Danhua Mei1,2, Shiyun Liu1, Jale Yanik3, Gartzen Lopez4,5, Martin Olazar4, Zhi Fang1, Xin Tu2. 1. College of Electrical Engineering and Control Science, Nanjing Tech University, Nanjing 211816, Jiangsu, China. 2. Department of Electrical Engineering and Electronics, University of Liverpool, Liverpool L69 3GJ, U.K. 3. Department of Chemistry, Faculty of Science, Ege University, 35100 Bornova, Izmir, Turkey. 4. Department of Chemical Engineering, University of the Basque Country UPV/EHU, P.O. Box 644, E48080 Bilbao, Spain. 5. IKERBASQUE, Basque Foundation for Science, 48013 Bilbao, Spain.
Abstract
Biomass gasification is a promising and sustainable process to produce renewable and CO2-neutral syngas (H2 and CO). However, the contamination of syngas with tar is one of the major challenges to limit the deployment of biomass gasification on a commercial scale. Here, we propose a hybrid plasma-catalytic system for steam reforming of tar compounds over honeycomb-based catalysts in a gliding arc discharge (GAD) reactor. The reaction performances were evaluated using the blank substrate and coated catalytic materials (γ-Al2O3 and Ni/γ-Al2O3). Compared with the plasma alone process, introducing the honeycomb materials in GAD prolonged the residence time of reactant molecules for collision with plasma reactive species to promote their conversions. The presence of Ni/γ-Al2O3 gave the best performance with the high conversion of toluene (86.3%) and naphthalene (75.5%) and yield of H2 (35.0%) and CO (49.1%), while greatly inhibiting the formation of byproducts. The corresponding highest overall energy efficiency of 50.9 g/kWh was achieved, which was 35.4% higher than that in the plasma alone process. Characterization of the used catalyst and long-term running indicated that the honeycomb material coated with Ni/γ-Al2O3 had strong carbon resistance and excellent stability. The superior catalytic performance of Ni/γ-Al2O3 can be mainly ascribed to the large specific surface area and the in situ reduction of nickel oxide species in the reaction process, which promoted the interaction between plasma reactive species and catalysts and generated the plasma-catalysis synergy.
Biomass gasification is a promising and sustainable process to produce renewable and CO2-neutral syngas (H2 and CO). However, the contamination of syngas with tar is one of the major challenges to limit the deployment of biomass gasification on a commercial scale. Here, we propose a hybrid plasma-catalytic system for steam reforming of tar compounds over honeycomb-based catalysts in a gliding arc discharge (GAD) reactor. The reaction performances were evaluated using the blank substrate and coated catalytic materials (γ-Al2O3 and Ni/γ-Al2O3). Compared with the plasma alone process, introducing the honeycomb materials in GAD prolonged the residence time of reactant molecules for collision with plasma reactive species to promote their conversions. The presence of Ni/γ-Al2O3 gave the best performance with the high conversion of toluene (86.3%) and naphthalene (75.5%) and yield of H2 (35.0%) and CO (49.1%), while greatly inhibiting the formation of byproducts. The corresponding highest overall energy efficiency of 50.9 g/kWh was achieved, which was 35.4% higher than that in the plasma alone process. Characterization of the used catalyst and long-term running indicated that the honeycomb material coated with Ni/γ-Al2O3 had strong carbon resistance and excellent stability. The superior catalytic performance of Ni/γ-Al2O3 can be mainly ascribed to the large specific surface area and the in situ reduction of nickel oxide species in the reaction process, which promoted the interaction between plasma reactive species and catalysts and generated the plasma-catalysis synergy.
