Characterization of acacia wood was evaluated
by FT-IR and TGA methods. The characterization of
the main compositions of acacia wood as cellulose
and lignin was also investigated for comparision and
making clearly about characterization of wood. The
cellulose spectrum has aromatic skeletal vibration at
1639 cm-1, C-H bending at 1382 cm-1, C-O-C
asymmetric stretching at 1164 cm-1 and β-glucosic
linkages at 897 cm-1. Lignin component of acacia
wood included many complexly functional groups
that is also shown in the fingerprint regions. The
bands of C=C, C–O stretching or bending vibrations
of different groups appeared around at 1604
and1509 cm-1. The bands of C–H, C–O deformation,
bending or stretching vibrations of many groups are
assigned at 1462, 1426, 1329, 1221, 1120 cm-1. The
strong band at 1034 cm-1 is assigned to C–O
stretching. The thermal decomposition of cellulose
was almost complete around 450 oC (in the air
atmosphere) and 549 oC (in the inert atmosphere).
Lignin is thermally stable in both inert environment
and air atmosphere. Thus, in the combustion process
to burn complete lignin needs high temperature to
555 oC with the residues 1.1 % at that temperature.
In pyrolysis and gasification process in the hypoxic
atmosphere, the changes of lignin were very
complex and lignin decomposed between 100 oC and
800 oC with residues 38.6 % at 800 oC. Lignin may
generate tar in the biomass gasification or pyrolysis
process that causes many problems for application of
these processes. The conclustion is the thermal
decomposition of acacia wood from 200 to 450 oC
that is the thermal decomposition of hemicellulose,
cellulose and lignin and at higher temperature almost
does not have dramatical change.
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Vietnam Journal of Chemistry, International Edition, 55(2): 259-264, 2017
DOI: 10.15625/2525-2321.2017-00456
259
Study on characteristics of acacia wood by ftir and thermogrametric
analysis
Dinh Quoc Viet
1,3
, Van Dinh Son Tho
1,2*
1School of Chemical Engineering, Hanoi University of Science and Technology (HUST)
2Vietnam Japan International Institute of Science for Technology, HUST
3Faculty of Chemistry, Quy Nhon University
Received 7 November 2016; Accepted for publication 11 April 2017
Abstract
Renewable energy is very important for future development of society. Biomass is a type of energy that can be
renewable. In this study, characterization of acacia wood is focused and discussed. The functional groups, crosslinking
in the biomass structures and thermal decomposition were mentioned. In that, functional groups, crosslinking of acacia
wood are analyzed by Fourier transform infrared spectroscopy and thermal decomposition is investigated with
thermogravimetric equipment. Acacia wood has typical group of wood from FT-IR such as O-H, C-H, C-O, C-O-C of
cellulose and lignin. The structure of cellulose is also very easy to be broken by thermal factor. In the inert atmosphere,
cellulose decomposed dramatically in the temperature range of 280 to 550 °C and degradation of lignin occurred in the
temperature range of 100 to 800 °C. Acacia wood decomposed in the temperature range of 200 to 580 °C with three
distinct weight loss stages. The first stage is water removal of biomass and it completes below 120 oC. The second stage
is in the range of 200-350 oC that is the initial decomposition of biomass and directly related to the formation of volatile
substances from decomposition of hemicellulose and cellulose. The last stage is the continuous decomposition of lignin
at higher temperature up to 580 oC. For cellulose, the thermal degradation in air atmosphere has decomposition
temperature higher than that in the nitrogen atmosphere but the ending temperature is lower. On the other hand, the
thermal decomposition of lignin just occurred from 150 to 560 oC. The reaction for acacia wood demonstrated three
stages. The water evaporated at lower than 120 oC in the first stage. The second stage is the devolatilization of biomass
(214-322 oC) and the third one (322-420 oC) is the combustion of char.
