S.F., Beckham, G.T., and Sels,B.F. (2018). Chemicals from lignin: an interplayof lignocellulose fractionation,depolymerization, and upgrading. Chem. Soc.Rev. 47, 852–908.
32. Chen, B., andMunson, E.J. (2002). Investigationof the mechanism of n-butane oxidation onvanadium phosphorus oxide catalysts:evidence from isotopic labeling studies. J. Am.Chem. Soc. 124, 1638–1652.
33. Rahimi, A., Azarpira, A., Kim, H., Ralph, J., andStahl, S.S. (2013). Chemoselective metal-freeaerobic alcohol oxidation in lignin. J. Am.Chem. Soc. 135, 6415–6418.
34. Long, J., Lou, W., Wang, L., Yin, B., and Li, X.(2015). [C4H8SO3Hmim]HSO4 as an efficientcatalyst for direct liquefaction of bagasselignin: decomposition properties of the innerstructural units. Chem. Eng. Sci. 122, 24–33.
35. Yan, T., Xu, Y., and Yu, C. (2009). The isolationand characterization of lignin of kenaf fiber.J. Appl. Polym. Sci. 114, 1896–1901.
36. Yang, Q., Wu, S., Lou, R., and Lv, G. (2011).Structural characterization of lignin from wheatstraw. Wood Sci. Technol 45, 419–431.
37. Sun, J.X., Sun, X.F., Sun, R.C., Fowler, P.,and Baird, M.S. (2003). Inhomogeneitiesin the chemical structure of sugarcanebagasse lignin. J. Agric. Food Chem. 51,6719–6725.
38. Lancefield, C.S., Ojo, O.S., Tran, F., andWestwood, N.J. (2015). Isolation offunctionalized phenolic monomers throughselective oxidation and C-O bond cleavage of
the b-O-4 linkages in lignin. Angew. Chem. Int.Ed. 54, 258–262.
39. Santos, A., Yustos, P., Quintanilla, A.,Rodrıguez, S., and Garcıa-Ochoa, F. (2002).Route of the catalytic oxidation of phenol inaqueous phase. Appl. Catal. B 39, 97–113.
40. Esguerra, K.V.N., Fall, Y., Petitjean, L., andLumb, J.P. (2014). Controlling the catalytic
aerobic oxidation of phenols. J. Am. Chem.Soc. 136, 7662–7668.
41. Lee, J.Y., Peterson, R.L., Ohkubo, K., Garcia-Bosch, I., Himes, R.A., Woertink, J., Moore,C.D., Solomon, E.I., Fukuzumi, S., and Karlin,K.D. (2014). Mechanistic insights into theoxidation of substituted phenols via hydrogenatom abstraction by a cupric-superoxocomplex. J. Am. Chem. Soc. 136, 9925–9937.
Chem 5, 2365–2377, September 12, 2019 2377
Chem, Volume 5
Supplemental Information
Selective Production of Diethyl Maleate
via Oxidative Cleavage
of Lignin Aromatic Unit
Zhenping Cai, Jinxing Long, Yingwen Li, Lin Ye, Biaolin Yin, Liam John France, JuncaiDong, Lirong Zheng, Hongyan He, Sijie Liu, Shik Chi Edman Tsang, and Xuehui Li
Materials and Methods
Materials. Tetrahydrofuran (THF, HPLC grade), N-methyl imidazole, 1, 4-butane sulfonate,
dealkaline lignin and the model compounds were purchased from J&K Chemical Co. Ltd.
CuSO4.5H2O, H3PW12O40
.5H2O, CuCO3.Cu(OH)2
.H2O, MnCO3, Na2CO3, NiCO3.2Ni(OH)2
.4H2O
and CoCO3 were purchased from Guangzhou Guanghua Chemical Reagents Factory Co. Ltd. All
materials and reagents were of analytical grade and used without further purification. Organosolv
lignins were extracted from raw biomass sources (10.0 g) using 150 mL 80% v/v aqueous ethanol
solution (containing 1.0 g 98% sulfuric acid) at 393 K for 4 h.1 The relative lignin concentrations
of H, G and S structural units were measured by quantitative 13C-nuclear magnetic resonance
(13C-NMR) spectroscopy.2,3
Table S1. The structural unit contents of different lignin.
Lignin Structural unit content (%)
H G S
Wheat stalk 29.9 32.8 37.3
Corn 13.5 47.2 39.3
Bagasse 14.8 45.6 39.6
Pine 0 81.9 18.1
Rice straw 22.2 37.8 40.0
Dealkaline 0 82.3 17.7
Preparation and characterization of polyoxometalate ionic liquids (POM-ILs).
Following reported procedures,4 N-methyl imidazole and equimolar 1, 4-butane sulfonate
were mixed and stirred magnetically at 313 K for 24 h forming a white precipitate (denoted as
[BSmim]). The as-obtained solid was washed with diethyl ether three times to remove residual
precursors and was then dried under vacuum.
Metal carbonate (consistent with 10 mmol transition metal ion) was dispersed in 20 mL
deionized water and added dropwise to a 20 mL aqueous solution of H3PW12O40.5H2O (10 mmol)
under agitation at ambient conditions. The resulting mixture was then stirred at room temperature
for 6.0 h. MHPW12O40 (M= Na, Mn, Co, Ni and Cu) was obtained after removing water and
vacuum drying at 353 K for 24 h.5 An aqueous MHPW12O40 solution was added dropwise to an
equivalent molar quantity of BSmim and stirred at room temperature for 24 h. The solvent was
then removed at 353 K for 24 h under vacuum,6 yielding [BSmim]MPW12O40 POM-IL.
1H-NMR and 13C-NMR spectra of POM-ILs were obtained on a Bruker AV-400 spectrometer
using D2O and DMSO-d6 solvents respectively. Fourier transform infrared spectroscopy (FT-IR)
was undertaken on a Bruker Tensor 27 FT-IR spectrophotometer (the range of 400-4000 cm-1,
KBr pelleting method). The thermal stability of ILs was analyzed thermogravimetrically (TG,
NETZSCH STA449C) from 313 to 923 K at 10 K min-1. The relative elemental contents of P, W,
Cu, Ni, Co, Mn and Na were determined on an Agilent 7700 Series ICP-MS apparatus. X-ray
diffraction (XRD) patterns were obtained using a Rigaku D/MAX-3A Auto X-ray diffractometer
with Cu Kα radiation (λ= 1.5418 Å). Intensity data were collected over a 2θ range of 5-80° with a
0.01° step. Hydrogen-temperature-programmed reduction (H2-TPR) was performed with a
Micromeritics Autochem II instrument (Micromeritics), equipped with a thermal conductivity
detector (TCD). Approximately 100 mg of catalyst was loaded into a U-shaped quartz reactor,
pre-treated at 373 K (20 K min-1) in Ar for 1 h, then cooled to 323 K, where it was maintained in
flowing 10% H2/Ar (30 mL min-1) for 2 h. The sample was heated from 323 K to 1073 K at 20 K
min-1 under the same reductive gas mixture and held at the final temperature for 10 min.
General procedure for catalytic oxidation of lignin and model compound.
