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Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8039
Deep Eutectic Solvents: Fractionation of Wheat Straw
Michal Jablonský,a,
* Andrea Škulcová,a
Lucia Kamenská,a
Milan Vrška,a
and
Jozef Šima b
Deep eutectic solvents (DESs) are a relatively new topic in science.
Their usage is not yet clearly defined, and the areas in which DESs may
be applied are constantly growing. A simple and clean fractionation of
the main components of biomass represents a very important step in
creating a clean, renewable carbon economy. A major challenge is the
use of DESs for fractionation of biomass components at lower
temperatures, without the use of expensive raw materials. In this work,
wheat straw was pretreated with six different DES systems composed of
choline chloride with urea (1:2), malonic acid (1:1), lactic (1:9; 1:10),
malic (1:1), and oxalic acid (1:1). The pretreated biomass was
characterized in terms of lignin content, ash, and holocellulose. A deep
eutectic solvent, composed of choline chloride and oxalic acid, was
found to produce the best delignification results. The solvents are not
selective in the process of delignification.
Keywords: Deep eutectic solvents; Fractionation; Lignin; Biomass pre-treatment; Delignification
Contact information: a: Slovak University of Technology, Faculty of Chemical and Food Technology,
Institute of Natural and Synthetic Polymers, Department of Wood, Pulp and Paper, Radlinského 9,
Bratislava, 812 37, Slovak Republic; b: Institute of Inorganic Chemistry, Technology and Materials,
Department of Inorganic Chemistry, Radlinského 9, Bratislava, 812 37, Slovak Republic;
* Corresponding author: michal.jablonsky@stuba.sk
INTRODUCTION
Biomass can be converted into diversified materials, biofuels, and biochemicals,
especially through the modernization of existing biorefinery technologies, accompanied
by the development of new procedures. Several methods have been developed for the
pretreatment of lignocellulosic biomass (Zavrel et al. 2009; Surina et al. 2015) in order to
obtain a high yield of the desired product. The methods must be adapted to the specific
source of lignocellulosic biomass (Mäki-Arvela et al. 2010). The unit operations may
cause significant degradation of various lignocellulosic components. In the course of
degradation, the original material undergoes modification, the proportions of its
individual components are changed, and it becomes thus more suitable for subsequent
processing. The pretreated material may be utilized mainly in hydrolytic or fermentation
processes. Moreover, the process of delignification and the substrate ability to interact
with other chemicals used in these processes may be improved. Some pretreatment
methods require extreme conditions such as high temperatures and pressures, or strong
acids and bases, and special facilities are frequently required.
One of the most promising technologies for fractionation of components is the use
of deep eutectic solvents. A deep eutectic solvent (DES) is a type of ionic solvent with
special properties. It is composed of a mixture which forms a eutectic with a melting
point much lower than either of its individual components (Abbott et al. 2004).
Frequently, DESs are formed by mixing choline chloride with hydrogen bond donors,
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Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8040
such as amines, acids, and alcohols. Recently, various applications of DES have been
reported (van Spronsen et al. 2011; Kroon et al. 2014; Kumar et al. 2015; Vigier et al.
2015). DESs were mentioned for the first time in the work of Abbott et al. (2003), which
highlighted the good dissolution properties of these mixtures. DESs are highly sensitive
(Kroon et al. 2014) and effective for extracting compounds from biological materials in
high yields (van Spronsen et al. 2011).
Several papers describe the delignification of different biomass using DESs.
Largo Garcia de Dios (2013) tested the delignification of pine wood and wheat straw.
The authors used five different DESs, such as choline chloride and lactic acid; malic acid;
oxalic acid; and lactic acid and tetramethylammonium chloride and 2-
chloroethyltrimethylammonium chloride in varying proportions (eight experiments). The
percentage of lignin obtained after delignification ranged from 0.6% to 7.8% for pine
wood, and from 0.6% to 9.5% for wheat straw. The researchers found that, depending on
the biomass, different types of lignin and lignin structures are extracted at different
yields.
Kumar et al. (2015) found that the delignification of rice straw by choline
chloride and lactic acid, after applying a pretreatment at the molar ratio of 1:5, resulted in
a decrease in lignin content from 9.1 to 3.8%.
In the aforementioned papers, selective dissolution of the pure fractions (lignin,
cellulose, and xylan) for lactic acid or betaine, and choline chloride was compared. The
conclusion was that only lignin undergoes dissolution. Although evidence and published
or patented applications make use of DES to dissolve the individual components of
biomass, which have been known for decades, the development of this area is expanding
significantly.
Similar to other investigations of actual or potential practical significance in the
field of natural material valorization, three principal issues should be taken into account.
One important issue is the environmental friendliness of the technology. Another is the
yield of the desired products, and the last one concerns the selectivity of the process.
Assessing the current published literature data, it is clear that in regards to yield and
selectivity of extraction of individual components from biomass using DESs, the issues
are open and detailed experiments must be performed and evaluated in order to reach a
definite answer.
