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UV/Vis Spectrometry as a Quantification Tool for Lignin Solubilized in Deep
Eutectic Solvents
Article  in  Bioresources · July 2017
DOI: 10.15376/biores.12.3.6713-6722
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Skulcova Andrea
Slovak University of Technology in Bratislava
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Slovak University of Technology in Bratislava
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6713
UV/Vis Spectrometry as a Quantification Tool for Lignin
Solubilized in Deep Eutectic Solvents
Andrea Skulcova,a
Veronika Majova,a
Michaela Kohutova,a
Maros Grosik,a
Jozef Sima,b
and Michal Jablonsky a,
*
In this short communication, UV/Vis spectrophotometry is described as
an analytical tool for the quantification of lignin content in deep eutectic
solutions. The lignin was solubilized with different deep eutectic solvent
(DES). DESs were prepared as binary mixtures of choline chloride with
lactic acid (1:9); (1:10); ethylene glycol (1:2); glycerol (1:2) and
alanine:lactic acid (1:9), and betaine:lactic acid (1:2). The UV-Vis
spectrometric quantification of the solubilized lignins was independent of
the type of solubilized lignin. The approach consists of measuring the
absorbance of a solution of lignins dissolved in the deep eutectic
solvents at an absorbance of 440 nm.
Keywords: Deep eutectic solvents; Lignin; UV/Vis spectrophotometry; Absorbance
Contact information: a: Institute of Natural and Synthetic Polymers, Department of Wood, Pulp, and
Paper; b: Department of Inorganic Chemistry, Slovak University of Technology, Radlinského 9, Bratislava,
812 37, Slovak Republic; *Corresponding author: michal.jablonsky@stuba.sk
INTRODUCTION
Valorisation is a key component of an economic and environmental
lignocellulosic biorefinery (Jablonsky et al. 2015b; Surina et al. 2015). There are many
new modes of pulp processing. Deep eutectic solvents (DESs) can be used to dissolve
lignocellulosic biomass or its individual components such as lignins (Francisco et al.
2012). DESs have potential applications in the pulp, paper, and recycling industries.
DESs have been used to delignify different biomasses such as wheat straw (de Dios 2013;
Jablonsky et al. 2015b; Skulcova et al. 2016), rice straw (Kumar et al. 2015), pine wood
(de Dios 2013), and thermomechanical pulp (Choi et al. 2016). Lignin is the second most
abundant natural polymer after holocellulose. Lignin is a complex phenolic polymer
found in biomass feedstocks and biomass-derived products. Lignin consists of three types
of units called p-hydroxyphenyl (H), guaiacyl (G), and syringyl (S) (Boerjan et al. 2003;
Davin and Lewis 2005). Lignin composition varies in different groups of vascular plants,
with only G, G and S, and then H, G, and S lignins being characteristic of the
combinations of lignin units for softwoods, hardwoods, and graminaceous plants,
respectively (Sun et al. 2012).
It is difficult to determine lignin content in complex systems via extraction.
Various separation (mainly high performance liquid chromatography) and optical
techniques have been exploited to eliminate the interferences caused by other
components (Lobbes et al. 1999).
UV/Vis spectroscopy is a user-friendly and adaptable analytical technique that
provides the best results with regard to the structural differences between lignins. Several
methods to determine lignin content use absorbance values at 205 or 280 nm for the
quantitative and qualitative analysis of native lignins (Janshekar et al. 1981) and
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6714
lignosulphonates and lignin precipitated with black liquor (Jablonsky et al. 2016). The
lignin concentration can be determined in different solutions (Lee et al. 2013). However,
the type and structure of lignin, solvent, and pH of the solution have a considerable
influence on the UV/Vis spectra (Kallavus et al. 2015). Mongeau and Brooks (2001)
found that using the acetyl bromide method overestimates the lignin concentration due to
the interference of polysaccharides.
The aim of the present investigation was to develop a simple and fast spectral
method for the evaluation of lignin content in the deep eutectic solvents.
EXPERIMENTAL
Materials
All chemicals were purchased from Sigma Aldrich (Bratislava, Slovakia). The
solutions were stirred in a water bath to form homogeneous liquids. The DESs used were
choline chloride and lactic acid (1:9) and (1:10), ethylene glycol (1:2), oxalic acid (1:1),
malic acid (1:1), malonic acid (1:1), glycerol (1:2), and the systems alanine: lactic acid
(1:9) and betaine : lactic acid (1:2) (Table 1).
