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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 en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 5
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Steam reforming of volatile fatty acids (VFAs) over supportedPt/Al2O3 catalysts
Chang Moon Jeong a, Gwon Woo Park a, Jin-dal-rae Choi a, Jong Won Kang a,Sung Min Kim a, Won-Ho Lee b, Seong Ihl Woo a, Ho Nam Chang a,*aDepartment of Chemical and Biomolecular Engineering, KAIST, 335 Gwahang-no, Yuseong-gu, Daejon 305-701, Republic of Koreab LG Chem. Ltd/Research Park, 104-1, Moonji-dong, Yuseong-gu, Daejon 305-741, Republic of Korea
a r t i c l e i n f o
Article history:
Received 12 January 2011
Received in revised form
17 March 2011
Accepted 20 March 2011
Available online 6 May 2011
Keywords:
Steam reforming
Volatile fatty acid
Biomass
Wastewater
Fermentation
* Corresponding author.E-mail address: [email protected] (H.N
0360-3199/$ e see front matter Copyright ªdoi:10.1016/j.ijhydene.2011.03.126
a b s t r a c t
Volatile fatty acids (VFAs), easily produced using acid fermentation of biomass, were used
to generate hydrogen via steam reforming. Three short-chain carboxylic acids (C2eC4) e
acetic, propionic and butyric acids e were used as model compounds in addition to VFAs
produced in a typical anaerobic batch reactor. Catalytic steam reforming of VFAs using
alumina-supported platinum catalysts was studied in a fixed-bed quartz reactor at various
temperatures between 300 and 600 �C. The influence of reaction conditions such as
temperature, oxygen to carbon ratio (O/C) and gas hourly space velocity (GHSV) was
investigated. VFAs were successfully converted to COx and hydrogen. A hydrogen yield of
up to 70% was achieved, based on typical stoichiometry at 600 �C and a GHSV of 25,000 h�1.
Temperature-programmed oxidation (TPO), X-ray diffraction (XRD) and pore size distri-
bution (PSD) were used to characterize coke deposition. Graphitic carbon on catalysts was
not identified by XRD, which implies that amorphous coke had formed in the small pores.
The catalysts could be reactivated by oxidation and reduction. A detrimental effect on
hydrogen yield was observed by adding a small amount of O2 to the VFA feed, due to the
high concentration of oxygen in the feed composition. Steam reforming of real VFAs (S/
C ¼ 9) in the acid fermentation of food waste was performed with different GHSVs at
a reaction temperature of 600 �C. Conversion of VFAs decreased significantly with
increasing GHSV, but the hydrogen selectivity was still above 60%. The conversion path-
ways of the VFAs to COx and hydrogen are most likely complex, particularly due to the
variety of the chemical compounds present in the real VFAs. The steam reforming of VFAs
was investigated over various noble metal (Ruthenium, Palladium, Rodium, Nickel) cata-
lysts supported on alumina, the specific activity based on the active surface area decreased
in the order of Ru > PdwRh > Pt > Ni.
Copyright ª 2011, Hydrogen Energy Publications, LLC. Published by Elsevier Ltd. All rights
reserved.
1. Introduction environmental pollution. Fuel cells using hydrogen have
Hydrogen is becoming a more attractive alternative energy
carrier due to the depletion of fossil fuels and the
. Chang).2011, Hydrogen Energy P
higher fuel efficiency than conventional gasoline and diesel
engines. They produce onlywater as a by-product without any
pollutant emission. However, hydrogen is currently produced
ublications, LLC. Published by Elsevier Ltd. All rights reserved.
i n t e rn a t i o n a l j o u r n a l o f h y d r o g e n en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 57506
from nonrenewable sources, such as natural gas and petro-
leum [1e3], which are accompanied by high CO2 emissions.
On the other hand, biomass can be used to produce hydrogen
without a net change of CO2 in the atmosphere and will play
an important role as a renewable and sustainable hydrogen
source in the future. Volatile fatty acids (VFAs) derived
anaerobically from organic biomass can be very useful in
serving as major platforms for bio-fuels and chemicals in post
fossil fuel era [4,5].
Various chemical and biological technologies are available
to generate hydrogen from biomass. For the past few decades,
renewable biomass has been considered as a potential feed-
stock for the gasification process to produce syngas (amixture
of hydrogen and carbon monoxide). This process can be per-
formed with or without a catalyst [6,7]. However, typical
gasification processes have the disadvantage of low thermal
efficiency (30e50%) due to large amounts of water in the
biomass. Thus, gasification requires a very large reactor [8].