This work tries to contribute to the yield and selectivity investigation regarding
the delignification of wheat straw using different types of deep eutectic solvents. Our aim
is to estimate the effectiveness of delignification in removing lignin, as well as the
selectivity of the process.
EXPERIMENTAL
Materials
Wheat straw was harvested from local agricultural fields in the Bratislava district
of Slovakia. After harvesting, the straw was cleaned, grinded (600 mesh), and dried.
Before delignification, the wheat straw was extracted using the accelerated
solvent extraction [according to NREL/TP-510-42619 (Sluiter et al. 2008)] and weighed,
dried, and analyzed to determine the content of lignin, ash, and holocellulose (Table 1).
The residual lignin content was determined as Klason lignin (TAPPI Method T222,
1998), and the extractive content was determined according to Sluiter et al. (2008).
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Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8041
Ash was determined using the TAPPI Method T211 (1998), and holocellulose
was quantified with sodium chlorite treatment according to the procedure of Wise et al.
(1946). Extracted, dried wheat straw was used as the lignocellulosic biomass and was
treated with DES reagent.
Table 1. Composition of Wheat Straw
Wheat straw Composition (%)
Extractives 7.3 ± 2.0
Ash 4.2 ± 0.4
Lignin 17.3 ± 1.0
Holocellulose 74.7 ± 0.2
Four replicates were measured, averaged, and evaluated.
DES Pretreatment
All chemicals were purchased from VWR®
(www.vwr.com). Six different DESs
were tested: choline chloride with urea, malonic, lactic, malic, lactic, and oxalic acid. The
solutions were stirred in an oil bath to form a homogeneous liquid. Extracted straw (2.5 g
absolute dry weight, STN EN ISO 638 (2009)) was added into individual DES at a ratio
of 1:20 (wt/wt). DESs, choline chloride and urea (1:2), and malonic acid (1:1), and lactic
(1:9; 1:10), malic (1:1) and oxalic acid (1:1) were used, and delignification was carried
out for 24 h in a drying oven with a preset temperature of 60 °C. For DESs (choline
chloride and urea; and choline chloride and malic acid) the temperature was 80 °C. The
slurry was washed with an anti-solvent (water, ethanol – for malic acid), and after
washing, the samples were dried at 105 °C. Properties of the prepared DESs are listed in
Table 2.
Table 2. Properties of Prepared DESs
Reagent ChCl/
Reag
Preparation
time of DES
(min)
Temperature
of preparation
(°C)
Refractive
index
at 25 °C
Density
(kg/m3
)
at 60 °C
Density
(kg/m3
)
at 45 °C
Urea
1:2 60 80 1.5117 1205 1213
Malonic acid
1:1 20 60 1.4861 - -
Lactic acid
1:9 20 60 1.4432 1191 1202
Malic acid 1:1 40 80 1.4813 1292 1291
Lactic acid 1:10 20 60 1.4426 1210 1223
Oxalic acid
x2.H2O
1:1 45 60 1.4662 1255 1267
Four replicates were measured, for refractive index at 25 °C standard deviation is less than
0.0005 units, for density less than 3 units, and for viscosity less than 0.35 units.
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Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8042
Refractive Index
The refractive index was measured using an Abbe refractometer at a temperature
of 25 °C. Densities were determined with a pycnometer at 60 °C and 45 °C.
RESULTS AND DISCUSSION
The present research was focused on the application of deep eutectic solvent for
the processing of wheat straw. The goal was to find an efficient solvent for lignin
isolation. Table 3 shows the wheat straw residue yields after delignification by individual
DES. The yield ranged from 59.1% to 94.9%. It is obvious from the results that each of
the DESs was able to dissolve lignin from the used material. However the amount of
dissolved lignin was different depending on the components of individual DES. The
highest amount of the material was extracted by the DES composed of choline chloride
and oxalic acid dihydrate. However, along with lignin, other biomass components were
passed along to the DES.
Theoretically, the yield should reach 82.7% if all lignin present in wheat straw
were dissolved. However, in this study, the determined yields of wheat straw residue after
delignification were lower. These results clearly indicate that other wheat straw
components (e.g., holocellulose) became dissolved as well. Based on these results, it may
be concluded that the used DESs did not act selectively. Rather, along with lignin, other
biomass components became dissolved as well. Therefore, the present results contradict
those reported by other authors (Kumar et al. 2015). Based on the yield, the cited article
implies a high selectivity of the DES based on choline chloride with lactic acid and lactic
acid with betaine. However, the authors have found that the process has not been well
proven, and therefore the mechanism remains ambiguous.
In the published works on solubility of pure cellulose, xylan, hemicellulose, and
lignin it was stated that cellulose, hemicellulose, and xylan are indissoluble in DESs
(Kumar et al. 2015). Other works (Francisco et al. 2012) tested the solubility of lignin,
cellulose, and starch in DESs. They found high solubility of lignin, but also negligible
cellulose solubility.
