Upload
hui-jin
View
217
Download
4
Embed Size (px)
Citation preview
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 0
Avai lab le a t www.sc iencedi rec t .com
j ourna l homepage : www.e lsev ier . com/ loca te /he
Hydrogen production by partial oxidative gasification ofbiomass and its model compounds in supercritical water
Hui Jin, Youjun Lu, Liejin Guo*, Changqing Cao, Ximin Zhang
State Key Laboratory of Multiphase Flow in Power Engineering, Xi’an Jiaotong University, Xi’an 710049, China
a r t i c l e i n f o
Article history:
Received 10 June 2009
Accepted 19 June 2009
Available online 15 July 2009
Keywords:
Partial oxidation
Supercritical water
Hydrogen production
Biomass
Glucose
* Corresponding author. Tel.: þ86 29 8266389E-mail address: [email protected] (
0360-3199/$ – see front matter Crown Copyright ª 2
doi:10.1016/j.ijhydene.2009.06.059
a b s t r a c t
Partial oxidative gasification in supercritical water is a new technology for hydrogen
production from biomass. Firstly in this paper, supercritical water partial oxidative gasi-
fication process was analyzed from the perspective of theory and chemical equilibrium
gaseous product was calculated using the thermodynamic model. Secondly, the influence
of oxidant equivalent ratio on partial oxidative gasification of model compounds (glucose,
lignin) and real biomass (corn cob) in supercritical water was investigated in a fluidized bed
system. Experimental results show that oxidant can improve the gasification efficiency,
and an appropriate addition of oxidant can improve the yield of hydrogen in certain
reaction condition. When ER equaled 0.4, the gasification efficiency of lignin was 3.1 times
of that without oxidant. When ER equaled 0.1, the yield of hydrogen from lignin increased
by 25.8% compared with that without oxidant. Thirdly, the effects of operation parameters
including temperature, pressure, concentration, and flow rate of feedstock on the gasifi-
cation were investigated. The optimal operation parameters for supercritical water partial
oxidative gasification were obtained.
Crown Copyright ª 2009 Published by Elsevier Ltd on behalf of Professor T. Nejat Veziroglu.
All rights reserved.
1. Introduction directly deal with high-moisture biomass to produce
Biomass is a renewable energy resource, and the net emission
of CO2 during its utilization process is zero [1]. In spite of the
large worldwide biomass resource potential and the opti-
mistic long-term contribution, quite a lot of biomass is not
efficiently used at present. Due to gradual depletion of fossil
energy and the deterioration of the ecological environment in
the process of energy utilization, the rational use of biomass
has attracted great interest [2].
Hydrogen production by biomass supercritical water gasi-
fication (SCWG) is an advanced technology developed
recently. In the conventional gasification technology, high
energy-consumption drying process is necessary. SCWG can
5; fax: þ86 29 82669033.L. Guo).009 Published by Elsevier Ltd
hydrogen-rich gas without drying process. High gasification
efficiency is achieved and the emission of criteria pollution is
negligible. Many researchers studied the supercritical water
gasification of various biomass and its model compounds
[3–10].
However, in certain reaction conditions, the problems of
slow heating and coking still exist. Supercritical water partial
oxidative (SCWPO) gasification can solve the problems
mentioned above by adding certain amount of oxidant less
than the stoichiometric requirements for complete oxidation
to the system, and the reasons are as follows. (1) Biomass
supercritical water gasification is an endothermic reaction,
moreover, high heating rate is needed to achieve complete
on behalf of Professor T. Nejat Veziroglu. All rights reserved.
Nomenclature
ER oxidant equivalent ratio, amount of oxidant
added divided by the required amount for
complete oxidation by stoichiometry
calculation
GE gasification efficiency, mass of gaseous product
divided by mass of dry matter in feedstock
CE carbon gasification efficiency, mass of carbon
elementary in gaseous product divided by mass
of carbon elementary in dry matter in feedstock
HGE hydrogen gasification efficiency, mass of
hydrogen elementary in gaseous product
divided by mass of hydrogen elementary in dry
matter in feedstock
gas yield the mass of certain gas product divided by the
mass of dry matter in feedstock
4 volume fraction of certain gas product
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 03002
gasification. If the temperature of the reaction increases
slowly, more tar and oil are generated in the heating process.