Table 1. Properties of DESs
Sample System DES
Solubility of
Lignin
Molar
Ratio
Density
(kg/m3)
at 25 °C
Refractive
Index
at 25 °C
Viscosity
(mPa∙s)
at 28 °C
DES1 *ChCl : lactic acid Yes 1:10 1241 1.4407 71.1
DES2 *ChCl : lactic acid Yes 1:9 1217 1.4432 70.9
DES3 *ChCl : ethylene glycol Yes 1:2 1141 - 38.7
DES4 Alanine : lactic acid Yes 1:9 1230 1.4397 168.0
DES5 Betaine : lactic acid Yes 1:2 1195 1.4620 -
DES6 *ChCl : glycerol Yes 1:2 1197 1.4781 292.3
DES7 *ChCl : oxalic acid No** 1:1 1280 1.4662 126.1
DES8 *ChCl : malic acid Partially** 1:1 1299 1.4790 -
DES9 *ChCl: malonic acid Partially** 1:1 - 1.4864 -
*ChCl – Choline chloride, ** Not used for UV/Vis analysis
Lignin Samples
The annual plants, hemp, and flax, used for obtaining black liquor were kindly
supplied by OP Papírna Ltd. (Olšany, Czech Republic). The cooking conditions were as
follows: active alkali sodium hydroxide and the presence of anthraquinone (AQ). The
black liquor obtained had the following characteristics: pH of 12.9 ±0.3
(determined by a digital Jenway (3510 pH-meter, UK) and density 1.242 g/mL
(determined by measuring the mass with the known volume of the black liquor), ash
45.75 wt%, and dry matter 36.80 wt%. The precipitation of lignin from black liquor was
used as a single step process in which a dilute solution of sulphuric acid (5 wt% (1.05 N))
was added to the black liquor with the pH adjusted to the desired value. 100 mL of the
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6715
black liquor was treated with diluted sulphuric acid to obtain a final pH value 3. The
precipitated straw lignin was washed twice with hot water (total volume 400 mL, pH=
6.8) to remove impurities. The lignin was then dried at 25 °C under a pressure of 0.5
mbar using lyophilisation equipment (LYOVAC (GT2, Germany) until reaching a
constant weight.
Lignoboost lignin was purchased from Innventia AB (Stockholm, Sweden), ash
content 0.6 wt%. Softwood kraft lignin was isolated from the original black liquor using
the LignoBoost process by Innventia AB. The lignin was then dried at 25°C under a
pressure of 0.5 mbar using lyophilisation equipment (LYOVAC (GT2, Germany)
until reaching a constant weight.
Absolutely dry lignin samples (lignoboost lignin or straw lignin; see Table 2)
were added to individual DESs, and the mixture in a closed flask was stirred in a water
bath at 80 °C for 20 min. Table 2 shows the lignin properties, and Fig. 1 shows the
solubilized lignin in cuvettes.
Table 2. Analysis of Lignin Properties
Sample
C
(%)
H
(%)
N
(%)
S
(%)
Ash
(%)
OCH3
*
(%)
HHV**
(MJ/kg)
Lignoboost lignin 65.00 5.44 0.12 1.14 0.42 ± 0.02 13.17 26.8 ± 0.5
Straw lignin 65.54 6.17 1.20 0.04 0.37 ± 0.04 15.73 23.61 ± 0.3
*Calculated according to Jablonsky et al. (2015a )
**Higher heating value
Fig. 1. Pure DES 1, solubilized lignin with different concentration of lignins, and straw lignin
UV/Vis spectrometry analysis of solubilized lignin in DES
Lignin content was determined using UV/VIS spectrophotometry with a UV-1600
series spectrophotometer (VWR, Leuven, Belgium). Absorbance within a 200 to 800 nm
spectral range was measured at 1 nm spectral resolution. Samples were referenced by
pure individual DESs.
RESULTS AND DISCUSSION
The UV/Vis absorbance spectra of various lignins at different concentrations
(lignin lignoboost; 0.09 to 0.78 mg/g DES; straw lignin 0.08 mg/g to 0.86 mg/g DES;
(Table 3)) solubilized in choline chloride : lactic acid (1:9) are depicted in Fig. 2. Given
the presence of lignins, a spectral maximum centered at about 280 nm was expected,
given that absorption bands centered at 280 nm and/or 205 nm are used for lignin
determination (Sun et al. 2001; Kline et al. 2010).
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6716
Fig. 2. UV-visible absorbance spectra of two lignin standards (L1 – lignin lignoboost (Fig. 2a); L2
– straw lignin (Fig. 2b)) at different concentrations of lignin in a deep eutectic solvent (Table 3).
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6717
Absorption bands in the lignin spectrum are assignable to a variety of groups or
compounds. Lignins contain several functional chemical groups, such as hydroxyl
(phenolic or alcoholic), methoxyl, carbonyl, and carboxyl, in various amounts, depending
on its origin and the applied isolation process (Sun et al. 2001; Gosselink et al. 2004).