Another hydrogen production technology is the fast pyrolysis
of biomass with catalytic steam reforming of the resulting
pyrolytic oil (bio-oil), a complex mixture of various aliphatic/
aromatic oxygenates [9]. Attempts to produce hydrogen from
bio-oil using commercial steam reforming catalysts have been
severely interrupted by rapid catalyst deactivation caused by
coke/oligomer deposition on the catalysts [10]. A more real-
istic approach has been proposed using individual compo-
nents present in bio-oil such as acetic acid, one of the model
oxygenated components of bio-oil (up to 32 wt%). Platinum
has been shown to be essential for hydrogen formation, and
that the support is needed to extend catalyst life [11]. Bio-
ethanol, a renewable material easily obtained from biomass,
has also been proposed as an intermediate in the hydrogen
production [12e14]. Recently, aqueous phase reforming (APR)
of sugars [15] or bio-ethanol [16] in generating hydrogen has
been proposed. APR is under development to process
oxygenated hydrocarbons or carbohydrates to produce
hydrogen. APR reactors are often operated at pressures up to
2e30 MPa and temperatures ranging from 220 to 270 �C. Most
research to-date has been focused on the use of supported
GroupVIIImetals as the activemetal, and sugars (e.g., glucose)
and polyols (e.g., methanol, ethylene glycol, glycerol and
sorbitol) as the substrates. However, until now, economically
feasible biomass utilization processes for hydrogen produc-
tion have not been well-developed.
In this paper, we propose an alternative process for the
production of hydrogen from biomass that involves acid
fermentation of biomass to generate volatile fatty acids (VFAs)
followed by reforming. Anaerobic digestion or acid fermen-
tation is a process in which microorganisms break down
biodegradable material in the absence of oxygen [17]. The
process is widely used to treat wastewater sludge and organic
wastes because it provides a significant reduction in the
volume andmass of the input waste. After hydrolysis of waste
by the extra-cellular enzymes of microorganisms, the organic
wastes, including carbohydrates, lipids and proteins, are
converted into various short-chain fatty acids, such as acetic
acid (HAc), propionic acid (HPr) and butyric acid (HBu). These
VFAs are converted anaerobically to carbon dioxide and
methane gas, i.e., biogas, a renewable energy source suitable
for energy production helping to replace fossil fuels. However,
methane formation is a very slow reaction due to the slow
growth of methane-forming microorganisms. In addition,
methane produced in such a manner contains many toxins
such as hydrogen sulfide. Furthermore, the greenhouse effect
caused by methane is much more severe than that caused by
carbon dioxide. For this reason, we propose to recover the
energy from VFAs before they are converted to methane,
which can be achieved by catalytic steam reforming of VFAs.
The steam reforming of VFA can be simplified to the steam
reforming of an oxygenated organic compound (CnHmOk) by
the following reaction:
CnHmOk þ ðn� kÞH2O/nCOþ ðnþm=2� kÞH2 (1)
The above reaction is followed by the wateregas shift
reaction:
nCOþ nH2O4nCO2 þ nH2 (2)
Therefore, the overall process can be represented as follows:
CnHmOk þ ð2n� kÞH2O/nCO2 þ ð2nþm=2� kÞH2 (3)
The process performance was measured by the hydrogen
yield calculated as the percentage of the stoichiometric
potential, assuming complete conversion of carbon to CO2,
according to Reaction (3). Thus, the potential yield of hydrogen
gas from an oxygenated feedstock is (2 þm/2n� k/n) moles of
H2 permole of carbon in the feed. In reality, the hydrogen yield
will always be lower than the stoichiometric potential because
the wateregas shift (WGS) reaction is reversible, resulting in
the presence of some carbon monoxide and methane in the
product gas. In addition, thermal cracking that occurs in
parallel to reforming produces carbonaceous deposits, which
are especially significant for thermally unstable compounds.
In this study, we consider the steam reforming of VFAs
obtained from acid fermentation of food waste on alumina-
supported platinum catalysts. The steam reforming of a few
different short-chain carboxylic acids typically found in VFAs
(e.g., acetic, propionic and butyric acid) was studied. The
influence of reaction conditions such as temperature, steam
to carbon ratio (S/C), oxygen to carbon ratio (O/C) and gas
hourly space velocity (GHSV) was investigated. Temperature-
programmed oxidation (TPO), X-ray diffraction (XRD) and pore
size distribution (PSD) were used to characterize the deacti-
vation of the catalysts. In addition, the steam reforming of
VFAs was investigated over various noble metal catalysts
supported by alumina.
2. Materials and methods
2.1. Catalyst preparation
Commercial g-alumina (Sigma Co. Ltd.) in powder form
was used as a support after 1 h calcinations at 600 �C. Thestudied Pt/Al2O3 catalysts were prepared by incipient
wetness impregnation with aqueous solutions of metallic
precursor salts (Pt(NH3)2(NO2)2) (Alfar Aesar) on a Al2O3
support. Metal loading was 5 wt %. The impregnated
catalyst was then dried at 120 �C and all catalysts were
activated by reduction under 5 mol % H2 at 600 �C for 2 h
before each run.
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 en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 5 7507
2.2. Catalyst characterization
The specific surface areas of the support and the supported
catalysts were measured by the Brunauer-Emmett-Teller
(BET) technique using the Tristar 3000 surface analyzer
(Micromeritics, USA), employing N2 physisorption at the
temperature of liquid N2. Prior to each measurement, the
sample was dried at 120 �C under a helium flow passing
through the sample cell.