And the tar or oil once generated is difficult to be gasified. The
heat resistance exists inevitably in the process of external
heating method. However, in the process of partial oxidative
gasification, in situ heat generated from the oxidation reaction
rapidly heat up the reaction fluid which reduces the char or tar
formation and favors the process of hydrogen production [11–
14]. (2) In the process of hydrogen production by biomass
supercritical water gasification, some reactants or interme-
diate products with complex structures, for instance, phenols
are difficult to be gasified and are referred to the ‘‘last hurdle’’
to get over for complete gasification [8,15]. However, hydrogen
peroxide is usually used as a source of free radicals to help
decompose the phenolic compound [16]. So the activation
energy of the reaction process is reduced, and the gasification
efficiency is improved [17–20]. (3) In some reaction conditions,
intermediate phenols are prone to polymerize with formal-
dehyde to produce tar and coke, and oxidant can fast react
with formaldehyde to prevent the polymerization reaction so
as to reduce coking problems [19,20].
Watanabe [21] reported the gasification of lignin and found
that the yield of hydrogen can be improved by supercritical
water partial oxidation. Some researchers studied the partial
oxidation of hydrocarbon [12,13,22]. GA in the USA has
established the demonstration plant of partial oxidative
gasification for hydrogen production, and planed to build an
industrial-scale waste treatment plant [14]. But till now, the
continuous operation of supercritical water partial oxidative
gasification from biomass for hydrogen production has
seldom been reported. In this paper, the process of super-
critical water partial oxidative gasification was analyzed from
the point of view of thermodynamics, and the supercritical
water partial oxidative gasification characteristics of glucose,
lignin and corn cob were experimentally studied in super-
critical water fluidized bed system and the effects of opera-
tion parameters upon gasification results were investigated.
The research work in this paper provides the theoretical
foundation and basic experimental results for the
development of supercritical water partial oxidative gasifi-
cation technology.
2. Thermodynamics analysis
Biomass gasification in supercritical water is a complex
process, and Antal [17] proposed the reaction process mainly
includes three reactions: steam reforming (1), water gas shift
reaction (2) and methanation reaction (3). Ethanol is taken as
an example.
C2H5OH(g)þH2O(g) / 2CO(g)þ 4H2(g) DH¼ 256 kJ/mol (1)
CO(g)þH2O(g) / CO2(g)þH2(g) DH¼�41 kJ/mol (2)
CO(g)þ 3H2(g) / CH4(g)þH2O(g) DH¼�206 kJ/mol (3)
If ethanol is fully converted into H2 and CO2, the reaction
equation is:
C2H5OH(g)þ 3H2O(g) / 2CO2(g)þ 6H2(g) DH¼ 174 kJ/mol (4)
If oxidant is added, the following reactions also occur:
C2H5OH(g)þ 3/2O2(g) / 2CO2(g)þ 3H2(g) DH¼�552 kJ/mol (5)
CH4(g)þ 1/2O2(g) / CO(g)þ 2H2(g) DH¼�36 kJ/mol (6)
CO(g)þ 1/2O2(g) / CO2(g) DH¼�283 kJ/mol (7)
The complete gasification reaction (4) is endothermal, and
the reactions (5)–(7) are exothermal, so partial oxidation
technology can integrate the endothermic gasification reac-
tion and exothermic oxidation reaction in one reactor to
realize the internal coupling of heat transfer and reaction
process. This kind of internal heating method eliminates the
heat resistance existing in the indirect external heating
process, so the heat transfer in the system is enhanced and
the gasification efficiency is improved. Simultaneously,
oxidant added can accelerate the reaction to increase the
biomass gasification efficiency.
Yan reported [23] a chemical equilibrium model for
hydrogen production by glucose and real biomass supercrit-
ical water gasification. Process of the reaction was analyzed,
and the thermodynamic rules were obtained. In present
paper, glucose was used as the model compound of biomass
and oxygen was used as oxidant, and the process of biomass
supercritical water partial oxidative gasification was analyzed
using the chemical equilibrium model. Fig. 1 shows, at 500 �C,
25 MPa, when the concentration of glucose is 10wt%, the
effects of ER on the amount of equilibrium gas production. As
can be seen from Fig. 1, when the chemical reaction reaches
0.0 0.2 0.4 0.6 0.8 1.00
1
2
3
4
5
6
0.0
1.0x10-4
2.0x10-4
3.0x10-4
4.0x10-4
H2 CH4 CO2
Gas yield
(m
ol/m
ol g
lu
co
se)
ER
CO
CO
yield
(m
ol/m
ol g
lu
co
se)
Fig. 1 – Effects of ER to the amount of equilibrium gas
production. (Temperature, 5008C; Pressure, 25MPa;
Feedstock, 10wt%glucose).
