Yingying Huang1, Shiming Qiu1, Jianben Xu1, Huan Lian1. 1. School of Chemistry and Biological Engineering, Guangxi Normal University for Nationalities, Chongzuo 532200, PR China.
Abstract
In this paper, a waste fluid catalytic cracking (FCC) catalyst is used as a carrier to prepare a supported non-noble metal nickel catalyst (Ni/wFCC), which is applied to the selective hydrogenation of citral to citronellal. X-ray powder diffraction, Fourier transform infrared spectroscopy, and scanning electron microscopy were used to analyze the structural characteristics of the Ni-loaded sample. The catalyst after loading Ni still maintained a good zeolite structure, and the surface impurities were reduced. The effect of reaction conditions on the Ni/wFCC-catalyzed hydrogenation of citral to citronellal was investigated, and the optimal reaction conditions were obtained as follows: a Ni loading of 20 wt %, a catalyst amount of 5.6%, a hydrogenation temperature of 180 °C, a hydrogenation time of 90 min, and a hydrogenation pressure of 3.0 MPa. Under these conditions, the conversion of citral and selectivity of citronellal were 98.5 and 86.6%, respectively, indicating that the Ni/wFCC catalyst had strong catalytic activity and selectivity. This research provided new ideas for the recycling of waste FCC catalysts and industrial synthesis of citronellal.
In this paper, a waste fluid catalytic cracking (FCC) catalyst is used as a carrier to prepare a supported non-noble metal nickel catalyst (Ni/wFCC), which is applied to the selective hydrogenation of citral to citronellal. X-ray powder diffraction, Fourier transform infrared spectroscopy, and scanning electron microscopy were used to analyze the structural characteristics of the Ni-loaded sample. The catalyst after loading Ni still maintained a good zeolite structure, and the surface impurities were reduced. The effect of reaction conditions on the Ni/wFCC-catalyzed hydrogenation of citral to citronellal was investigated, and the optimal reaction conditions were obtained as follows: a Ni loading of 20 wt %, a catalyst amount of 5.6%, a hydrogenation temperature of 180 °C, a hydrogenation time of 90 min, and a hydrogenation pressure of 3.0 MPa. Under these conditions, the conversion of citral and selectivity of citronellal were 98.5 and 86.6%, respectively, indicating that the Ni/wFCC catalyst had strong catalytic activity and selectivity. This research provided new ideas for the recycling of waste FCC catalysts and industrial synthesis of citronellal.
Naturalcitral exists
in plant essential oils, such as lemonwormwoodoil, lemongrass oil, and Litsea cubebaoil.[1−3] Citral can be used in cosmetics, flavors, food, and
other industries and is a key raw material for the synthesis of ionone
and vitamin A, and other pharmaceutical intermediates.[4,5] The citral molecule has three hydrogenated double bonds: C=C double
bond, C=O double bond, and C=C double bond conjugated with the carbonyl
group. Therefore, the common citralhydrogenation products are geraniol,
citronellol, and citronellal.[6] From a thermodynamic
point of view, the C=C double bond of citral is more likely to be
hydrogenated to generate citronellal. Citronellal has a unique fragrance
and is often used as a food flavor additive or intermediate for further
synthesis of isopulegol, menthol, citronellol, and hydroxydihydrocitronellal
and has high economic value.[7]Salminen
et al.[8] fixed ionic liquid-dispersed
Pd nanoparticles on an activated carbon cloth and used them for the
selective catalytic hydrogenation of citral. At a reaction temperature
of 100 °C and a hydrogen pressure of 0.5 MPa, the citralconversion
rate was 100% and citronellal selectivity was 70%. Syunbayev et al.[9] studied the activity of group VIII metal (Pd,
Ni, Pt, Os, Rh, Ru, Ir-black, and NiR) catalysts in the liquid phase
hydrogenation of citral to produce citronellal and the effect of reaction
conditions. The results showed that Ru, Ni, and Pd showed high selectivity,
which were 93.7, 87.0 and 75.3%, respectively, under the conditions
of 2.0 MPa, 30 °C, and 96% ethanol solvent. Zhao et al.[10] loaded Pd onto graphite oxide and catalyzed
the selective hydrogenation of citral to citronellal under the action
of an alkali accelerator (NaOH/NaCO3). The selectivity