In a typical process, 0.25 g lignin, 0.9 mmol POM-IL catalyst and 20 mL 100% ethanol were
charged into a 100 mL stainless autoclave (Andorra MED1220, Premex Co. Ltd.). After air
purging with pure oxygen five times and pressurizing to 0.8 MPa, the reactor was heated to the
designated temperature and maintained for the desired time. Once the latter elapsed, the autoclave
was cooled rapidly to room temperature in an ice water bath. The reaction mixture was removed
and the reactor was washed with anhydrous ethanol (3 5.0 mL). The IL catalyst was precipitated
at room temperature and used for the next run after drying (extra fresh catalyst was added to
offset transfer losses). The liquid mixture was then diluted by ethanol to 50 mL for qualitative and
quantitative analysis, while dimethyl phthalate was used as the internal standard. When aqueous
solutions of ethanol were used, the spent mixture was rotary evaporated under reduced pressure
for solvent recovery. The concentrated liquor was esterified with 10 mL anhydrous ethanol at 373
K for 2 h and then diluted to 50 mL with ethanol. Volatile products were qualitatively and
quantitatively analyzed via gas chromatography-mass spectrometry (GC-MS) and gas
chromatography-flame ionization detection (GC-FID). Residual lignin can be obtained through
simple precipitation processes. Organosolv lignin was recovered as follows: 60 mL deionized
water was added into 20 mL of the above reaction mixture causing precipitation. The mixture was
then separated using centrifugation and was dried until a constant weight was obtained. For the
recovery of dealkaline lignin the mixture obtained after reaction was acidified to pH=2 with 1.0
mol L-1 HCl solution and the same procedure described for organosolv lignin was conducted.
In the atmosphere investigation, a mixture of nitrogen and oxygen with various molar ratios
was used, while depolymerization of lignin was conducted at 433 K for 5.0 h in the single stage
experiments. For a typical two-stage process, the lignin was first depolymerized employing the
aforementioned conditions. When the mixture was cooled to room temperature, an extra 0.8 MPa
nitrogen or oxygen was purged into the reactor and the reaction was heated to 433 K for 1.0 or 2.0
h. The product separation and analysis procedure remained unchanged to that described
previously. In comparative and control experiments, a series of model compounds (monolignols
and potential intermediate products) were tested under the same procedures as that for lignin (i.e.,
0.25 g model compound, 0.9 mmol POM-IL catalyst and 20 mL 100% ethanol solvent). Triplicate
experiments were conducted and the data shown in this study is the average.
The conversion of lignin/model compound was calculated according to Eq.1, while the
product yield and selectivity were determined according to Eq. 2 to 4 respectively.
R
F
WConversion(%) (1- ) 100%
W Eq.1
P1
F
WYield(mg g )
W Eq.2
D
P
WSelectivity of DEM (%) 100%
W Eq.3
E
4
P
WSelectivity of C ester (%) 100%
W Eq.4
WR: the weight of regenerated lignin (g); WF: the weight of feed lignin/model compound (g); WP:
the weight of total volatile products determined by GC-FID (mg); WD: the weight of DEM (mg);
WE: the weight of C4 ester including DEM, diethyl succinate, diethyl fumarate, diethyl malate.
Product analysis. The reaction products were identified by GC-MS based on an Agilent library
(Agilent 7890B/5977A GC-MS apparatus). The capillary column of HP-5 MS (5% phenyl Methyl
silox, 30 m×250 μm×0.25 μm) was used for chemical separation. The oven temperature was
programmed from 323 (held for 3 min) to 553 K (held for another 5 min) with the rate of 8 K
min-1. The quantitative analysis of these products was conducted on an Agilent 7890B GC with a
flame ionization detector (GC-FID) using the same chromatography column and temperature
program as the GC-MS analysis. Dimethyl phthalate was selected as the internal standard
compound.
Gel permeation chromatography (GPC) analysis of the original and regenerated lignin was
carried out on an Agilent 1260 HPLC apparatus with a differential refraction detector (RID). THF
was used as eluent at a flow rate of 1 mL min-1 with the polystyrene standards for the molecular
weight calibration curve measurement. FT-IR spectra were obtained by Bruker Tensor 27 FT-IR
spectrophotometer (the range of 400-4000 cm-1, KBr pelleting method). 13C-NMR and
heteronuclear single quantum (HSQC) spectra were performed on a Bruker ABANCE III HD 600
spectrometer using DMSO-d6 as solvent. The elemental analysis was characterized by vario EL III
element analyzer and oxygen content were based on the assumption that the residue only contains
C, H, N, S, and O.
The carbon balance, C9 unit utilization efficiency and TON were calculated according to
Eq.5 to 10 respectively:
O O
F F
W CCarbon yield of oligomer (%)= 100%
W C
Eq.5
P P
F F
W CCarbon yield of volatile products (%) 100%
W C
Eq.6
9
F CC
C
W CN (mmol) 1000 mmol / mol
M 9
Eq.7
DEM FDEM
DEM
Y WN (mmol)
M
Eq.8
9
DEM9
C
N C unit utilization efficiency (%) 100%
N Eq.9
9C DEM
catalyst
N TON 100%
N
Eq.10
WO: the weight of oligomer (g); CO: the carbon content of oligomer determined by element
analysis (%); WF: the weight of feed lignin (g); CF: the carbon content of raw bagasse lignin; WP:
the weight of volatile products determined by GC-FID; CP: the carbon content of volatile products
= carbon obtained from lignin/molecular weight; NC9: the content of C9 unit in lignin (mmol); CC:
the content of Carbon based on the elemental analysis (%); MC: the mass number of carbon, 12 g
mol-1; YDEM: the yield of DEM determined by GC-FID (mg g-1); MDEM: the molecular mass of
DEM, 172 g mol-1; NC9-DEM: the C9 unit transformed into DEM (mmol); Ncatalyst: the catalyst used
in this process (mmol).
Characterization of polyoxometalate ionic liquid catalysts
13C-NMR, 1H-NMR, FT-IR and TG analysis of POM-ILs
[BSmim]CuPW12O40.a 1H-NMR (400 MHz, D2O): δ ppm 8.71 (s, 1H), 7.59-7.54 (m, 2H), 4.37
(m, 2H), 4.07 (s, 3H), 3.05 (m, 2H), 2.14 (m, 2H), 1.84 (m, 2H). 13C-NMR (400 MHz, DMSO-d6):
δ ppm 135.51, 123.25, 121.82, 49.82, 48.47, 35.35, 27.78, 20.70. FT-IR (KBr): ν (cm-1) 3562,
3490, 3153, 2938, 1971, 1606, 1448, 1169, 1076, 976, 890, 789, 596, 518. Onset decomposition
temperature: 572.4 K.
[BSmim]NiPW12O40. 1H-NMR (400 MHz, D2O): δ ppm 8.70 (s, 1H), 7.61-7.56 (m, 2H), 4.39 (m,
2H), 4.11 (s, 3H), 3.08 (m, 2H), 2.17 (m, 2H), 1.86 (m, 2H). 13C-NMR (400 MHz, DMSO-d6): δ
ppm 134.57, 122.13, 120.75, 48.83, 47.30, 34.29, 26.80, 19.78. FT-IR (KBr): ν (cm-1) 3554, 3440,
3203, 2945, 1971, 1621, 1448, 1162, 1076, 970, 904, 789, 603, 518. Onset decomposition
temperature: 592.5 K.
[BSmim]CoPW12O40. 1H-NMR (400 MHz, D2O): δ ppm 8.36 (s, 1H), 7.29 (s, 1H), 7.23 (s, 1H),
4.11 (m, 2H), 3.77 (s, 3H), 2.85 (m, 2H), 1.90 (m, 2H), 1.56 (m, 2H). 13C-NMR (400 MHz,
DMSO-d6): δ ppm 136.33, 123.81, 122.44, 51.16, 48.94, 35.98, 28.56, 21.58. FT-IR (KBr): ν
(cm-1) 3504, 3368, 3218, 2945, 1971, 1621, 1456, 1162, 1076, 983, 897, 789, 610, 518. Onset
decomposition temperature: 566.2 K.
[BSmim]MnPW12O40. 1H-NMR (400 MHz, D2O): δ ppm 8.62 (s, 1H), 7.39-7.33 (m, 2H), 4.14
(m, 2H), 3.78 (s, 3H), 2.84 (m, 2H), 1.91 (m, 2H), 1.63 (m, 2H). 13C-NMR (400 MHz, DMSO-d6):
δ ppm 135.73, 123.33, 121.95, 49.21, 48.49, 35.66, 28.08, 21.03. FT-IR (KBr): ν (cm-1) 3447,
3354, 3153, 2953, 1971, 1621, 1456, 1169, 1084, 983, 897, 783, 603, 510. Onset decomposition
temperature: 607.9 K.