Non-covalent interactions play an important role in the cellulosic microfibrils and
between individual components. It is known that the cellulosic microfibril surfaces are
coated with noncellulosic polysaccharides (Iiyama et al. 1994). These polysaccharides
are hydrogen bonded to the surfaces of cellulose microfibrils. There are also possibilities
for ionic and salt interactions between polysaccharides, proteins, and one another (Iiyama
et al. 1994). Furthermore certain covalent interactions take place between different kinds
of polysaccharides-polysaccharides, polysaccharides-lignin, polysaccharides-proteins,
and lignin-proteins (Taherzadeh and Jeihanipour 2012). Also it is known that
polysaccharides are covalently linked with lignin by covalently-linked bridging
molecules. However, the lignin present in lignocellulosic biomass is concealed within the
hemicellulose and cellulosic microfibrils, necessitating extraction for efficient processing
(Cooper et al. 1984; Iiyama et al. 1994). Given the conditions, it seems likely that lignin
and hemicellulose and cellulose are depolymerized and extracted by the DES-antisolvent
mixture. It can be supposed that holocellulose will be degraded as well. These results
were confirmed by the present work.
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Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8043
Table 3. Yield after Delignification by DESs and Content of Lignin in Initial Wheat
Straw and Delignified Straw
Reagent ChCl/Reag
Temperature of
delignification
(°C)
Lignin
in
wheat
straw
(g)
Yield after
delignification
(%)
Lignin in
delignified
wheat
straw
Decrease
of lignin
content
(%)
Urea 1:2 80 0.437 94.93 0.431 1.3
Malonic
acid
1:1 60 0.433 90.57 0.417 3.8
Lactic acid 1:9 60 0.433 85.28 0.369 14.6
Malic acid*a
1:1 80 0.436 80.74 0.341 21.6
Lactic acid 1:10 60 0.433 83.49 0.307 29.1
Oxalic acid
x
2 H2O
1:1 60 0.435 59.07 0.183 57.9
*a - the slurry was washed with ethanol
Fig. 1. Composition of delignified wheat straw and DES after delignification by choline chloride
and urea (1:1), choline chloride and malonic acid (1:1), choline chloride and oxalic acid dihydrate
(1:1), choline chloride and lactic acid (1:9), choline chloride and malic acid (1:1) and choline
chloride and lactic acid (1:10) in %
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Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8044
The measured data documented that the highest portion of lignin was withdrawn
using choline chloride and oxalic acid dihydrate. The applicability of oxalic acid is,
however, restricted due to its toxic and caustic properties. Accordingly, DESs composed
of ChCl/lactic acid (1:10) or ChCl/malic acid (1:1) are more suitable alternatives. It may
be hypothesized that the reduction in delignification efficiency is a result of the presence
of CH2 groups in a long chain and NH2. On the contrary, a higher content of the acid and
a higher temperature can increase DES efficiency at delignification. The acid strength is
an important factor, and it is a function of the solvent. Due to the acid environment the
hydrolysis occurs and it leads to depolymerization of individual components. This
contributes to the depolymerization and thus affects efficiency of DES.
Largo Garcia de Dios (2013) found that by increasing the choline chloride to
lactic acid ratio, the amount of withdrawn lignin is increased. This was confirmed for a
sample of wheat straw and beech wood, and is consistent with the results of the present
study.
In Fig. 1, the composition of wheat straw after delignification and that of the used
DESs are shown. When comparing the selectivity of lignin and holocellulose removal, it
is obvious that the selectivity of DESs differed. When using ChCl/urea, the ratio of lignin
removed to holocellulose (the ratio of the individual components after delignification by
DESs) was 1:18, whereas it was 1:12 for ChCl/malonic acid, and 1:3 for ChCl/oxalic
acid. In the case of ChCl/lactic acid (at molar ratio 1:9) the selectivity was 1:4.3, and for
molar ratio 1:10 it was 1:2.2. When using ChCl/malic acid the ratio was 1:3.8.
From this viewpoint, the least suitable eutectic mixture was found to be ChCl/urea
due to the lowest ratio of removed lignin. When comparing the ratio of removed lignin to
holocellulose, and the portion of removed lignin, the best result was obtained by applying
ChCl/lactic acid (molar ratio 1:10).
Singh et al. (2011) applied the soda pulping procedure to wheat straw. It was
found that depending on conditions (130 to 160 °C, 0.25 to 2.5 h), the yield ranged from
35.70% to 56.25%, and the lignin content in pulp ranged from 2.62% to 12.85%. Within
the present work, comparable results were reached using ChCl/oxalic acid dihydrate. In
this case, 40.93% of wheat straw was dissolved in the eutectic mixture, i.e. the yield was
59.07%. However, Deniz et al. (2004) studied delignification of wheat straw using the
kraft process with yield 42.6%. An interesting comparison has been reported in the paper
of Rodriguez et al. (2008). Delignification of rice straw using the kraft process attained
yields 32.9 to 42.1%, whereas when using a soda process the yields were 33.9 to 35.3%,
and when using a soda-anthraquinone process the yield was 37.0%. Soda-anthraquinone
cooking method of straw was used also in the paper of Ates et al. (2015) with the yield
37.9% (wheat straw) and 42.6% (rice straw).
