The effects of combustion temperature on the tar
formation and the syngas composition using oxygenenriched air were studied experimentally in a pilot
scale two-stage biomass gasification system with
different oxygen-enriched air. In this study, the
oxygen level in the gasifying agent was increased
from 21 to 42 vol.%. The experiments of several
tests show that the oxygen levels have a strong
influence on the tar formation and the syngas
composition. When the oxygen concentration
increased from 21 vol.% to 42 vol.%, the low
heating value increased from 4.45 to 7.3 MJ/Nm3,
carbon conversion efficiency increased from 7.4 to
80.04 %, gasification efficiency increased from 54.7
to 67.2 %, temperature profiles of combustion zone
increased from 687 to 1008 oC, tar content reduced
significantly from 67.4 to 30 mg/Nm3 (figure 2).
Moreover, the concentration of the syngas
composition along the gasifier also increased from
combustion zone to reduction zone when higher
oxygen concentration was used in the gasifer.
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Vietnam Journal of Chemistry, International Edition, 55(4): 465-469, 2017
DOI: 10.15625/2525-2321.2017-00492
465
The effect of combustion temperature to low-tar gas production
using oxygen-enriched air
Dinh Quoc Viet
1,4
, Nguyen Van Vinh
1
, Nguyen Tien Cuong
3
,
Pham Hoang Luong
2
, Van Dinh Son Tho
2*
1
School of Chemical Engineering
2
Vietnam Japan International Institute of Science for Technology
3
School of Heat Engineering and Refrigeration, Hanoi University of Science and Technology
4
Faculty of Chemistry, Quy Nhon University
Received 7 November 2016; Accepted for publication 28 August 2017
Abstract
Tar content in producer gas from biomass gasification is a serious problem for fuel gas utilization in downstream
applications. This work presents the experimental studies of acacia woodchip gasification in a downdraft gasifier with
two stages air supply. The effects of oxygen concentration in gasified agent on the temperature of gasifier, the syngas
composition, the lower heating value and tar content in the producer gas are investigated. Results indicate that oxygen-
enriched air rate not only favors to reduce tar component but also improves the heating value of the producer gas. When
increasing oxygen concentration from 21 vol.% to 42 vol.% in the gasified agent, the tar content of the producer gas
decreases from 67.4 mg/Nm
3
to 30 mg/Nm
3
, hydrogen concentration increases from 7.28 to 13.15 vol.%, CO
concentration increases from 19.65 vol.% to 26.52 vol.%, CH4 concentration increases from 1.4 to 3.3 vol.% and the
low heating value increases from 4.45 MJ/m
3
to 7.30 MJ/m
3
, respectively. On the other hand, the carbon conversion
efficiency, gasification efficiency and gas yield of the gasifier are also presented in this approach.
Keywords. Downdraft gasification, acacia woodchip, tar content, oxygen-enriched air.
1. INTRODUCTION
Global climate change due to CO2 emissions is
currently debated around the world. This issue have
become a major concern and has encouraged the
researchers to look for greener sources of energy as
alternatives to replace the fossil fuels. Therefore,
research activities on renewable energy sources has
become more and more important. One of the
renewable energy sources is biomass. Biomass can
be converted into energy via thermo-chemical
processes such as gasification, direct combustion,
and pyrolysis. Among them, biomass gasification
presents highly interesting possibilities for
expanding the utilization of biomass. Biomass
gasification is a thermal conversion process where
solid fuel is converted into a combustible gas using
gasifying agent such as air and steam. Producer gas
from biomass gasification can be utilized in internal
combustion engines or turbines as power generation,
especially in remote areas with no electricity supply.
In gasification process, the main technical
obstacle is the efficient elimination of tar from the
product gas. Therefore, tar removal remains an
important part of the development of advanced
techniques. Several options are available for tar
reduction such as using catalytic cracking, thermal
catalytic, steam reforming which may be called as
in-situ tar reduction and the other method is called
post-gasification reduction [1]. According to
Joujaruek et al. [2], using throttles downdraft
gasifier with singles and double air supply position
could reduce tar significantly from 114 to 43.2
mg/Nm
3
, while S.C. Bhattacharya et al. have
reported that tar content of the product gas was in
the range 19-34 mg/Nm
3
for charcoal gasifier
coupled to a two-stage wood gasifier [3]. Gong
Cheng et al. have studied the oxygen-enriched
gasification of biomass micron fuel (BMF). When
the oxygen concentration increased from 21% to
31.4 % the yield of tar distribution decreased from
12.17 % to 3.75 % [4]. Cuong Van Huynh etl al. [5]
have investigated the oxygen content in the enriched
air. When 40 % oxygen was used, hydrogen
increases by 70 %, 47 % and 32 % for pine, maple-
oak and seed corn, while CO increases by 34 %, 18
VJC, 55(4), 2017 Van Dinh Son Tho et al.