of citronellal was 89.6%. The adsorption of molecules on the catalyst
surface and the ability to activate the C=C and carbonyl groups can
directly affect the conversion and selectivity of citral. If the reaction
occurs in the macroporous and mesoporous network of the catalyst,
then its wide pore size will not affect the product and the main product
of the diffusion will be citronellal.[6] The
commonly used catalysts for selective hydrogenation of citral to produce
citronellalare precious metal catalysts, which are expensive and
require the participation of alkaline additives or a large amount
of solvents (96% ethanol, etc.). Besides, the process is complicated,
and the industrial production cost is high.Fluid catalytic
cracking (FCC) is an important unit operation in
the petroleum refining industry, and the waste FCC catalysts account
for 700,000–900,000 metric tons per year in the world.[11] Because of the precipitation of heavy metals
(Fe, Al, Ni, V, Sb, Co, etc.), waste FCC catalysts are highly hazardous
and are listed as hazardous solid waste by the 2016 revised “National
Hazardous Waste List” in China. Waste FCC catalysts are not
only a huge quantity but also difficult to handle. In recent years,
the resource utilization of waste FCC catalysts has become a hot research
issue in the oil refining industry. FCC catalysts use zeolites as
the main active ingredient, in which activity is reduced after being
discarded, but they still maintain the basic porous structure of zeolites.
Therefore, waste FCC catalysts have stable porous structures and good
adsorption performances, which make them potential carriers for catalyst
preparation. According to the different properties of the supported
active components, the new catalyst prepared from the waste FCC catalysts
can be used for different catalytic reactions. Vasireddy et al.[12] used the waste FCC catalyst as the carrier of
the iron-based catalyst to prepare the FT catalyst with high abrasion
resistance. Liu et al.[13] loaded MgO onto
the waste FCC catalyst, and the obtained new catalyst had good catalytic
ozone oxidation degradation performance of phenol-containing wastewater.
Ding et al.[14] used the sol–gel method
to prepare waste FCC catalyst supported nano-zinc oxide, which was
applied to the catalytic esterification reaction of rosin. A nickel-based
catalyst supported on a waste FCC catalyst also shows high catalytic
activity and stability on catalytic hydrogenation reactions.[15,16]In this paper, the waste FCC catalyst is used as a carrier,
and
the non-noble metal Ni is the active component. A supported nickel-based
catalyst is prepared for selective catalytic hydrogenation of citral
to citronellal. X-ray powder diffraction (XRD), Fourier transform
infrared spectroscopy (FT-IR), and scanning electron microscopy were
used to analyze the structural characteristics of the Ni-loaded sample.
The conversion of citral and selectivity of citronellal under different
hydrogenation conditions were studied. The optimization conditions
of citralhydrogenation were obtained, and the mechanism of the reaction
process of citralhydrogenation catalyzed by Ni/wFCC was proposed,
providing new ideas for studying the industrialized production of
citral and recycling of waste FCC catalysts.
Results
and Discussion
Physical and Chemical Properties
of the Catalyst
XRD was performed on the wFCC, NiO/wFCC,
and Ni/wFCC samples after
reduction activation, and the results are shown in Figure . As shown in Figure , the wFCC sample presents
strong Y-type zeolite and Al2O3 diffraction
peaks, and a small amount of ZSM-5 is also found. The overall peak
shape is chaotic, and the peak intensity is low, indicating the amorphous
structure of wFCC.[17] Evident characteristic
peaks of NiO appear in the spectrum of the precursor NiO/wFCC, corresponding
to the 111, 200, 220, and 311 crystal planes.[18] After reduction, the oxidation state of Ni on wFCC is fully reduced
to a metal with catalytic hydrogenation activity of state Ni (111,
200, and 220 crystal planes). The Al2O3, ZSM-5,
and Y-type zeolitecomponents in the wFCC sample are all good carriers
for the catalyst. After the active components are successfully loaded,
all the samples have no evident structural changes, indicating that
the obtained catalyst has a certain structural stability.