These results suggest that eutectic mixtures behave similarly to those applied in
classic delignification procedures. After delignification, the content of holocellulose and
lignin in wheat straw was 48.7% and 7.3% in undissolved part and 29.8% and 10.1% in
dissolved part (Fig. 1). Applying the other DESs, the content of holocellulose ranges
from 64.35% to 74.71% that of lignin from 12.27% to 17.08% in undissolved parts, and
the yield from 80.74% to 94.93%.
PEER-REVIEWED ARTICLE bioresources.com
Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8045
CONCLUSIONS
Deep eutectic solvents represent promising alternative solvent systems for the
treatment of biomass. The distinct behaviors after the fractionation of wheat straw with
various deep eutectic solvents, such as choline chloride and urea (1:2), and malonic (1:1),
and lactic (1:9; 1:10), malic (1:1) and oxalic acid (1:1), were established in this study.
Furthermore, the characterization of delignified samples was performed. There were clear
differences between the samples obtained with differing DESs, especially when
considering the content of removed of lignin and holocellulose.
1. The highest amount of lignin (57.9%) was removed using ChCl/oxalic acid dihydrate.
2. Based on the selectivity of lignin:holocellulose removal, (1:2.2) and the content of
lignin (29.1%) removed from wheat straw, the best results was reached using
ChCl/lactic acid at a molar ratio 1:10.
3. It was unveiled in this work that the investigated DESs do not act selectively during
the delignification process.
ACKNOWLEDGEMENTS
This publication was supported by the Slovak Research and Development Agency
under the contract No. APVV-14-0393, and by the projects VEGA 1/0775/13 and VEGA
1/0543/15.
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DOI: 10.15376/biores.10.4.8039-8047

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Jablonsky des fractionation_bioresources_2015

  • 1. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8039 Deep Eutectic Solvents: Fractionation of Wheat Straw Michal Jablonský,a, * Andrea Škulcová,a Lucia Kamenská,a Milan Vrška,a and Jozef Šima b Deep eutectic solvents (DESs) are a relatively new topic in science. Their usage is not yet clearly defined, and the areas in which DESs may be applied are constantly growing. A simple and clean fractionation of the main components of biomass represents a very important step in creating a clean, renewable carbon economy. A major challenge is the use of DESs for fractionation of biomass components at lower temperatures, without the use of expensive raw materials. In this work, wheat straw was pretreated with six different DES systems composed of choline chloride with urea (1:2), malonic acid (1:1), lactic (1:9; 1:10), malic (1:1), and oxalic acid (1:1). The pretreated biomass was characterized in terms of lignin content, ash, and holocellulose. A deep eutectic solvent, composed of choline chloride and oxalic acid, was found to produce the best delignification results. The solvents are not selective in the process of delignification. Keywords: Deep eutectic solvents; Fractionation; Lignin; Biomass pre-treatment; Delignification Contact information: a: Slovak University of Technology, Faculty of Chemical and Food Technology, Institute of Natural and Synthetic Polymers, Department of Wood, Pulp and Paper, Radlinského 9, Bratislava, 812 37, Slovak Republic; b: Institute of Inorganic Chemistry, Technology and Materials, Department of Inorganic Chemistry, Radlinského 9, Bratislava, 812 37, Slovak Republic; * Corresponding author: michal.jablonsky@stuba.sk INTRODUCTION Biomass can be converted into diversified materials, biofuels, and biochemicals, especially through the modernization of existing biorefinery technologies, accompanied by the development of new procedures. Several methods have been developed for the pretreatment of lignocellulosic biomass (Zavrel et al. 2009; Surina et al. 2015) in order to obtain a high yield of the desired product. The methods must be adapted to the specific source of lignocellulosic biomass (Mäki-Arvela et al. 2010). The unit operations may cause significant degradation of various lignocellulosic components. In the course of degradation, the original material undergoes modification, the proportions of its individual components are changed, and it becomes thus more suitable for subsequent processing. The pretreated material may be utilized mainly in hydrolytic or fermentation processes. Moreover, the process of delignification and the substrate ability to interact with other chemicals used in these processes may be improved. Some pretreatment methods require extreme conditions such as high temperatures and pressures, or strong acids and bases, and special facilities are frequently required. One of the most promising technologies for fractionation of components is the use of deep eutectic solvents. A deep eutectic solvent (DES) is a type of ionic solvent with special properties. It is composed of a mixture which forms a eutectic with a melting point much lower than either of its individual components (Abbott et al. 2004). Frequently, DESs are formed by mixing choline chloride with hydrogen bond donors,