[BSmim]Na2PW12O40. 1H NMR (400 MHz, D2O): δ ppm 8.71 (s, 1H), 7.59 (s, 1H), 7.54 (s, 1H),
4.37 (t, J = 7.0 Hz, 2H), 4.07 (s, 3H), 2.98 (t, J = 7.4 Hz, 2H), 2.17-2.09 (m, 2H), 1.85-1.77 (m,
2H). 13C-NMR (400 MHz, DMSO-d6): δ ppm 136.21, 123.83, 122.43, 50.39, 49.01, 35.98, 28.46,
21.41. FT-IR (KBr): ν (cm-1) 3525, 3419, 3160, 2945, 1978, 1628, 1442, 1162, 1076, 976, 897,
783, 603, 518. Onset decomposition temperature: 563.1 K.
Recovered [BSmim]CuPW12O40. 1H-NMR (400 MHz, D2O): δ ppm 8.72 (s, 1H), 7.55 (m, 2H),
4.37 (m, 2H), 4.06 (s, 3H), 3.05 (m, 2H), 2.14 (m, 2H), 1.83 (m, 2H). 13C-NMR (400 MHz,
DMSO-d6): δ ppm 136.23, 123.83, 122.44, 50.49, 49.00, 35.98, 28.47, 21.42. FT-IR (KBr): ν
(cm-1) 3568, 3483, 3160, 2960, 1978, 1606, 1448, 1162, 1076, 983, 890, 789, 603, 518. Onset
decomposition temperature: 569.0 K.
Notes: [BSmim] represents the Methyl-3-(butyl-4-sulfonate) imidazolium cation.
f g h i j Ba b c d e
A
Figure S1. The ILs [BSmim]MPW12O40 (from a to e, M= Cu, Ni, Co, Mn, and Na) (A) and the
solubility of CuHPW12O40 and [BSmim]CuPW12O40 (B). (f): 0.5 g CuHPW12O40 in 5 mL 80%
ethanol-water solvent at room temperature. (g): mixture of 0.5 g [BSmim]CuPW12O40 and 5 mL
80% ethanol-water solvent at room temperature. (h) g at 353 K; (i) added 5 mL of ethanol to f. (j):
added 5 mL of ethanol to h.
50 150 250 350 450 550 650 750
a
TC
D S
ign
al (
a.u
.)
Temperature (oC)
a--BSmimCuP12O40
c
c--BSmimCoP12O40
d
d--BSmimMnP12O40
b
b--BSmimNiP12O40
f
e
e--BSmimNa2P12O40
f--H3PW12O40
Figure S2. Temperature programmed reduction (TPR) data of the POM-ILs showing their
reduction from 160oC
Figure S3. XRD patterns of POM-IL catalysts and synchrotron PXRD refinement and the
structure of Cu-POM. (A) XRD patterns of IL catalysts. (B) Comparison of the experiment data
(black line) and Le Bail profile refinement (red circle). Red circle is the sum of the phase
1(Cu-POM1) blue line and the phase 2 (Cu-POM2) green line and the difference between them
(grey line) from 2.5 ~ 30°. (C) The structure of Cu-POM is obtained by transforming the space
group Pcca to Pncn using winGX software, which was based on the Le Bail profile refinement
data. The framework of Cu-POM is using the ball-stick mode, framework O: red, WVI: blue,
(W/Cu)V: green, P: pink. (Unit cell parameters illustrate in Supplementary Table S2)
High resolution Synchrotron PXRD data were collected on Beamline I11, Diamond Light Source,
UK. Detailed description of the beamline can be found elsewhere.7 The incident X-ray beam energy
was set at 15 keV. The wavelength and the 2θ zero-point correction were refined using a diffraction
pattern obtained from a high-quality silicon powder (SRM640c). Unit cell parameters for Cu-POM1
and Cu-POM2 were obtained from powder diffraction data which was based on a Le Bail profile
refinement using TOPAS and summarized in Supplementary Table S2. The Pncn structure of the
A B
C
Cu-POM was deduced from the Pcca space group transformed through the matrix
using WinGX software.
Table S2. Crystallographic data and details of the Cu-POM sample.
Samples Cu-POM1 Cu-POM2
Crystal system Orthorhombic Orthorhombic
Space group Pncn Pncn
Chemical formula [P(W/Cu)V4W
VI8O39 ]
n- n (O2/H2O) [P(W/Cu)V4W
VI8O39 ]
n-·n (O2/H2O)
2θ range refinement (o) 2.5 – 30
Detector Multi-analyser crystals
Refinement methods Rietveld refinement
a (Å) 20.48624(9) 17.61397(4)
b (Å) 14.40534(9) 11.46489(5)
c (Å) 16.48389(1) 15.19459(7)
V (Å3) 4856.1(1) 3068.1(1)
Rwp / Rp / Rexp (%) 9.975/7.861/6.605
Wavelength (Å) 0.825255 (2)
2θ Zero point (°) -0.0001 (2)
Gof χ2 1.510
Table S3. The detailed parameters Rietveld refinement of POM-IL.
Species Atom X Y Z SOF Beq(Å2)
Cu-POM1/2 site P1 0 0.4457 0.25 1 2
site W1 0.2467 0.4503 0.3217 1 2
site W2 0.1126 0.4413 0.0953 1 2
site W3 0.0729 0.5802 0.3617 1 2
site W4 -0.0606 0.3122 0.1352 1 2
site W5 0.1816 0.5794 0.2128 1 2
site W6 0.1764 0.3123 0.2041 1 2
site O1 0.0863 0.4926 0.2749 1 2
site O2 0.0392 0.3988 0.1955 1 2
site O3 0.1124 0.2879 0.2824 1 2
site O4 0.0526 0.6029 0.1784 1 2
site O7 0.0013 0.5058 0.0967 1 2
site O8 0.1606 0.3848 0.3646 1 2
site O9 0.1442 0.6214 0.2923 1 2
site O10 0.0655 0.2699 0.1595 1 2
site O11 0.2769 0.5237 0.2598 1 2
site O12 0.1992 0.3682 0.127 1 2
site O13 0.1955 0.5232 0.3757 1 2
site O14 0.0148 0.3686 0.0753 1 2
site O15 0.3633 0.4354 0.3536 1 2
site O16 0.1686 0.4567 0.0216 1 2
site O17 0.0856 0.6408 0.4208 1 2
site O18 -0.1119 0.2507 0.0859 1 2
site O19 0.258 0.641 0.1791 1 2
site O20 0.2729 0.2521 0.1968 1 2
site O5 0.1821 0.5061 0.1497 1 2
site O6 0.2422 0.3856 0.2522 1 2
O atoms of water O 0.32482 -0.15407 1.36937 5.78(6) 2
For Cu-POM-1 O 0.73191 -0.27770 -0.50310 1.96(6) 2
O 0.30770 1.18390 -1.05108 12.56(7) 2
O -0.72126 1.16347 0.48646 7.09(6) 2
Table S4. Mn K-edge and W L3-edge EXAFS curve Fitting parameters of [BSmim]MnPW12O40.a
sample Shell N R (Å) σ2 (Å2) ΔE0 (eV) R, %
MnO2b Mn−O 6 1.90 0.005 4.3 0.01
[BSmim]MnPW12O40c Mn−O 6.0 2.16 0.007 8.7 0.01
W−O1
W−O2
W−O3
1.0
3.9
1.0
1.70
1.90
2.41
0.001
0.004
0.011
1.4 0.03
[BSmim]MnPW12O40_H2c Mn−O 5.6 2.15 0.007 8.9 0.01
W−O1
W−O2
W−O3
0.9
4.1
1.0
1.71
1.91
2.43
0.001
0.004
0.011
2.5 0.05
a N, coordination number; R, distance between absorber and backscatter atoms; σ2, Debye–Waller factor to
account for both thermal and structural disorders; ΔE0, inner potential correction; R factor (%) indicates the
goodness of the fit. Error bounds (accuracies) that characterize the structural parameters obtained by EXAFS
spectroscopy were estimated as N ± 20%; R ± 1%; σ2 ± 20%; ΔE0 ± 20%. S02 were determined from MnO2 and
WO3 standard fitting and fixed. Bold numbers indicate fixed coordination number (N) according to the crystal
structure. O1, O2, and O3 represent the first, second, and third nearest neighbor coordination O atoms. b Fitting
range: 2.0 ≤ k (/Å) ≤ 12.6 and 1.0 ≤ R (Å) ≤ 2.0. cMn K-edge fitting range: 2.5 ≤ k (/Å) ≤ 12.0 and 1.0 ≤ R (Å) ≤
2.4; W L3-edge fitting range: 2.5 ≤ k (/Å) ≤ 14.5 and 1.0 ≤ R (Å) ≤ 2.4.
