Barbara Rietzler1, Maria Karlsson1, Isabella Kwan1, Martin Lawoko1, Monica Ek1. 1. Division of Wood Chemistry and Pulp Technology, Department Fibre and Polymer Technology and Wallenberg Wood Science Centre (WWSC), School of Engineering Sciences in Chemistry, Biotechnology and Health (CBH), KTH Royal Institute of Technology, Teknikringen 56, Stockholm SE-100 44, Sweden.
Abstract
The interest in the bark and the attempt to add value to its utilization have increased over the last decade. By applying an integrated bark biorefinery approach, it is possible to investigate the recovery of compounds that can be used to develop green and sustainable alternatives to fossil-based materials. In this work, the focus is on extracting Norway spruce (Picea abies) bark lignin via organosolv extraction. Following the removal of the extractives and the subcritical water extraction to remove the polysaccharides, a novel cyclic organosolv extraction procedure was applied, which enabled the recovery of lignin with high quality and preserved structure. Main indicators for low degradation and preservation of the lignin structure were a high β-O-4' content and low amounts of condensed structures. Furthermore, high purity and low polydispersity of the lignin were observed. Thus, the obtained lignin exhibits high potential for use in the direct development of polymer precursors and other bio-based materials. During the extraction sequence, around 70% of the bark was extracted. Besides the lignin, the extractives as well as pectic polysaccharides and hemicelluloses were recovered with only minor degradation, which could potentially be used for the production of biofuel or other high-value products such as emulsifiers or adhesives.
The interest in the bark and the attempt to add value to its utilization have increased over the last decade. By applying an integrated bark biorefinery approach, it is possible to investigate the recovery of compounds that can be used to develop green and sustainable alternatives to fossil-based materials. In this work, the focus is on extracting Norway spruce (Picea abies) bark lignin via organosolv extraction. Following the removal of the extractives and the subcritical water extraction to remove the polysaccharides, a novel cyclic organosolv extraction procedure was applied, which enabled the recovery of lignin with high quality and preserved structure. Main indicators for low degradation and preservation of the lignin structure were a high β-O-4' content and low amounts of condensed structures. Furthermore, high purity and low polydispersity of the lignin were observed. Thus, the obtained lignin exhibits high potential for use in the direct development of polymer precursors and other bio-based materials. During the extraction sequence, around 70% of the bark was extracted. Besides the lignin, the extractives as well as pectic polysaccharides and hemicelluloses were recovered with only minor degradation, which could potentially be used for the production of biofuel or other high-value products such as emulsifiers or adhesives.
In respect of the increasing environmental
concerns caused by the
production of chemicals, energy, and materials from fossil fuels,
the search for alternatives has gained attention over the last decade.
The forest industry provides a large amount of available lignocellulosic
biomass and thus a source of renewable materials to replace fossil-based
materials.[1] However, the increased interest
in these materials requires efficient and optimal exploitation of
the resources. Currently, large amounts of side products, such as
bark and lignin, are generated in the timber, paper, and pulp industries
in the Nordic countries, and these are mainly used in an inefficient
way for energy production by combustion.[2] The production of value-added materials, fuels, and chemicals from
this biomass in an integrated biorefinery will provide full valorization
while pursuing a zero-waste philosophy.[3]One of the main side products generated by the forest industry
is the tree bark. Due to its chemical richness, high availability,
and low cost, it shows great potential for the production of value-added
materials. To provide a more efficient use of this inexpensive raw
material, integrated bark biorefinery concepts have been investigated.[4−8] The composition of the bark can vary considerably compared to the
respective wood; however, the main constituents are the same, namely,
cellulose, hemicellulose, lignin, and extractives.[9,10] Considering
these compounds and their already known properties, their utilization
for the production of high-value materials seems to be obvious. The
most challenging aspect, though, is to separate the different components
because the chemical richness also results in higher complexity. Therefore,
it is very important to understand the structure and composition in
detail. Only a detailed knowledge of the individual components will
allow for the creation of a feasible strategy to generate an integrated
biorefinery of the bark that can be applied on an industrial scale.Several studies on the fundamental structure and composition of
the bark of various tree species have been performed in recent years.[5,9−12] One of the most abundant species and also readily available as a
side product of the forest industry in large quantities is the Norway
spruce bark. Its chemical composition and structure and the potential
applications of the individual constituents have already been studied.[9] Substantial research has been performed on the
characterization of the hydrophilic extractives, condensed tannins,
and stilbene glucosides, which have attracted great attention because
of their bioactivity and antibacterial and antioxidant properties.[13−15] Furthermore, the extraction and recovery of the polysaccharides
as well as the isolation of nanocellulose from the bark have been
examined, although in a smaller number of studies compared to the
extractives.[13,16,17] Hence, substantial work has to be done on the valorization of the
bark.Nonetheless, the fourth main component, lignin, has only
been dealt
with in a few studies. In general, lignin was already revealed to
show high potential as a replacement for fossil-based materials.[18−21] It is a complex, natural aromatic compound that is built from the
three main hydroxycinnamyl alcohols, p-coumaryl,
coniferyl, and sinapyl alcohol.[22] Recently,
a study on the fundamental structure of Norway spruce bark lignin
has been published. By extracting milled bark lignin (MBL), it was
shown that phenolic compounds, such as the hydroxy stilbene glucosides,
are incorporated in the structure of Norway spruce bark lignin and
behave as true lignin monomers.[23] Yet,
the structure of lignin depends strongly on the extraction method
used to recover the lignin. The commonly recovered kraft and sulfite
lignin from the pulping industry show a nonuniform structure and low
purity, which limits their use for high-value application.[24] An alternative extraction method is the organosolv
process, where aqueous organic solvents such as alcohols or ketones
are used in combination with organic or mineral acids as catalysts.