  • 2. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8040 such as amines, acids, and alcohols. Recently, various applications of DES have been reported (van Spronsen et al. 2011; Kroon et al. 2014; Kumar et al. 2015; Vigier et al. 2015). DESs were mentioned for the first time in the work of Abbott et al. (2003), which highlighted the good dissolution properties of these mixtures. DESs are highly sensitive (Kroon et al. 2014) and effective for extracting compounds from biological materials in high yields (van Spronsen et al. 2011). Several papers describe the delignification of different biomass using DESs. Largo Garcia de Dios (2013) tested the delignification of pine wood and wheat straw. The authors used five different DESs, such as choline chloride and lactic acid; malic acid; oxalic acid; and lactic acid and tetramethylammonium chloride and 2- chloroethyltrimethylammonium chloride in varying proportions (eight experiments). The percentage of lignin obtained after delignification ranged from 0.6% to 7.8% for pine wood, and from 0.6% to 9.5% for wheat straw. The researchers found that, depending on the biomass, different types of lignin and lignin structures are extracted at different yields. Kumar et al. (2015) found that the delignification of rice straw by choline chloride and lactic acid, after applying a pretreatment at the molar ratio of 1:5, resulted in a decrease in lignin content from 9.1 to 3.8%. In the aforementioned papers, selective dissolution of the pure fractions (lignin, cellulose, and xylan) for lactic acid or betaine, and choline chloride was compared. The conclusion was that only lignin undergoes dissolution. Although evidence and published or patented applications make use of DES to dissolve the individual components of biomass, which have been known for decades, the development of this area is expanding significantly. Similar to other investigations of actual or potential practical significance in the field of natural material valorization, three principal issues should be taken into account. One important issue is the environmental friendliness of the technology. Another is the yield of the desired products, and the last one concerns the selectivity of the process. Assessing the current published literature data, it is clear that in regards to yield and selectivity of extraction of individual components from biomass using DESs, the issues are open and detailed experiments must be performed and evaluated in order to reach a definite answer. This work tries to contribute to the yield and selectivity investigation regarding the delignification of wheat straw using different types of deep eutectic solvents. Our aim is to estimate the effectiveness of delignification in removing lignin, as well as the selectivity of the process. EXPERIMENTAL Materials Wheat straw was harvested from local agricultural fields in the Bratislava district of Slovakia. After harvesting, the straw was cleaned, grinded (600 mesh), and dried. Before delignification, the wheat straw was extracted using the accelerated solvent extraction [according to NREL/TP-510-42619 (Sluiter et al. 2008)] and weighed, dried, and analyzed to determine the content of lignin, ash, and holocellulose (Table 1). The residual lignin content was determined as Klason lignin (TAPPI Method T222, 1998), and the extractive content was determined according to Sluiter et al. (2008).
  • 3. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8041 Ash was determined using the TAPPI Method T211 (1998), and holocellulose was quantified with sodium chlorite treatment according to the procedure of Wise et al. (1946). Extracted, dried wheat straw was used as the lignocellulosic biomass and was treated with DES reagent. Table 1. Composition of Wheat Straw Wheat straw Composition (%) Extractives 7.3 ± 2.0 Ash 4.2 ± 0.4 Lignin 17.3 ± 1.0 Holocellulose 74.7 ± 0.2 Four replicates were measured, averaged, and evaluated. DES Pretreatment All chemicals were purchased from VWR® (www.vwr.com). Six different DESs were tested: choline chloride with urea, malonic, lactic, malic, lactic, and oxalic acid. The solutions were stirred in an oil bath to form a homogeneous liquid. Extracted straw (2.5 g absolute dry weight, STN EN ISO 638 (2009)) was added into individual DES at a ratio of 1:20 (wt/wt). DESs, choline chloride and urea (1:2), and malonic acid (1:1), and lactic (1:9; 1:10), malic (1:1) and oxalic acid (1:1) were used, and delignification was carried out for 24 h in a drying oven with a preset temperature of 60 °C. For DESs (choline chloride and urea; and choline chloride and malic acid) the temperature was 80 °C. The slurry was washed with an anti-solvent (water, ethanol – for malic acid), and after washing, the samples were dried at 105 °C. Properties of the prepared DESs are listed in Table 2. Table 2. Properties of Prepared DESs Reagent ChCl/ Reag Preparation time of DES (min) Temperature of preparation (°C) Refractive index at 25 °C Density (kg/m3 ) at 60 °C Density (kg/m3 ) at 45 °C Urea 1:2 60 80 1.5117 1205 1213 Malonic acid 1:1 20 60 1.4861 - - Lactic acid 1:9 20 60 1.4432 1191 1202 Malic acid 1:1 40 80 1.4813 1292 1291 Lactic acid 1:10 20 60 1.4426 1210 1223 Oxalic acid x2.H2O 1:1 45 60 1.4662 1255 1267 Four replicates were measured, for refractive index at 25 °C standard deviation is less than 0.0005 units, for density less than 3 units, and for viscosity less than 0.35 units.