Table S5. Co K-edge and W L3-edge EXAFS curve fitting parameters of [BSmim]CoPW12O40.a
sample Shell N R (Å) σ2 (Å2) ΔE0 (eV) R, %
Co bulkb Co−Co 12 2.49 0.008 0.7 0.01
CoOc Co−O
Co−Co
6
12
2.12
3.01
0.009
0.009 -9.9 1.0
[BSmim]CoPW12O40d Co−O 6.0 2.08 0.006 -3.1 0.01
W−O1
W−O2
W−O3
1.0
3.9
1.0
1.70
1.91
2.42
0.001
0.004
0.011
3.0 0.09
[BSmim]CoPW12O40_H2d Co−O 5.8 2.08 0.006 -3.3 0.01
W−O1
W−O2
W−O3
0.8
3.8
1.0
1.71
1.91
2.44
0.001
0.004
0.011
4.7 0.05
a N, coordination number; R, distance between absorber and backscatter atoms; σ2, Debye–Waller factor to
account for both thermal and structural disorders; ΔE0, inner potential correction; R factor (%) indicates the
goodness of the fit. Error bounds (accuracies) that characterize the structural parameters obtained by EXAFS
spectroscopy were estimated as N ± 20%; R ± 1%; σ2 ± 20%; ΔE0 ± 20%. S02 were determined from CoO and
WO3 standard fitting and fixed. Bold numbers indicate fixed coordination number (N) according to the crystal
structure. O1, O2, and O3 represent the first, second, and third nearest neighbor coordination O atoms. b Fitting
range: 3.2 ≤ k (/Å) ≤ 14.0 and 1.4 ≤ R (Å) ≤ 2.7. cFitting range: 3.2 ≤ k (/Å) ≤ 14.5 and 1.0 ≤ R (Å) ≤ 3.2. dCo
K-edge fitting range: 3.2 ≤ k (/Å) ≤ 11.9 and 1.0 ≤ R (Å) ≤ 2.4; W L3-edge: fitting range: 2.5 ≤ k (/Å) ≤ 14.5 and
1.0 ≤ R (Å) ≤ 2.4.
Table S6. Ni K-edge and W L3-edge EXAFS curve fitting parameters of [BSmim]NiPW12O40.a
sample Shell N R (Å) σ2 (Å2) ΔE0 (eV) R, %
Ni bulkb Ni-Ni 12 2.48 0.008 0.7 0.01
NiOc Ni-O
Ni-Ni
6
12
2.08
2.95
0.005
0.006 1.8 0.01
[BSmim]NiPW12O40d Ni−O 5.9 2.04 0.007 -10.9 0.01
W−O1
W−O2
W−O3
1.0
3.9
1.0
1.70
1.91
2.49
0.001
0.004
0.011
3.2 0.07
[BSmim]NiPW12O40_H2d Ni−O 5.7 2.03 0.007 -11.9 0.2
W−O1
W−O2
W−O3
1.0
3.8
0.5
1.72
1.92
2.44
0.002
0.004
0.011
5.1 0.08
a N, coordination number; R, distance between absorber and backscatter atoms; σ2, Debye–Waller factor to
account for both thermal and structural disorders; ΔE0, inner potential correction; R factor (%) indicates the
goodness of the fit. Error bounds (accuracies) that characterize the structural parameters obtained by EXAFS
spectroscopy were estimated as N ± 20%; R ± 1%; σ2 ± 20%; ΔE0 ± 20%. S02 were determined from NiO and
WO3 standard fitting and fixed. Bold numbers indicate fixed coordination number (N) according to the crystal
structure. O1, O2, and O3 represent the first, second, and third nearest neighbor coordination O atoms. b Fitting
range: 3.9 ≤ k (/Å) ≤ 13.9 and 1.6 ≤ R (Å) ≤ 2.6. cFitting range: 3.7 ≤ k (/Å) ≤ 14.5 and 1.0 ≤ R (Å) ≤ 3.2. dNi
K-edge fitting range: 3.2 ≤ k (/Å) ≤ 11.9 and 1.0 ≤ R (Å) ≤ 2.4; W L3-edge fitting range: 2.5 ≤ k (/Å) ≤ 14.5 and
1.0 ≤ R (Å) ≤ 2.4.
Table S7. Cu K-edge and W L3-edge EXAFS curve fitting parameters of [BSmim]CuPW12O40.a
sample Shell Na R (Å) σ2 (Å2) ΔE0 (eV) R, %
Cu bulkb Cu−Cu 12 2.54 0.008 1.0 0.01
Cu2Oc Cu−O 2 1.86 0.003 4.0 0.04
CuOc Cu−O 4 1.96 0.005 2.1 0.01
[BSmim]CuPW12O40d Cu−O1
Cu−O2
4.6
1.0
1.96
2.26
0.005
0.010 3.6 0.01
W−O1
W−O2
W−O3
1.0
4.0
1.0
1.70
1.91
2.49
0.001
0.004
0.011
3.2 0.07
[BSmim]CuPW12O40_H2d Cu−O1
Cu−O2
4.0
1.0
1.96
2.21
0.005
0.010 2.5 0.05
W−O1
W−O2
W−O3
1.0
3.6
0.8
1.71
1.91
2.49
0.001
0.004
0.011
3.3 0.14
a N, coordination number; R, distance between absorber and backscatter atoms; σ2, Debye–Waller factor to
account for both thermal and structural disorders; ΔE0, inner potential correction; R factor (%) indicates the
goodness of the fit. Error bounds (accuracies) that characterize the structural parameters obtained by
EXAFS spectroscopy were estimated as N ± 20%; R ± 1%; σ2 ± 20%; ΔE0 ± 20%. S02 were determined
from CuO and WO3 standard fitting and fixed. Bold numbers indicate fixed coordination number (N)
according to the crystal structure. O1, O2, and O3 represent the first, second, and third nearest neighbor
coordination O atoms. b Fitting range: 2.5 ≤ k (/Å) ≤ 12.5 and 1.6 ≤ R (Å) ≤ 2.8. cFitting range: 2.5 ≤ k (/Å)
≤ 12.5 and 1.0 ≤ R (Å) ≤ 2.0. dCu K-edge fitting range: 2.9 ≤ k (/Å) ≤ 12.5 and 1.0 ≤ R (Å) ≤ 2.6; W
L3-edge fitting range: 2.5 ≤ k (/Å) ≤ 14.5 and 1.0 ≤ R (Å) ≤ 2.4.
To understand the coordination environment and chemical states of M/W in POM-ILs,
X-ray absorption fine structure spectra were collected at 1W1B beamline of Beijing
Synchrotron Radiation source in China in fluorescence mode using a Si (111) double crystal
monochromator under ambient condition. The incident and fluorescence X-ray intensities were
detected by standard ionization chambers and Lytle-type detectors, respectively. The EXAFS
raw data were then background-subtracted, normalized and Fourier transformed by the standard
procedures with the ATHENA program;8 least-squares curve fitting analysis of the EXAFS χ(k)
data was carried out using the ARTEMIS program.