The depletion of fossil
resources and environmental problems associated
with significant greenhouse gas emissions have promoted the development
of renewable energy utilization technologies.[1,2] Biomass
is considered a renewable carbon-neutral energy source. Gasification
represents an attractive avenue to convert biomass into clean producer
gas (a gas mixture of CO, H2, CO2, and CH4). The producer gas is ideally suitable to be utilized in
gas turbines and fuel cells to produce heat and electricity or upgraded
to synthesize value-added chemical compounds.[3] However, tar is inevitably formed in gasification, which contains
complicated organic compounds, including multiple ring aromatic compounds,
and some oxygen-containing hydrocarbons.[4] The content of tar typically varies between 0.5 and 100 g/m3 depending on the type of gasifier.[5] The presence of tar can cause serious hazards to the end-user devices
such as fouling, clogging, and corrosion, lowering the gasification
efficiency, as well as increasing the maintenance frequency and the
operation cost.[6] Therefore, effective control
and removal of tar is the main challenge to the practical application
of producer gas with high efficiency.Significant efforts have
been directed toward tar removal from
producer gas using a variety of physical and chemical approaches.[5,7,8] Mechanical separation mainly removes
tar physically using scrubbers, cyclones, and filters. This process
is commonly used due to its easy application but will generate secondary
pollution and lose the chemical energy contained in tar compounds.[5] Thermal cracking and catalytic reforming can
recycle the energy contained in tar while removing it.[7] However, transforming tar by thermal cracking normally
requires a high reaction temperature of around 1250 °C, which
increases the requirement of the reactor and therefore both the capital
and operational costs.[8] Catalytic reforming
of tar can achieve promising tar conversions at relatively lower temperatures
around 500 °C and high-quality producer gas.[9] A variety of catalysts have been investigated for catalytic
tar reforming, including transition-metal catalysts (Ni, Mn, Fe, and
Co), noble-metal catalysts (Pt, Ru, and Rh), and natural catalysts.[10−12] Among them, Ni-based catalysts have been extensively investigated
for tar reforming due to their high reactivity and dehydrogenation
capacity.[13] However, the conventional catalytic
reforming process faces major limitations such as rapid catalyst deactivation
induced by coke deposition and sintering at high temperatures.[14]Nonthermal plasmas (NTPs) offer an effective
and sustainable alternative
approach for converting tars to syngas and other valuable chemicals
at lower temperatures.[15,16] Compared to conventional thermal
cracking and catalytic processes, NTP shows unique characteristics
of high activity and fast reaction rate, which overcomes the limitation
of high reaction temperature and reduces the overall energy cost.[17] However, the industrial applications of this
technology are limited due to low selectivity toward the specific
products and the generation of byproducts.[18] To deal with this issue, the hybrid plasma-catalysis technology
has shown great potential as it can combine the advantages of the
fast reaction rate of NTPs and the high selectivity of the catalyst
with the high activity.[19−22] The synergistic effect might be generated in the
hybrid plasma-enhanced catalytic system, where the catalysts can be
activated at low temperatures with high reactivity and strong carbon
resistance.[23−26] Currently, dielectric barrier discharge (DBD) has attracted intense
attention in the plasma-catalytic reforming of biomass tars as it
has strong flexibility to be combined with catalysts to promote the
conversion of tar model compounds and the yield of specific products
while suppressing the formation of undesired byproducts.[27−29] Nevertheless, the energy efficiency of the tar reforming process
based on DBD plasma coupled with catalysis is still unsatisfactory
due to the limited treatment capability and power levels.Compared
to DBD, gliding arc discharge (GAD) is featured by simple
configuration, high processing capacity, and relative higher energy
density, which enable it to show more potential for efficient destruction
and reforming of tar.[30−34] Moreover, the enhanced reaction performance could be achieved by
introducing suitable catalysts into the GAD reactor, which has been
confirmed in CO2 conversion and CH4 activation
using GAD.[35−37] For the biomass gasification tar, we previously performed
the conversion of naphthalene and toluene mixture (model tar compound)
in GAD coupled with a Ni-Co/γ-Al2O3 bimetallic
catalyst to obtain the highest total tar conversion (95.1%) and overall
energy efficiency (40.3 g/kWh).[38] Xu and
co-workers found that packing a Ni/γ-Al2O3 catalyst bed 62 mm downstream of an anode in a rotating GAD reactor
resulted in a toluene conversion of 91.9%, which was 21% higher than
that obtained without using any catalyst.[39] These previous studies demonstrated the effectiveness and benefits
of incorporating catalysts into GAD for biomass gasification tar conversion.
However, the catalysts were mainly placed in the GAD reactor in the
form of a packed-bed, which would cause high pressure drop and therefore
enhance the power for fluid flow,[40] especially
for the conditions of high gas flow rate like that required in GAD.
To date, little research has attempted to explore an efficient plasma-catalysis
configuration using GAD, which can achieve promising performance with
high gas flow rate.Herein, we performed the plasma-catalytic
reforming of biomass
gasification tar in GAD coupled with honeycomb catalysts. This kind
of catalyst offers unique features of the uniform gas flow distribution,
the strong capability of treating gas with large volumes compared
to conventional packed-bed catalysts, and the easiness of scaling
up for industrial applications.[41] The effect
of different packing materials downstream of electrodes in GAD was
evaluated with respect to tar conversions, selectivities and yields
of gaseous products as well as energy efficiencies of the hybrid process.
Moreover, a plausible reaction mechanism and pathway involved in our
systems were discussed based on the results from catalyst characterizations
and a comprehensive analysis of liquid and gas products.