The relatively mild conditions allow for the extraction of lignin
with a more uniform structure and higher purity.[25] However, economic aspects have so far prevented its application
on an industrial scale. Thus, although the quality of the lignin is
comparable or even superior to conventionally recovered lignin, these
methods cannot be replaced yet.Precisely, the extraction of
lignin from the bark by organosolv
extraction has been studied only in a few works. Organosolv lignin
(OSL) has been extracted and characterized from sugar maple bark,[26] pine and oak bark[27] and willow bark.[28] In all works, high
purity of the lignin has been reported. In many cases, organosolv
pulping is used for the production of biofuels from the resulting
residue as well as the aqueous phase where the dissolved polysaccharides
can be found. Thus, the organosolv process can be seen as a circular
bioeconomy concept that facilitates the production of valuable biopolymers
(lignin and cellulose) and advanced biofuels obtained from a low-cost
byproduct of the forest industry. Environmental and cost assessment
of this process show that there is potential for the OSL production
process from the bark.[29] The use of an
inexpensive raw material from which high-value lignin is obtained
could increase the economic feasibility of the process.In this
study, we hypothesize that high-quality lignin can be extracted
from Norway spruce bark while also recovering the other individual
constituents for value-added applications and biofuel production in
a sustainable engineered concept. A sequence of Soxhlet extraction
and subcritical water extraction in an accelerated solvent extractor
(ASE) was followed by a mild organosolv extraction to recover the
lignin with ethanol/water and 1.5 wt % sulfuric acid (H2SO4) as a catalyst. The subcritical water extraction has
already been investigated and reported in a previous work.[30] A novel cyclic extraction process[31] was investigated for bark, which was expected
to reduce degradation of lignin by the cyclic concept. Investigation
of the extracted lignin by two-dimensional (2D) NMR and molecular
weight analysis gave an insight into the fundamental structure of
OSL from the bark with low degradation and will help to improve the
process for future applications.
Materials and Methods
Materials
The bark of Norway spruce was sampled from
a tree cut in Norra Djurgården (Stockholm, Sweden) in July
2020. The inner and outer barks were manually separated using a scalpel.
The inner bark was freeze-dried and ground with a Wiley mill (3383L70,
Thomas Scientific, New Jersey, USA) to a particle size of 20 mesh.All chemicals were purchased from Sigma-Aldrich in analytical grade
and used without further purification, unless stated otherwise.
Sequential Extraction of Inner Bark
The ground inner
bark was sequentially extracted starting with Soxhlet extraction in
acetone/water (9:1 v/v, 40 cycles) to remove the extractives (hydroxy
stilbene glucoside, and condensed tannins). The acetone was evaporated
under reduced pressure, and the extractives were obtained in a powder
form. Then, subcritical water extraction with an ASE (Dionex, California,
USA) was performed at 100, 140, and 160 °C and a pressure of
100 bar. An extraction program with three cycles of 20 min was used
at each temperature. The fractions were freeze-dried before further
analysis.
Lignin Extraction
After subcritical water extraction,
the extraction of lignin with the solvent ethanol/water (70:30, v/v,
1.5 wt % H2SO4) at 160 °C and 100 bar was
also performed using an ASE. The extraction was carried out in 15
cycles for 5 min each. MilliQ water was added to the extract to precipitate
the lignin, and ethanol was removed by rotary evaporation under reduced
pressure. The aqueous solution containing the precipitated lignin
was centrifuged at 4688 G for 30 min in a Rotina 420 (Hettich Zentrifugen,
Tuttlingen, Germany) instrument, and the precipitate was washed with
MilliQ water two times. The obtained lignin was lyophilized before
further analysis. The supernatant after precipitation and centrifugation
was neutralized using sodium hydroxide solution 1 M, and the liquid
was evaporated in a rotavapor, and complete dryness was reached after
3 h of drying in an oven at 60 °C. The bark residue after all
ASE extractions was lyophilized.