The metal dispersion of fresh catalyst was determined by
hydrogen chemisorption using the ASAP 2000 volumetric
adsorption analyzer (Micromeritics, USA). Prior to each
measurement, the catalyst sample (ca. 200mg) was pretreated
by: (a) dynamic vacuum at 50 �C for 1 h, (b) reduction in
flowing H2 at 600 �C for 1 h, (c) evacuation for 1 h at 400 �C, and(d) cooling to the chemisorption temperature of 35 �C.Hydrogen uptake at the monolayer of the platinum particles
was obtained by extrapolation of the linear portion of the
adsorption isotherm to zero pressure. The exposed surface
area was calculated by assuming a H: Pt stoichiometry of 1:1
[18]. The actual metal loadings of the reduced catalysts were
measured by inductively coupled plasma mass spectroscopy
using HP 4500 (Hewlett Packard, USA).
XRD patterns of the supports and the supported catalysts
were obtained using a Multi-Purpose Attachment X-ray
Diffractometer (D/MAX 2500, Japan) equipped with Cu Ka
radiation (lK ¼ 0.1542 nm). Crystalline phases were identified
by comparison with PDF standards (powder diffraction files)
from the International Center for Diffraction Data (ICDD). The
average crystallite size (D) was determined using the Scherrer
equation as follows:
D ¼ Klk=bcos q (4)
where lK is the wavelength of the X-rays used, q is Bragg angle
of diffraction peak, b is the full width at half maximum of
diffraction peak and K is the Scherrer Constant (here, K ¼ 0.9).
2.3. Experimental procedure and apparatus
Fig. 1-(a) shows a schematic representation of the experi-
mental apparatus used for the reforming reaction with VFAs.
The quartz reactor (20 mm (O.D.), 18 mm (I.D.), 400 mm
(height)) was located inside a tubular electric furnace and the
temperature inside the catalyst bed was measured with
a thermocouple. Helium was used as an inert carrier. The
input flow of helium to the pre-heater was controlled by
a mass flow controller. The pre-heater temperature was
maintained at 170 �C for all experiments. VFA aqueous solu-
tion was fed by a High Performance Liquid Chromatography
(HPLC) pump and vaporized at 170 �C. Oxygen was used in
some experiments to enhance the reforming by supplying
combustion heat and also suppressing the coke deposition. In
the experiments with oxygen feed, co-feeding both VFA/
Steam and oxygen with one inlet resulted in the oxidation of
reactants in the upper part of the quartz reactor, between
furnace and pre-heater (marked in Fig. 1-b). We made a new
type reactor with independent oxygen feeing line to eliminate
this phenomenon (Fig 1-c) and measured actual temperature
in the catalysts bed. The reactor effluent was passed through
a cold trap to remove condensable product. The composition
of the gases after the trap was analyzed by an on-line gas
chromatograph (HP 6890) equipped with TCD and FID to
determine the concentrations of H2, CO2, O2, CH4 and CO. The
hydrogen yieldwas defined as the ratio of the concentration of
H2 in the actual outlet gas to the theoretical amount of
hydrogen that could be obtained when complete reforming to
generate CO2 and H2 occurred (Eq. (3)). The selectivity was
defined (for each compound) as the ratio of the moles of each
H2, CO2, CH4 and CO in the actual outlet gas to the total moles
of outlet gases, with the exception of the carrier gas. The
concentration of each VFA (HAc, HPr, HBu, etc.) wasmeasured
by HPLC (Hitachi L-3300 RI detector, Japan) equipped with an
ion exchange column (Aminex HPX-87H, Hercules, USA) using
5 mM H2SO4 as the mobile phase. All samples were filtered
through a 0.22-micron (pore diameter) membrane filter prior
to measurement.
3. Results and discussion
3.1. Catalyst characterization
The physical and chemical characteristics of fresh supports
and catalysts are shown in Table 1. The BET area of the fresh
g-Al2O3 supports before calcinations was 327.74 m2/g, but
during the 1 h calcinations at 600 �C, the BET surface area
decreased due to the sintering effect. The specific surface
areas of the g-Al2O3 support and the Pt/Al2O3 catalysts were
166.01 and 142.98 m2/g, respectively, suggesting that the
loading of Pt decreased the surface area of the alumina
support only slightly. Metal dispersion of Pt/Al2O3 catalysts by
hydrogen chemisorptions is also reported in Table 1.
In general, catalysts performance based on their configu-
ration (i.e. pellet form) is limited by mass-heat-transport
phenomena especially at a high flow rate, to increase the total
H2 production, volume and weight of reactors must be
dramatically increased together with the catalyst cost [19].
However, we can assume that the large surface area in
a powder form and small-scale quartz reactors leads to good
heat and mass transfer property.
The XRD patterns of fresh supports and catalysts are
shown in Fig. 2. As expected, the most visible features in
platinum,which are equivalent to themain peaks (PDF No. 00-
004-0802) of platinum nano-particles, occurred at 39.75�(111),46.20�(200), 67.42�(220), 81.22�(311) and 85.60�(222).