466
% and 8.6 %. Overall, it was found that oxygen and
steam gasification was most effective for feedstock
with low nitrogen and moisture contents. The
purpose of this study is to characterize the effects of
oxygen-enriched air as the gasifying agent on the tar
content as well as the composition of syngas
including the main constituents in the producer gas
from two-stage biomass downdraft gasifier.
2. MATERIALS AND METHOD
2.1. Material
In this approach, acacia woodchips from acacia
woodchips factory that were collected from remote
areas and then cut into small pieces with a size of
length about 3-4 cm were dried for a period of 2-3
weeks and used for a downdraft gasifier. In the other
hand, for the appproximation, ultimate analysis and
heating value, the sample was kept in closed
polyethylene bags to avoid contamination prior to
carrying out the tests. The samples were milled to
powder and sieved to a particle size less than 1 mm
before carrying out the tests. The proximate analysis
was used to determine the volatile matter, fixed
carbon and ash content. Moisture content was
determined using the ASTM E871 standard. The
volatile matter was measured by following
procedures described in ASTM standard E872. The
heating value of the sample was measured using Parr
1266 Bomb Calorimeter followed standard ASTM
5865-04 [6, 9]. The component of material will
determine low heating value and the effect on the
calorific value of producer gas.
2.2. System description
This study is done by a pilot-scale downdraft
gasifier with two-stage air supply. The gasifier
operate at atmospheric pressure and can use pure air
or oxygen-enriched air as the gasified agent. The
gasification system approximately corresponds to
30-50 kg/hr of raw material with an average heating
value of 16 MJ/kg. In the main reactor of the
gasifier, eight thermocouples were installed at
different heights along the gasifier to measure the
temperature of the dry, pyrolysis, combustion and
reduction zone. The experiments were tested on the
two-stage gasifier by varying oxygen-enriched rate
21 vol.%, 26 vol.% and 42 vol.% oxygen-enriched
in 700 l/min of gasified medium flow. Oxygen
(99.8%, supplied by Cryotech Vietnam Joint Stock
Company) from a liquefied oxygen tank was
employed as the gasifying agent, while air was
supplied by fan blower. Air flow was measured and
controlled by using rotameter and oxygen was
measured and controlled by using a pre-calibrated
flow meter to produce blends of oxygen and air up
to desired oxygen levels, then oxygen and air join
together and then were added into the gasifier. In
this approach, different oxygen concentrations were
employed to investigate the effect of oxygen
concentration on the temperature of combustion
zone that influence to tar content in producer gas.
The acacia woodchip feed quantity of 100 kg was
added into the gasifier. After the steady operation
was achieved, a sample of producer gas was
collected and analyzed off-line compositions (H2,
O2, N2, CO, CO2, CH4) using a gas chromatograph
(GC) with detector TCD. Tar measurement unit was
condenser system. The container was rinsed with
dichloromethane to remove tar from the wall of
container and kept in an oven at 105
o
C for about 3
to 4h to evaporate the added liquid and water.
3. RESULTS AND DISCUSSION
The results of the appproximation, ultimate analysis
and LHV of acacia wood are given in table 1. The
proximate analysis showed that the acacia wood was
comprised of 13.78 db.% of fixed carbon content,
85.92 db.% of volatile matter, 0.3 db.% of ash
content and 6.02 db.% of moisture content. The low
heating value of acacia woodchip was 19.02 MJ/kg.
3.1. The effect of oxygen enriched air on
temperature profiles and tar content in producer
gas
It was observed that increasing oxygen-enriched air
rate from 21 vol.% to 42 vol.%, the temperature of
combustion and reduction zone increase figure 2.
The averaged temperature of combustion zone rise
from 697 to 1008
o
C could reduce tar content in the
producer gas from 67.4 mg/Nm
3
to 30 mg/Nm
3
. This
trend can be explained by the exothermic rate and
exothermic intensity. When increasing oxygen
content in gasifying agent from 21vol.% to 42vol.%,
reaction rate was accelerated remarkedly and more
power was released to the surroundings than
absorbed compared with lower oxygen-enriched rate
due to less nitrogen absorbs heat. Furthermore,
according to figure 1, oxygen-enriched air rate in the
gasifying agent also has great effect on the
gasification temperature along the gasifier.