MBL
Acetone extracted bark (AEB) and the bark residue
after all extractions [organosolv residue (OSR)] were ball-milled
in a Retsch PM-400 planetary ball mill (Duesseldorf, Germany). The
samples (ca. 8 g) were placed in 250 mL stainless-steel jars together
with 40 grinding balls. The samples were milled for 24 h at 300 rpm
in 1 h intervals with 30 min breaks. The ball-milled samples were
extracted following the classical procedure.[32] 5 g of sample was mixed with 125 mL of 96% (v/v) aqueous dioxane
(25 mL solvent/g ball-milled bark). The mixture was stirred for 72
h at room temperature. The obtained lignin after centrifugation was
freeze-dried, and no further purification was carried out.
Carbohydrate Analysis
Carbohydrate composition of the
samples was determined by acid hydrolysis in accordance with the TAPPI
T222 om-06 standard.[33] 200 mg of sample
was mixed with 3 mL of 72% H2SO4 and placed
under vacuum for 80 min with occasional stirring. MilliQ water (84
mL) was then added, and the hydrolysis was completed in an autoclave
2540EL (Tuttnauer Europe, Breda, The Netherlands) at 125 °C for
60 min. The mixtures were filtered on glass fiber filters to determine
the Klason lignin, and the hydrolysate was further diluted for analysis
with high-performance anion-exchange chromatography with pulsed-amperometric
detection using an ICS 3000 system (Dionex, Thermo Scientific, California,
USA).
Size Exclusion Analysis
The samples were acetylated
according to the protocol by Gellerstedt,[34] dissolved in tetrahydrofuran (THF; 2 mg/mL), and filtered through
a 0.45 μm PTFE syringe filter before injection. The separation
was carried out on a Waters system (Waters Sverige AB, Sollentuna,
Sweden) using Waters Ultrastyragel HR4, HR2, and HR0.5 (4.6 ×
300 mm) solvent-efficient analytical columns in series with a Styragel
guard column (THF, 4.6 × 300 mm) coupled to a Waters-2998 photodiode
array detector operated at 254 and 280 nm and an RI detector. Calibration
was performed with polystyrene standard solutions with molecular weights
ranging from 176 kDa to 266 Da using the UV detector 254 nm channel.
THF (HPLC grade) was used as the eluent.
1D and 2D NMR Analyses
All nuclear magnetic resonance
(NMR) analyses were performed with a Bruker Avance III HD 400 MHz
instrument (Bruker Corporation, Massachusetts, USA) at 300 K with
a BBFO probe equipped with a Z-gradient coil. Sensitivity
was improved with the gradient (e/a TAPPI). For the heteronuclear
single quantum coherence (HSQC) experiments, 80 mg of sample was dissolved
in 550 μL of deuterated dimethyl sulfoxide (DMSO). HSQC experiments
were carried out with the “hsqcetgpsi” pulse program.
A relaxation delay of 1.5 s was selected with a minimum of 80 scans
using 1024 × 256 increments with additional 16 dummy scans. The
spectra were processed with MestreNova software (version 9.0.0, Mestrelab Research). The spectra were Fourier
transformed, and a baseline and manual phase correction was applied
to both dimensions. The DMSO peak at δC/δH 39.5/2.50 ppm was used as the internal reference. For the
quantification, the signals of C2/H2 in lignin were selected as the
internal standard.31P NMR samples were prepared
following the protocol reported by Argyropoulos et al.[35] In short, 30 mg of lyophilized sample was dissolved
in 100 mL of N,N-dimethylformamide
and 100 mL of pyridine and phosphorylated with 2-chloro-4,4,5,5-tetramethyl-1,3,2-dioxaphospholane.
The internal standard was endo-N-hydroxy-5-norbornene-2,3-dicarboximide.
Results and Discussion
In order to investigate and
get a deeper insight into the structure
of Norway spruce bark lignin while recovering other constituents,
a mild extraction sequence was applied, as shown in Figure . Starting from the whole bark,
separation into inner and outer bark was done to reduce the complexity
and focus on the investigation of the inner bark. The sequential extractions
were chosen based on previous studies.[17,30]
Figure 1
Schematic depiction
of the extraction sequence of Norway spruce
bark; AEB—acetone extracted bark, SWB—subcritical water
extracted bark, SWE—subcritical water extracts, MBL—milled
bark lignin, OSE—organosolv extract, OSR—organosolv
residue, MRL—milled residue lignin, OSL—organosolv lignin,
PRF—polysaccharide-rich fraction. The percentage represents
the yield of the fraction in wt %.