Keywords. Biomass, acacia wood, cellulose and lignin, FT-IR, characterization of biomass
1. INTRODUCTION
The demand for energy sources to satisfy human
energy consumption continues to increase.
Currently, the main energy source in the world is
fossil fuels. Although it is not known how much
fossil fuel is still available, it is generally accepted
that it is being depleted and is non-renewable. Other
consequences associated with fossil fuel use include
the release of the trapped carbon in the fossil fuels to
the atmosphere in the form of carbon dioxide which
has led to increased concerns about global warming
[1]. Given these circumstances, searching for other
renewable forms of energy sources is reasonable.
Biomass is one of our most important renewable
energy. However, the efficient use of biomass for
energy production required a detailed knowledge of
its physical and chemical properties. These
properties are also essential for modeling and
analysis of energy conversion processes [2, 3]. On
the other hand, the investigation of chemical
elemental characteristics of biomass fuels would
help them find not only suitable and appropriate
energy conversion technologies, but also different
existing conversion technologies to effectively use
biomass feedstock. Extensive research to determine
the physical and chemical properties of the
indigenous available biomass resources has been
conducted in several countries and international
networks [3, 4].
Wood is also biomass that consists of an orderly
arrangement of cells with walls composed of varying
amounts of cellulose, hemicellulose and lignin. The
great diversity of woody plants is reflected in their
varied morphology and chemical composition. FTIR
spectroscopy using the traditional transmission
technique in KBr-pellets has increasingly been used
in wood chemistry to characterize cellulose and
lignin both qualitatively and quantitatively [5].
Thermogravimetric study is also one of the precious
VJC, 55(2), 2017 Van Dinh Son Tho et al.
260
analysis for studying the combustion, pyrolysis or
gasification of biomass. Thermogravimetric analysis
of biomass in the inert environment with three
values of heating rate 3.5 and 10 oC/min was
reported by Viet et al. [6].
The present research is aimed to perform a basic
characteristization as functional groups, linking of
acacia wood and thermal behaviors of acacia wood,
cellulose and lignin were also mentioned. The
experimental technique used was the
thermogravimetric analysis (TGA), which is one of
the most commonly used techniques to study the
primary reactions of thermal decomposition of the
solid. On the other hand, Fourier transform infrared
(FT-IR) was also performed to help identify
functional groups, linking of acacia woodchip.
Obtained data could serve to prepare a database of
national biomass fuel of acacia wood that very
helpful in understanding about biomass pyrolysis,
gasification or combustion process.
2. MATERIALS AND METHODS
The acacia woodchip was collected from the
factory in Thai Nguyen province, Vietnam and dried
for a period of 2-3 weeks. Cellulose and lignin were
provided by the School of Chemical Engineering,
Hanoi University of Science and Technology. The
samples were kept in closed polyethylene bags to
avoid contamination prior to the tests. The samples
were milled to powder and sieved to a particle size
less than 1 mm before the tests. Thermogravimetric
analysis (TG/DTG) with PerkinElmer PYRIS
Diamond model was used for pyrolysis analysis. 10
mg sample was loaded into an alumina crucible and
heated at programmed temperature by the rates of
10oC/min in air environment [6]. FT-IR spectra were
obtained by Nicolet 6700 M spectrometer
equipment. The method for preparation the samples
by dispersing of powder sample in a matrix of KBr,
followed by compression at 160 MPa to compact the
pellet. Reduced absorbance values were used in
order to avoid the spectral differences arising from
the preparation of KBr pellets. In order to normalize
the infrared spectra obtained, we used the 4000 cm-1
band and was measured at Laboratory of the
Petrochemical Refinery and Catalytic Materials,
Hanoi University of Science and Technology.