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 0 3003
equilibrium, glucose is completely gasified, and the main
product is hydrogen, carbon dioxide, carbon monoxide and
methane. When the amount of oxidant is small, the amount
order of produced gases is H2>CO2>CH4>CO, within which
the amount of carbon monoxide is very small, almost can be
neglected compared with other gases. As ER increases, the
production of hydrogen, methane, carbon monoxide gradu-
ally decreases, while the amount of carbon dioxide increases.
When ER is comparatively large, the amount order of gas
produced is: CO2>H2>CH4>CO, It can be seen that from the
point of view of thermodynamics, the addition of oxidant
decreases hydrogen yield. Fig. 2 shows the effects of ER on the
equilibrium gas fraction, from which we can see, the regu-
larity of gas fraction in equilibrium with ER is in close agree-
ment with the regularity of the amount of gas produced with
ER. When ER equals 1.0, that is to say the amount of oxidant
equals the required amount for complete oxidation by stoi-
chiometry calculation. As can be seen from Fig. 2, in this
reaction condition by chemical equilibrium calculation, the
amount of hydrogen, methane and carbon monoxide
decreases to zero. Although oxidant can accelerate the rate of
the gasification reaction, too much oxidant leads to reaction
between combustible product such as hydrogen, methane and
carbon monoxide. As a result, finding the optimal oxidant
amount for hydrogen production is very important.
0.0 0.2 0.4 0.6 0.8 1.00
20
40
60
80
100
ER
H2CH4CO2
/%
Fig. 2 – Effects of ER to the equilibrium gas composition
(Temperature, 5008C; Pressure, 25MPa; Feedstock,
10wt%glucose).
3. Apparatus and experimental procedures
The experimental system in this paper is shown in Fig. 3. A
fluidized bed reactor made of 316 stainless steel is equipped in
the experimental system. The inside diameters of the fluid-
ization part and suspension part are 30 mm and 40 mm,
respectively. The whole length of the fluidized bed reactor is
915 mm. The designed temperature and pressure are 650 �C
and 30 MPa, respectively. Five K-armored thermocouples are
equipped along the axial direction of the reactor to measure the
fluid temperature in the reactor. Quartz sand with the diameter
of 0.1–0.15 mm is used as the bed material. Detailed experi-
mental device and method can be seen in the literature [22].
The corn cob used in the experiment was collected in the
city of Xi’an, Shaanxi Province, China. The ultimate and
proximate analysis of the corn cob is shown in Table 1. The
corn cob was pulverized into particles smaller than 60 mesh
and mixed with sodium carboxymethyl cellulose (CMC) to
realize continuous delivery under high pressure. Alkali lignin,
substitute of lignin, was purchased from Wuhan Donghua
chemical Co., Ltd. CMC was purchased from Shanghai Shanpu
chemical Co., Ltd. Glucose and 30wt% analytically pure H2O2
was purchased from Tianjin Jinbei fine chemical Co., Ltd. H2O2
was used as oxidant in the experiment.
The composition of the gaseous phase was measured by
HP6890 gas chromatograph, which is equipped with thermal
conductivity detector and capillary column C-2000 that was
purchased from LanZhou Institute of Chemical Physics in
China. High purity He was used as carrier gas with a flow rate
of 10 ml/min.
4. Partial oxidative gasification of biomass
The three main components of biomass are cellulose, semi-
cellulose and lignin. Glucose, as the monomer of cellulose, is
a representative biomass model compound. Lignin consists of
phenolic structure not only is difficult to be gasified but
also adversely affects the hydrogen production [21,24,25],
and it is also usually used as the model compound of
biomass to study the rules of hydrogen production from
biomass in supercritical water. Corn cob is a typical agricul-
tural residual frequently seen. So glucose, lignin and corn cob
were selected to study the gasification characteristics of
biomass by supercritical water partial oxidation. Gasification
efficiency (GE), carbon gasification efficiency (CE) and
hydrogen gasification efficiency (HGE) are used to evaluate the
effect of gasification.
4.1. Glucose
Fig. 4 shows the influence of ER upon the gasification results in
the reaction condition: temperature (without special decla-
ration in this paper, temperature means the average temper-
ature of the external wall of the reactor) 600 �C, pressure
25 MPa and flow rate of glucose 24.7 g/min, concentration
10wt%. It can be seen from Fig. 4(c) that as the amount of
oxidant added increased, the GE and CE increased. Carbon
monoxide is a typical partial oxidant product [26] through the
Fig. 3 – Scheme diagram of experimental system.1:feedstock tank; 2,3: feeder; 4: fluidization bed reactor; 5: heat exchanger;
6: pre-heater; 7: cooler; 8,9,10: back pressure regulator; 11: high pressure separator; 12: low pressure separator; 13,14: wet
test meter; 15,16,17,18: high pressure metering pump; 19,20,21,22: mass flow meter; 23: water tank.