3.2. Effects of reaction temperature
The steam reforming of each acid was performed in
a temperature range of 300e650 �C and the effects of
temperature on H2 yield and acid conversion are shown in
Fig. 3. To avoid catalyst deactivation caused by carbon depo-
sition, the reactions were performed for a short duration (1 h)
and fresh catalyst was used for every temperature point.
GHSV was controlled at 25,000 h�1 and the S/C of 9 was used
for all experiments in this section. The homogeneous (non-
catalyst) reaction over the temperature was studied, but the
VFA conversion was less than 1% and any H2 and CO2 was not
measured in product line. The reaction in the presence of the
Fig. 1 e (a) Schematic diagram of the experimental apparatus, (b) general quartz reactor, (c) new type quartz reactor with
oxygen feeding line and thermocouple.
Table 1 e Characteristics of supports and catalysts.
Characteristics Al2O3a Al2O3
b 5 wt% Pt/Al2O3c
Total surface area
(B.E.T.) (m2/g)
327.74 166.01 142.98
Metal dispersion (%) e e 16.35
Metal surface area
(m2/g metal)
e e 40.38
Metal loading (%)d e e 5.13
a Fresh supports.
b Support after 1 h calcinations at 600 �C.c after a 1 h H2 reduction at 600 �C.d ICP/MS measurements.
i n t e rn a t i o n a l j o u r n a l o f h y d r o g e n en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 57508
alumina supports was also examined (data not shown). The
major products of this reaction were CO2 and CH4, with only
small amounts of CO and H2. The conversion of VFAs to CH4
and CO2wasmost likely caused by the thermal decomposition
of VFAs. The conversion of VFAs was less than 5% and
significant carbon deposits were found on the surface of the
supports surface after the reaction, which might be caused by
following reaction [20]:
CnH2nO2/CO2 þ nH2 þ ðn� 1ÞCads (5)
However, the gaseous product composition changed
significantly in the presence of the alumina-supported plat-
inum catalyst with a large increase in hydrogen yield and
Fig. 2 e XRD patterns of Al2O3 supports (a) before
calcinations, (b) after calcinations at 600 �C and (c) Pt/Al2O3
catalysts.
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 en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 5 7509
reactant conversion. This phenomenon implies that the
presence of platinum is essential for steam reforming. At
300 �C, the conversion of HAc, HPr and HBu was just 29.4%,
11.2% and 2.7%, respectively, but it reached above 98% after
a temperature increase to 600 �C. At the same time, CO
selectivity decreased from 23.3% to nearly 0%; in contrast, the
selectivity of H2 formation increased dramatically with these
Fig. 3 e Steam reforming of each acid andwater mixture on the P
acetic acid; ,, propionic acid; A, butyric acid), (c)w(e) product g
>, CH4; 6,CO). Experimental conditions: Pt/Al2O3 catalyst [ 20
conditions. The large amount of CO generation at 300 �C may
have been caused by the fact that the steam reforming
(Eq.(1)) and the wateregas shift (Eq.(2)) reactions could not
occurred substantially due to reactant acid and steam
adsorbed on the surface of the catalyst blocking sufficient
catalyst activation because of the low reaction temperature.
Above 400 �C, the steam reforming and WGS reactions pro-
ceeded normally. As a result, both reactant conversions and
selectivity in producing H2 increased significantly. When the
temperature increased consecutively to 600 �C, the catalyst
exhibited the best performance and reactant acids were
converted completely. Also, the CO2/H2 ratio reached near
theoretical values, which indicates complete steam reform-
ing, while the selectivity in producing the by-product CH4
was about 0.2% and only a negligible amount of CO was
detected. However, when the temperature continuously
increased to higher ranges, such as above 650 �C, the selec-
tivity in producing CH4 and CO became remarkable. There
were trace and negligible amounts of acetone, C2 hydro-
carbon (i.e. C2H4, C2H6) detected from 300 to 450 �C, hence, we
did not express it in the figures.
The CO2/H2 ratio was calculated to estimate the carbona-
ceous conversion of VFAs at 600 �C. The carbonaceous
conversion of VFAs was 92.4, 91.3 and 86.9% from HAc to HBu,
respectively. This result shows that the longer chain acids
favor conversion via thermal decomposition, which can
produce CH4 or acetone and so on. Interestingly, a trace
t/Al2O3 catalysts. (a) Acid conversion, (b) hydrogen yield (C,
as selectivity from acetic acid to butyric acid (C, H2; -, CO2;
0 mg, GHSV [ 25,000 hL1, S/C [ 9.
Fig. 4 e Steam reforming of VFAmixture on the Pt/Al2O3
catalyst. Experimental conditions: Pt/Al2O3
catalyst[200mg,GHSV[25,000hL1, temperature[600 �C,S/C[ 9. (B, VFA conversion;,, H2 yield;C, H2 selectivity;-,
CO2 selectivity;:, CO selectivity;>, CH4 selectivity).
i n t e rn a t i o n a l j o u r n a l o f h y d r o g e n en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 57510
amount of higher carbon chain carboxylic acids, such as
valeric (C5) and caproic (C6) acid were observed in butyric acid
reforming.