3. RESULTS AND DISCUSSION
Wood is a biomass consisting of cellulose,
hemicellulose and lignin, along with smaller
quantities of extractives. Cellulose is a linear
polymer of glucose units which can form intrachain
and interchain bonds yielding a crystalline
macromolecule with higher molecular weight that of
the other wood components. Hemicelluloses
comprise a group of polysaccharides composed of a
combination of 5 and 6 carbon ring sugars and have
a more irregular structure with side groups,
substituent groups, and sugars present along the
length of the chain (figure 1). Cellulose is an
optically anisotropic system made up of poly(1 4)–
b–D-glucose (polysaccharides) chains (figure 2). At
first sight, the molecular structure gives the
impression of being very simple, but in fact the
structural characteristics of the molecule have not
yet been fully resolved [7]. The cellulose molecule
chain itself is not very stiff, but rather semi-flexible.
It is generally known and accepted that the hydrogen
bonds play an important role in the conformational
and mechanical properties of cellulosic materials
[7]. Lignin is a randomized condensed polymer with
many aromatic groups and is much more
hydrophobic than cellulose or hemicellulose (figure
3). According to Dien et al., [8], cellulose and lignin
in acacia woodchip sawdust in Vietnam are 39-42%
and 24-25 %, respectively.
The FT-IR spectra of cellulose and lignin were
recorded. The results informed the functional groups
of cellulose, lignin in region between 4000–2500
cm-1 and 2000-500 cm-1 and they supported the
comparison of functional groups vibrations that were
existed in acacia wood.
Figure 1: Molecular structure of hemicellulose [19]
VJC, 55(2), 2017 Study on characteristics of acacia
261
Figure 2: Molecular structure of cellulose [20]
Figure 3: Some structural units of lignin [20]
The results were also showed in figures 4 and 5.
In figure 4, cellulose has the absorbance around at
3420 cm-1 in strong spectrum that is attributed to the
stretching of O–H in the structure. In lignin’s
spectrum has also the high and wide peak around at
3420 cm-1; two clear peaks around at 2917 and 2850
cm-1 are C–H stretching in aromatic methoxyl
groups. The relative intensity of absorption band
around at 3420 cm-1 of lignin is higher and wider
than cellulose. This results are the same as of
Popescu et al. [7] who studied characteristics of
eucalyptus wood. According to Popescu et al. [7] the
absorbance at 2938-2920 cm-1 is symmetric C–H
stretching and 2840-2835 cm-1 is asymmetric C–H
stretching in aromatic methoxyl groups. In the
spectra the range 2500-2000 cm-1 just has the
vibration of CO2 in the measuring environment and
all the samples have this vibration, so that we don’t
show this in the result. In the “fingerprint” region,
the spectra contain several bands assigned to the
main wood components, as can be seen in figure 5.
The absorption bands of cellulose just displayed at
1639, 1382, 1164 and 897 cm-1 clearly in figure 5.
The aromatic skeletal vibration at 1639 cm-1 was so
clear and it revealed that the content of aromatic
compounds in acacia wood cell walls was almost of
cellulose.
The absorption bands at 1375-1365 cm-1 is C–H
bending in cellulose and hemicellulose [9]. The
absorption bands at 1164 cm-1 in cellulose is C–O–C
asymmetric stretching in cellulose, hemicellulose
[1]. The small sharp band at 897 cm-1 is originated
from the β-glucosidic linkages between the sugar
units (polysaccharides) in cellulose. The absorbance
bands of lignin are different with cellulose. The
4000 3750 3500 3250 3000 2750 2500
0
20
40
60
80
100
T
ra
n
sm
it
ta
n
ce
(
%
)
cellulose
acacia wood
lignin
2917
2850
3420
Wave number (cm
-1
)
Figure 4: FT-IR spectra of acacia wood, cellulose
and lignin in region between 4000-2500 cm-1
2000 1750 1500 1250 1000 750 500
0
20
40
60
80
100
1252
1462
1164
1509
1639
T
ra
n
sm
it
ta
n
ce
(
%
)
cellulose
acacia wood
lignin
1736
1056
1120
1425 834
897
1382
1329
16041711
1376
1112
Wave number (cm
-1
)
Figure 5: FT-IR spectra of acacia wood, cellulose,
lignin in region between 2000-500 cm-1
VJC, 55(2), 2017 Van Dinh Son Tho et al.