Schematic depiction
of the extraction sequence of Norway spruce
bark; AEB—acetone extracted bark, SWB—subcritical water
extracted bark, SWE—subcritical water extracts, MBL—milled
bark lignin, OSE—organosolv extract, OSR—organosolv
residue, MRL—milled residue lignin, OSL—organosolv lignin,
PRF—polysaccharide-rich fraction. The percentage represents
the yield of the fraction in wt %.Soxhlet extraction with acetone/H2O
(9:1, v/v) is commonly
used to remove the hydrophilic and lipophilic compounds such as tannins,
stilbene glucoside, and fatty acids. The removal of these components
enables a more efficient extraction of the polysaccharides. The use
of a Soxhlet apparatus reduces the amount of solvent that is required
because of the cyclic extraction process, and the low temperatures
facilitate mild extraction conditions.Subcritical water extraction
was selected to recover the polysaccharides
from the bark with good yield and low degradation. At three temperatures
100, 140, and 160 °C, different fractions of polysaccharides
were extracted. At 100 °C, some residual extractives, oligosaccharides,
as well as some low-molecular-weight pectins were extracted. At 140
°C the fraction contained mainly pectic polysaccharides, whereas
at 160 °C, hemicelluloses were extracted.In order to extract
and recover bark lignin within this extraction
sequence, an organosolv extraction process was applied following the
subcritical water extraction. In this study, a temperature of 160
°C, a solvent composition of EtOH/H2O (70:30, v/v),
and 1.5 wt % sulfuric acid as a catalyst were selected. The extraction
was performed directly after the subcritical water extraction, and
the liquid–solid ratio (L/S) was kept at around 9. By using
an ASE, a dynamic cyclic extraction was possible to be applied, which
enables very mild extraction conditions by physical protection of
the sensitive lignin bonds.
Cyclic Organosolv Extraction Process
The organosolv
process has been investigated in several studies regarding the recovery
of lignin from wood; however, only a limited number of studies have
investigated the extraction of lignin from bark. In the following,
the focus is mainly on the properties of lignin extracted by a cyclic
organosolv extraction process. The cyclic organosolv process has previously
been developed by Karlsson et al.,[31] where
an additive-free process using physical protection to preserve the
lignin structure was designed. Within this study, the mildness of
the extraction process as well as the lignin properties of Norway
spruce inner bark lignin are studied.The β-O-4′
content was used as an indication for mild extraction conditions and
low degradation of the lignin. The amount of β-O-4′ linkages
and other native linkages in lignin were determined by semiquantitative
2D HSQC NMR analysis (Table ). By integration of the β-O-4′ Cα position
(hydroxylated and etherified), an amount of 30% was determined and
was similar to that found in the extracted wood lignin by the cyclic
organosolv process.[31] In general, organosolv
processes are known to degrade the lignin, and the recovered lignin
usually shows low β-O-4′ content. For example, Liu et
al. extracted pine bark using an organosolv one-batch process and
obtained a significantly lower β-O-4′ content compared
to dioxane-extracted lignin from the pine bark.[27] It is presumed that the cyclic extraction process provides
physical protection of the labile β-O-4′ bonds, and therefore
they are not cleaved as much as in the one-batch process. This is
because the dissolved material is removed from the reaction vessel
before it reacts significantly. Second, replacement of the removed
volume ensures a dilution of solutes, limiting the collisions necessary
for condensation reactions.
Table 1
Lignin Interunit Linkage Type Contents
from Integration of 2D HSQC NMR Spectra of Lignin Extracted from Norway
Spruce Inner Barka
OSL
MBL
MRL
β-O-4′
aryl ethers
30 ± 2
31
17
β-5′phenylcoumarans
12 ± 1
12
6.2
β–β′resinols
1.9 ± 0.2
2.2
1.9
5-5′ dibenzodioxocins
(DBDO)
0.5 ± 0.2
3.8
0.1
enolether
1.3 ± 0.1
1.0
coumaraldehyde
2.3 ± 0.2
0.8
Hibbert’s ketone
2.0 ± 0.1
1.2
2.1
Stilbene-β1
3.5 ± 0.5
1.4
1.1
Stilbene-β5
3.0 ± 0.3
0.4
1.5
The results of the OSL linkage values
are the mean of four measurements and the corresponding standard deviation.
The standard deviation also applies for the measurement of MBL and
MRL; OSL—lignin extracted by organosolv extraction, MBL—milled
raw bark extracted with dioxane, and MRL—milled residue after
organosolv treatment extracted with dioxane. The interunit linkages
are semiquantified per 100 Ar units using the C2 region in the aromatic
region as an internal standard.
The results of the OSL linkage values
are the mean of four measurements and the corresponding standard deviation.
The standard deviation also applies for the measurement of MBL and
MRL; OSL—lignin extracted by organosolv extraction, MBL—milled
raw bark extracted with dioxane, and MRL—milled residue after
organosolv treatment extracted with dioxane. The interunit linkages
are semiquantified per 100 Ar units using the C2 region in the aromatic
region as an internal standard.The β-O-4′ content for spruce bark lignin
extracted
by dioxane in this study was found to be around 31 per 100 Ar units
(MBL, Table ). This value has rarely been reported before in the literature;
only Neiva et al. reported a value of 44% based on total lignin interunit
linkages.[18] Thus, the OSL extracted by
the cyclic process shows merely a slight reduction of β-O-4′
linkages compared to the MBL, which is an indication for very low
degradation.It is observed for the extracted lignin that the
β-O-4′
Cα position appears to be both hydroxylated and etherified.