  • 4. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8042 Refractive Index The refractive index was measured using an Abbe refractometer at a temperature of 25 °C. Densities were determined with a pycnometer at 60 °C and 45 °C. RESULTS AND DISCUSSION The present research was focused on the application of deep eutectic solvent for the processing of wheat straw. The goal was to find an efficient solvent for lignin isolation. Table 3 shows the wheat straw residue yields after delignification by individual DES. The yield ranged from 59.1% to 94.9%. It is obvious from the results that each of the DESs was able to dissolve lignin from the used material. However the amount of dissolved lignin was different depending on the components of individual DES. The highest amount of the material was extracted by the DES composed of choline chloride and oxalic acid dihydrate. However, along with lignin, other biomass components were passed along to the DES. Theoretically, the yield should reach 82.7% if all lignin present in wheat straw were dissolved. However, in this study, the determined yields of wheat straw residue after delignification were lower. These results clearly indicate that other wheat straw components (e.g., holocellulose) became dissolved as well. Based on these results, it may be concluded that the used DESs did not act selectively. Rather, along with lignin, other biomass components became dissolved as well. Therefore, the present results contradict those reported by other authors (Kumar et al. 2015). Based on the yield, the cited article implies a high selectivity of the DES based on choline chloride with lactic acid and lactic acid with betaine. However, the authors have found that the process has not been well proven, and therefore the mechanism remains ambiguous. In the published works on solubility of pure cellulose, xylan, hemicellulose, and lignin it was stated that cellulose, hemicellulose, and xylan are indissoluble in DESs (Kumar et al. 2015). Other works (Francisco et al. 2012) tested the solubility of lignin, cellulose, and starch in DESs. They found high solubility of lignin, but also negligible cellulose solubility. Non-covalent interactions play an important role in the cellulosic microfibrils and between individual components. It is known that the cellulosic microfibril surfaces are coated with noncellulosic polysaccharides (Iiyama et al. 1994). These polysaccharides are hydrogen bonded to the surfaces of cellulose microfibrils. There are also possibilities for ionic and salt interactions between polysaccharides, proteins, and one another (Iiyama et al. 1994). Furthermore certain covalent interactions take place between different kinds of polysaccharides-polysaccharides, polysaccharides-lignin, polysaccharides-proteins, and lignin-proteins (Taherzadeh and Jeihanipour 2012). Also it is known that polysaccharides are covalently linked with lignin by covalently-linked bridging molecules. However, the lignin present in lignocellulosic biomass is concealed within the hemicellulose and cellulosic microfibrils, necessitating extraction for efficient processing (Cooper et al. 1984; Iiyama et al. 1994). Given the conditions, it seems likely that lignin and hemicellulose and cellulose are depolymerized and extracted by the DES-antisolvent mixture. It can be supposed that holocellulose will be degraded as well. These results were confirmed by the present work.
  • 5. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8043 Table 3. Yield after Delignification by DESs and Content of Lignin in Initial Wheat Straw and Delignified Straw Reagent ChCl/Reag Temperature of delignification (°C) Lignin in wheat straw (g) Yield after delignification (%) Lignin in delignified wheat straw Decrease of lignin content (%) Urea 1:2 80 0.437 94.93 0.431 1.3 Malonic acid 1:1 60 0.433 90.57 0.417 3.8 Lactic acid 1:9 60 0.433 85.28 0.369 14.6 Malic acid*a 1:1 80 0.436 80.74 0.341 21.6 Lactic acid 1:10 60 0.433 83.49 0.307 29.1 Oxalic acid x 2 H2O 1:1 60 0.435 59.07 0.183 57.9 *a - the slurry was washed with ethanol Fig. 1. Composition of delignified wheat straw and DES after delignification by choline chloride and urea (1:1), choline chloride and malonic acid (1:1), choline chloride and oxalic acid dihydrate (1:1), choline chloride and lactic acid (1:9), choline chloride and malic acid (1:1) and choline chloride and lactic acid (1:10) in %