Experimental Section
Experimental Setup
The steam reforming
of tar was performed
in a GAD reactor coupled with honeycomb catalysts (Figure ). The experimental setup contains
a GAD reactor, a carrier gas and reactant supply system, an AC power
system, as well as a measurement system for discharge characteristics
and reaction performance. The details of the reactor structure and
other systems have been presented in our previous studies.[32,38] A mixture of naphthalene (C10H8) and toluene
(C7H8) was used as model tar compounds since
they represent the typical stable light mono-aromatic and polycyclic
aromatic tar compounds from the biomass gasification.[5] Powders of solid naphthalene were dissolved in toluene
to create a mixture of tar compounds. Nitrogen with a high purity
of 99.999% was applied as the working gas. Water and the model tar
compounds were fed continuously into a gas flow tube using two KDS
Legato syringe pumps and evaporated in a tube furnace working at 300
°C. After that, the evaporated mixture was carried to the GAD
reactor by the N2 flow. The content of naphthalene and
toluene in the feed gas was fixed at 1.1 and 15.0 g/Nm3, respectively, concerning their amount from the practical biomass
gasification process.[30] The total feed
gas flow was kept constant at 3.5 L/min to maintain a stable discharge
in the reactor, and the molar ratio of steam-to-carbon was fixed at
1.5. There was no obvious plasma polymerization on the electrodes
or reactor walls under these conditions. Similar findings were also
reported in our previous works.[30,38] The plasma reactor
was controlled by a 50 Hz neon high-voltage (HV) transformer with
an adjustable applied voltage range of 0–10 kV. The discharge
power was determined by integrating the applied voltage and arc current,
as shown in eq . It
can be changed by adjusting the applied voltage and was fixed at 56
W for this study.The packing
materials exhibited a honeycomb
structure, which was round-shaped with a diameter of 45 mm and a length
of 25 mm. The shape of the cell hole in the honeycomb monolith was
square with 1 mm sides and cell density was around 400 CPSI (cells
per square inch, cell/in2). The bare honeycomb substrate
was made up of cordierite. γ-Al2O3 was
coated on the substrate and used as the catalyst support. The active
metal Ni was then loaded on the catalyst support by the impregnation
approach. The bare honeycomb substrate, the catalyst support, and
the supported Ni catalyst were all tested in the GAD reactor for biomass
gasification tar reforming, and they are denoted as blank, γ-Al2O3, and Ni/γ-Al2O3,
respectively. The honeycomb materials were placed 2 mm below the electrode
end supported by an annular flange during the steam reforming process,
as shown in Figure . This distance allows the arc to make contact with the catalyst
and facilitate the interaction between plasma reactive species and
the catalyst, thereby generating the potential plasma-catalysis synergy.
The temperatures in the packing materials during the steam reforming
process were recorded by a thermocouple. The time evolution of the
temperature when using different honeycomb materials is plotted in Figure . Clearly, no obvious
difference in the temperature was observed in the presence of different
honeycomb materials, and they all stabilized at around 350 °C
when running the steam reforming reactions for 10 min. We also performed
the thermal-catalytic reactions using these three materials at 350
°C to evaluate the plasma-catalysis synergy.
Figure 1
Experimental system for
plasma tar reforming.
Figure 2
Time evolution of the
temperatures in the presence of different
honeycomb materials.
Experimental system for
plasma tar reforming.Time evolution of the
temperatures in the presence of different
honeycomb materials.
Catalyst Characterization
The physicochemical properties
of the catalysts before and after the reaction were analyzed using
the following characterization approaches. The N2 adsorption
and desorption isotherms of the fresh and used catalysts were analyzed
on a Micromeritics ASAP 2020 system. Before the measurement, all prepared
samples were vacuum degassed at 150 °C for 5 h to remove the
impurities. The pore size and specific surface area of the samples
were determined by applying the Brunnauer-Emmett-Teller (BET) method.
X-ray diffraction (XRD) patterns were collected using an Empyrean
diffractometer with a Mo-Ag radiation source in the range 2θ
= 5–80° using a turning speed of 4°/min. The morphologies
of materials were examined by scanning electron microscopy (SEM) on
JEM-2100F SEM equipment at 15 kV. An energy-dispersive X-ray spectrometer
(EDX) was also used for the mapping and analysis of the surface elements.
The used catalyst was characterized by thermogravimetric analysis
(TGA) in an air flow (20 ml/min) using Netzsch STA-449-F3 TGA equipment.
The temperature was increased from 20 to 900 °C at a 10 °C/min
heating rate.
Analytical Methods and the Definition of
Parameters
The effluent gases from the reactor were first
fed into absorption
bottles set inside an ice-water mixture cold trap to collect the condensable
products and un-converted reactants. The liquid samples were analyzed
using gas chromatography-mass spectrometry (GC/MS, 7820A-5975C, Agilent)
equipped with an HP-5 capillary column. The recorded mass spectra
were analyzed using the National Institute of Standards and Technology
(NIST) library. The gaseous products were sampled using gas bags and
analyzed by a Shimadzu 2014 GC equipped with dual detectors.The conversion (X) of model tar compound (C7H8 and C10H8) and the yields
(Y) of main gaseous products including H2, CO, and CH were determined using the following
equationsThe selectivities (S) of CO and CH were calculated by eqs and 7, respectively.The energy efficiency
(E) was defined using eq .