The signal of the β-O-4′ Cα etherified is observed
at δC/δH 79.7/4.5 ppm in the 2D
HSQC NMR spectra (see Figure ), and it is estimated by integration that around 57% of the
β-O-4′ linkages are etherified, which is in accordance
with the previously reported results from organosolv extracted lignin
from spruce wood.[31] The etherification
of the Cα position happens through a nucleophilic addition reaction
of ethanol to the benzylic cations formed under acidic conditions.[36] Etherification of the β-O-4′ linkages
increases the solubility of the lignin in ethanol. However, the etherification
does not prevent cleavage of the β-O-4′ linkages, which
is mainly avoided by the cyclic extraction process. Hence, the cyclic
approach in this study facilitates the extraction of lignin with a
preserved structure from Norway spruce inner bark and reduces the
degradation of the lignin usually occurring in the organosolv process.
Figure 2
2D HSQC
NMR of lignin extracted by cyclic organosolv process from
Norway spruce inner bark in DMSO-d6. The main lignin
interunit linkages are depicted to the right of the spectrum. β-O-4′ aryl ethers; β-5′ phenylcoumarans; β–β′ resinols; 5-5′ dibenzodioxocins (DBDO); Hibbert’s
ketone (HK); β-O-4’/3-O-α benzodioxane structure formed through coupling of coniferyl alcohol
and astringin; 8-O-4’/3′-O-7 benzodioxane
structure formed by stilbene glucoside units; Stilbene-β1’; Stilbene-β5’. Note that the glucoside
units of the hydroxystilbene glucosides have been cleaved under the
organosolv conditions.
2D HSQC
NMR of lignin extracted by cyclic organosolv process from
Norway spruce inner bark in DMSO-d6. The main lignin
interunit linkages are depicted to the right of the spectrum. β-O-4′ aryl ethers; β-5′ phenylcoumarans; β–β′ resinols; 5-5′ dibenzodioxocins (DBDO); Hibbert’s
ketone (HK); β-O-4’/3-O-α benzodioxane structure formed through coupling of coniferyl alcohol
and astringin; 8-O-4’/3′-O-7 benzodioxane
structure formed by stilbene glucoside units; Stilbene-β1’; Stilbene-β5’. Note that the glucoside
units of the hydroxystilbene glucosides have been cleaved under the
organosolv conditions.The amount of typical lignin interunit linkages
such as β-O-4′,
β-5′, and β–β′ detected in
the OSL compared to the milled raw bark lignin (MBL) are shown in Table . The 2D HSQC NMR spectra of MBL are shown in Figure
S1 in the Supporting Information. It can
be seen that the values are in the same range, and they are also in
accordance with the values reported for cyclic-extracted OSL from
spruce wood; however, the values reported in the literature for milled
raw bark lignin from spruce bark are marginally higher. Some minor
signals in the 2D HSQC NMR were observed at around δC/δH 112.5/6.75 ppm and δC/δH 120.5/6.60 ppm, which can be assigned to C2/H2 and C6/H6
of 5-5′ condensed substructures. Although the signals are still
weak, compared to the MBL, they are slightly stronger. These 5-5′
linkages are both native and could be formed.[31,37] It can be assumed that during the organosolv extraction, some of
the β-O-4′ linkages are cleaved, which leads to the formation
of β- and phenoxy radicals. From the phenoxy radicals, C5 radicals
emerge, which then couple to the 5-5′ condensed substructures.
Also, by quantitative 31P NMR analysis, it was determined
that the amount of C5-substituted OH groups was higher compared to
the MBL (Figure ).
Figure 3
Comparison
of hydroxy functionalities determined by 31P NMR between
OSL, MBL, and MRL; the values are the mean of at least
two measurements; the standard deviation was only determined for OSL.
Comparison
of hydroxy functionalities determined by 31P NMR between
OSL, MBL, and MRL; the values are the mean of at least
two measurements; the standard deviation was only determined for OSL.In another technical lignin, for example, in softwood
kraft lignin,
an amount of 0.9–1.3 mmol g–1 C5-substituted
OH functionality is reported, which is considerably higher.[38]Hibbert’s ketone are formed as
minor products through an
acidolysis reaction of aryl ether bonds. In summary, the OSL seems
to be slightly more condensed and degraded compared to the MBL, but
many indicators reveal mild extraction conditions with a perseverance
of the lignin structure. Besides, the OSL shows less degradation compared
to the other technical lignin.Additionally, from the 2D HSQC
NMR analysis, it can be said that
the OSL from the bark has high purity since signals assigned to polysaccharides
are only detected at trace levels. However, there are signals observed
that suggest the presence of incorporated stilbene glucoside structures
in the bark lignin, which has been reported recently on MBL by Rencoret
et al.[23] For example, by 8-O-4′coupling
of an isorhapontin and an astringin unit, benzodioxane structures
could be formed that would result in a peak at around δC/δH 79.0/5.0 ppm, which was observed in the
2D HSQC NMR spectra of the OSL from the spruce bark (Figure ). Similar signals have been
reported for dimeric hydroxy stilbene structures detected in the extracts
of Norway spruce bark, but the presence of dimeric hydroxy stilbene
structures can be excluded since these structures are highly soluble
in water; thus they are removed by the intensive extraction sequence.[39] Therefore, it was proposed by Rencoret et al.