However, it was found that the region of 200 to 400 nm is not suitable for determination
of lignin solubilized in DESs. Similar spectral characteristics were identified also by
Kline et al. (2010), who investigated lignin spectra in the ionic liquid 1-n-butyl-3-methyl-
imidazolium chloride [Bmim]Cl. In the present work, a partial least squares analysis was
applied to the visible spectrum region, 380 to 1100 nm. The absorbance maximum at
about 440 nm represented a better solution for lignin quantification.
Table 3. Concentration of Lignin in a Deep Eutectic Solvent
Sample Concentration of lignin
lignoboost in DES1*
(mg/g)
Sample Concentration of
straw lignin in DES2**
(mg/g)
1_L1 0.087 1_L2 0.08
2_L1 0.133 2_L2 0.196
3_L1 0.236 3_L2 0.407
4_L1 0.351 4_L2 0.486
5_L1 0.762 5_L2 0.602
6_L1 0.784 6_L2 0.858
* choline chloride : lactic acid (1:10)
** choline chloride : lactic acid (1:9)
Fig. 3a. Calibration curves for the chosen wavelengths (400, 440, 450, 500, and 550 nm) are
shown for different pure lignoboost lignin L1; and deep eutectic solvent: DES6: choline chloride :
glycerol (1:2).
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6718
Various lignin standards were tested at different wavelengths and concentrations
to calibrate the UV/Vis spectra (Fig. 3a and Fig. 3b). There was a remarkable correlation
between the adsorption and lignin concentrations between 0.07 and 0.86 mg of lignin in 1
g of DES. This linear correlation was apparent for the used lignin types and further for
the various wavelengths used (from 400 to 550 nm).
Fig. 3b. Calibration curves for the chosen wavelengths (400, 440, 450, 500, and 550 nm) are
shown for different pure straw lignin L2; and deep eutectic solvent: DES3: choline chloride and
ethylene glycol (1:2).
Based on promising results obtained by Kline et al. (2010), the lignin content in
DESs was quantified using spectrophotometry at a wavelength of 440 nm. In the
experiment, lignin was dissolved in DES and prepared at 80 °C, and the absorbance
spectra were measured. Plots of absorbance at this wavelength vs. lignin concentration in
the DES for different lignin standards are depicted in Fig. 4. These experimental results
are depicted in Fig 4. Different types of deep eutectic solvents and of lignins were
compared. The proposed method allows quantification of lignins irrespective of the type
of DES used. The concentration of the solubilized lignin was determined with little or no
pretreatment of analysed samples using a short list of easily available chemicals.
At the absorbance at 440 nm, the A440 nm/lignin concentration plot exhibited a fair
linear relationship in most measurements. The correlation coefficient R2
ranged from
0.849 to 0.998; individual equations are shown in Table 4. Figure 5 illustrates the
relationship between absorbance at 440 nm and the concentration of the solubilized lignin
for lignoboost lignins (L1) and a straw lignin (L2), as described by Eq. 1,
A = − 0.01221 + 2.46982 × Conc., R2
= 0.8912 (1)
where Conc is mg lignin / g DES.
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6719
Fig. 4. Absorbance at 440 nm versus concentration for solution of lignin dissolved in deep
eutectic solvents. L1 – lignin lignoboost; L2 – straw lignin; DES1 – ChCl : lactic acid (1:10);
DES2– ChCl : lactic acid (1:9); DES3 – ChCl : ethylene glycol (1:2); DES4 – alanine : lactic acid
(1:9); DES5 – betaine : lactic acid (1:2); DES6 – ChCl : glycerol (1:2)
Table 4. Linear Equation for Different Lignin (L1 - Lignoboost Lignin, L2 – Straw
Lignin) and Deep Eutectic Solvent, Dependence Absorbance at 440 nm (A) vs.