Figure 1
XRD patterns
of wFCC (a), NiO/wFCC (b), and Ni/wFCC (c).
XRD patterns
of wFCC (a), n class="Chemical">NiO/wFCC (b), and Ni/wFCC (c).
The wFCC, precursor NiO/wFCC, and Ni/wFCC samples after reduction
activation were subjected to FT-IR, and the results are shown in Figure . The FCC catalyst
is composed of a Y-type zeolite and matrix. The main components of
the matrix are Al2O3 and SiO2. Therefore,
the infrared spectra of the three samples all reflect the structural
characteristics of Al2O3 and SiO2. As shown in Figure , given the zeolite structure, the vibration peaks of the samples
are primarily concentrated in the mid–far-infrared region.
The characteristic peak at 811 cm–1 is the symmetrical
stretching vibration absorption peak of Si–O–Si, and
the strong absorption peak at 1080 cm–1 is the antisymmetric
stretching vibration peak of Si–O–Si. Moreover, the
weak absorption peak at 1631 cm–1 is the bending
vibration peak of the zeolite adsorbing water–OH. In the infrared
spectrum of the wFCC sample, the weak absorption peak at 1385 cm–1 is considered to be the −N=C=O phase in-plane
stretching vibration because the coke produced in the FCC process
is derived from the aromatic hydrocarbons and N-containing materials
in the cracking raw materials.[19] The absorption
peak of NiO/wFCC and Ni/wFCC samples loaded with Ni at 1385 cm–1 is enhanced because of the presence of nitrate, which
is a common phenomenon when the supported Ni catalyst is prepared
by the equal volume impregnation method. The broad absorption peak
near 3453 cm–1 is caused by the stretching vibration
of the zeolite adsorbing molecularwater and hydroxyl OH.
Figure 2
FT-IR characterization
of wFCC (a), NiO/wFCC (b), and Ni/wFCC (c).
FT-IR chn class="Chemical">aracterization
of wFCC (a), NiO/wFCC (b), and Ni/wFCC (c).
TPR was adopted to investigate the reduction behavior of NiO/wFCC
with different Ni loadings, and the profiles are presented in Figure . As can be seen,
all samples show a narrow hydrogenconsumption peak centered at 386.5
°C, which corresponds to the reduction of the NiO particle interacting
weakly with the wFCC support.[20] The high-temperature
hydrogenconsumption peaks at 678.8 and 835.0 °C were attributed
to spinel NiAl2O4 or strongly interacting metal–support
phases.[21] The reduction peaks at high temperature
were gradually decreased with increasing Ni loading, indicating that
Ni/wFCC with low Ni loading is difficult to completely reduce.
Figure 3
H2-TPR profiles of NiO/wFCC with different Ni loadings.
H2-TPR profiles of n class="Chemical">NiO/wFCC with different Ni loadings.
H2 pulse chemisorption was performed to determine
the
metal dispersion, metallic surface area, and cubic crystallite size
of the Ni/wFCC samples. As shown in Table , when the Ni loading increases from 10 to
20 wt %, the Ni dispersion increases from 0.67 to 0.74% and the metallic
surface area increases from 4.49 m2/gsample to
4.96 m2/gcal., respectively. The reason is that
Ni/wFCC with 20 wt % is easier to completely reduce than the first
two catalysts, which corroborated with the results obtained using
H2-TPR. Furthermore, as the amount of Ni increases to 25
wt %, the corresponding metal dispersion and metallic surface area
decrease to 0.47% and 2.77 m2/gsample., respectively.
It may be attributed to the migration and agglomeration of excess
Ni particles. It was generally considered that catalysts presenting
high metal dispersion and large metallic surface area have good catalytical
activities.