that these hydroxy stilbene glucosides are incorporated in the lignin
structure.[23] Further evidence was provided
by the detection of signals at δC/δH 75.8/4.90 ppm and δC/δH 78.0/4.15
ppm, which are assumed to result from the correlation of Cα/Hα and Cβ/Hβ of
the formed benzodioxane structure by the cross-coupling of coniferyl
alcohol and the catechol moiety of astringin (Figure ). From the presence of these signals in
the OSL, it can be speculated that the organosolv extraction is not
cleaving these linkages either, and it is possible to extract lignin
with incorporated stilbene structures by organosolv treatment. A significant
difference compared to the previous work on MBL, however, is that
in the OSL, the presence of glucose from the glucoside residue is
very low. Thus, it is assumed that the linkage between the stilbene
incorporated in the lignin and the glucoside residue is cleaved during
the organosolv extraction through hydrolysis. The integration of stilbene
glucosides into the lignin structure would provide the lignin with
exceptional properties, such as antibacterial and antioxidant properties.
The possibility to extract lignin with these additional structure
types increases the potential for high-value applications.Furthermore,
the presence of stilbene structures formed as a result
of the extraction process was detected by 2D HSQC NMR. Stilbene-β1′
and stilbene-β5′ are formed during the elimination of
formaldehyde from phenylcoumaran (β5′) and spirodienone
(β1′) (mechanism can be found in Scheme S1 in the Supporting Information). It can be clearly seen
that those structures are formed during the extraction since their
amount is significantly higher in the OSL than in the MBL. The signals
of Stilbene-β1′ and stilbene-β5′ occur in
the aromatic region at δC/δH 120-130/6.9–7.4
ppm, which can be seen in Figure . In comparison, in the spectrum of MBL in Figure S1, the signals of the stilbene glucosides
have a lower shift of δC/δH 110—120/6.2—6.8
ppm.The OSL was further analyzed by size exclusion chromatography
(SEC)
analysis to determine the molecular weight and polydispersity (PD).
The number- and weight-average molecular weights as well as the PD
are shown in Figure . As can be seen, the number-average molecular weight (Mn) does not change significantly between the OSL and the
MBL; however, the weight-average molecular weight (Mw) seems to be higher in the OSL. The differences in Mw might be due to the fact that some of the
low-molecular-weight lignin is already extracted during the subcritical
water extraction; thus the OSL contains lignin with higher molecular
weight. Also, the MBL was extracted with dioxane, and no further purification
to remove polysaccharides was performed; therefore, the MBL contains
a significant amount of low-molecular-weight polysaccharides.
Figure 4
Weight-average
(Mw) and number-average
(Mn) molecular weights and corresponding
PD of the OSL, the MBL, and the MRL determined by THF SEC; the values
are the mean of at least two measurements; the standard deviation
was only determined for OSL. Chemical composition before and after
organosolv extraction.
Weight-average
(Mw) and number-average
(Mn) molecular weights and corresponding
PD of the OSL, the MBL, and the MRL determined by THF SEC; the values
are the mean of at least two measurements; the standard deviation
was only determined for OSL. Chemical composition before and after
organosolv extraction.Mn, however, is considered
to be the
more representative value when it comes to molecular weight determination
of lignin. The ball milling of the bark before dioxane extraction
to obtain the MBL and MRL might also have an effect on the molecular
weight of the lignin since it might cleave some interunit linkages;
therefore, it does not represent the true molecular weight before
ball milling. It can be seen that the PD of the OSL is low, which
is especially preferred when it comes to the application of lignin
as polymer precursors.[40,41]To determine the efficiency
of the extraction sequence, the chemical
composition of the raw bark and the residue after organosolv extraction
was analyzed by acid hydrolysis. In the beginning, the raw inner bark
is composed of 20.6% extractives, 28.5% noncellulosic polysaccharides,
18.7% cellulose, 21.1% lignin, and 11.1% other minor components; the
exact composition can be found in Table S1 in the Supporting Information. As shown in Figure , 70.8% of the bark is extracted within the
extraction sequence, and the obtained residue is rich in cellulose,
as well as some remaining lignin. The residue contains 18.7% cellulose,
7.9% lignin, 0.6% noncellulosic polysaccharides, and 2.0% other minor
components based on the initial mass of the raw bark. Thus, most of
the noncellulosic polysaccharides are removed during the extraction;
the cellulose is preserved and around 63% of the lignin is removed,
although in the organosolv extraction itself, only 3.4% lignin (based
on initial raw bark mass) representing 16.1% of the total lignin is
recovered. Therefore, further analysis of the subcritical water extracts
was performed.
Figure 5
Chemical composition of Norway spruce bark before and
after organosolv
extraction.