Concentration of Dissolved Lignin in DES (Conc. (mg Lignin / g DES))
Sample DES Equation R-square
L1_DES1 *ChCl : lactic acid A = −0.08723 + 3.3868 × Conc. 0.8490
L1_DES2 *ChCl : lactic acid A = −0.02532 + 2.2886 × Conc. 0.9860
L1_DES3 *ChCl : ethylene glycol A = 0.02081 + 2.04415 × Conc. 0.9814
L1_DES4 Alanine : lactic acid A = −0.0383 + 1.3514 × Conc. 0.9840
L1_DES6 *ChCl : glycerol A = 0.18447 + 2.2479 × Conc. 0.8488
L2_DES1 *ChCl : lactic acid A = 0.00399 + 2.6948 × Conc. 0.9965
L2_DES2 *ChCl : lactic acid A = 0.0631 + 2.62279 × Conc. 0.9982
L2_DES3 *ChCl : ethylene glycol A = −0.00907 + 2.02545 × Conc. 0.9858
L2_DES4 Alanine : lactic acid A = 0.01883+2.4768× Conc. 0.9973
L2_DES5 Betaine : lactic acid A = 0.12271 + 2.39905 × Conc. 0.9941
*Choline chloride, L1 – lignoboost lignin, L2 – straw lignin
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6720
As mentioned before, there are papers describing lignin quantification in DESs
through absorbance at 280 nm (Kumar et al. 2015). Kumar et al. (2016) noticed that the
absorption maximum varied and was not centered in all cases at 280 nm. They deduced
that the most important factor was probably the pH of extracts after applying deep
eutectic solvents. When extracting lignins at a pH of 2 to 3, the absorption maximum lies
at about 280 nm; with neutral green solvents (pH 6 to 7), an additional peak at 305 to 315
nm was observed. An open question relates to a pH range of 3 to 6. The absorption
maximum depends on the DES composition and shifts from 328 nm for ChCl : oxalic
acid (1:1) to 265 nm for alanine : lactic acid (1:9) (data not shown). This shift was also
observed by Kumar et al. (2016), but they did not explain this result.
In this short communication, the lignin content in DES was quantified using the
UV/VIS methods through absorbance at 440 nm. One weakness of this mode of lignin
concentration determination is that the absorbance is not measured at its maximum but on
the slope of spectral curves. However, the R-square values clearly documented that this
weak point is dismissable by simplicity and reliability of the absorbance.
Fig. 5. Absorbance at 440 nm versus concentration for solution of lignins (L1 – lignoboost lignin)
dissolved in deep eutectic solvents. DES: ChCl : lactic acid (1:10); ChCl : lactic acid (1:9); ChCl :
ethylene glycol (1:2); alanine : lactic acid (1:9); betaine : lactic acid (1:2); ChCl : glycerol (1:2)
CONCLUSIONS
1. In this study, UV/Vis spectrometry was investigated as an easy, quick technique for
the analysis of lignin dissolved in DES.
2. The concentration of solubilized lignins in different types of DESs was determined
without having to significantly modify the analytical process.
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Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6721
3. The UV/Vis spectrometric quantification of solubilized lignins was independent of
the type of solubilized lignin.
ACKNOWLEDGMENTS
This work was supported by the Slovak Research and Development Agency under
the contracts No. APVV-15-0052, APVV-16-0088, and VEGA grants 1/0543/15. The
authors would like to thank for financial assistance from the STU Grant scheme for
financial assistance from the STU Grant scheme for Support of Young Researchers under
the contract no.1625, 1688.
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Article submitted: June 5, 2017; Peer review completed: July 15, 2017; Revised version
received and accepted: July 24, 2017; Published: July 31, 2017.
DOI: 10.15376/biores.12.3.6713-6722
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UV/Vis Spectrometry as a Quantification Tool for Lignin Solubilized in Deep Eutectic Solvents

  • 1. See discussions, stats, and author profiles for this publication at: https://www.researchgate.net/publication/318792557 UV/Vis Spectrometry as a Quantification Tool for Lignin Solubilized in Deep Eutectic Solvents Article  in  Bioresources · July 2017 DOI: 10.15376/biores.12.3.6713-6722 CITATIONS 4 READS 708 6 authors, including: Some of the authors of this publication are also working on these related projects: BIOFOODS - Complex utilization of plant biomass in biofoods with added value View project PlasmArt (APVV-15-0460 SK) - Conservation and stabilisation of cultural heritage objects from natural organic compounds by low temperature plasma. View project Skulcova Andrea Slovak University of Technology in Bratislava 46 PUBLICATIONS   133 CITATIONS    SEE PROFILE Veronika Majová Slovak University of Technology in Bratislava 21 PUBLICATIONS   34 CITATIONS    SEE PROFILE Michal Jablonsky Slovak University of Technology in Bratislava 186 PUBLICATIONS   463 CITATIONS    SEE PROFILE All content following this page was uploaded by Michal Jablonsky on 31 July 2017. The user has requested enhancement of the downloaded file.