3.3. Effect of steam to carbon ratio (S/C)
The influences of S/C on the reactions were studied at 600 �C,the optimum temperature used in the previous section. The S/
C was varied from 3 to 9, controlling constant GHSV of
25,000 h�1. Results on the H2 yield and reactant conversion are
shown in Table 2. The H2 yield increases with increasing S/C.
S/C also had a significant effect on the conversion of reactants,
which dropped substantially from 100% to 65.4% with
a decrease in S/C decrease from 9 to 3 for the case of HAc.With
regard to selectivity in producing the products, the S/C also
had remarkable effects: significant amounts of CH4 and CO
were observed at a low S/C of 3. The generation of CH4 and CO
can greatly affect the selectivity in producing H2. The
production of 1 mol CH4 will result in a 4 mol loss of H2.
Similarly, the production of 1mol COwill result in a 1mol loss
of H2. As a result, when the S/C decreased from 9 to 3 in the
case of VFAs reforming, the selectivity in producing H2
decreased remarkably from 70.2% to 59.9%.
3.4. Steam reforming of acid mixture
The steam reforming reactionwas performed for 52 h at 600 �Cto study the stability of the Pt/Al2O3 catalyst. The reaction was
conducted under the steady-state condition with a GHSV of
25,000 h�1 and a feed mixture consisting of VFAs (S/C ¼ 9)
(molar ratio of HAc:HPr:HBu ¼ 6:1:3), which is the typical
molar ratio of the acidmixture in anaerobic digestion [21]. The
results are given in Fig. 4. A gradual deactivation of the cata-
lyst was observed, corresponding to a decrease of 40% in VFAs
conversion after 52 h. However, the selectivity of carbon-
containing compounds did not change during the experiment.
In the initial stage of 30 h, the conversion of VFAs was still
around 80%, owing to the slow deactivation of the catalyst.
After 30 h, the conversion of VFAs decreased significantly and
a small amount of acetone ranging from 0.1 to 0.2 wt% was
Table 2 e Effect of steam to carbon ratio.
Feedstocks
S/C Conversion(%)
H2 yield(%)
Recoverya
(%)
HAc 3 65.4 57.2 101.7
6 87.8 65.8 98.2
9 100.0 68.5 99.5
HPr 3 53.6 55.4 99.4
6 79.5 64.7 98.7
9 99.7 71.1 101.3
HBu 3 49.1 53.3 99.3
6 74.7 64.1 100.1
9 99.4 73.4 101.0
VFAs 3 87.2 59.9 99.1
6 93.0 66.6 98.4
9 99.1 70.2 100.4
a Recovery was calculated from gas and liquid yield in the product
line.
also detected with increasing time. Thus, it is likely that
catalyst deactivation by carbon deposition or catalyst aging
would affect the performance of steam reforming, which will
be discussed in the following section.
3.5. Characterization of carbon deposition andreactivation of catalysts
Carbon deposition is one of the major problems in catalytic
reforming reactions because it leads to rapid deactivation of
the catalysts due to poisoning of the active sites and/or pore
blockage [22e24]. To study the nature of the carbon deposits
formed, TPO experiments were performed after running the
steam reforming reaction under the steady-state condition
described in the previous section. After cooling the catalyst to
room temperature, the catalyst was exposed to a mixture of
2mol % of O2 in heliumwith a flow rate of 200mL/min, and the
temperature was increased at a linear rate of 5 �C/min up to
700 �C. During the TPO experiment, carbon oxides (CO, CO2)
were detected with the CO2 analyzer and gas chromatography
(GC). In the TPO and GC results, either no CO was observed or
negligible amounts were observed; however, two peaks of CO2
were observed at around 428 and 534 �C. These peaks indicate
that two distinct carbon species exist on the catalyst surface
(Fig. 5). The amount of coke deposited was also estimated by
integration of the CO2 curves. The percentage of carbon
deposited at the lower temperature peak at 428 �C was 4.3% (g
coke/g carbon in the feed), and the corresponding percentage
of the higher temperature peak at 534 �C was 2.7% (g coke/g
carbon in the feed). Generally, the lower temperature peak is
thought to be due to coke deposited on the metal surface,
while the higher temperature peakdthemost significant peak
and the least reactivedis attributed to coke deposited on the
support [25]. Similar results have been reported, but it has
been suggested that the first peak around 440 �C is attributed
to the coke deposited on the metalesupport interface [26].
Fig. 5 e Temperature-programmed oxidation (TPO) profiles
of the Pt/A2O3 catalysts after steam reforming of VFAs. Fig. 6 e XRD patterns of (a) the fresh catalysts, (b) after the
first reforming reaction, (c) after oxidation and reduction at
600 �C and (d) the second reforming reaction.