Figure S4a. EXAFS and XANES analyses of POM-ILs
Figure S4b. XANES analyses of [BSmim]CuPW12O40
Table S8. ICP-MS analysis of POM-ILs.a
IL catalyst Element Concentration
(mg L-1) b
Analysis 1
(mg L-1)
Analysis 2
(mg L-1)
Average
(mg L-1)
Error
(%)
[BSmim]CuPW12O40
Cu 6.06 5.97 5.88 5.93 2.15
P 3.18 3.21 3.15 3.18 0.06
W 20.93 20.16 19.98 20.07 4.11
[BSmim]NiPW12O40
Ni 5.60 5.34 5.40 5.37 4.11
P 3.23 3.20 3.27 3.24 0.28
W 20.96 20.76 20.84 20.80 0.76
[BSmim]CoPW12O40
Co 5.69 5.35 5.47 5.41 4.92
P 3.20 3.21 3.23 3.22 0.77
W 20.95 20.79 20.81 20.80 0.72
[BSmim]MnPW12O40
Mn 5.22 5.11 5.09 5.10 2.30
P 3.17 3.20 3.19 3.20 0.69
W 20.98 20.14 20.28 20.21 3.67
[BSmim]Na2PW12O40
Na 4.39 4.15 4.21 4.18 4.78
P 3.20 3.26 3.19 3.23 0.80
W 21.05 19.98 19.87 19.93 5.32
a The concentration of IL catalyst is 300 mg.L-1 for Cu, Co, Mn, Ni, Na and P, and is 30 mg.L-1 for
W; b Theoretical value.
The selective oxidation of lignin and model compounds
Table S9. Selective oxidation of bagasse lignin over various catalysts.
Entry
Catalysts
Conv.
(%)
Yield (mg g-1)
DEM
selectivitya
(%)
Average molar mass of
regenerated lignin
1 2 3 4 5 6 7 8 9 10 total Mw Mn D
1 None 48.2 —b — — — — 1.1 2.0 3.4 5.7 2.5 14.7 0 1643 990 1.66
2 [BSmim]HSO4 82.4 6.5 4.4 4.1 0.9 — 10.0 1.8 17.9 2.5 — 48.1 13.5 688 375 1.83
3 [BSmim]Na2PW12O40 81.3 53.6 3.7 2.5 — — 1.6 7.7 — — — 69.1 77.6 999 688 1.45
4 [BSmim]MnPW12O40 80.9 87.7 12.5 4.0 3.4 7.1 — 15.6 — — — 130.3 67.3 949 663 1.43
5 [BSmim]CoPW12O40 80.6 93.3 6.8 4.1 1.4 7.3 7.6 26.0 — — — 146.5 63.7 933 652 1.43
6 [BSmim]NiPW12O40 84.3 100.4 5.1 7.3 3.2 8.1 11.2 27.1 — 3.9 — 166.3 60.4 920 647 1.42
7 [BSmim]CuPW12O40 90.7 153.6 4.8 12.0 5.8 16.9 25.2 31.7 — 9.1 — 259.1 59.3 786 613 1.28
8c [Bmim]CuPW12O40 80.8 11.0 1.7 2.1 1.9 1.4 13.7 1.8 9.7 2.9 — 46.2 23.8 1132 846 1.34
9d H2SO4/CuSO4 86.8 16.5 0.9 1.6 1.8 11.4 12.0 10.7 10.2 9.4 — 74.5 22.1 898 648 1.39
10e [BSmim]Na2PW12O40/CuSO4 90.0 100.9 3.1 5.9 1.3 15.2 17.9 16.7 — 1.6 — 162.6 62.1 886 682 1.30
11f [BSmim]CuPW12O40 31.3 — — — — — — — — — — 78.6 0 954 726 1.31
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol catalyst, 20 mL of 80% ethanol-water, 0.8 MPa O2, 433 K, 5 h. a the selectivity of DEM is based on the volatile product determined by GC-MS; b not
added or detected; c After removed the solvents, then 10 mL ethanol and 0.45 mmol H2SO4 were added at 373 K for 2 h; d 0.45 mmol H2SO4/0.9 mmol CuSO4; e 0.9 mmol [BSmim]Na2PW12O40/(0.9 mmol)
CuSO4. f 0.8 MPa N2, volatile products: guaiacol (1.6 mg g-1), phenol (2.7 mg g-1), 4-ethylguaiacol (5.3 mg g-1), 4-ethylphenol (54.1 mg g-1), 5-methyl-2-isopropylphenol (4.2 mg g-1), 2,6-dimethoxyphenol
(3.6 mg g-1), 2-hydroxy-1-(4-hydroxy-3-methoxyphenyl) ethanone (7.1 mg g-1). 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate; 4: Diethyl malate; 5: Ethyl ethoxyacetate; 6: Ethyl
4-hydroxybenzoate; 7: Ethyl vanillate; 8: 4-Hydroxybenzaldehyde; 9: Vanillin; 10: Syringaldehyde. Original bagasse lignin with the Mw, Mn and D values of 2698, 1156 and 2.33, respectively, see Table S16,
D=Mw/Mn.
4 8 12 16 20
b
10
987
6
5
4
3
2
Inte
nsity
Retention time (min)
1
a
Figure S5. GC-MS analysis of the volatile products with (a) and without (b) [BSmim]CuPW12O40.
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol [BSmim]CuPW12O40 catalyst, 20 mL 80%
ethanol-water, 433 K, 5 h, 0.8 MPa O2.
Table S10. The volatile products detected by GC-MS.
Entry Retention
time (min) Products Structure Formula
Molecular weight
(g mol-1)
1 5.94 Ethyl ethoxyacetate
C6H12O3 132
2 11.68 Diethyl maleate
C8H12O4 172
3 12.03 Diethyl succinate
C8H14O4 174
4 12.95 Diethyl fumarate
C8H12O4 172
5 13.58 Diethyl malate
C8H14O5 190
6 15.80 4-hydroxybenzaldehyde
C7H6O2 122
7 16.08 Vanillin
C8H8O3 152
8 18.23 Ethyl 4-hydeoxybenzoate
C9H10O3 166
9 19.15 Ethyl vanillate
C10H12O4 196
10 20.26 Syringaldehyde
C9H10O4 182
Diethyl maleate
(a)
(b)
Diethyl succinate
(a)
(b)
Figure S6a. The MS spectra of C4 esters produced in this process. a: the data from the reaction
mixture; b: the data from MS library.
(a)
(b)
Diethyl fumarate
Diethyl malate
(a)
(b)
Figure S6b. The MS spectra of C4 esters produced in this process. a: the data from the reaction
mixture; b: the data from MS library.
Figure S7. Effect of POM-IL catalysts dosage on the oxidation of lignin.
Reaction condition: 0.25 g bagasse lignin, [BSmim]CuPW12O40 as catalyst, 20 mL 80%
ethanol-water, 433 K, 3 h, 0.8 MPa O2. 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl
fumarate; 4: Diethyl malate; 5: Ethyl ethoxyacetate; 6: Ethyl 4-hydroxybenzoate; 7: Ethyl
vanillate; 8: 4-Hydroxybenzaldehyde; 9: Vanillin; 10: Syringaldehyde.
Figure S8. Effect of reaction temperature on the oxidation of lignin.
Reaction condition: 0.25 g bagasse lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 80%
ethanol-water, 3 h, 0.8 MPa O2. 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate; 4:
Diethyl malate; 5: Ethyl ethoxyacetate; 6: Ethyl 4-hydroxybenzoate; 7: Ethyl vanillate; 8:
4-Hydroxybenzaldehyde; 9: Vanillin; 10: Syringaldehyde.
Figure S9. Effect of reaction time on the oxidation of lignin.
Reaction condition: 0.25 g bagasse lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 80%
ethanol-water, 433 K, 0.8 MPa O2. 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate;
4: Diethyl malate; 5: Ethyl ethoxyacetate; 6: Ethyl 4-hydroxybenzoate; 7: Ethyl vanillate; 8:
4-Hydroxybenzaldehyde; 9: Vanillin; 10: Syringaldehyde.