Chemical composition of Norway spruce bark before and
after organosolv
extraction.From 2D HSQC NMR, it can be concluded that some
lignin is extracted
during the subcritical water extraction since signals occurring in
the aromatic region (δC/δH 100-140/5-8
ppm) are observed in all spectra of the subcritical water extracts
(Figure S2). These signals can be assigned
to C2/H2, C5/H5, and C6/H6 of the G units of the bark lignin. Nevertheless,
the intensity of the signals was low compared to the signals resulting
from the carbohydrates present in the extract. The 100 °C fraction
also showed some characteristic signals of the aromatic ring of the
stilbene glucoside at δC/δH 102.5/6.35
ppm C4/H4, δC/δH 104.5/6.75 ppm
C2/H2, and δC/δH 106.9/6.55 ppm
C6/H6. Therefore, the strong glucose and especially the C1/H1 signal
around δC/δH 100.4/4.8 ppm can be
assigned to the glucoside residue. Thus, not all extractives were
removed during the acetone/H2O extraction in the first
step. Still some signals from rhamnose and galactose, which indicate
the extraction of some pectic polysaccharides, are detected. On the
contrary, the 140 °C fraction shows mainly signals resulting
from correlations that can be assigned to pectic polysaccharides,
such as rhamnose, arabinose, galactose, and galacturonic acid. A more
detailed analysis of the pectin present in the Norway spruce bark
has recently been reported by Le Normand et al.[42] In the 160 °C fraction, signals of xylose and mannose
in addition to the pectic sugar signals were observed. It was observed
from 2D NMR HSQC that the polysaccharides found in all three extracts
show almost no degradation. The pectin obtained from the extraction
could therefore be used in higher-value applications, for example,
as emulsifier or thickener in food applications.In total, 20.7%
of the bark is extracted in the subcritical water
extraction (100 °C—5.0%; 140 °C—8.0%; 160
°C—7.7%). To determine the amount of lignin, acid hydrolysis
was performed on the extracts. The detailed carbohydrate composition
of the extracts can be found in Table S2 in the Supporting Information. In Figure the amount of lignin extracted in each step
is shown. It was found that around 17.2% of all lignin was extracted
during subcritical water extraction. Summing up the lignin from subcritical
water extraction and organosolv extraction, ca. 33.3% of lignin is
extracted; however, when looking at the amount remaining in the residue
after the extraction sequence (37.4%), still 29.3% is missing. It
is assumed that those are not precipitated from the organosolv extract
and remain in the aqueous polysaccharide-rich fraction (PRF). 2D HSQC
NMR analysis of the neutralized aqueous phase also confirms the presence
of some lignin in the PRF, but exact determination of the mass is
difficult since neutralization of the extract was performed to avoid
further degradation. The 2D NMR spectrum is shown in Figure S3 in
the Supporting Information; the presence
of the methoxyl signal at δC/δH 55.4/3.7
ppm was used as an indication. Additionally, UV/vis was performed
on the aqueous phase to corroborate the presence of lignin (Figure
S4 in the Supporting Information). Another
hypothesis could be that the lignin content of the raw bark is overestimated.
By the commonly used Klason lignin determination, it is possible that
some extractives (tannin and stilbene glucoside) are condensed during
the harsh acid treatment and end up in the Klason lignin, which would
give the appearance of a higher lignin content than actually present
in the raw bark.
Figure 6
Illustration of each extraction step and the amount of
lignin extracted
in each; SWB—subcritical water extracted bark, SWE—subcritical
water extract, OSE—organosolv extract, OSL—organosolv
lignin, OSR—organosolv residue, PRF—polysaccharide-rich
fraction. The lignin percentage represents the total amount of lignin
in each fraction; KL—Klason lignin, ASL—acid-soluble
lignin.
Illustration of each extraction step and the amount of
lignin extracted
in each; SWB—subcritical water extracted bark, SWE—subcritical
water extract, OSE—organosolv extract, OSL—organosolv
lignin, OSR—organosolv residue, PRF—polysaccharide-rich
fraction. The lignin percentage represents the total amount of lignin
in each fraction; KL—Klason lignin, ASL—acid-soluble
lignin.Since the presence of some extractives was observed
in the 100
°C fraction, this is absolutely possible. In that case, the amount
of missing lignin might be much lower.
Investigation of Residual Lignin after Organosolv Extraction
Moreover, the structure of the remaining lignin, which was not
extracted, was investigated to get a better understanding of the extraction
process and its limitations. The residue after organosolv extraction
was ball-milled and extracted with dioxane to recover the MRL. Analysis of the 2D HSQC NMR spectra reveals some interesting characteristics
of the residual lignin (Figure ). In the following, the chemical and physical properties
of the MRL are evaluated, and possible reasons for the limited extractability
of it are discussed. First of all, the amount of β-O-4′
linkages was determined by integration to be around 18%, which is
significantly lower compared to the OSL and MBL (see Table ). This observation suggests
that lignin with a higher β-O-4′ content is easier to
be extracted in the organosolv process, and hence the remaining lignin
is poorer in β-O-4′ linkages.