Fig. 7 e Pore size distribution of the Pt/Al2O3 catalysts
using different conditions. (B, Fresh catalysts; C, After
first reforming, 6, after oxidation and reduction; :, after
second reforming).
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 en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 5 7511
Martin et al. suggested that coke at the metalesupport inter-
face has intermediate reactivity and that, this reactivity
presumably accounts for the continuity of the TPO profiles at
temperatures between those required to oxidize coke on the
metal and those required oxidize coke on the support [27]. In
hydrocarbon reforming, three different types of coke have
been reported to form on the supported metal catalysts:
polymeric, filamentous, and graphitic cokes [28]. Polymeric
coke originates from the gas-phase decomposition of hydro-
carbons, whereas formation of the filamentous and graphitic
cokes requires the participation of metallic sites on the cata-
lyst. Coke can also be characterized based on its reactivity.
Soft coke can be gasified by treatment in hydrogen using
relatively mild conditions and does not accumulate on the
active sites. Soft coke is thought to consist of secondary
reaction products or intermediates. Hard coke is typically
graphitic, unreactive with hydrogen and also blocks active
sites. Although these gross and overall coke properties are
reasonably simple to measure, determining the exact chem-
ical and physical nature of the coke is difficult [25,29].
XRD analysis and N2-adsorption measurements were also
conducted to characterize structural change and carbon
deposition on the catalysts during reaction and after regen-
eration via subsequent oxidation (10 mL/min, 1 mol % O2 for
half hour at 500 �C) and reduction (10 mL/min, 1 mol % H2 for
half hour at 600 �C) treatments. The XRD results are shown in
Fig. 6. A significant difference was not observed around
2q ¼ 26� when comparing the spectra before and after the
reaction, indicative of graphitic carbon (PDF No. 12-0212 and
26-1077). This observation confirmed that no significant
amount of carbon was deposited on the support and metal
surface, which was consistent with TPO experiment. Alter-
natively, only amorphous carbon could be deposited, which
can be fully oxidized for reactivation [30]. As summarized in
Fig. 7 and Table 3, BET area, pore volume and average pore size
were significantly decreased after the first and second reac-
tion, indicating the formation of cokes which might cause
blockage of the active site. Average crystallite size of platinum
determined from XRD line width did not significantly change
during the reaction and regeneration processes, indicating
that the present reaction and regeneration conditions do not
change the metal dispersion. The catalyst activity could be
recovered by greater than 90% based on hydrogen yield using
aforementioned regeneration condition. However, relative
catalyst activity based on hydrogen yield andmetal dispersion
determined by H2 chemisorptions were significantly reduced
to 5% and 0.1%, respectively, by oxidation over 650 �C. Thisphenomenon is probably due to the platinum crystallite size
growth by sintering. It has been reported that calcinations
treatment in the air results in an increase of platinum particle
size, which is larger than particles treated under either inert or
H2 atmospheres [31]. Fig. 8 shows the morphology of catalysts
(a) before and (b) after the reaction. They can be hardly iden-
tified at the nano-scale because the catalysts used in this
study were micro-structured. However, scanning electron
Table 3 e Porosity and crystallite size of Pt/Al2O3 catalysts using different conditions.
Conditions BET surface area(m2/g)
Average Pt crystallite size(nm)a
Pore volume(cm3/g)b
Pore area(m2/g)b
Mean pore diameter(nm)c
Fresh after reduction 142.98 12.8 0.396 205.58 10.6
After first reforming 84.15 13.0 0.219 112.72 7.8
After regeneration 115.60 14.6 0.405 156.54 10.5
After second reforming 96.25 13.9 0.224 125.33 7.2
a Average Pt crystallite size was calculated from the XRD results shown in Fig. 6.
b Pore volume and area (smaller than 300 nm) was measured by the Barrett-Joyner-Halenda (BJH) method.
c The mean pore diameter was calculated assuming cylindrical pore geometry.
i n t e rn a t i o n a l j o u r n a l o f h y d r o g e n en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 57512
microscopy (SEM) images show that the catalysts were
aggregated by coke formation after reaction.
3.6. Effect of oxygen to carbon ratio (O/C)
Oxygen used in the auto-thermal steam reforming or partial
oxidation reaction for thermodynamic advantage also
suppresses carbon deposition on the catalyst surface. The
steam reforming of VFAs is highly endothermic (DH¼þ357 kJ/
mol of VFAs at 25 �C). There are two ways of supplying heat to
the reacting system: (i) externally, by burning fuels and
transporting heat into the reaction mixture, or (ii) internally,
by co-feeding oxygen or air and burning a portion of the VFAs.
In the latter case, 1.2 mol of O/mol of C in feed VFAs are
required to achieve thermal neutrality, based on the following
stoichiometry:
C2H4O2 þ 0:17C3H6O2 þ 0:5C4H8O2 þ 1:04O2
þ 3:58H2O/4:5CO2 þ 8:08H2 (6)
To reduce carbon deposition and supply heat via the
internal combustion of VFAs, various amounts of oxygenwere
added (so-called auto-thermal conditions). Table 4 shows the
effect of the addition of various concentrations of oxygen on
the conversion to COx and the hydrogen yields at 600 �C.