Results
and Discussion
Figure shows the textural
properties of the honeycomb
materials before and after the reaction. The blank material exhibited
a low specific surface area (SBET) and
small pore size, which can be ascribed to the compact nonporous structure
of the bare honeycomb substrate. Coating γ-Al2O3 on the substrate significantly increased the SBET and pore size as γ-Al2O3 is well known for its high porosity.[42] After further loading the active metal Ni, the SBET, average pore diameter, and pore volume slightly dropped,
which suggests that the support surface was covered and/or its pores
were partially blocked by the active metal.[39] After the plasma steam reforming reaction, the SBET and pore size of the blank material and γ-Al2O3 were decreased, especially for the blank material,
which can be due to the formation of carbon deposition. This was further
investigated by TGA analysis. However, the SBET and pore size of the used γ-Al2O3 and Ni catalysts were slightly increased, which suggests that the
higher SBET for the reaction was obtained
by the bombardment of ions and/or electrons produced by the GAD plasma
during the steam reforming process.
Figure 3
Textural characters of the honeycomb materials.
Textural characters of the honeycomb materials.Figure illustrates
the XRD patterns of the honeycomb materials before and after the reaction.
Clearly, the diffraction peaks of all of the materials were similar
with the major peaks located at 2θ = 10.5, 18.2, 21.7, 26.4,
28.5, 29.5, 33.9, and 54.3°, which corresponded to the typical
phase of cordierite.[43] However, compared
with the blank substrate, the intensities of the diffraction peaks
of γ-Al2O3 and Ni/γ-Al2O3 were obviously reduced, revealing that the crystallinity
of the honeycomb materials was decreased and the dispersion was enhanced
after loading γ-Al2O3 and active metal
Ni successively.[44] For the blank substrate,
its diffraction peaks presented sharper and stronger intensities after
the steam reforming reaction. This finding suggests that the crystallite
size was increased during the reaction process, which lowered the
specific surface area,[45] as confirmed by
the analysis of their textural properties. A slight increase in the
diffraction peak intensities was also observed for γ-Al2O3. Nevertheless, no discernible difference was
detected in the diffraction peaks of Ni/γ-Al2O3 before and after the reaction, which reveals that this honeycomb
material could maintain a relatively stable structure in the reaction
process. Moreover, the peaks of NiO and Ni were detected at 43.3 and
44.6° in the diffraction peaks of both fresh and spent Ni/γ-Al2O3, respectively. This phenomenon reveals that
the metal oxide NiO species were reduced to Ni in the reaction process.
The collision by the energetic electrons generated in the plasma contributed
to the reduction as it could dissociate the Ni–O bond in the
metal oxide.[46] The presence of the metal
and metal oxide enhances the surface conductivity in the channels
of the honeycomb materials, which is beneficial for the propagation
of the plasma along the surface of the channels and provides catalytically
active sites for steam reforming of tar.[47] Moreover, the NiO and Ni diffraction peaks were weak and broad,
indicating the high dispersion of the reactive species on the catalyst
surface.
Figure 4
XRD patterns of the honeycomb catalysts.
XRD patterns of the honeycomb catalysts.Figure illustrates
the SEM images of all of the fresh and spent honeycomb materials and
the EDX graphs of the Ni/γ-Al2O3 catalyst
before and after reaction. Clearly, the surface of the fresh blank
substrate was very coarse and contained many cavities (Figure a). The crystal grains of γ-Al2O3 covered the irregular surface of the fresh substrate
by coating, which partially filled the cavities and decreased the
surface roughness (Figure b). The γ-Al2O3 layer was chemically
bonded to the blank substrate and produced a smaller crystallite size,
evidenced by the XRD analysis. The relatively uniform metal clusters
were attached to the surface of γ-Al2O3 coated substrate after loading active metal nickel, as shown in
the SEM image of Ni/γ-Al2O3 at higher
magnification (Figure c). After the plasma reaction, the surface morphologies of the blank
material and γ-Al2O3 were significantly
changed due to the production of amorphous and disordered carbon deposition
(Figure d,e). The
deposited carbon might have dissolved into the pores and destroyed
these two materials, which decreased their SBET and pore volumes. This agrees well with their textural
properties in Figure . For the Ni/γ-Al2O3 catalyst, the crystalline
structure did not show significant changes and the distribution of
active species became more uniform, as shown in Figure f. This phenomenon reveals that the GAD plasma
contacted with Ni/γ-Al2O3 promoted the
dispersion of Ni species, generating more active sites to interact
with tar compounds on the catalyst surface. This positive effect is
suggested to come from the bombardment of ions and the attack by the
chemically reactive species,[48] which resulted
in the reduction of NiO to Ni as evidenced by the XRD patterns in Figure .