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 03004
partial oxidative reaction (8), so as can be seen in Fig. 4(b), the
amount of carbon monoxide increased as ER increased.
CmHn / COþ other hydrocarbons (8)
It can be seen from Fig. 4(a) that the fraction of hydrogen
and carbon dioxide in gas production decreased and the
fraction of carbon monoxide increased as ER increased. It can
be seen from Fig. 4(b) that the yield of hydrogen increased first
and then decreased. GE of glucose was improved by the
oxidant added comparatively faster when ER was small, even
though hydrogen fraction in the gas production decreased,
when ER equaled 0.2, the yield of hydrogen obtained its
maximum value at the investigated experimental conditions.
The trend of HGE with oxidant amount was in close agree-
ment with the yield of hydrogen. Thus, oxidant could improve
the gasification efficiency of glucose and appropriate amount
of oxidant can improve hydrogen production. The experiment
by Williams [25] was in agreement with our experimental
results: as oxidant concentration increased, the yield of
hydrogen increased first and then decreased, but the yield of
hydrogen peaked when ER¼ 0.53. The reason for the deviation
of the optimal ER value maybe the experiment done by
Williams was in relatively low temperature 350 �C, and then
the reaction rate was lower, so more oxidant was needed to
achieve the maximum yield of hydrogen.
Table 1 – The ultimate and proximate analysis of corn coba.
w/% (Ultimate analysis)
C H N S Ob M
40.22 4.11 0.39 0.04 42.56 9.71
a Air dry basis.
b Difference.
The fraction of carbon monoxide was relatively high,
which was not consistent with thermodynamic result
mentioned above. That is mainly because the gas fraction
calculated by chemical equilibrium model only shows the
thermodynamic limit of the reaction. However, the real gasi-
fication reaction is controlled by kinetics of the reactions.
4.2. Lignin
It can be seen from Fig. 5(c) that as the ER increased from 0 to
0.4, GE increased from 0.216 to 0.679, CE increased more than
threefold, from 0.165 to 0.518. Formaldehyde, benzene and
polymers with phenolic structure are generated from lignin in
supercritical water, as reaction (9), and phenolic resins are
easily produced through the polymerization reaction (10)
between phenolic compounds and formaldehyde. Thus,
formaldehyde must decompose fast before the polymerization
reaction with phenolic compounds [21]. When oxidant is
present, on one hand, as mentioned above, oxidant can help
decompose compounds with phenolic structure to improve the
gasification efficiency. On the other hand, hydrogen peroxide
in supercritical water can form free radicals OH� through
reaction (11), and the presence of free radicals OH� can greatly
facilitate the reaction (12), and decrease the concentration of
formaldehyde, so the reaction (10) is inhibited greatly. Thus the
production of char and tar decreased and the gasification
w/% (Proximate analysis) Heat value/kJ kg�1
A V FC
2.97 71.21 16.11 16650.0
0.0 0.2 0.4 0.6 0.80
10
20
30
40
50
H2 CO
CH4 CO2
ER
a
0.0 0.2 0.4 0.6 0.80
4
8
12
G
as Y
ield
/m
ol.kg
-1
ER
H2 CO
CH4 CO2
b
0.0 0.2 0.4 0.6 0.80.2
0.4
0.6
0.8
CE
, G
E o
r H
GE
ER
GECEHGE
c
/%
Fig. 4 – Effects of ER on gasification characteristics of
glucose: (a) molar fraction; (b) gas yield; (c) CE, GE and HGE.
(Temperature, 6008C; Pressure, 25MPa; Feedstock, 10wt%
glucose; Feedstock flow rate, 24.7g/min).
0.0 0.1 0.2 0.3 0.40
20
40
60
ER
H2
COCH4
CO2
0.0 0.1 0.2 0.3 0.40
4
8
12
16
H2
COCH4
CO2
Gas Y
ield
/m
ol.kg
-1
ER
b
0.0 0.1 0.2 0.3 0.40.1
0.2
0.3
0.4
0.5
0.6
0.7
GE
, H
GE
, o
r C
E
ER
GEHGECE
c
a
/%
/%
Fig. 5 – Effects of ER on gasification characteristics of lignin:
(a) molar fraction; (b) gas yield; (c) CE, GE and HGE.
(Temperature, 6008C; Pressure, 25MPa; Feedstock, 2wt%
lignin D 2wt%CMC; Feedstock flow rate, 25g/min).
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 0 3005
20
40
60
H2 CO
CH4 CO2
a
%
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 03006
efficiency of lignin increases .So the continuous operation of
the system is guaranteed, as it was observed that as ER
increases, the colour of the liquid products become lighter.