262
absorbance of lignin at 1711, 1604, 1513, 1462,
1426, 1329, 1221, 1120 and 1034 cm-1 were seen in
the spectrum. The bands at 1604, 1509 cm-1 are
assigned to C=C, C–O stretching or bending
vibrations of different groups present in lignin. The
bands at 1462, 1426, 1329, 1221, 1120 cm-1 are
characteristic of C–H, C–O deformation, bending or
stretching vibrations of many groups in lignin and
carbohydrates. The strong band around 1034 cm-1 is
assigned to C–O stretching. FT-IR spectra of acacia
wood forming tissue display significant difference
between cellulose and lignin in “fingerprint” region
between 2000-500 cm-1.
On the other hand, FT-IR spectrum of the acacia
wood is also shown in figures 4 and 5 for the regions
4000–2500 cm-1 and 2000-500 cm-1, respectively.
Sixteen peaks are clearly defined at: 3420 cm-1 for
O–H strectching, 2917 and 2850 cm-1 for symmetric
and asymmetric C–H stretching in aromatic methoxy
groups. In addition, acacia wood has also three
peaks with the same FT-IR spectrum of lignin but
the peaks at 2920 and 2850 cm-1 are a little higher
than lignin. The results aslo agree with the previous
publication of Yang et al. [10] who reported
hemicellulose appeared more C=O contained
organics compounds, while higher contents of OH
and C–O was found with cellulose. The band at
1736 cm-1 for unconjugated C=O in hemicellulose
[9] and did not observation for cellulose and lignin.
The band at 1639 cm-1 assigned for aromatic skeletal
vibration and this showed clearly in cellulose and
acacia wood samples. Vibration at 1604 cm-1 and
1509 cm-1 assigned for aromatic skeletal in lignin
that we can see in the FT-IR spectrum of lignin,
1462 cm-1 and 1425 cm-1 for C–H deformation, 1376
cm-1 for C–H deformation in polysaccharides [7],
1252 cm-1 for O–H in plane in polysaccharides, 1164
cm-1 for C–O–C vibration in polysaccharides, 1112
cm-1 for aromatic skeletal and C–O stretch, 1056
cm-1 for C–O stretch in polysaccharides and 897
cm-1 for C–H deformation in cellulose [11] that was
seen clearly in the FT-IR spectrum of cellulose. The
result is the same as the previous research of
Popescu et al [7] about eucalyptus wood.
According to Bodîrlǎu et al. [12] the spectrum of
hardwood shows the same basic structure as all
wood samples and it is also true for acacia wood. A
group of complex FT-IR absorbance of lignin was
found there, indicating that lignin might be rich of
methoxy–O–CH3, C–O–C and C=C (aromatic ring)
containing compounds.
Thermal degradation of cellulose, lignin and
acacia wood in nitrogen atmosphere and air
atmosphere were also investigated. TG graphics of
acacia wood, cellulose and lignin in nitrogen
0 200 400 600 800
0
20
40
60
80
100
T
G
(
%
)
Temperature (
o
C)
lignin
acacia wood
cellulose
Figure 6: TGA graphics of acacia wood, cellulose
and lignin in nitrogen atmosphere
atmosphere at heating rate 10 oC/min was show in
Figure 6. It could be said that the thermal behavior
of acacia wood and lignin was nearly different and
the thermal behavior of acacia wood and cellulose
was nearly similar. Cellulose decomposed
dramatically in the temperature range of 280 °C to
550 °C. Degradation of lignin occurred at a slower
rate over a much wide temperature range from 100
°C to 800 °C. The cellulose chemically decomposes
at high decomposition rate within narrow
temperature range. While, decomposition rate of the
lignin becomes slower than that of the cellulose.