Figure 5
SEM images of blank,
γ-Al2O3 and Ni/γ-Al2O3 before (a–c) and after (d–f) reaction;
EDX graphs of Ni/γ-Al2O3 before (g) and
after (h) reaction.
SEM images of blank,
γ-Al2O3 and Ni/γ-Al2O3 before (a–c) and after (d–f) reaction;
EDX graphs of Ni/γ-Al2O3 before (g) and
after (h) reaction.The EDX profiles of the
Ni/γ-Al2O3 catalysts
are presented in Figure g,h. In addition to Ni and Al, the components of cordierite including
Mg and Si were detected on the catalyst surface before and after the
reaction.[49] The presence of Mg in the catalyst
enhanced the adsorption of steam due to its hydrophilicity, which
would lead to a better performance of steam reforming.[50] After the reaction, the atomic percentage of
O was decreased while that of Ni was increased, which also confirmed
the reduction of NiO by the plasma active species. The enhanced atomic
percentage of C on the spent Ni catalyst suggests the carbon-containing
species were deposited on the catalyst surface. This result is in
accordance with the TGA analysis.
Catalytic Performance of
the Honeycomb Materials
Figure shows the steam
reforming performance under different reaction conditions. Clearly,
placing the honeycomb materials downstream of the knife-shaped electrode
in the reactor substantially increased the reactant conversion and
energy efficiency. The maximum conversion of toluene (86.3%) and naphthalene
(75.5%) and total energy efficiency (50.9 g/kWh) were achieved using
Ni/γ-Al2O3, which were 31.8, 132.3, and
35.4% greater than those attained during the plasma reaction without
a catalyst, respectively. Because naphthalene and toluene have different
molecular structures and stability, as well as kinetic reactivity,
naphthalene had a lower conversion than toluene under the same operating
conditions. This phenomenon was also reported in previous work.[33] In comparison to toluene, the lower naphthalene
content and conversion yielded less converted naphthalene at the same
discharge power, thus lowering the energy efficiency for naphthalene
conversion. The addition of porous honeycomb materials in the GAD
reactor prolonged the residence time of reactants for degradation,
which enabled the toluene and naphthalene molecules more susceptible
to being attacked by the plasma reactive species and enhanced their
conversions. The catalytic performance of the honeycomb materials
was basically associated with their SBET and pore size.[51] The material with a
higher SBET could normally enlarge the
contact area for reactant conversion. Loading Ni to the γ-Al2O3 coated blank substrate slightly reduced the
specific surface area but further promoted the energy efficiency and
tar conversion, which indicates the core catalytic role of Ni species
in the steam reforming reaction. This has been demonstrated in previous
studies.[27,39]
Figure 6
Variations in (a) the tar conversion and (b)
the energy efficiency
of the plasma reforming under different conditions.
Variations in (a) the tar conversion and (b)
the energy efficiency
of the plasma reforming under different conditions.The purely thermal-catalytic experiment was performed when
the
honeycomb materials were heated at 350 °C in the same GAD reactor
without discharge to evaluate the function of plasma in the tar reforming
reaction (Figure a).
Clearly, almost no tar compounds were converted in the thermal-catalytic
reactions regardless of the honeycomb material type. A comparison
of the reaction performance using thermal-catalytic, plasma alone,
and plasma-catalytic processes indicates that the performance of the
plasma-catalytic system was greater than the sum of that in the thermal-catalytic
and plasma alone systems, suggesting the formation of a synergistic
effect during the plasma-catalytic process.The yields and selectivities
of the gaseous products are displayed
in Figure . In general,
the major gas products consisted of CO, H2, CO2, C2H2, and CH4 with trace amounts
of C2H4 and C2H6. Combining
the GAD plasma with the honeycomb materials remarkably enhanced the
syngas yield, in agreement with the tendency of tar compound conversion.
The highest yield of H2 (35.0%) and CO (49.1%) was obtained
when using Ni/γ-Al2O3, which was 17.9
and 32.1% greater than that attained using plasma alone, respectively.
Integrating Ni/γ-Al2O3 into the GAD reactor
also gave the highest CO selectivity of 57.3%. It is evidenced that
CO2 was not produced in the plasma alone process, while
introducing the honeycomb materials dramatically promoted the formation
of CO2. The highest yield (6.3%) and selectivity (7.3%)
of CO2 were obtained when using the supported Ni catalyst.