Lignin / HCHOþ phenolic compoundsþ others (9)
HCHOþ phenolic compounds / resins (10)
0.0 0.1 0.2 0.3 0.40
ER
0.0 0.1 0.2 0.3 0.4
0
5
10
15
20
Gas Y
ield
/m
ol.kg
-1
ER
H2 CO
CH4 CO2
b
0.8
0.9c
H2O2 / 2OH� (11)
HCHO / COþH2 (12)
It can be seen from Fig. 5(b) and (c) that as ER increases
from 0 to 0.4, the yield of hydrogen and hydrogen gasification
efficiency increased first and then decreased. This trend is
mainly caused by two aspects. On one hand, the presence of
oxidant inhibits the reaction (10), so more hydrogen and
carbon elements in the liquid intermediate product are
released. Reaction (12) is also promoted, and then the carbon
monoxide produces carbon dioxide and hydrogen through the
water gas shift reaction (2). On the other hand, as ER increases,
as can be seen in Fig. 5(a), the fraction of hydrogen and carbon
monoxide decreased, because the reaction between oxidant
and hydrogen became intense and resulted in the decrease of
hydrogen yield. Summing up the above factors, experiment
results show that the yield of hydrogen peaked when ER
equaled 0.1, and the yield of hydrogen increased by 25.8%
compared with that without oxidant.
It can be seen from Fig. 5(a) and (b), the yield of carbon
monoxide was lower than that in Fig. 4(a) and (b), because the
feedstock was alkali lignin as the substitute of lignin, and
reaction (2) was catalyzed by the presence of alkali so the yield
of carbon monoxide decreased greatly.
0.0 0.20.1 0.3 0.40.3
0.4
0.5
0.6
0.7
GE
, C
E o
r H
GE
ER
GE
CE
HGE
Fig. 6 – Effects of ER on gasification characteristics of corn
cob: (a) molar fraction; (b) gas yield; (c) CE, GE and HGE
(Temperature, 6508C; Pressure, 25MPa; Feedstock,
5wt%corn cobD2wt% CMC; Feedstock flow rate, 25.1g/min).
4.3. Corn cob
Fig. 6 shows the relation of corn cob gasification results and the
amount of oxidant added in the condition temperature 650 �C,
pressure 25 MPa and flow rate of feedstock 25.1 g/min, and the
concentrations of corn cob and CMC are 5wt% and 2wt%,
respectively. As can be seen from the Fig. 6(c) and (b), GE and CE
increasedrapidlyandHGEdecreased.WhentheERwasrelatively
small, the hydrogen yield’s deviation was small, and when ER
was more than 0.1, the yield of hydrogen decreased rapidly. Itcan
be seen from Fig. 6(a) that the fraction of hydrogen in gas
production gradually decreased as the concentration of oxidant
increased. When the ER was 0.4, the hydrogen fraction was only
24.20%. The fraction of carbon dioxide increased as ER increased,
because increasing ER enhanced direct oxidation to carbon
dioxide. Compared with the glucose partial oxidative gasification
result, the fraction of carbon monoxide was much lower, that is
mainlybecauseof thesmallamountofalkalinecompoundK2CO3
in real biomass, which can be a catalyst to accelerate the water
gas shift reaction (2) to convert carbon monoxide to hydrogen.
Compared with the gasification characteristics of model
compounds mentioned above, there was no maximum yield of
hydrogen as ER increased. Average external wall temperature
as high as 650 �C was adopted to realize the continuous
23 25 270
10
20
30
40
50
Pressure/MPa
H2
COCH4
CO2
a
23 25 270
4
8
12
16
Gas Y
ield
/m
ol.kg
-1
Pressure/MPa
H2
CO CH4
CO2
b
23 25 270.0
0.2
0.4
0.6
0.8
1.0
GE
, H
GE
o
r C
E
Pressure/MPa
GE HGE CE
c
/%
Fig. 8 – Effects of pressure on the gasification
characteristics: (a) molar fraction; (b) gas yield; (c) CE, GE
and HGE(Temperature, 6508C; Feedstock, 10wt% glucose;
Feedstock flow rate, 25g/min; ER[0.4).
550 600 6500
10
20
30
40
50
Temperature/°C
H2
COCH4
CO2
a
b
550 600 6500
4
8
12
Gas Y
ield
/m
ol.kg
-1
Temperature/°C
H2 CO
CH4 CO2
550 600 6500.0
0.2
0.4
0.6
0.8
1.0
GE
, H
GE
o
r C
E
Temperature/°C
GEHGECE
c
/%
Fig. 7 – Effects of temperature on the gasification
characteristics: (a) molar fraction; (b) gas yield; (c) CE, GE
and HGE (Pressure, 25MPa; Feedstock,10wt% glucose;
Feedstock flow rate, 25g/min, ER[0.4).