  • 2. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6713 UV/Vis Spectrometry as a Quantification Tool for Lignin Solubilized in Deep Eutectic Solvents Andrea Skulcova,a Veronika Majova,a Michaela Kohutova,a Maros Grosik,a Jozef Sima,b and Michal Jablonsky a, * In this short communication, UV/Vis spectrophotometry is described as an analytical tool for the quantification of lignin content in deep eutectic solutions. The lignin was solubilized with different deep eutectic solvent (DES). DESs were prepared as binary mixtures of choline chloride with lactic acid (1:9); (1:10); ethylene glycol (1:2); glycerol (1:2) and alanine:lactic acid (1:9), and betaine:lactic acid (1:2). The UV-Vis spectrometric quantification of the solubilized lignins was independent of the type of solubilized lignin. The approach consists of measuring the absorbance of a solution of lignins dissolved in the deep eutectic solvents at an absorbance of 440 nm. Keywords: Deep eutectic solvents; Lignin; UV/Vis spectrophotometry; Absorbance Contact information: a: Institute of Natural and Synthetic Polymers, Department of Wood, Pulp, and Paper; b: Department of Inorganic Chemistry, Slovak University of Technology, Radlinského 9, Bratislava, 812 37, Slovak Republic; *Corresponding author: michal.jablonsky@stuba.sk INTRODUCTION Valorisation is a key component of an economic and environmental lignocellulosic biorefinery (Jablonsky et al. 2015b; Surina et al. 2015). There are many new modes of pulp processing. Deep eutectic solvents (DESs) can be used to dissolve lignocellulosic biomass or its individual components such as lignins (Francisco et al. 2012). DESs have potential applications in the pulp, paper, and recycling industries. DESs have been used to delignify different biomasses such as wheat straw (de Dios 2013; Jablonsky et al. 2015b; Skulcova et al. 2016), rice straw (Kumar et al. 2015), pine wood (de Dios 2013), and thermomechanical pulp (Choi et al. 2016). Lignin is the second most abundant natural polymer after holocellulose. Lignin is a complex phenolic polymer found in biomass feedstocks and biomass-derived products. Lignin consists of three types of units called p-hydroxyphenyl (H), guaiacyl (G), and syringyl (S) (Boerjan et al. 2003; Davin and Lewis 2005). Lignin composition varies in different groups of vascular plants, with only G, G and S, and then H, G, and S lignins being characteristic of the combinations of lignin units for softwoods, hardwoods, and graminaceous plants, respectively (Sun et al. 2012). It is difficult to determine lignin content in complex systems via extraction. Various separation (mainly high performance liquid chromatography) and optical techniques have been exploited to eliminate the interferences caused by other components (Lobbes et al. 1999). UV/Vis spectroscopy is a user-friendly and adaptable analytical technique that provides the best results with regard to the structural differences between lignins. Several methods to determine lignin content use absorbance values at 205 or 280 nm for the quantitative and qualitative analysis of native lignins (Janshekar et al. 1981) and
  • 3. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6714 lignosulphonates and lignin precipitated with black liquor (Jablonsky et al. 2016). The lignin concentration can be determined in different solutions (Lee et al. 2013). However, the type and structure of lignin, solvent, and pH of the solution have a considerable influence on the UV/Vis spectra (Kallavus et al. 2015). Mongeau and Brooks (2001) found that using the acetyl bromide method overestimates the lignin concentration due to the interference of polysaccharides. The aim of the present investigation was to develop a simple and fast spectral method for the evaluation of lignin content in the deep eutectic solvents. EXPERIMENTAL Materials All chemicals were purchased from Sigma Aldrich (Bratislava, Slovakia). The solutions were stirred in a water bath to form homogeneous liquids. The DESs used were choline chloride and lactic acid (1:9) and (1:10), ethylene glycol (1:2), oxalic acid (1:1), malic acid (1:1), malonic acid (1:1), glycerol (1:2), and the systems alanine: lactic acid (1:9) and betaine : lactic acid (1:2) (Table 1). Table 1. Properties of DESs Sample System DES Solubility of Lignin Molar Ratio Density (kg/m3) at 25 °C Refractive Index at 25 °C Viscosity (mPa∙s) at 28 °C DES1 *ChCl : lactic acid Yes 1:10 1241 1.4407 71.1 DES2 *ChCl : lactic acid Yes 1:9 1217 1.4432 70.9 DES3 *ChCl : ethylene glycol Yes 1:2 1141 - 38.7 DES4 Alanine : lactic acid Yes 1:9 1230 1.4397 168.0 DES5 Betaine : lactic acid Yes 1:2 1195 1.4620 - DES6 *ChCl : glycerol Yes 1:2 1197 1.4781 292.3 DES7 *ChCl : oxalic acid No** 1:1 1280 1.4662 126.1 DES8 *ChCl : malic acid Partially** 1:1 1299 1.4790 - DES9 *ChCl: malonic acid Partially** 1:1 - 1.4864 - *ChCl – Choline chloride, ** Not used for UV/Vis analysis Lignin Samples The annual plants, hemp, and flax, used for obtaining black liquor were kindly supplied by OP Papírna Ltd. (Olšany, Czech Republic). The cooking conditions were as follows: active alkali sodium hydroxide and the presence of anthraquinone (AQ). The black liquor obtained had the following characteristics: pH of 12.9 ±0.3 (determined by a digital Jenway (3510 pH-meter, UK) and density 1.242 g/mL (determined by measuring the mass with the known volume of the black liquor), ash 45.75 wt%, and dry matter 36.80 wt%. The precipitation of lignin from black liquor was used as a single step process in which a dilute solution of sulphuric acid (5 wt% (1.05 N)) was added to the black liquor with the pH adjusted to the desired value. 100 mL of the
  • 4. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6715 black liquor was treated with diluted sulphuric acid to obtain a final pH value 3. The precipitated straw lignin was washed twice with hot water (total volume 400 mL, pH= 6.8) to remove impurities. The lignin was then dried at 25 °C under a pressure of 0.5 mbar using lyophilisation equipment (LYOVAC (GT2, Germany) until reaching a constant weight. Lignoboost lignin was purchased from Innventia AB (Stockholm, Sweden), ash content 0.6 wt%. Softwood kraft lignin was isolated from the original black liquor using the LignoBoost process by Innventia AB. The lignin was then dried at 25°C under a pressure of 0.5 mbar using lyophilisation equipment (LYOVAC (GT2, Germany) until reaching a constant weight. Absolutely dry lignin samples (lignoboost lignin or straw lignin; see Table 2) were added to individual DESs, and the mixture in a closed flask was stirred in a water bath at 80 °C for 20 min. Table 2 shows the lignin properties, and Fig. 1 shows the solubilized lignin in cuvettes. Table 2. Analysis of Lignin Properties Sample C (%) H (%) N (%) S (%) Ash (%) OCH3 * (%) HHV** (MJ/kg) Lignoboost lignin 65.00 5.44 0.12 1.14 0.42 ± 0.02 13.17 26.8 ± 0.5 Straw lignin 65.54 6.17 1.20 0.04 0.37 ± 0.04 15.73 23.61 ± 0.3 *Calculated according to Jablonsky et al. (2015a ) **Higher heating value Fig. 1. Pure DES 1, solubilized lignin with different concentration of lignins, and straw lignin UV/Vis spectrometry analysis of solubilized lignin in DES Lignin content was determined using UV/VIS spectrophotometry with a UV-1600 series spectrophotometer (VWR, Leuven, Belgium). Absorbance within a 200 to 800 nm spectral range was measured at 1 nm spectral resolution. Samples were referenced by pure individual DESs. RESULTS AND DISCUSSION The UV/Vis absorbance spectra of various lignins at different concentrations (lignin lignoboost; 0.09 to 0.78 mg/g DES; straw lignin 0.08 mg/g to 0.86 mg/g DES; (Table 3)) solubilized in choline chloride : lactic acid (1:9) are depicted in Fig. 2. Given the presence of lignins, a spectral maximum centered at about 280 nm was expected, given that absorption bands centered at 280 nm and/or 205 nm are used for lignin determination (Sun et al. 2001; Kline et al. 2010).
  • 5. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6716 Fig. 2. UV-visible absorbance spectra of two lignin standards (L1 – lignin lignoboost (Fig. 2a); L2 – straw lignin (Fig. 2b)) at different concentrations of lignin in a deep eutectic solvent (Table 3).
  • 6. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6717 Absorption bands in the lignin spectrum are assignable to a variety of groups or compounds. Lignins contain several functional chemical groups, such as hydroxyl (phenolic or alcoholic), methoxyl, carbonyl, and carboxyl, in various amounts, depending on its origin and the applied isolation process (Sun et al. 2001; Gosselink et al. 2004). However, it was found that the region of 200 to 400 nm is not suitable for determination of lignin solubilized in DESs. Similar spectral characteristics were identified also by Kline et al. (2010), who investigated lignin spectra in the ionic liquid 1-n-butyl-3-methyl- imidazolium chloride [Bmim]Cl. In the present work, a partial least squares analysis was applied to the visible spectrum region, 380 to 1100 nm. The absorbance maximum at about 440 nm represented a better solution for lignin quantification. Table 3. Concentration of Lignin in a Deep Eutectic Solvent Sample Concentration of lignin lignoboost in DES1* (mg/g) Sample Concentration of straw lignin in DES2** (mg/g) 1_L1 0.087 1_L2 0.08 2_L1 0.133 2_L2 0.196 3_L1 0.236 3_L2 0.407 4_L1 0.351 4_L2 0.486 5_L1 0.762 5_L2 0.602 6_L1 0.784 6_L2 0.858 * choline chloride : lactic acid (1:10) ** choline chloride : lactic acid (1:9) Fig. 3a. Calibration curves for the chosen wavelengths (400, 440, 450, 500, and 550 nm) are shown for different pure lignoboost lignin L1; and deep eutectic solvent: DES6: choline chloride : glycerol (1:2).