When increasing oxygen concentration from 21
vol.% to 42 vol.% in the gasifying agent, the
temperature of reduction zone and pyrolysis also
gradually increased, the temperature of reduction
zone increases from 447 to 700
o
C, while the
VJC, 55(4), 2017 The effect of combustion temperature to
467
temperature of pyrolysis zone increases from 138 to
369
o
C. This trend may be due to that combustion
process or partial oxidation occurs remarkedly
where oxygen was added to form carbon monoxide
and carbon dioxide, which provides large heat for
the subsequent gasification reactions in reduction
zone and pyrolysis zone. Therefore, temperature
profiles of reduction and pyrolysis zone also
increased when increasing oxygen-enriched air rate
in the gasifying agent.
Table 1: Proximate analysis and heating values of
acacia woodchip
Characteristics acacia woodchip
Proximate analysis
Ash content( %-dry basis) 0.3
Volatile matter (%-dry basis) 85.92
Fixed carbon (%-dry basis) 13.78
Moisture content (%-air dry) 6.02
LHV (MJ/kg) 19.02
Table 2: Syngas composition, heating value and tar
content at different oxygen concentrations
Feedstock acacia woodchip
Oxygen (vol.%) 21 26 42
H2(vol.%) 7.28 10.55 13.15
CO (vol.%) 19.65 24.56 26.52
CO2 (vol.%) 13.91 17.81 21.66
CH4 (vol.%) 1.39 2.62 3.29
N2(vol.%) 57.20 42.82 33.69
LHV(MJ/m
3
) 4.45 6.23 7.30
Tar content
(mg/Nm
3
)
67.4 48 30
Figure 1: Temperature profiles along the gasifier
Figure 2: Tar contents as functions of temperature in
the combustion zone
3.2. The effect of oxygen enriched air on syngas
composition
The effect of oxygen-enriched air rate on the gas
composition was showed figure 3.
The hydrogen content in producer gas for acacia
woodchip gasification increases from 7.28 and 13.15
vol.%.
Figure 3: Effect of oxygen concentration on the
producer gas composition
According to Zhou et al., [7] the temperature is
one of the most important parameters for increasing
hydrogen content of the syngas. Increasing
temperature will favor the forward water-gas shift
reaction and reforming reaction to release more CO
and H2. Hydrogen is mainly formed from reaction
(1) and reaction (2).
CH4 + H2O = CO + 3H2, ∆H = 206 KJ/kg (1)
C +H2O =CO + H2, ∆H = 131.3 kJ/kg (2)
According to previous studies [5,8], reaction (1)
and (2) are the most favorable when gasification
VJC, 55(4), 2017 Van Dinh Son Tho et al.
468
temperature is above 800
o
C because higher
temperature provides more energy endothermic
reaction of steam (water or steam can be formed
from the combustion of hydrogen and the moisture
in biomass). The temperature of combustion zone of
the tests are gradually increased to above 1008
o
C
(figure 2), so higher hydrogen concentration is
improved when increasing oxygen-enriched air rate
in the gasifier. The trend of higher hydrogen content
is an agreement with the results of Cuong Van
Huynh et al and Gong Cheng et al. [4, 5]. CO
concentration in producer gas also increases when
oxygen percentage increases from 21 to 42 vol.%.
The CO content in the syngas achieved from acacia
woodchip increases from 19.65 to 26.52 vol.%.
When oxygen-enriched air is added into the gasifier,
the concentration of CO increases because more
oxygen volume is to enhance the oxidation reaction,
partial oxidation reaction and even pyrolysis
reaction and then releasing more heat to improve the
gasification process. Moreover, CO component is
mainly formed from reaction (1), (2) and reaction
(3).
Figure 4: Effect of oxygen concentration on
gasification efficiency and LHV
C + CO2 = 2CO, ∆H = 172.6 kJ/mol (3)
Higher temperature also improves the
concentration of CO in reaction (3) which is an
endothermic reaction. As shown in figure 4, the
temperature of combustion and reduction zone
increase with increasing oxygen-enriched air rate in
the gasifying agent. Therefore, the decrease in the
nitrogen dilution and higher temperature of
combustion zone favor to increase CO content in
producer gas by reaction (3). The trend of the
increase of CO content is an agreement with the
results of Gong Cheng et al. [4] for another material.