The hydrogen yield gradually decreased with increasing
concentration of O2 in the feed. The hydrogen yield dropped
from 63% to 29% at an O/C ¼ 2.06. However, severe catalyst
deactivation as well as decrease of the hydrogen yield was
observedwhen oxygen feedwas excessive (O/C> 2.06) and the
hydrogen yield was decreased less than 1% after 1 h, probably
owing to the sintering effect by remaining air and increased
Fig. 8 e SEM images of (a) the fresh catalysts and (
temperature in the catalysts bed, as mentioned previous
section.
TPO experiments were also conducted with different O/C
ratios to estimate carbon deposition. Between O/C ¼ 0.74 and
1.53, the carbon deposition percent, defined as mass of coke
per mass of carbon in the feed, decreased gradually. The
carbon deposition percent was drastically reduced at an O/C
of 2.06. Furthermore, the visual observation of the reactor
and the catalyst color clearly revealed that the carbon
deposition was significantly reduced when oxygen was
added. In the steam reforming of ethanol, the addition of
oxygen already proved beneficial for the conversion to COx
and no significant reduction of the hydrogen yield was
reported [32]. Otherwise, in steam reforming of acetic acid
with fluidized bed, an excess of oxygen (8%) can lead to
a lower reforming activity decreasing the H2 and CO2 yields
and increasing the CO and CH4 yield. On the other hand, 4%
oxygen resulted in almost no penalty in hydrogen yield [33].
In this study, a detrimental effect of oxygen was observed in
the hydrogen yield due to the VFAs containing more oxygen
than ethanol.
3.7. Influence of GHSV
Space velocity (or GHSV) is one of the key operating parameters
that affects production rates. Generally, an increase in space
velocitywill result in lowerconversion.SteamreformingofVFAs
(S/C ¼ 9) produced from acid fermentation of food waste was
performed with different GHSVs at 600 �C (Fig. 9). Typical VFAs
produced frombiomassare3e4wt%and largeamountsofwater
must be removed to save the input energy in steam reforming.
There are many kinds of recovery methods to concentrate
b) used catalysts after the reforming reaction.
Table 4 e Influence of oxygen to carbon ratio (O/C).
Temperaturea O/C ratio Conversion (%) H2 yieldb H2 yield (%) Cokec (%) Selectivity (%)
H2 CO CH4 CO2
595 0.74 82.7 3.84 62.9 0.90 62.1 1.5 0.0 36.4
595 1.00 78.5 3.25 53.2 0.86 54.4 1.5 0.0 43.1
596 1.27 85.5 3.11 50.9 0.82 49.8 1.4 0.9 47.9
597 1.53 92.3 2.98 48.8 0.80 51.4 1.4 0.8 46.3
612 2.06 96.3 1.77 29.0 0.33 33.5 3.7 0.8 62.5
a Temperature in the catalysts bed (Fig. 1-C).
b H2 mol/VFA mol.
c g coke/g carbon in the feed.
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 en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 5 7513
organic acids. We have used membrane-based liquid/liquid
extraction with Alamine 336/octanol as solvent [34].
Conversion of VFAs significantly decreasedwith increasing
GHSV. However, hydrogen selectivity did not change signifi-
cantly. After long-term operation of 50 h, the catalyst activity
for hydrogen production decreased slightly, probably due to
carbon deposition or catalyst aging. The details of the
conversion pathway of the VFAs to COx and hydrogen are
most likely complex, in particular due to the variety of the
chemical compounds present in the real VFAs. For example,
VFAsmay contain sulfur compounds, such as sulfate ions and
sulfur-containing amino acids (cysteine and methionine)
depending on the feed source, which could cause catalyst
poisoning. These sulfur compounds must be removed by
separation techniques before the reaction or research for
sulfur-tolerant catalysts is required [35].
3.8. Relative activity for various noble metal catalysts
The steam reforming of VFAs was investigated over various
noble metal catalysts supported on alumina with a VFA
Fig. 9 e Influence of GHSV with real VFAs. Experimental
conditions: Pt/Al2O3 catalyst [ 200 mg,
GHSV [ 25,000 hL1, temperature [ 600 �C, S/C [ 9. (B,
VFAs conversion; ,, H2 yield; C, H2 selectivity; -, CO2
selectivity; :, CO selectivity; >,CH4 selectivity).
concentration of 13.7 wt% (S/C ¼ 9) and a GHSV of 25,000 h�1
at 600 �C. Palladium (Pd), rhodium (Rh), ruthenium (Ru) sup-
ported on alumina were supplied by Johnson Matthey (UK).