This phenomenon implies that the catalysts under the plasma conditions
initiated the water–gas shift reaction () while promoting the steam reforming of tar
compounds (R2) due to the accumulation of H2O molecules
on the honeycomb material surface.[52,53] This finding
was consistent with that reported by Cimerman et al.[54] They found that the combination of plasma with packing
materials (e.g., TiO2 and Pt/γ-Al2O3) for reforming of naphthalene significantly promoted the
formation of CO2. In addition, the presence of these honeycomb
materials inhibited the formation of C2H2 and
CH4. The lowest yield and selectivity of these two hydrocarbons
were obtained when using the Ni/γ-Al2O3 catalyst. It has been reported that C2H2 is
prone to be hydrogenated to form C2H4 and C2H6 in the presence of metal-supported catalysts
under plasma conditions.[55] This might be
the main reason for the decline in the yield and selectivity of C2H2. CH4 is mainly generated from the
recombination of H and CH3 (R3). In plasma-catalytic reforming
process, the CH4 decomposition reaction
() and CO disproportion reaction ( are considered to be the
primary pathways for carbon deposition.[18,29] The use of
honeycomb materials increased CO yield and selectivity, indicating
that the CO disproportion reaction was less important for carbon deposition
in this study. However, the low yield and selectivity of CH4 when using the supported Ni catalyst would contribute to the formation
of limited carbon on the used catalyst.Figure displays the time variations in the conversion
of naphthalene
and toluene under different conditions. The presence of the honeycomb
materials exhibited higher reactant conversions compared with the
plasma alone process. A significant decline in the reactant conversions
with reaction time was observed when using the blank substrate. This
might be resulted from the severe carbon deposition due to its lower SBET. In the reaction using plasma catalysis,
the Ni sample was activated with the increasing temperature in the
initial 20 min. In addition, the NiO species were reduced to Ni during
this stage, as evidenced by the XRD patterns. The reduced metal Ni
has been reported to show better activity than its metal oxide NiO
in the steam reforming reaction.[46] These
factors contributed to the enhancement in the reactant conversions
in the initial stage of the reaction process. In Figure , only a slight fluctuation
in the reactant conversions was observed when the supported Ni catalyst
was fully activated, which implies that the plasma-catalytic process
using GAD and the Ni catalyst with honeycomb support showed promising
stability.
Figure 7
Variations in the (a) yield and (b) selectivity of primary gas
products under different conditions.
Figure 8
Time variations
in the conversions of tar compounds in the different
processes.
Variations in the (a) yield and (b) selectivity of primary gas
products under different conditions.Time variations
in the conversions of tar compounds in the different
processes.
Characterization of the
Used Honeycomb Materials
The
used honeycomb materials running the plasma steam reforming process
for 60 min were characterized by TGA to estimate the carbon deposition
on their surface (Figure ). The used blank, γ-Al2O3 and
Ni/γ-Al2O3 exhibited a continuous weight
loss over two main steps with a total mass loss of 4.9, 2.7, and 2.3%,
respectively. The first weight loss step in the temperature range
between 25 and 150 °C represents the evaporation of adsorbed
H2O. The second weight loss between 150 and 800 °C
corresponds to the removal of the deposited carbon. Specifically,
the weight loss at ∼200 to 380 °C can be ascribed to the
oxidation of amorphous carbon, while that at temperatures higher than
500 °C can be due to the oxidation of graphitic and whisker carbon.[56] The formation of whisker and graphitic carbon
is the main contribution to the catalyst deactivation as they could
not be oxidized in the GAD reactor due to the low temperature in the
honeycomb materials (around 350 °C). The TGA curve of Ni/γ-Al2O3 showed the smallest amount of weight loss at
500–800 °C, indicating the outstanding capability to limit
the carbon formation on the honeycomb material with the addition of
metal elements. This was responsible for its superior performance
including tar conversion, yield and selectivity of the primary gaseous
products, and reforming efficiency.
Figure 9
TGA curves of the used honeycomb materials
after 60 min plasma
reaction.
TGA curves of the used honeycomb materials
after 60 min plasma
reaction.
Liquid Byproducts and Mechanisms
Analysis
To elucidate
the possible reaction pathways and underlying mechanism, liquid byproducts
from different processes under the same operation condition were analyzed
using GC-MS (Figure and Table ). The
distribution of liquid products in the three reaction systems was
quite different. Notably, the introduction of honeycomb materials
into GAD narrowed the distribution of the liquid byproducts. For example,
the type of liquid byproducts and their characteristic peak height
were significantly decreased when using the Ni/γ-Al2O3 catalyst. These phenomena suggest that combining GAD
with suitable catalysts could inhibit the accumulation of macromolecular
hydrocarbons and the partial polymerization of hydrocarbon intermediates,
as a variety of plasma species (e.g., electrons, OH, O, and/or N2*) were generated on the catalyst surface and participated
in heterogeneous surface reactions to improve the degradation and
oxidation of the tar compounds and their molecular fragments.[57] Measures to further reduce the formation of
byproducts should be taken from the perspectives of developing more
effective and stable catalysts for biomass gasification tar reforming
in plasma environments, as well as designing novel plasma-catalysis
configurations to enhance the synergy between plasma discharge and
catalyst.