  • 6. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8044 The measured data documented that the highest portion of lignin was withdrawn using choline chloride and oxalic acid dihydrate. The applicability of oxalic acid is, however, restricted due to its toxic and caustic properties. Accordingly, DESs composed of ChCl/lactic acid (1:10) or ChCl/malic acid (1:1) are more suitable alternatives. It may be hypothesized that the reduction in delignification efficiency is a result of the presence of CH2 groups in a long chain and NH2. On the contrary, a higher content of the acid and a higher temperature can increase DES efficiency at delignification. The acid strength is an important factor, and it is a function of the solvent. Due to the acid environment the hydrolysis occurs and it leads to depolymerization of individual components. This contributes to the depolymerization and thus affects efficiency of DES. Largo Garcia de Dios (2013) found that by increasing the choline chloride to lactic acid ratio, the amount of withdrawn lignin is increased. This was confirmed for a sample of wheat straw and beech wood, and is consistent with the results of the present study. In Fig. 1, the composition of wheat straw after delignification and that of the used DESs are shown. When comparing the selectivity of lignin and holocellulose removal, it is obvious that the selectivity of DESs differed. When using ChCl/urea, the ratio of lignin removed to holocellulose (the ratio of the individual components after delignification by DESs) was 1:18, whereas it was 1:12 for ChCl/malonic acid, and 1:3 for ChCl/oxalic acid. In the case of ChCl/lactic acid (at molar ratio 1:9) the selectivity was 1:4.3, and for molar ratio 1:10 it was 1:2.2. When using ChCl/malic acid the ratio was 1:3.8. From this viewpoint, the least suitable eutectic mixture was found to be ChCl/urea due to the lowest ratio of removed lignin. When comparing the ratio of removed lignin to holocellulose, and the portion of removed lignin, the best result was obtained by applying ChCl/lactic acid (molar ratio 1:10). Singh et al. (2011) applied the soda pulping procedure to wheat straw. It was found that depending on conditions (130 to 160 °C, 0.25 to 2.5 h), the yield ranged from 35.70% to 56.25%, and the lignin content in pulp ranged from 2.62% to 12.85%. Within the present work, comparable results were reached using ChCl/oxalic acid dihydrate. In this case, 40.93% of wheat straw was dissolved in the eutectic mixture, i.e. the yield was 59.07%. However, Deniz et al. (2004) studied delignification of wheat straw using the kraft process with yield 42.6%. An interesting comparison has been reported in the paper of Rodriguez et al. (2008). Delignification of rice straw using the kraft process attained yields 32.9 to 42.1%, whereas when using a soda process the yields were 33.9 to 35.3%, and when using a soda-anthraquinone process the yield was 37.0%. Soda-anthraquinone cooking method of straw was used also in the paper of Ates et al. (2015) with the yield 37.9% (wheat straw) and 42.6% (rice straw). These results suggest that eutectic mixtures behave similarly to those applied in classic delignification procedures. After delignification, the content of holocellulose and lignin in wheat straw was 48.7% and 7.3% in undissolved part and 29.8% and 10.1% in dissolved part (Fig. 1). Applying the other DESs, the content of holocellulose ranges from 64.35% to 74.71% that of lignin from 12.27% to 17.08% in undissolved parts, and the yield from 80.74% to 94.93%.
  • 7. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8045 CONCLUSIONS Deep eutectic solvents represent promising alternative solvent systems for the treatment of biomass. The distinct behaviors after the fractionation of wheat straw with various deep eutectic solvents, such as choline chloride and urea (1:2), and malonic (1:1), and lactic (1:9; 1:10), malic (1:1) and oxalic acid (1:1), were established in this study. Furthermore, the characterization of delignified samples was performed. There were clear differences between the samples obtained with differing DESs, especially when considering the content of removed of lignin and holocellulose. 1. The highest amount of lignin (57.9%) was removed using ChCl/oxalic acid dihydrate. 2. Based on the selectivity of lignin:holocellulose removal, (1:2.2) and the content of lignin (29.1%) removed from wheat straw, the best results was reached using ChCl/lactic acid at a molar ratio 1:10. 3. It was unveiled in this work that the investigated DESs do not act selectively during the delignification process. ACKNOWLEDGEMENTS This publication was supported by the Slovak Research and Development Agency under the contract No. APVV-14-0393, and by the projects VEGA 1/0775/13 and VEGA 1/0543/15. REFERENCES CITED Abbott, A. P., Capper, G., Davies, D. L., Rasheed, R. K., and Tambyrajah, V. (2003). “Novel solvent properties of choline chloride/urea mixtures,” Chem Commun. (1), 70-71. DOI:10.1039/B210714G Abbott, A. P., Boothby, D., Capper, G., Davies, D. L., and Rasheed, R. K. (2004). “Deep eutectic solvents formed between choline chloride and carboxylic acids: Versatile alternatives to ionic liquids,” J. Am. Chem. Soc. 126(29), 9142-9147. DOI: doi:10.1021/ja048266j Ates, S., Deniz, I., Kirci, H., Atik, C., and Okan, O.T. (2015). “Comparison of pulping and bleaching behaviors of some agricultural residues,” Turk. J. Agric. For. 39, 144- 153. DOI: 10.3906/tar-1403-41. Cooper, J. B. and Varner, J. E. (1984). “Cross-linking of soluble extensin in isolated cell walls,” Plant Physiol. 