Similar results of lignin degradation at temperature
ranges were presented in the literatures [10]
Ligninic polymers are highly branched, substituted,
mononuclear aromatic polymers forming a
lignocellulosic complex in the biomass and this
amorphous structure of lignin accounts for 16 % to
33 % of the mass of woody biomass [13]. On the
other hand, according to Jin et al., the thermal
decomposition of lignin occurs at 280 to 500 °C
yielding phenol via cleavage of ether and carbon-
carbon linkages [14]. Lignin is composed of
aromatic rings with multiple branches, whose
degradation occurs in a broad temperature range.
Different thermal degradation behavior of
hemicellulose, cellulose and lignin are attributed to
their individual chemical natures of biomass [15].
Cellulose, which has only glucose in its chain
structure, hemicellulose contains
heteropolysaccharide and thermally degrades in the
temperature range of 130-194 °C [13]. In contrast,
cellulose is a linear polymer of glucose (5000-10000
glucose units). The cellulose degrades at 240-350 °C
producing anhydrocellulose and levoglucosan [13].
Cellulose consists of long unbranched glucose
polymers, which have an ordered and strong
VJC, 55(2), 2017 Study on characteristics of acacia
263
structure and high thermal stability. According to
Yang., [10], organics compounds (C=O, C–O–C,
etc.) in hemicellulose and cellulose were mainly
released out at low temperatures, i.e., 200-400 oC
and 300-450 oC. Hemicellulose is degraded at low
temperatures because it consists of several
saccharides, which are amorphous structures rich in
branching and easy to be removed. Acacia wood
decomposed in the temperature range of 30 to 584
°C with three distinct weight loss stages. The first
stage is water removal of biomass and it completes
below 120 oC [6]. The second stage is between 205
oC and 385 oC with the total content loss about 65 %
in the dry ash free and it is the initial decomposition
of biomass or called active pyrolysis and directly
related to the formation of volatile substances from
hemicellulose, cellulose and lignin decomposition.
The last stage is the continuous decomposition of
lignin at higher temperature to 584 oC with the total
content loss about 37 % in the dry ash free and at
higher temperature it almost does not have
dramatical change.
0 100 200 300 400 500 600
0
20
40
60
80
100
T
G
(
%
)
Temperature (
o
C)
acacia wood
cellulose
lignin
Figure 7: TGA graphics of acacia wood, cellulose
and lignin in air atmosphere
The behavior decomposion of acacia wood,
cellulose and lignin in air atmosphere is also
investigated. The experiment of thermal degradation
of acacia wood, cellulose and lignin was conducted
from 30 °C to 800 °C at the heating rate of 10
°C/min and the results were shown in figure 7. The
TGA curves show the percentage weight remaining
over the temperature range. Beside the
demoisturization at lower than 120 oC, it is clearly
observed that there were two distinct stages
presented. The first stage was the devolatilization of
biomass (214-322 oC) and the second one (322-420
oC) was the combustion of char. The results showed
that for the first stage, the cellulose component of
acacia wood was decomposed and generated volatile
substances [16]. The functional groups and linking
in cellulose such as C-O, C-O-C broke and reacted
with oxygen generating CO, CO2 [10]. The
decomposition reaction rate of the samples became
faster than the pyrolysis reaction in this stage. It is
also observed that as cellulose, the starting and end
point temperature lower than acacia wood may be
due to that cellulose has light volatile matter in
higher content. On the other hand, lignin just has one
weight loss region from 150 oC to 560 oC and may
be lignin has aromatic hydrocarbon compositions.
These results are the same as earlier publications
[17, 18]. The thermal degradation in air atmosphere
has decomposition temperature higher than one in
the nitrogen atmosphere but the end temperature is
lower. This may be due to the reactivity of oxygen
[21-22].