  • 7. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6718 Various lignin standards were tested at different wavelengths and concentrations to calibrate the UV/Vis spectra (Fig. 3a and Fig. 3b). There was a remarkable correlation between the adsorption and lignin concentrations between 0.07 and 0.86 mg of lignin in 1 g of DES. This linear correlation was apparent for the used lignin types and further for the various wavelengths used (from 400 to 550 nm). Fig. 3b. Calibration curves for the chosen wavelengths (400, 440, 450, 500, and 550 nm) are shown for different pure straw lignin L2; and deep eutectic solvent: DES3: choline chloride and ethylene glycol (1:2). Based on promising results obtained by Kline et al. (2010), the lignin content in DESs was quantified using spectrophotometry at a wavelength of 440 nm. In the experiment, lignin was dissolved in DES and prepared at 80 °C, and the absorbance spectra were measured. Plots of absorbance at this wavelength vs. lignin concentration in the DES for different lignin standards are depicted in Fig. 4. These experimental results are depicted in Fig 4. Different types of deep eutectic solvents and of lignins were compared. The proposed method allows quantification of lignins irrespective of the type of DES used. The concentration of the solubilized lignin was determined with little or no pretreatment of analysed samples using a short list of easily available chemicals. At the absorbance at 440 nm, the A440 nm/lignin concentration plot exhibited a fair linear relationship in most measurements. The correlation coefficient R2 ranged from 0.849 to 0.998; individual equations are shown in Table 4. Figure 5 illustrates the relationship between absorbance at 440 nm and the concentration of the solubilized lignin for lignoboost lignins (L1) and a straw lignin (L2), as described by Eq. 1, A = − 0.01221 + 2.46982 × Conc., R2 = 0.8912 (1) where Conc is mg lignin / g DES.
  • 8. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6719 Fig. 4. Absorbance at 440 nm versus concentration for solution of lignin dissolved in deep eutectic solvents. L1 – lignin lignoboost; L2 – straw lignin; DES1 – ChCl : lactic acid (1:10); DES2– ChCl : lactic acid (1:9); DES3 – ChCl : ethylene glycol (1:2); DES4 – alanine : lactic acid (1:9); DES5 – betaine : lactic acid (1:2); DES6 – ChCl : glycerol (1:2) Table 4. Linear Equation for Different Lignin (L1 - Lignoboost Lignin, L2 – Straw Lignin) and Deep Eutectic Solvent, Dependence Absorbance at 440 nm (A) vs. Concentration of Dissolved Lignin in DES (Conc. (mg Lignin / g DES)) Sample DES Equation R-square L1_DES1 *ChCl : lactic acid A = −0.08723 + 3.3868 × Conc. 0.8490 L1_DES2 *ChCl : lactic acid A = −0.02532 + 2.2886 × Conc. 0.9860 L1_DES3 *ChCl : ethylene glycol A = 0.02081 + 2.04415 × Conc. 0.9814 L1_DES4 Alanine : lactic acid A = −0.0383 + 1.3514 × Conc. 0.9840 L1_DES6 *ChCl : glycerol A = 0.18447 + 2.2479 × Conc. 0.8488 L2_DES1 *ChCl : lactic acid A = 0.00399 + 2.6948 × Conc. 0.9965 L2_DES2 *ChCl : lactic acid A = 0.0631 + 2.62279 × Conc. 0.9982 L2_DES3 *ChCl : ethylene glycol A = −0.00907 + 2.02545 × Conc. 0.9858 L2_DES4 Alanine : lactic acid A = 0.01883+2.4768× Conc. 0.9973 L2_DES5 Betaine : lactic acid A = 0.12271 + 2.39905 × Conc. 0.9941 *Choline chloride, L1 – lignoboost lignin, L2 – straw lignin
  • 9. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6720 As mentioned before, there are papers describing lignin quantification in DESs through absorbance at 280 nm (Kumar et al. 2015). Kumar et al. (2016) noticed that the absorption maximum varied and was not centered in all cases at 280 nm. They deduced that the most important factor was probably the pH of extracts after applying deep eutectic solvents. When extracting lignins at a pH of 2 to 3, the absorption maximum lies at about 280 nm; with neutral green solvents (pH 6 to 7), an additional peak at 305 to 315 nm was observed. An open question relates to a pH range of 3 to 6. The absorption maximum depends on the DES composition and shifts from 328 nm for ChCl : oxalic acid (1:1) to 265 nm for alanine : lactic acid (1:9) (data not shown). This shift was also observed by Kumar et al. (2016), but they did not explain this result. In this short communication, the lignin content in DES was quantified using the UV/VIS methods through absorbance at 440 nm. One weakness of this mode of lignin concentration determination is that the absorbance is not measured at its maximum but on the slope of spectral curves. However, the R-square values clearly documented that this weak point is dismissable by simplicity and reliability of the absorbance. Fig. 5. Absorbance at 440 nm versus concentration for solution of lignins (L1 – lignoboost lignin) dissolved in deep eutectic solvents. DES: ChCl : lactic acid (1:10); ChCl : lactic acid (1:9); ChCl : ethylene glycol (1:2); alanine : lactic acid (1:9); betaine : lactic acid (1:2); ChCl : glycerol (1:2) CONCLUSIONS 1. In this study, UV/Vis spectrometry was investigated as an easy, quick technique for the analysis of lignin dissolved in DES. 2. The concentration of solubilized lignins in different types of DESs was determined without having to significantly modify the analytical process.