Figure S10. Recycle performances of IL [BSmim]CuPW12O40 catalyst.
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 100% ethanol,
433 K, 5 h, 0.8 MPa O2. 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate; 4: Ethyl
ethoxyacetate; 5: Ethyl 3-ethoxypropionate; 6: Diethyl oxalate; 7: Diethyl malonate; 8: Ethyl
diethoxyacetate; 9: Ethyl 3,3-diethoxypropionate; 10: Ethyl 4-hydroxybenzoate; 11: Ethyl
vanillate.
Table S11. Selective oxidation of bagasse lignin in different aqueous ethanol.
Entry
Ethanol
concentration
(%)
Conversion
(%)
Yield (mg g-1) DEM
selectivity
(%)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 Total
1 0 29.3 1.7 2.7 2.0 1.9 —a — — — — — — — — — 8.3 20.5
2 20 46.8 16.6 2.6 7.3 9.5 — 4.2 1.1 8.4 4.2 — — — — — 53.9 30.8
3 40 84.4 61.0 8.0 16.6 25.6 8.3 — — — — — — — — — 119.5 51.0
4 60 87.3 83.1 12.5 16.3 23.1 0.9 16.5 5.1 19.5 11.3 0.3 — — — 188.6 44.1
5 80 90.7 153.6 4.8 12.0 5.8 16.9 25.2 31.7 — 9.1 — — — — — 259.1 59.3
6 100 92.9 274.7 13.8 22.4 — 3.4 8.3 12.1 — — — 3.9 13.8 44.4 1.6 398.4 69.0
7b 40 100 152.9 — 163.5 179.3 — — — — — — — — — — 495.7 30.8
8b 80 100 416.3 — 41.3 31.3 — — — — — — — — — — 488.9 85.1
9b 100 100 1111.5 — — — — — — — — — — — — — 1111.5 100.0
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol [BSmim]CuPW12O40 catalyst, 20 mL ethanol-water, 433 K, 5 h, 0.8 MPa O2. a not detected. b 0.25 g of maleic aicd as substrate. 1: Diethyl
maleate. 2: Diethyl succinate. 3: Diethyl fumarate. 4: Diethyl malate. 5: Ethyl ethoxyacetate. 6: Ethyl 4-hydroxybenzoate. 7: Ethyl vanillate. 8: 4-Hydroxybenzaldehyde. 9: Vanillin. 10:
Syringaldehyde. 11: Ethyl 3-ethoxypropionate. 12: Diehtyl malonate. 13: Ethyl diethoxyacetate. 14: Ethyl 3,3-diethoxypropionate.
Table S12. The elemental analysis of lignin before and after the reaction.
Entry Material Element content (%)
C H O[a] N S
1 Raw bagasse lignin 59.59 6.42 33.12 0.40 0.47
2 Oligomer 42.97 4.42 52.53 0.08 0.00
3 Regenerated lignin 43.11 4.27 52.31 0.31 0.00
Reaction condition: 0.25 g bagasse lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 100% ethanol, 433 K, 5 h,
0.8 MPa O2. a Oxygen content (%) = (100-C-H-N-S)%; raw bagasse lignin :C9H11.65O3.75N0.05S0.02
(180.99 g/mol)
Table S13. The selective oxidation of bagasse lignin.
Entry
Atmosphere/time(h) Conv.
(%)
Yield (mg g-1)a DEM Sel.
(%) 1st run 2nd runb 1 2 3 4 5 6 7 8 9 10 11 Total
1 0.8 MPa O2/5.0 — 92.9 274.7 13.8 22.4 — 3.4 13.8 3.9 44.4 1.6 8.3 12.1 398.4 69.0
2 0.8 MPa O2/5.0 0.8 MPa N2/1.0 91.4 281.6 13.8 23.3 8.3 9.6 18.2 5.3 8.2 4.1 20.2 12.2 404.8 69.6
3 0.8 MPa O2/5.0 0.8 MPa O2/1.0 96.5 483.8 21.0 47.5 13.3 10.0 24.1 5.7 10.1 4.3 15.4 9.3 644.5 75.1
4 0.8 MPa O2/5.0 0.8 MPa O2/2.0 100 522.3 30.3 56.1 22.5 9.6 23.5 5.3 9.8 3.9 — — 683.3 76.4
5
0.2MPa N2-0.8 MPa
O2/5.0
— 94.2 348.6 17.3 32.7 12.0 10.1 20.1 4.2 9.3 4.6 16.2 11.2 486.3 71.7
6
0.4MPa N2-0.8 MPa
O2/5.0
— 94.2 350.1 18.7 31.2 13.2 11.3 20.2 4.7 10.1 5.2 18.7 12.4 495.8 70.6
7
0.2MPa N2-1.0 MPa
O2/5.0
— 94.4 357.2 18.1 33.6 14.1 10.9 19.8 5.3 9.7 5.8 19.3 13.1 506.9 70.5
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol BSmimCuPW12O40 catalyst, 20 mL 100% ethanol, 433 K. a 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate; 4: Diethyl malate;
5. Ethyl ethoxyacetate; 6: Diethyl malonate; 7: Ethyl 3-ethoxypropionate; 8: Ethyl diethoxyacetate; 9: Ethyl 3,3-diethoxypropionate; 10: Ethyl 4-hydroxybenzoate; 11: Ethyl vanillate. b change
in conversion and product distribution after re-testing the obtained product mixture from 1st run by injecting additional gas into the autoclave (2nd run) for the time specified.
Table S14. Gaseous composition before and after reaction.
Entry
Before/after reaction (vol. %)
O2 N2 CO2 CO
1a 94.1/79.5 5.9/16.1 -/4.4 -/-
2b 78.6/65.5 21.4/28.9 -/4.9 -/0.7
3c 65.9/51.3 34.1/44.2 -/3.7 -/0.8
4d 83.2/73.3 16.8/21.9 -/4.1 -/0.7
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol BSmimCuPW12O40 catalyst, 20 mL
ethanol, 433 K, 5h. a 0.8 MPa O2; b 0.2MPa N2 and 0.8 MPa O2;
c 0.4 MPa N2 and 0.8 MPa
O2; d 0.2 MPa N2 and 1.0 MPa O2.
Table S15. The molar content changes of gaseous fraction.
Entry
Before/after reaction(mmol)
O2 CO2 CO
1a 25.4/15.7 -/1.17 -/0.17
2b 25.5/15.3 -/1.11 -/0.24
3c 32.2/21.8 -/1.22 -/0.21
Reaction conditions: 0.25 g bagasse lignin, 0.9 mmol BSmimCuPW12O40 catalyst, 20 mL
ethanol, 433 K, 5h. a 0.2MPa N2 and 0.8 MPa O2; b 0.4 MPa N2 and 0.8 MPa O2;
c 0.2
MPa N2 and 1.0 MPa O2.
Table S16. Average molecular weight of raw lignin.
Sample Mw (g mol-1) Mn (g mol-1) Da
Rice stalk lignin 3319 2170 1.53
Wheat stalk lignin 3094 1693 1.83
Pine lignin 2984 1338 2.23
Bagasse lignin 2698 1156 2.33
Corn stalk lignin 2090 1170 1.79
Dealkaline ligninb 17029 15613 1.09
a D= Mw/Mn. b the acetylated dealkaline lignin.
Table S17. The oxidative ring cleavage of various lignin feedstocks.