76(2), 414-417. DOI: 10.1104/pp.76.2.414 Deniz, I., Kirci, H., and Ates, S. (2004). “Optimization of wheat straw Triticum drum Kraft pulping,” Ind Crops Prod 19(3), 237–243. DOI: 10.1016/j.indcrop.2003.10.011 Francisco, M., van den Bruinhorst, A., and Kroon, M. C. (2012). “New natural renewable low transition temperature mixtures (LTTMs): Screening as solvents for lignocellulosic biomass processing,” Green Chem. 14(8), 2153-2157. DOI: 10.1039/c2gc35660k
  • 8. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8046 Iiyama, K., Lam, T. B. T, and Stone, B. A. (1994). “Covalent crosslinks in the cell wall,” Plant Physiol. 104, 315-320. DOI: 10.1104/pp.104.2.315 Kumar, A. K., Pharik, B. S., and Pravakar, M. (2015). “Natural deep eutectic solvents mediated pretreatment of rice straw: Bioanalytical characterization of lignin extract and enzymatic hydrolysis of treated biomass residue,” Environ Sci. Pollut. Res. Epub. DOI: 10.1007./S11356-015-4780-4 Kroon, M. C., Casal, M. F., and Vanden Bruinhorst A. (2014). “Pretreatment of lignocellulosic biomass and recovery of substituents using natural deep eutectic solvents/compound mixtures with low transition temperatures,” International Patent WO 2013/153203(A). Largo Garcia de Dios, S. (2013). “Phase equilibria for extraction processes with designer solvent,” Doctoral Thesis, University of Santiago de Compostela, Santiago de Compostela, Spain, 137. Mäki-Arvela, P., Anugwom, I., Virtanen, P., Sjöholm, R., and Mikkola, J. P. (2010). “Dissolution of lignocellulosic materials and its constituents using ionic liquids a review,” Ind. Crop. Prod. 32(3), 175-201. DOI: 10.1016/j.indcrop.2010.04.005 Rodríguez, A., Moral, A., Serrano, L., Labidi, J., and Jiménez, L. (2008). “Rice straw pulp obtained by using various methods,” Bioresour. Technol. 99, 2881-2886. DOI: 10.1016/j.biortech.2007.06.003 STN EN ISO 638. (2009). “Paper, board and pulps - Determination of dry matter content - Oven-drying method”. Singh, S., Dutt, D., and Tyagi, C. H. (2011). “Complete characterization of wheat straw (Triticum aestivum PBW-343 L. Emend. Fiori & Paol.) – A renewable source of fibres for pulp and paper making,” BioResources 6(1), 154-177. DOI: 10.15376/biores.6.1.154-177 Sluiter, A., Hames, B., Ruiz, R., Scarlata, C., Sluiter, J., Templeton, D., and Crocker, D. (2008). "Determination of extractives in biomass," Technical Report, NREL/TP-510- 42619. Surina, I., Jablonsky, M., Haz, A., Sladkova, A., Briskarova, A., Kacik, F., and Sima, J. (2015). “Characterization of non-wood lignin precipitated with sulphuric acid of various concentrations,” BioResources 10(1), 1408-1423. DOI: 10.15376/biores.10.1.1408-1423 Taherzadeh, M. J., and Jeihanipour, A. (2012) “Chapter 2. Recalcitrance of lignocellulosic biomass to anaerobic digestion,” Biogas Production: Pretreatment Methods in Anaerobic Digestion, Mudhoo, A. (ed), John Wiley & Sons, Inc., Hoboken, NJ, USA, p. 40. DOI: 10.1002/9781118404089.ch2 TAPPI Method T211 om-93. (1998). “Ash in wood, pulp, paper and paperboard: combustion at 525 °C, “Tappi Test Methods, TAPPI Press, Atlanta, GA. TAPPI Method T222 om-98. (1998). “Acid-insoluble lignin in wood and pulp, “Tappi Test Methods, TAPPI Press, Atlanta, GA. van Spronsen, J., Witkamp, G. J., Hollman, F., Choi, Y. H., and Verpoorte, R. (2011). “Process for extracting materials from biological material,” International Patent WO2011155829 (A1). Vigier, K., De, O., Chatel, G., and Jérôme, F. (2015). “Contribution of deep eutectic solvents for biomass processing: Opportunities, challenges, and limitations,” Chem. Cat. Chem. 7(8), 1250-1260, DOI: 10.1002/cctc.201500134
  • 9. PEER-REVIEWED ARTICLE bioresources.com Jablonský et al. (2015). “Deep eutectic solvents,” BioResources 10(4), 8039-8047. 8047 Wise, L. E., Murphy, M., and Daddieco, A. A., (1946). “Chlorite holocellulose, its fractionation and bearing on summative wood analysis and on studies on the hemicelluloses,” Tech. Assoc. Pap. 29(6), 210–218. Zavrel, M., Bross, D., Funke, M., Buchs, J., and Spiess, A. C. (2009). “High-throughput screening for ionic liquids dissolving (ligno-)cellulose,” Bioresour. Technol. 100(9) 2580–2587. DOI: 10.1016/j.biortech.2008.11.052 Article submitted: June 30, 2015; Peer review completed: September 6, 2015; Revised version received and accepted: September 25, 2015; Published: October 15, 2015. DOI: 10.15376/biores.10.4.8039-8047