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 0 3007
operation of the system, and the temperature was high enough
for the fast gasification reaction for corn cob, and the addition
of oxidant can also combust the hydrogen and carbon
monoxide fast in high temperature. Portela [16] also reported
that at 500 �C the effect of hydrogen peroxide appears to be
negligible. In our experiment system, when the average
external wall temperature is 650 �C, the average temperature of
the fluid is about 500 �C [22], so the effect of oxidant for
hydrogen yield is more obvious in lower temperature.
10 17.5 240
20
40
60
Concentration/%
H2
COCH4
CO2
a
10 17.5 240
4
8
12
16
Gas Y
ield
/m
ol.kg
-1
Concentration/%
H2
CO
CH4
CO2
b
10 17.5 240.0
0.2
0.4
0.6
0.8
1.0
GE
, H
GE
o
r C
E
Concentration/%
GEHGECE
c
/%
Fig. 9 – Effects of concentration on the gasification
characteristics: (a) molar fraction; (b) gas yield; (c) CE, GE
and HGE(Temperature, 6508C; Pressure, 25MPa; Feedstock
flow rate, 25g/min; ER[0.4).
14 25 370
10
20
30
40
50
Flow rate/g.min-1
H2
CO
CH4
CO2
14 25 370
4
8
12
16
Gas Y
ield
/m
ol.kg
-1
Flow rate/g.min-1
H2
COCH4
CO2
14 25 370.0
0.2
0.4
0.6
0.8
1.0
GE
, H
GE
o
r C
E
Flow rate/g.min-1
GEHGECE
/%
a
b
c
Fig. 10 – Effects of flow rate of feedstock on the gasification
characteristics:(a) molar fraction; (b) gas yield; (c) CE, GE
and HGE (Temperature, 6008C; Pressure, 25MPa; Feedstock,
10wt% glucose; ER[0.4).
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 03008
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 0 3009
5. Effects of operation parameters
5.1. Temperature
From Fig. 7(a) and (b), we can see that when the temperature
increased from 550 �C to 650 �C the fraction of hydrogen
increased from 14.68% to 29.30%, and the yield of hydrogen
increased from 4.425 mol/kg to 8.939 mol/kg. Temperature
showed a great effect on supercritical water partial oxidative
gasification. The occurrence of two competing reaction ways
was reported [27]. One way consists of ionic reaction step,
which is preferred at higher pressure and/or lower tempera-
ture. The second reaction pathway is a free radical degradation
and dominates at lower pressures and/or higher temperatures.
High temperature favors the free radical reaction in which gas
is produced. What’s more, high temperature accelerates the
approaching to the chemical equilibrium state. Based on the
thermodynamics analysis above, gasification is complete in
the chemical equilibrium state, so high temperature favors
complete gasification. As is shown in Fig. 7(c), CE, GE, HGE
increased with temperature. It also can be seen that the yield of
methane decreased with temperature, which was determined
by the exothermic nature of the methanation reaction.
5.2. Pressure
The mechanisms of pressure on supercritical water partial
oxidative gasification are very complicated. (1) If the other
operation parameters such as temperature, concentration,
flowrateare kept constant, thedensity and ionproduct of water
increase as pressure increases. Increased density and ion
product of water accelerate the hydrolysis reaction, water gas
shift reaction and oxidant reaction, which favors gas produc-
tion. (2) Gases are typical products of the free radical reactions,
therefore, high pressure inhibits gas formation reaction [27]. (3)
In general, a reaction that increases the number of molecules is
inhibited in thehigh-pressureregion according to Le Chatelier’s
principle [28]. Therefore, lower pressure favors gasification
process. In conclusion, the influence of pressure on gasification
results from the integrated actions of the factors mentioned
above [10]. The experimental results as shown in Fig. 8 indi-
cated that the pressures had no significant effect on the partial
oxidative gasification of biomass. However, when the pressure
is below the supercritical pressure, the special physical and
chemical properties disappear, which goes against hydrogen
production. At the same time, higher pressure causes trouble
for the design and maintenance of the system and also
increases the operating costs. Experiment experience shows
that the ideal operation pressure is about 25 MPa.
5.3. Concentration
From Fig. 9(a) and (b), we can see that as the concentration of
glucose increased from 10wt% to 24wt%, the fraction of
hydrogen decreased from 29.3% to 10.14% and the yield
of hydrogen decreased from 8.939 mol/kg to 1.933 mol/kg.