Entry Lignin resource
Yield (mg g-1) Selectivity of
DEM (%) 1 2 3 4 5 6 7 8 9 10 11 Total
1 Wheat stalk 404.8 26.6 35.0 5.0 —a — 18.0 50.3 3.9 — 13.1 556.7 72.7
2 Corn stalk 308.7 15.9 22.9 3.5 — 13.4 12.2 46.1 1.9 7.9 8.7 441.2 70.0
3 Bagasse 274.7 13.8 22.4 3.4 3.9 — 13.8 44.4 1.6 8.3 12.1 398.4 69.0
4 Pine 255.2 19.4 32.0 2.4 — — 5.9 25.5 2.8 — 18.3 361.5 70.6
5 Rice straw 254.3 15.8 18.3 3.1 3.3 17.0 13.3 46.6 2.6 — 8.4 382.7 66.4
6 Dealkaline 210.6 13.7 24.6 — 3.3 — 3.8 20.6 2.4 — 17.9 296.9 70.9
Reaction conditions: 0.25 g lignin, 0.9 mmol [BSmim]CuPW12O40, 20 mL 100% ethanol, 433 K, 5 h, 0.8 MPa O2. a not detected. 1: Diethyl maleate; 2: Diethyl succinate; 3:
Diethyl fumarate; 4: Ethyl ethoxyacetate; 5: Ethyl 3-ethoxypropionate; 6: Diethyl oxalate; 7: Diethyl malonate; 8: Ethyl diethoxyacetate; 9: Ethyl 3,3-diethoxypropionate; 10:
Ethyl 4-hydroxybenzoate; 11: Ethyl vanillate.
Table S18. Assignment of FT-IR spectra.
Wave numbers (cm-1) The attributions of the main absorptions
3,443 OH stretching
2,941 C-H stretching in methyl and methylene groups
2,859 -CH2-symmetry stretching in methyl and methylene groups
1,702 C=O stretching in unconjugated ketones, carbonyls and in ester groups
1,608 Aromatic skeleton and C=O (S>G, G condensed>G etherified)
1,509 Aromatic skeleton (G>S)
1,467 C-H deformation (asymmetric CH3 and CH2)
1,426 Aromatic skeletal vibrations combined with C-H in plane deformations
1,368 C-H stretching of side groups (CH3)
1,327 S unit plus G unit condensed (G unit bound via position 5)
1,274 G ring and C=O stretching
1,233 C-C, C-O and C=O stretching
1,129 typical of S unit
1,087 secondary alcohol and aliphatic ether
1040 C-O of primary alcohol, Guaiacyl C-H
988 C-O valence vibration
894 C-H bending in aromatic skeleton
831 C-H out plane deformation
S: syringyl unit. G: guaiacyl unit
Figure S11. 13C-NMR spectra of original and regenerated bagasse lignin
Table S19. The oxidation of model compounds over [BSmim]CuPW12O40.
Entry Substrates Conversion
(%)
Yield (mg g-1)a DEM
selectivity
(%) 1 2 3 4 5 6 7 8 9 10 Total
1
100 176.7 16.9 20.6 3.5 — 7.7 23.9 2.5 — — 251.8 70.2
2
100 442.4 27.1 32.6 6.8 18.1 9.9 40.4 4.4 — — 581.7 76.1
3
100 446.5 28.0 36.2 6.9 17.5 11.5 38.7 2.9 — — 588.2 75.9
4
100 205.2 14.7 15.4 4.5 30.3 15.0 33.3 3.2 — — 321.6 63.8
5
100 257.3 12.9 21.7 4.9 25.8 21.3 41.8 2.4 — — 388.1 66.3
6
100 228.2 13.3 14.1 5.0 23.0 14.1 35.6 3.4 — — 336.7 67.8
7
100 368.4 19.7 24.1 5.0 14.6 14.1 51.7 4.8 — — 502.4 73.3
8
86.0 243.9 16.1 21.8 3.8 15.8 8.0 29.8 2.9 108.0 — 450.1 54.2
9
86.2 315.1 15.8 18.4 9.2 30.0 6.3 9.2 2.9 490.2b 64.3
10
100 357.8 14.6 16.2 3.9 21.5 13.7 37.4 3.2 — 48.6 516.9 69.2
11
100 360.5 13.7 21.8 4.6 36.5 24.1 48.1 2.3 — — 511.6 70.5
12
100 8.2 — — — — — — — 944.7 — 952.9 0.9
13
100 114.8 5.8 6.1 1.3 9.6 8.7 24.8 2.4 — 457.2 630.7 18.2
14
100 223.2 12.9 31.6 4.2 25.4 31.5 66.1 3.0 — — 397.9 56.1
15
3.5 5.1 — — — — — — — — — 5.1 100.0
16
63.0 102.5 3.0 4.6 2.0 11.8 0.6 21.1 2.0 — — 147.6 69.4
17
(4-O-5)
100 36.6 — — — — — — — — — 48.7c 75.2
18
(α-O-4)
91.7 27.5 — — 20.7 — — — — — — 902.8d 3.0
19
(5-5)
0.0 — — — — — — — — — — — —
20
(β-1)
100 30.4 0.8 — — — — — — — — 529.5e 5.7
Reaction conditions: 0.25 g model compound, 0.9 mmol [BSmim]CuPW12O40 catalyst, 20 mL 100% ethanol, 433 K, 5 h, 0.8 MPa O2. a not detected;
b including 83.3 mg g-1 of other volatile products; c propanedioic acid, diethyl ester: 12.1 mg g-1; d benzoic acid, ethyl ester: 839.9 mg g-1, benzoic
acid:14.7 mg g-1; e benzene, 1-methoxy-4-methyl-: 10.6 mg g-1; benzene, 1-ethyl-4-methoxy-: 6.6 mg g-1; benzenemethanol, 4-methoxy-, formate:
19.3 mg g-1; benzaldehyde, 4-methoxy-: 50.1 mg g-1; benzoic acid, 4-methoxy-, ethyl ester: 396.3 mg g-1; benzoic acid, 4-methoxy-,4-ethylphenyl
ester: 15.4 mg g-1. 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate; 4: Ethyl ethoxyacetate; 5: Diethyl oxalate; 6: Diethyl malonate; 7:
Ethyl diethoxyacetate; 8: Ethyl 3,3-diethoxypropionate; 9: Ethyl 4-hydroxybenzoate; 10: Ethyl vanillate.
Plausible pathway for lignin depolymerization and oxidative ring cleavage
Based on above mentioned process of lignin oxidative ring cleavage, product distribution and
typical lignin depolymerization product oxidation, a plausible pathway for this efficient
depolymerization of lignin and DEM formation from the renewable lignin is proposed in the context
of literature (Figure S12).9-12 For the DEM production, the lignin (1) is firstly dehydrated under
strong acidic condition to form vinyl ether (2)11 in adjacent to the β-aryl ether bond probably via
benzylic carbocation formation. Without catalyst, the reactive carbocation may attack electron-rich
lignin aromatic rings leading to C-C formation (Shuai et al. used formaldehyde to block this
reactive species during hydrogenolysis of lignin to produce improved yields of monomers).13-15
However, we show that in the intimate contact of Cu2+ polyoxometalate in air, this ether reacts with
superoxo species from the Cu active site (see Cu catalyst elucidation in next section) to produce a
dioxetane intermediate (3). Subsequently, the C−C and O−O bond cleavage of compound 4 occurs
to afford ester (5) and aldehyde (6). It should be emphasized here that the initial aromatic aldehydes
and glycolic acid which is produced by the above-mentioned intermediates can be directly detected
by gas chromatography mass spectrometry (GC-MS) in form of esters (Table S10).
Figure S12. The pathway for lignin depolymerization and in situ aromatic ring oxidation.