Figure 7
2D HSQC NMR of lignin
extracted from the residue after organosolv
extraction in DMSO-d6. The main lignin interunit
linkages are assigned in the spectrum, and the associated structures
are depicted in Figure .
2D HSQC NMR of lignin
extracted from the residue after organosolv
extraction in DMSO-d6. The main lignin interunit
linkages are assigned in the spectrum, and the associated structures
are depicted in Figure .It can be noticed, however, that even in the residual
lignin, the
β-O-4′ Cα position appears to be both hydroxylated
and etherified (Figure ). As mentioned earlier, the etherification of the β-O-4′
Cα position is assumed to improve the solubility of the lignin
in ethanol. It seems that the lignin in the residue is not dissolved
in ethanol, although it is etherified. The proportion of β-O-4′
Cα etherified with regard to the total amount of β-O-4′
is around 64%, which is even higher compared to the OSL. It was suspected
that the MRL exhibits lower etherification, which could cause lower
solubility and extractability of the lignin; however, from this result,
this theory can be rejected.It was further noticed that the
signals of 5-5′ substructures
are stronger compared to the OSL, which would confirm the assumption
that the MRL is more condensed in its structure and therefore limits
the extraction by the mild organosolv process. Lignin condensation
could occur in the residual lignin since this fraction remains in
the extraction vessel all through the extraction period, but it is
also likely that these condensed structures are already present in
the lignin of the raw bark and are enriched. Lignin condensation of
the residual lignin was further investigated by 31P NMR
quantification, and it seems that the hydroxy functionalities are
similar to the OSL as can be seen in Figure . Other condensations might have occurred
between C6 on lignin and Cα on another lignin moiety, which
cannot be detected by 31P NMR due to the too far distance
from the phenolic OH group to give a shift.Similar to MBL in
the 2D HSQC NMR spectrum, MRL signals of some
polysaccharides are detected. From carbohydrate analysis it is known
that the only monosaccharides found in the residue are xylose and
mannose (Table S1). Thus, the presence
of pectic polysaccharides can be excluded. The identity of the structures
resulting in the correlation peaks around δC/δH 88.0–97.5/4.6–5.2 ppm has not yet been determined
and will need further investigation, but it is assumed that they are
resulting from xylose and mannose structures. It is also observed
that the cross-coupling peak of coniferyl alcohol and the catechol
moiety of astringin at δC/δH 75.8/4.90
ppm and δC/δH 78.0/4.15 ppm is still
present in the residue, but the 8-O-4′coupling of isorhapontin
and astringin at around δC/δH 79.0/5.0
ppm is not detected anymore. Their integration into the lignin structure
might also be a reason for the limited extractability of the bark
lignin. It can be some indication for limited accessibility of the
solvent in the organosolv extraction, which is overcome in the dioxane
extraction by the ball milling of the sample.Finally, the molecular
weight of the lignin plays an important
role when it comes to solubility. In Figure , the molecular weights of OSL, MBL, and
MRL are compared. It can be clearly seen that the PD of the MRL is
significantly higher compared to OSL and MBL, but with regard to the
molecular weight, no distinct conclusion can be drawn. Although the
weight-average molecular weight of MRL is considerably higher, the
number-average molecular weight of all three lignins is not significantly
different. Although it was expected to find a significantly higher
molecular weight of the MRL and MBL, this was not confirmed by SEC
analysis. An important thing to consider is the ball milling of the
sample, which also might induce some degradation and cleavage of bonds
that could result in lower molecular weight of MBL and MRL.In conclusion, the most plausible factor that reduces the extractability
of the lignin from the bark could be the limited accessibility of
the lignin by the solvent and possibly condensation reactions. Parameters
such as higher molecular weight were not confirmed by the methods
used in this study.
Conclusions
Extraction of lignin from Norway spruce
bark will be an interesting
process for the development of future bio-based materials. The use
of a cyclic organosolv process allows for the extraction of high-quality
lignin with promising properties. The high β-O-4′ content,
low condensation, and favored low PD facilitates the application of
lignin in direct development processes of polymer precursors. Incorporated
structures such as hydroxystilbene glucosides arising from hydroxystilbene
glucoside moieties originally incorporated into the lignin of Norway
spruce bark add antimicrobial and antioxidant properties, which further
increase the interest into this precious bark lignin type. The integrated
biorefinery enables the recovery of pectic polysaccharides and extractives
from the bark, which have already been investigated to show interesting
properties. In general, bio-based materials from the bark, an inexpensive
raw material generated as a side product of the pulp and paper industry,
can reduce the environmental impact created by non-bio-based materials.
While the raw material is inexpensive, technical feasibility and sustainability
of the process are critical and remain to be assessed.
Authors: Duarte M Neiva; Jorge Rencoret; Gisela Marques; Ana Gutiérrez; Jorge Gominho; Helena Pereira; José C Del Río Journal: ChemSusChem Date: 2020-06-02 Impact factor: 8.928