Nickel catalysts were prepared by the incipient wetness
method using nickel nitrate hexahydrate as the metal
precursor. All metal loading contents were 5 wt%. The results
are given in Table 5. As shown in fifth column, hydrogen
production rate per gram catalyst did not show great differ-
ences due to relatively short reaction time (1 h) and low
molecular weight of nickel. However, it was found that the
specific activity based on the active surface area (as calcu-
lated by the rate of H2 production and metal dispersion)
decreases in the following order for alumina-supported
metals:
Ru > PdwRh > Pt > Ni
Studies have identified copper-based catalysts as effective
materials to produce hydrogen by the steam reforming of
methanol at temperature near 300 �C [36]. However, copper-
based catalysts are not effective for steam reforming of
heavier hydrocarbons or oxygenated compounds, since they
show low activity for cleavage of CeC bonds [37]. Therefore, it
is more likely that an effective catalyst for oxygenated
compound reforming would be based on Group VIII metals,
which generally show higher activities for breaking CeC
bonds. The catalytic activities of different metals for CeC
bond breaking during ethane hydrogenolysis have been
studied by Sinfelt [37]. It can be seen that Pt shows reason-
able CeC bond breaking activity, although not as high as
metals such as Ru, Ni and Rh, which show highest activities
for CeC bond breaking in vapor-phase ethane hydro-
genolysis. An effective catalyst for reforming of VFAs must
not only be active for cleavage of the CeC bond, but it must
also be active for the wateregas shift reaction to remove CO
from the metal surface. In this respect, Grenoble et al. have
reported the relative wateregas shift activities for different
metals supported on alumina [38]. It can be seen that Cu
exhibits the highest wateregas shift rates among all the
metals (but shows no activity for CeC bond breaking) and Pt,
Ru and Ni also show appreciable wateregas shift activity.
Finally, to obtain a high selectivity for hydrogen production,
the catalyst must not facilitate undesired side reactions, such
as methanation of CO and FischereTropsch synthesis. It can
be seen that Ru, Ni and Rh exhibit the highest rates of
methanation, whereas Pt and Pd show lower catalytic activ-
ities for the methanation reaction [16]. Thus, on comparing
Table 5 e Characteristics and activity for steam reforming of various catalysts.
Catalyst BET surface area(m2/g)
Metal dispersion(%)
Metal surface area(m2/gmetal)
Rate (H2)(mol/h$gcat)
TOF(H2)a (s�1)
Pt/Al2O3 142.98 16.35 40.38 5.79 1.92
Pd/Al2O3 144.38 5.73 25.55 5.43 2.80
Rh/Al2O3 158.27 5.41 24.25 5.09 2.64
Ru/Al2O3 149.38 4.56 21.76 6.14 3.77
Ni/Al2O3 152.97 11.31 70.11 5.77 0.86
a TOF(H2) ¼ moles of hydrogen produced per moles of surface metal per second.
i n t e rn a t i o n a l j o u r n a l o f h y d r o g e n en e r g y 3 6 ( 2 0 1 1 ) 7 5 0 5e7 5 1 57514
the metals based on all the three reactions, it can be inferred
that Pt and Pd should show suitable catalytic activity and
selectivity for reforming of VFAs, which requires reasonably
high activity for CeC bond breaking and wateregas shift
reactions, and low activity for methanation. The rate of
a particular reaction can be compared for the different
metals, however, for specific metal, the absolute rates of the
three different reactions cannot be compared relative to each
other. In case of VFAs steam reforming according to on our
study, Ru exhibits the highest TOF among all the metals,
suggesting that activity for CeC bond cleavage and water-
egas shift reaction is more important feature rather than
methanation and thermal decomposition.
4. Conclusions
VFAs as representative model compounds of biomass were
reformed effectively in a fixed-bed reactor in the presence of
alumina-supported platinum catalysts. A hydrogen yield above
60% was maintained over 10 h using a 5 wt% Pt/Al2O3 catalyst
and operating at a steam to carbon ratio of 13.7. Catalysts were
deactivated by amorphous coke formed in their small pores.
However, the catalytic activity was recovered by oxidation
followed by reduction. The use of auto-thermal conditions (i.e.,
addition ofmolecular oxygen to the feed) reduced the extent of
carbon formation but also led to a significant loss in hydrogen
yield. Nevertheless, the continuous reforming of VFAs is
concluded to be feasible using these catalysts. Additionally,
catalytic activity studies based on TOF were conducted for VFA
steam reforming. Finally, effective catalyst for the production
of H2 fromVFA steam reforming should be active for CeC bond
cleavage and the wateregas shift reaction.
However, a metal loading of 5 wt% is relatively high;
therefore, further research in seeking inexpensive and active
catalysts is needed. By combining a proper reactor designwith
catalytic materials that minimize the catalytically produced
coke, VFAs have potential to become an important hydrogen
production method with significant environmental benefits.
Acknowledgement
This study was supported by Grant No. 2007-07001-0094-
0 from the Korea Institute of Environmental Science and
Technology and Grant No. M10309020000-03B5002-00000 from
the Korea Ministry of Education, Science and Technology. The
authors wish to thank Professor M.K. Choi of KAIST for his
thorough and helpful comments on the chemical aspects of
the reforming catalysts.
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