Figure 10
Analysis of liquid byproducts using GC-MS.
Table 1
Summary of the Liquid Compounds Based
on Figure (Toluene
is Excluded)a
no
chemicals
GAD alone
GAD + blank
GAD + γ-Al2O3
GAD + Ni/γ-Al2O3
1
ethylbenzene,
C8H10
√√
√√
√√
√√
2
o-xylene, C8H10
√√
√
√
√
3
phenylethyne,
C8H6
√
√√
√
√
4
styrene, C8H8
√√
√√
√
√
5
1-phenyl-2-nitropropene, C9H9NO2
√
√
√
6
benzonitrile, C7H5N
√
√
√
7
benzene,1-propenyl, C9H10
√
√
√
8
benzene,1-ethynyl-4-methyl,
C9H8
√√
√√
√√
√
9
1H-Indene,2-methyl,
C10H10
√
√
10
naphthalene,1,2-dihydro, C10H10
√√
√
11
1,4-dihydronaphthalene, C10H10
√
√
√
12
naphthalene, C10H8
Δ
Δ
Δ
Δ
13
naphthalene,2-methyl, C11H10
√
√
14
benzocycloheptatriene,
C11H10
√
15
diphenyl ether, C12H12O
√
16
bibenzyl, C14H14
√
√√ and Δ represent
the major liquid byproducts and reactant, respectively.
Analysis of liquid byproducts using GC-MS.√√ and Δ represent
the major liquid byproducts and reactant, respectively.By reasoning and analyzing the experimental
and chromatogram results
as well as the catalyst characterization, the possible mechanism of
tar compound conversion is proposed in Figure . The conversion of tar compounds in the
hybrid plasma-catalytic system mainly includes three aspects: direct
plasma reaction, catalytic conversion, and the synergistic effect
between these two processes through the plasma-catalytic surface reaction.
As discussed in the previous works, a large number of highly energetic
electrons (1–10 eV) are generated in the GAD system, which
could react with N2 and H2O to form the reactive
species including the metastable states of N2*, O, and
OH radicals in the gas phases (R6–R9). These reactive species
then induce the degradation of toluene and naphthalene via the oxidation
and ring-opening process, and form H2O and CO eventually.[30,32,33,38,58]In the presence of the honeycomb
materials
(blank substrate and γ-Al2O3), the toluene
and naphthalene molecules could be adsorbed on their surface to increase
the probability of reacting with the plasma-generated excited species.
Various aromatic hydrocarbons such as phenylethyne, benzonitrile,
H-indene, 2-methyl, naphthalene, and 1,2-dihydro were then formed,
and some of them experienced aromatic ring opening to generate light
hydrocarbons and further converted into H2O, CO and CO2 as well as CH4 and C2H2,
as shown in Figure a. When the active element Ni was loaded on the γ-Al2O3 surface, the Ni2+ in the metal oxide NiO
was initially reduced to Ni0 by the energetic electrons
and generated O radicals. These O radicals then react with the reactants
adsorbed on the catalyst, resulting in the benzene ring opening and
creating favorable conditions for the further conversion of the molecular
fragments to H2O, CO, CO2, CH4, and
C2H2.[52] These molecules
finally desorbed from the catalyst surface into the gas phases (see Figure b). In the meantime,
the H2O molecules could also be adsorbed onto the active
sites of the catalyst and dissociated while releasing active oxygen,
which oxidized the catalyst from elemental Ni0 to Ni2+. The reduction and oxidation cycle of the Ni element was
continued during the plasma reforming via the facile inter-conversion
between Ni0 and Ni2+ state,[27] and maintained the stable performance of the catalyst during
the steam reforming of tar using plasma catalysis.
Figure 11
Possible reaction mechanism
of tar reforming over honeycomb materials
in the GAD reactor.
Possible reaction mechanism
of tar reforming over honeycomb materials
in the GAD reactor.