4. CONCLUSIONS
Characterization of acacia wood was evaluated
by FT-IR and TGA methods. The characterization of
the main compositions of acacia wood as cellulose
and lignin was also investigated for comparision and
making clearly about characterization of wood. The
cellulose spectrum has aromatic skeletal vibration at
1639 cm-1, C-H bending at 1382 cm-1, C-O-C
asymmetric stretching at 1164 cm-1 and β-glucosic
linkages at 897 cm-1. Lignin component of acacia
wood included many complexly functional groups
that is also shown in the fingerprint regions. The
bands of C=C, C–O stretching or bending vibrations
of different groups appeared around at 1604
and1509 cm-1. The bands of C–H, C–O deformation,
bending or stretching vibrations of many groups are
assigned at 1462, 1426, 1329, 1221, 1120 cm-1. The
strong band at 1034 cm-1 is assigned to C–O
stretching. The thermal decomposition of cellulose
was almost complete around 450 oC (in the air
atmosphere) and 549 oC (in the inert atmosphere).
Lignin is thermally stable in both inert environment
and air atmosphere. Thus, in the combustion process
to burn complete lignin needs high temperature to
555 oC with the residues 1.1 % at that temperature.
In pyrolysis and gasification process in the hypoxic
atmosphere, the changes of lignin were very
complex and lignin decomposed between 100
o
C and
800 oC with residues 38.6 % at 800 oC. Lignin may
generate tar in the biomass gasification or pyrolysis
process that causes many problems for application of
these processes. The conclustion is the thermal
decomposition of acacia wood from 200 to 450 oC
that is the thermal decomposition of hemicellulose,
cellulose and lignin and at higher temperature almost
does not have dramatical change. In the air
VJC, 55(2), 2017 Van Dinh Son Tho et al.
264
atmosphere, the decomposition of cellulose, lignin
and acacia wood starts later and ends sooner than in
the inert atmosphere
Acknowledgements. This research was carried out
with the financial support of the research
collaboration between Hanoi University of Science
and Technology and Gent University, Belgium:
“Research and application of Biomass gasification
technology for electric/energy application of
Vietnam remote areas, code ZEIN2013RIP021.
REFERENCES
1. P. McKendry. Energy production from biomass (part
1): overview of biomass, Bioresour. Technol., 83, 37-
46 (2002).
2. A. Nordin. Chemical elemental characteristics of
biomass fuels, Biomass and Bioenergy, 6(5), 339-347
(1994).
3. S. Garivait, U. Chaiyo, S. Patumsawad, and J.
Deakhuntod. Physical and Chemical Properties of
Thai Biomass Fuels from Agricultural Residues, 2nd
Jt. Int. Conf. Sustainable Energy Environ, 48, 1-5
(2006).
4. L. Cuiping, W. Chuangzhi, Yanyongjie, and H.
Haitao. Chemical elemental characteristics of
biomass fuels in China, Biomass and Bioenergy,
27(2), 119-130 (2004).
5. M. Schwanninger, J. C. Rodrigues, H. Pereira, and B.
Hinterstoisser. Effects of short-time vibratory ball
milling on the shape of FT-IR spectra of wood and
cellulose, Vib. Spectrosc., 36(1), 23-40 (2004).
6. D. Q. Viet, N. Van Vinh, and V. D. S. Tho.
Thermogravimetric analysis and Kinetic study of
acacia wood pyrolysis, Vietnam J. Chem., 53(6e4),
185-191 (2015).
7. C. M. Popescu, M. C. Popescu, G. Singurel, C.
Vasile, D. S. Argyropoulos, and S. Willfor. Spectral
characterization of eucalyptus wood, Appl.
Spectrosc., 61(11), 1168-1177 (2007).