Then, extensively acetalization of aldehyde (6) in ethanol occurs with
4-(diethoxymethyl)-2-methoxyphenol as the product. This compound can be easily oxidized to
benzoquinones, the main intermediate for maleic acid production in the phenol oxidation
technology, after a series continuous process of oxidation and demethoxylation.10,16,17 Further, the
quinones are converted to maleic acid via ring cleavage.18 Finally, the product of stable DEM is
achieved by the rapid esterification of maleic acid in ethanol without much side reactions. On the
other hand, lignin (1) can also be initially oxidized to ketones (7), which undergoes Keto-enol
tautomerism step (this process can be confirmed by above HSQC, FT-IR, and 13C-NMR
characterization of the original and regenerated lignin as shown in Figure 3 and Figure S11) to form
the vinyl ether (8). The compound (8) is then transformed to ester (5) and carboxylic acid (10)
through intermediate 9 via a similar C-C bond and O-O bond cleavage as that of chemical (3).9,12,19
Simultaneously, the carboxylic acid (10) is esterified with ethanol. Both the carboxylic acid and
ester would be decarboxylated20 as anticipated over the POM-IL catalyst. The decarboxylation
product is then oxidized to benzoquinones, which finally gives the target product of DEM through
the same oxidation and esterification process as that of aldehyde (6). To support this cleavage
pathway, oxidation of quinones is investigated. As shown in Table S20, the intermediates could be
converted efficiently with 100% conversion in the ethanol, giving DEM selectivity of higher than
70% for each run.
Table S20. Selective oxidation of typical model compounds.
Entry Substrates
Conversion
(%)
Yield (mg g-1)a DEM
selectivity
(%)
1 2 3 4 5 6 7 8 total
1
100 447.2 26.4 32.4 6.4 18.3 10.8 37.9 2.7 582.1 76.8
2
100 377.3 19.7 23.2 7.5 25.2 12.7 36.3 — 501.9 75.2
3
100 585.4 29.6 43.0 7.3 — 14.0 40.3 2.4 722.0 81.1
4
100 412.5 24.3 31.2 6.3 25.6 15.6 44.1 2.8 562.4 73.3
5
100 389.5 20.2 27.2 5.7 14.5 9.7 31.7 2.4 500.9 77.8
6
100 356.2 21.6 34.8 5.8 22.1 13.1 43.1 2.2 498.9 71.4
7
100 451.5 21.2 37.9 5.3 10.2 11.9 44.3 2.5 584.8 77.2
Reaction conditions: 0.25 g substrate, 0.9 mmol [BSmim]CuPW12O40, 20 mL 100% ethanol, 433 K, 5 h, 0.8 MPa O2. a not
detected. 1: Diethyl maleate; 2: Diethyl succinate; 3: Diethyl fumarate 4: Ethyl ethoxyacetate; 5: Diethyl oxalate; 6:
Diethyl malonate; 7: Ethyl diethoxyacetate; 8: Ethyl 3,3-diethoxypropionate.
Potential Separation of DEM
DEM can be separated with chromatographic techniques using an eluent composed of
n-hexane and petroleum ether at the bench-scale. At larger scale it can be separated using
rectification on the basis of boiling point differences between the products. There are several filed
patents regarding the recovery and purification of maleic acid esters: process for the recovery of
dialkyl succinate or dialkyl maleate (WO2016174388A1), process for the production of dimethyl
maleate (EP1678117B1), process for the preparation of dimethyl maleate (US4827022A),
dimethyl maleate purification method (CN106187775A).
Supplemental References
1. Long, J., Li, X., Guo, B., Wang, L., and Zhang, N. (2013). Catalytic delignification of sugarcane bagasse in
the presence of acidic ionic liquids. Catal. Today 200, 99-105.
2. Evtuguin, D.V., Neto, C.P., Silva, A.M.S., Domingues, P.M., Amado, F.M.L., Robert, D., and Faix, O.
(2001). Comprehensive study on the chemical structure of dioxane lignin from plantation Eucalyptus
globulus wood. J. Agric. Food Chem. 49, 4252-4261.
3. Capanema, E.A., Balakshin, M.Y., and Kadla, J.F. (2005). Quantitative characterization of a hardwood
milled wood lignin by nuclear magnetic resonance spectroscopy. J. Agric. Food Chem. 53, 9639-9649.
4. Cole, A.C., Jensen, J.L., Ntai, I., Tran, K.L.T., Weaver, K.J., Forbes, D.C., and Davis, J.H. (2002). Novel
brønsted acidic ionic liquids and their use as dual solvent-catalysts. J. Am. Chem. Soc. 124, 5962-5963.
5. Langpape, M., Millet, J.M.M., Ozkan, U.S., and Boudeulle, M. (1999). Study of cesium or
cesium-transition metal-substituted Keggin-type phosphomolybdic acid as isobutane oxidation catalysts: I.
structural characterization. J. Catal. 181, 80-90.
6. Leng, Y., Wang, J., Zhu, D., Ren, X., Ge, H., and Shen, L. (2009). Heteropolyanion-based ionic liquids:
reaction-induced self-separation catalysts for esterification. Angew. Chem. Int. Ed. 48, 168-171.
7. Thompson, S.P., Parker, J.E., Potter, J., Hill, T.P., and Birt, A. (2009). Beamline Ill at diamond: a new
instrument for high resolution powder diffraction. Rev. Sci. Instrum. 80, 075107.
8. Ravel, B., and Newville, M. (2005). Athena, Artemis, Hephaestus: data analysis for X-ray absorption
spectroscopy using IFEFFIT. J. Synchrotron Rad. 12, 537-541.
9. Rahimi, A., Azarpira, A., Kim, H., Ralph, J., and Stahl, S.S. (2013). Chemoselective metal-free aerobic
alcohol oxidation in lignin. J. Am. Chem. Soc. 135, 6415-6418.
10. Santos, A., Yustos, P., Quintanilla, A., Rodríguez, S., and García-Ochoa, F. (2002). Route of the catalytic
oxidation of phenol in aqueous phase. Appl. Catal. B: Envir. 39, 97-113.
11. Nichols, J.M., Bishop, L.M., Bergman, R.G., and Ellman, J.A. (2010). Catalytic C-O bond cleavage of
2-aryloxy-1-arylethanols and its application to the depolymerization of lignin-related polymers. J. Am.
Chem. Soc. 132, 12554-12555.
12. Lancefield, C.S., Ojo, O.S., Tran, F., and Westwood, N.J. (2015). Isolation of functionalized phenolic
monomers through selective oxidation and C-O bond cleavage of the β-O-4 linkages in lignin. Angew.
Chem. Int. Ed. 54, 258-262.
13. Shuai, L., Amiri, M.T., Questell-Santiago, Y.M., Héroguel, F., Li, Y., Kim, H., Meilan, R., Chapple, C.,
Ralph, J., and Luterbacher, J.S. (2016). Formaldehyde stabilization facilitates lignin monomer production
during biomass depolymerization. Science 354, 329-333.
14. Renders, T., Bosch, S.V.d., Koelewijn, S.F., Schutyser, W. and Sels, B.F. (2017). Lignin-first biomass
fractionation: the advent of active stabilisation strategies. Energ. Environ. Sci. 10, 1551-1557.
15. Kärkäs, M.D. (2017). Lignin hydrogenolysis: improving lignin disassembly through formaldehyde
stabilization. ChemSusChem 10, 2111-2115.
16. Dodds, D.R., and Gross, R.A. (2007). Chemicals from biomass. Science 318, 1250-1251.
17. Minh, D.P., Aubert, G., and Besson, G.M. (2007). Degradation of olive oil mill effluents by catalytic wet air
oxidation: 2-oxidation of p-hydroxyphenylacetic and p-hydroxybenzoic acids over Pt and Ru supported
catalysts. Appl. Catal. B: Envir. 73, 236-246.
18. Ma, R., Xu, Y., and Zhang, X. (2015). Catalytic oxidation of biorefinery lignin to value-added chemicals to
support sustainable biofuel production. ChemSusChem 8, 24-51.
19. Rahimi, A., Ulbrich, A., Coon, J.J., and Stahl, S.S. (2014). Formic-acid-induced depolymerization of
oxidized lignin to aromatics. Nature 515, 249-252.
20. Mundle, S.O.C., and Kluger, R. (2009). Decarboxylation via addition of water to a carboxyl group: acid
catalysis of pyrrole-2-carboxylic acid. J. Am. Chem. Soc. 131, 11674-11675.