  • 10. PEER-REVIEWED BRIEF COMMUNICATION bioresources.com Skulcova et al. (2017). “UV/Vis spectra for lignin,” BioResources 12(3), 6713-6722. 6721 3. The UV/Vis spectrometric quantification of solubilized lignins was independent of the type of solubilized lignin. ACKNOWLEDGMENTS This work was supported by the Slovak Research and Development Agency under the contracts No. APVV-15-0052, APVV-16-0088, and VEGA grants 1/0543/15. The authors would like to thank for financial assistance from the STU Grant scheme for financial assistance from the STU Grant scheme for Support of Young Researchers under the contract no.1625, 1688. REFERENCES CITED Boerjan, W., Ralph, J., and Baucher, M. (2003). “Lignin biosynthesis,” Annu. Rev. Plant Biol. 54, 519-546. DOI: 10.1146/annurev.arplant.54.031902.134938 Choi, K.-H., Lee, M.-K., and Ryu, J.-Y. (2016). “Effect of molar ratios of DES on lignin contents and handsheets properties of thermomechanical pulp,” JTAPPIK 48(2), 28- 33. DOI: 10.7584/ktappi.2016.48.2.028 Davin, L. B., and Lewis, N. G. (2005). “Lignin primary structures and dirigent sites,” Curr. Opin. Biotechno. 16, 407-415, DOI: 10.1016/j.copbio.2005.06.011 de Dios, S. L. G. (2013). Phase Equilibria for Extraction Processes with Designer Solvent, Ph.D. Dissertation, University of Santiago de Compostela, Santiago de Compostela, Spain. Francisco, M., van den Bruinhorst, A., and Kroon, M. C. (2012). “New natural and renewable low transition temperature mixtures (LTTMs): Screening as solvents for lignocellulosic biomass processing,” Green Chem. 14(8), 2153-2157. DOI: 10.1039/c2gc35660k Gosselink, R. J. A., Abächerli, A., Semke, H., Malherbe, R., Käuper, P., Nadif, A., and van Dam, J. E. G. (2004). “Analytical protocols for characterisation of sulphur-free lignin,” Ind. Crops Prod. 19, 271-281. DOI: 10.1016/j.indcrop.2003.10.008 Jablonsky, M., Botkova, M., and Adamovská, J. (2015a). “Prediction of content of methoxyl groups in lignin from ultimate analysis,” Cell Chem. Technol. 49(2), 165- 168. Jablonsky, M., Skulcova, A., Kamenska, L., and Vrska, M. (2015b). “Deep eutectic solvents: Fractionation of wheat straw,” BioResources 10(4), 8039-8047. DOI: 10.15376/biores.10.4.8039-8047 Jablonsky, M. , Skulcova, A., Hascicova, Z., Haz, A., Majova, V., Strizincova, P., and Kreps, F. (2016). “Contribution of deep eutectic solvents for separation processing,” in: Proceedings of the Zem v pasci? Conference, Hodrusa- Hamre, Slovak Republic, p. 10. ISBN 978-80-228-2888-8 Janshekar, H., Brown, C., and Fiechter, A. (1981). “Determination of biodegraded lignin by ultraviolet spectrometry,” Anal. Chim. Acta 130, 81-91. DOI: 10.1016/S0003- 2670(01)84153-2. Kallavus, U., Kärner, K., Kärner, K., and Elomaa, M. (2015). “Rapid semi-quantitative determination of aspen lignin in lignocellulosic products,” Proceedings of the Estonian Academy of Sciences, 64(1S), 105-112.
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