8. L. Q. Dien, N. T. M. Nguyet, P. H. Hoang, and T. D.
Cuong. Properties of lignocellulosic biomass and
aspects of their biochemical refineries in Vietnam: a
review of recent, in Workshop Proceedings of
Vietnam Forestry University - International Academy
of wood science cooperation for development, 56-63
(2015).
9. C. M. Popescu, G. Singurel, M. C. Popescu, C.
Vasile, D. S. Argyropoulos, and S. Willfir.
Vibrational spectroscopy and X-ray diffraction
methods to establish the differences between
hardwood and softwood, Carbohydr. Polym., 77(4),
851-857 (2009).
10. H. Yang, R. Yan, H. Chen, D. H. Lee, and C. Zheng.
Characteristics of hemicellulose, cellulose and lignin
pyrolysis, Fuel, 86(12-13), 1781-1788 (2007).
11. O. Faix. Classification of Lignins from Different
Botanical Origins by FT-IR Spectroscopy,
Holzforschung, 45(1), 21-28 (1991).
12. R. Bodîrlǎu and C. A. Teacǎ. Fourier transform
infrared spectroscopy and thermal analysis of
lignocellulose fillers treated with organic anhydrides,
Rom. Reports Phys., 54(1-2), 93-104 (2009).
13. D. Mohan, C. U. Pittman, and P. H. Steele. Pyrolysis
of Wood/Biomass for Bio-oil: A Critical Review,
Energy Fuels, 20(3), 848-889 (2006
14. W. Jin, K. Singh, and J. Zondlo. Pyrolysis Kinetics of
Physical Components of Wood and Wood-Polymers
Using Isoconversion Method, Agriculture, 3, 12-32
(2013).
15. H. Yang, R. Yan, H. Chen and C. Zheng. Influence of
mineral matter on pyrolysis of palm oil wastes,
Combustion Flame, 146, 605-611 (2006).
16. D. Q. Viet, N. Van Vinh, P. H. Luong, and V. D. S.
Tho. Thermogravimetric Study on Rice, Corn and
Sugar Cane Crop Residue, J. Sustain. Energy
Environment, 6, 87-91 (2015).
17. K. G. Mansaray and A. E. Ghaly. Determination of
kinetic parameters of rice husks in oxygen using
thermogravimetric analysis, Energy Sources, 21,
899-911 (1999).
18. D. Lv, M. Xu, X. Liu, Z. Zhan, Z. Li and H. Yao.
Effect of cellulose, lignin, alkali and alkaline earth
metallic species on biomass pyrolysis and
gasification, Fuel Process. Technol., 91(8), 903-909
(2010).
19. W. Chen, L.-X. Zhong, X.-W. Peng, K. Wang, Z.-F.
Chen, and R.-C. Sun. Xylan-type hemicellulose
supported palladium nanoparticles: a highly efficient
and reusable catalyst for the carbon–carbon
coupling reactions, Catal. Sci. Technol., 4, 1426-
1435 (2014).
20. P. Basu, Biomass Gasification and Pyrolysis
Handbook, Elsevier (2010).
21. M. A. Saffe, M. E. Echegaray, G. D. Mazza, and R.
A. Rodriguez. Thermo gravimetric analysis of peach
pits under inert and air atmosphere, Int. J. Eng. Sci.
Innov. Technol., 3(6), 21-30 (2014).
22. A. Rastrogi, M. K. Jha, and A. K. Sarma.
Environmental Effects A comparative study of
kinetics for combustion versus pyrolysis of Mesua
ferrea husk, soya husk and Jatropha curcas husk
using thermogravimmetry and different methods,
Energy Sources Part A Recover. Util. Environ. Eff.,
38(10), 1355-1363 (2016).
Corresponding author: Van Dinh Son Tho
School of Chemical Engineering, Hanoi University of Science and Technology
No 1., Dai Co Viet, Hai Ba Trung, Hanoi
E-mail: tho.vandinhson@hust.edu.vn; Telephone number: 0973604372.
265
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