From Fig. 9(c) we can see that GE, HGE and CE decreased in
varying degrees. High concentration of feedstock means that
the concentration of water around reactants decrease, so the
hydrolysis reaction of reactants and the water gas shift reac-
tion are inhibited. Therefore, high concentration biomass is
difficult to be gasified. But high concentration gasification is the
basis for large-scaled commercial application, so how to gasify
high concentration feedstock is the focus of future research.
5.4. Flow rate of feedstock
Different flow rate affects the partial oxidative gasification
from the following two aspects. (1) Volume of the reactor kept
constant, when the flow rate is higher, the resident time is
limited, so high flow rate of feedstock probably leads to
incomplete reaction. So it can be seen from Fig. 10(c) and (b) the
GE and the yield of hydrogen were lower. (2) According to the
report by Matsumura [29], the range of flow rate investigated in
this paper made sure that the velocity of bed material was
between the minimum fluidization velocity and terminal
velocity. Higher flow rate leads to a fiercer fluidization condi-
tion and enhances heat and mass transfer so as to favor the
gasification reaction. It can be seen from Fig. 10(a) that when
the flow rate of feedstock increased from 14 g/min to 37 g/min,
the fraction of hydrogen decreased from 29.30% to 10.14%.
From Fig. 10(b) we can see that the yield of hydrogen decreased
from 8.75 mol/kg to 4.68 mol/kg, and the fraction of carbon
monoxide increased. It can be seen from Fig. 10(c), GE, HGE and
CE decreased in different degrees. From the experiment result
we can deduce that the former factor was the dominant one in
the experiment range investigated, in another words, low flow
rate of feedstock favored the hydrogen production.
6. Conclusions
Supercritical water partial oxidative gasification is an effective
method to produce hydrogen from biomass. Oxidant can
improve the gasification efficiency and decreases the produc-
tion of char and tar to guarantee the system’s continuous
operation. Thermodynamic analysis shows that when the
chemical reaction reaches equilibrium, the gasification is
complete. The amount order of produced gases is
H2>CO2>CH4>CO. when the oxidant amount is small. As ER
increases, yields of hydrogen, methane and carbon monoxide
and the molar fraction of hydrogen decrease, and the yield of
carbon dioxide increases. Experimental results show that yield
of hydrogen from lignin increased from 6.45 mol/kg to 8.11 mol/
kg when ER increased from 0 to 0.1. GE of lignin increased from
0.216 to 0.679 when ER increased from 0 to 0.4. Supercritical
water partial oxidative gasification is influenced by operating
parameters. High temperature favors hydrogen production.
Pressure has no significant effect on the gasification result. High
flow rate of feedstock leads to incomplete gasification and low
concentration is favorable for hydrogen production and GE.
Acknowledgements
This work is currently supported by the National Key Project
for Basic Research of China through Contract No.
2009CB220000 and the National High Technology Research
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 5 ( 2 0 1 0 ) 3 0 0 1 – 3 0 1 03010
and Development Program of China (863 Program) through
contract No. 2007AA05Z147.
r e f e r e n c e s
[1] Izumizaki Y, Park KC, Tachibana Y, Tomiyasu H, Fujii Y.Organic decomposition in supercritical water by an aid ofruthenium (IV) oxide as a catalyst-exploitation of biomassresources for hydrogen production. Prog Nucl Energy 2005;47(1–4):544–52.
[2] Guo LJ, Lu YJ, Zhang XM, Ji CM, Guan Y, Pei AX. Hydrogenproduction by biomass gasification in supercritical water:a systematic experimental and analytical study. Catal Today2007;129(3-4):275–86.
[3] Antal MJ, Allen SG, Schulman D, Xu XD. Biomass gasificationin supercritical water. Ind Eng Chem Res 2000;39(11):4040–53.
[4] Lin SY, Harada M, Suzuki Y, Hatano H. Continuousexperiment regarding hydrogen production by coal/CaOreaction with steam (I) gas products. Fuel 2004;83(7–8):869–74.
[5] Hao XH, Guo LJ, Zhang XM, Guan Y. Hydrogen productionfrom catalytic gasification of cellulose in supercritical water.Chem Eng J 2005;110(1-3):57–65.
[6] Lee IG, Kim MS, Ihm SK. Gasification of glucose insupercritical water. Ind Eng Chem Res 2002;41(5):1182–8.
[7] Hao XH, Guo LJ, Mao XA, Zhang XM, Chen XJ. Hydrogenproduction from glucose used as a model compound ofbiomass gasified in supercritical water. Int J Hydrogen Energy2003;28(1):55–64.