The effect of oxygen-enriched air rate on
methane and carbon dioxide composition is also
shown in figure 3. It can be seen that the amount of
CO2 content in the producer gas changes between
13.91 and 21.66 vol.% for acacia woodchip when
oxygen concentration in oxygen-enriched air
increases from 21 vol.% to 42 vol.%. The decrease
of CO2 content in the syngas is expected because
more oxygen in the oxygen-enriched air is added
into the gasifier will generate more and more CO2
but improve CO and enhance combustion reaction in
the gasifier. The concentration of CH4 in the syngas
is the lowest in producer gas of gasification process.
figure 3 depicts that the amount of CH4 content
slowly increases from 1.39 to 3.29 vol.% when
increasing oxygen concentration in oxygen-enriched
air. The increase might be caused by reduced
nitrogen content in the gasifying agent. This
tendency is an agreement with the results of Cuong
Van Huynh, Gong Cheng for another biomass [4, 5].
3.3. Gasification efficiency, LHV, carbon
conversion efficiency (Ceff) and syngas yield (Gy)
The gasification efficiency and low heating value of
acacia woodchip with oxygen-enriched air in the
gasifier were shown in figure 4. It can be seen that
the increasing trend of LHV and gasification is
similar. The LHV of the product gas strongly
increased from 4.45 to 7.3 MJ/m
3
when increasing
oxygen concentration in oxygen-enriched air from
21 vol.% to 42 vol.%. The low heating value of the
syngas is directly regarding the concentration of
combustible gas composition such as H2, CO, CH4.
Figure 5: Effect of oxygen concentration on carbon
conversion efficiency and the syngas yield
According to previous discussion figure 3, the
concentration of CH4, CO, H2 remarkedly increased
when increasing oxygen concentration and the
decrease of nitrogen content in the gasifying agent.
It is two main reasons to favor the increase of LHV
VJC, 55(4), 2017 The effect of combustion temperature to
469
of the syngas. Furthermore, gasification efficiency
gradually increased with the increasing oxygen
concentration in oxygen-enriched air. The increase
might be explained by the fact that more tar was
cracked into the fuel gas when combustion
temperature increased from 697 to 1008
o
C
(previous discussion). This trend is an agreement
with the results of Gong Cheng [4].
Syngas yield capacity is the most important
parameter to evaluate the performance of the
gasifier. Fig 5 depicts syngas yield (Gy) and carbon
conversion efficiency (Ceff) with varying oxygen
concentration levels in the gasifying agent. The Gy
decreases from 2.1 to 1.43 Nm
3
/kg (figure 5) when
increasing oxygen concentration in the gasifying
agent. However, the carbon conversion efficiency
(Ceff) increases slightly from 74.6 to 80.04 % (figure
5) whith increasing oxygen levels. The decrease of
Gy might be explained by reduced nitrogen content
in the gasifying agent and the increase of Ceff caused
by more tar was craked into the fuel gas when when
increasing oxygen-enriched air rate in the gasifying
agent. Hence, the introduction of oxygen-enriched
air significantly improve the performance of
gasification process and the quality of the syngas.
4. CONCLUSION
The effects of combustion temperature on the tar
formation and the syngas composition using oxygen-
enriched air were studied experimentally in a pilot
scale two-stage biomass gasification system with
different oxygen-enriched air. In this study, the
oxygen level in the gasifying agent was increased
from 21 to 42 vol.%. The experiments of several
tests show that the oxygen levels have a strong
influence on the tar formation and the syngas
composition. When the oxygen concentration
increased from 21 vol.% to 42 vol.%, the low
heating value increased from 4.45 to 7.3 MJ/Nm
3
,
carbon conversion efficiency increased from 7.4 to
80.04 %, gasification efficiency increased from 54.7
to 67.2 %, temperature profiles of combustion zone
increased from 687 to 1008
o
C, tar content reduced
significantly from 67.4 to 30 mg/Nm
3
(figure 2).
Moreover, the concentration of the syngas
composition along the gasifier also increased from
combustion zone to reduction zone when higher
oxygen concentration was used in the gasifer.
Hence, the introduction of oxygen-enriched air
significantly improve the performance of
gasification and the quality of the fuel gas.
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.
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Corresponding author: Van Dinh Son Tho
School of Chemical Engineering
Hanoi University of Science and Technology
No 1., Dai Co Viet Road, Hai Ba Trung Dist., Hanoi
E-mail: tho.vandinhson@hust.edu.vn; Telephone: 0973604372.
470
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