Performance Comparison
of Different Processes for Tar Conversion
Table presents
the performance comparison of different processes for biomass gasification
tar reforming. In thermal cracking systems, an extremely high temperature
(1000 °C) was required to achieve acceptable tar conversion,
while with aid of plasma discharge could significantly reduce the
reaction temperature without the losses in tar conversion.[59] Using the metal-supported catalysts lowered
the temperature (600 °C–700 °C) for thermal conversion
of tar and showed excellent performance.[60,61] Plasma systems can decompose tar even at room temperature and numerous
types of nonthermal plasma have shown the ability to achieve high
tar conversion including DBD, GAD, and microwave plasmas.[62−65] The hybrid plasma-catalytic systems demonstrated a higher potential
to completely convert tar with high energy efficiency. Obviously,
the combination of noble-metal (e.g., Rh) catalyst with plasma offered
enhanced performance over Ni-based catalysts and photocatalyst (e.g.,
TiO2).[64,66] In addition, using the honeycomb
structure catalysts as in this work could decrease the overall energy
consumption in the plasma process, providing a promising alternative
for tar elimination. However, the tar conversion is still low and
carbon deposition is detected on the used catalyst, which would negatively
influence the long-term running of the plasma-catalytic system. Further
investigations are still required to promote the production of syngas
and the reforming efficiency while keeping a high processing capacity
in the real biomass gasification conditions. The previous investigation
demonstrated that the nanosecond pulsed high-voltage power source
benefited the production of energetic electrons and other chemically
active species for a better performance of biomass tar conversion.[66] Using biomass char as the catalyst or support
for tar conversion has received increasing interest due to its unique
features of a large specific area and pore volume, high mineral content,
long-term thermal stability, abundant distribution of nanoscale active
clusters, and low operation cost.[67] Therefore,
approaches like developing power supply with adjustable parameters
and preparing the cost-effective catalysts suitable for the hybrid
plasma-catalytic systems are the directions worth working toward.
Table 2
Comparison of Tar Reforming Using
Different Processes
process
tar surrogate
carrier gas
tar
content (g/m3)
flow rate (m3/h)
conversion (%)
energy efficiency (g/kWh)
refs
thermal cracking (1000 °C)
C8H10
N2
1.6
0.240
100.0
(59)
plasma + thermal (800 °C)
100.0
20.5
fixed bed + Ni/char (600 °C)
C7H8
N2/H2O
218
0.03
83.9
(60)
fixed bed + bauxite/biochar (700 °C)
C8H10
producer gas
1.6
0.023
95.0
(61)
DBD
C7H8
H2
33
0.0024
97.0
1.5
(62)
rotating GAD
C7H8/C8H10/C6H5OH
N2/H2O
10.0
0.360
85.7
9.5
(65)
microwave + TiO2
C7H8
N2/Ar/H2O
43.0
0.036
98.0
1.7
(64)
DBD + Rh/LaCoO3/Al2O3
C6H6/C7H8/C10H8
producer gas
10.0
0.012
100.0
25.1
(66)
DBD + Ni/γ-Al2O3
C7H8
N2/H2O
180.0
0.009
96.0
25.0
(27)
rotating GAD + Ni/γ-Al2O3
C7H8/C8H10/C14H10
N2/H2O
12.0
0.720
89.0
19.1
(63)
rotating GAD + Ni/γ-Al2O3
C7H8
N2/H2O
20.0
0.360
93.5
20.4
(39)
GAD+ Ni/γ-Al2O3 (honeycomb structure)
C7H8/C8H10
N2/H2O
16.1
0.210
85.6
50.9
this work
Conclusions
Herein,
the plasma-enhanced catalytic steam reforming of model
tar compounds was performed in a GAD reactor combined with honeycomb
materials. The influence of different honeycomb materials on the reaction
performance was evaluated including the blank substrate as well as
that coated γ-Al2O3 and Ni/γ-Al2O3. These findings indicate that introducing the
honeycomb materials into the plasma environment enhanced the tar conversion
and the overall energy efficiency to different extents. The best reaction
performance was achieved using honeycomb material coated with Ni/γ-Al2O3, reflected by the high conversion of toluene
(86.3%) and naphthalene (75.5%), the yield of H2 (35.0%)
and CO (49.1%) and reforming efficiency (50.9 g/kWh). During the plasma-catalytic
reforming, the nickel oxide species on Ni/γ-Al2O3 with a large surface area were reduced to Ni0 and
distributed more uniformly on the support with the aid of GAD. This
increased the contact and interaction between the catalyst and plasma
reactive species, and generated plasma-catalysis synergy for the tar
conversion with high energy efficiency and excellent catalyst stability
for coke resistance. The combination of the honeycomb catalyst with
GAD has shown the potential to achieve high tar conversion and acceptable
energy consumption as well as attain a high yield of syngas in the
gaseous products. Further investigations can focus on developing power
supplies with adjustable parameters and preparing cost-effective catalysts
suitable for hybrid plasma-catalytic systems.
Authors: J Karuppiah; E Linga Reddy; P Manoj Kumar Reddy; B Ramaraju; R Karvembu; Ch Subrahmanyam Journal: J Hazard Mater Date: 2012-08-24 Impact factor: 10.588
Authors: Maria Ronda-Lloret; Yaolin Wang; Paula Oulego; Gadi Rothenberg; Xin Tu; N Raveendran Shiju Journal: ACS Sustain Chem Eng Date: 2020-11-17 Impact factor: 8.198