[8] Sınag A, Kruse A, Schwarzkopf V. Key Compounds of thehydropyrolysis of glucose in supercritical water in thepresence of K2CO3. Ind Eng Chem Res 2003;42(15):3516–21.
[9] Byrd AJ, Pant KK, Gupta RB. Hydrogen production fromglucose using Ru/Al2O3 catalyst in supercritical water. IndEng Chem Res 2007;46(11):3574–9.
[10] Lu YJ, Guo LJ, Ji CM, Zhang XM, Hao XH, Yan QH. Hydrogenproduction by biomass gasification in supercritical water:a parametric study. Int J Hydrogen Energy 2006;31(7):822–31.
[11] Matsumura Y, Minowa T, Potic B, Kersten SRA, Prins W,Swaaij WPM, et al. Biomass gasification in near- and super-critical water: status and prospects. Biomass Bioenergy 2005;29(4):269–92.
[12] Watanabe M, Mochiduki M, Sawamoto S, Adschiri T, Arai K.Partial oxidation of n-hexadecane and polyethylene insupercritical water. J Supercrit Fluids 2001;20(3):257–66.
[13] Armbruster U, Martin A, Krepel A. Partial oxidation ofpropane in sub- and supercritical water. J Supercrit Fluids2001;21(3):233–43.
[14] Johanson NW, Spritzer MH, Hong GT, Rickman WS.Supercritical water partial oxidation. In: Proceedings of the2001 U.S. DOE hydrogen program review. NREL/CP-570-30535.
[15] Kruse A, Henningsen T, Sinag A, Pfeiffer J. Biomassgasification in supercritical water: influence of the drymatter content and the formation of phenols. Ing Eng ChemRes 2003;42(16):3711–7.
[16] Protela JR, Lopez J, Nebot E, Ossa EM. Elimination of cuttingoil wastes by promoted hydrothermal oxidation. J HazardMater 2001;88(1):95–106.
[17] Yu DH, Aihara M, Antal MJ. Hydrogen production by steamreforming glucose in supercritical water. Energy Fuel 1993;7(5):574–7.
[18] Savage PE. Organic chemical reactions in supercritical water.Chem Rev 1999;99(2):603–21.
[19] Martino CJ, Savage PE. Supercritical water oxidation kinetics,products, and pathways for CH3- and CHO-substitutedphenols. Ind Eng Chem Res 1997;36(5):1391–400.
[20] Yoshida T, Oshima Y. Partial oxidative and catalytic biomassgasification in supercritical water: a promising flow reactorsystem. Ind Eng Chem Res 2004;43(15):4097–104.
[21] Wantanabe M, Inomata H, Osada M, Sato T, Adschin T,Arai K. Catalytic effects of NaOH and ZrO2 for partialoxidative gasification of n-hexadecane and lignin insupercritical water. Fuel 2003;82(5):545–52.
[22] Lu YJ, Jin H, Guo LJ, Zhang XM, Cao CQ, Guo X. Hydrogenproduction by biomass gasification in supercritical waterwith a fluidized bed reactor. Int J Hydrogen Energy 2008;33(21):6066–75.
[23] Yan QH, Guo LJ, Lu YJ. Thermodynamic analysis of hydrogenproduction from biomass gasification in supercritical water.Energy Convers Manage 2006;47(11–12):1515–28.
[24] Yoshida T, Matsumura Y. Gasification of cellulose, xylan, andlignin mixtures in supercritical water. Ind Eng Chem Res2001;40(23):5469–74.
[25] Williams PT, Onwudili J. Composition of productsfrom the supercritical water gasification of glucose:a model biomass compound. Ind Eng Chem Res 2005;44(23):8739–49.
[26] Arai K, Adschiri T, Watanabe M. Hydrogenation ofhydrocarbons through partial oxidation in supercriticalwater. Ind Eng Chem Res 2000;39(12):4697–701.
[27] Buhler W, Dinjus E, Ederer HJ, Kruse A, Mas C. Ionic reactionsand pyrolysis of glycerol as competing reaction pathways innear- and supercritical water. J Supercrit Fluids 2002;22(1):37–53.
[28] Takafumi S, Takeshi F, Yasuyoshi I, Hirokazu S,Yasutomo M, Masahide S, et al. Effect of water density onthe gasification of lignin with magnesium oxide supportednickel catalysts in supercritical water. Ind Eng Chem Res2006;45(2):615–22.
[29] Matsumura Y, Minowa T. Fundamental design ofa continuous biomass gasification process usinga supercritical water fluidized bed. Int J Hydrogen Energy2004;29(7):701–7.