Table 1
Hydrogen Chemisorption Results for
Ni/wFCC with Different Ni Loadings
Ni loading/wt %
metal dispersion/%
metallic
surface area/m2/gcat.
cubic crystallite size/nm
10
0.67
4.49
125.14
15
0.70
4.87
119.56
20
0.74
4.96
113.32
25
0.47
2.77
216.66
The structures of the
wFCC and NiO/wFCC samples were analyzed by
SEM, and the results are shown in Figure . Considering that the FCC process produces
high-temperature coking and carbon deposits, the surface of the wFCC
sample is uneven. After the load roasting treatment, the surface roughness
of the NiO/wFCC particles is reduced. The reason may be that some
impurities are eliminated at high temperature during the preparation
of the catalysts.
Figure 4
SEM images of wFCC (a) and NiO/wFCC (b).
SEM images of wFCC (a) and n class="Chemical">NiO/wFCC (b).
Ni/wFCC-Catalyzed Citral Hydrogenation Process
After analyzing the components of the samples before and after
the reaction by GC–MS, the citralhydrogenation process catalyzed
by Ni/wFCC was explored (Figure ). The main components of citralare neral (cis-citral) and geranial (trans-citral).
In Ni/wFCC-catalyzed hydrogenation of citral, the main reaction is
the hydrogenation of neral and geranial to produce citronellal. The
side reactions are as follows: (1) citronellal is isomerized to isopulegol,
which is further hydrogenated to form menthol; (2) citronellal is
further hydrogenated to form tetrahydrocitronellol; (3) citral is
isomerized into cis-oxylimonene and α-terpineol.
The by-products of Ni/wFCC-catalyzed citralhydrogenation are isopulegol
and menthol, and the contents of tetrahydrocitronellol, oxylimonene,
and α-terpineol are small. The reaction mechanism of the selective
hydrogenation of citral on the Ni/wFCC catalyst is shown in Figure . Hydrogen molecules
are adsorbed on the active center of the catalyst and decompose to
form free radicals H· under the action of heat. The molecules
of neral and geranialare combined with carbon and oxygen. The conjugated
C=C bond of the double bond is polarized by Ni in the active center.
After polarization, the C=C bond becomes unstable, and producing citronellal
instead of unsaturated alcohols is easy (nerol and geraniolare not
found on GC–MS).
Figure 5
Hydrogenation of citral over the Ni/wFCC catalyst.
Figure 6
Mechanism of citral hydrogenation over the Ni/wFCC catalyst.
Hydrogenation of n class="Chemical">citral over the Ni/wFCC catalyst.
Mechanism of citraln class="Chemical">hydrogenation over the Ni/wFCC catalyst.
In this paper, the waste FCC catalyst supported
Ni is used as the
catalyst to determine the effects of Ni loading, catalyst amount,
hydrogenation temperature, reaction time, and hydrogen pressure on
Ni/wFCC catalytic citralhydrogenation.The effect of the Ni/wFCC
catalyst with Ni loadings of 10, 15,
20, and 25 wt % on citralhydrogenation over Ni/wFCC was studied under
the following conditions: an amount of catalyst of 5.6%, a hydrogen
pressure of 4 MPa, a hydrogenation temperature of 180 °C, and
a hydrogenation time of 90 min. The results are shown in Figure . With the increase
of Ni loading, the citralconversion rate and citronellal selectivity
show similar trends, and both gradually increase to the maximum when
the Ni loading is 20 wt %, which are 98.4 and 83.8%, respectively
(Figure ). The reason
is that the metal dispersion and large metallic surface area increase
when Ni loading increases from 10 to 20 wt % (Table ). The decrease occurs when the Ni loading
exceeds 20 wt % because excessive Ni loading will block the pores
of the Ni/wFCC catalyst, and migration and agglomeration are prone
to occurring during calcination reduction, resulting in insufficient
reduction activation and reducing the catalyst’s activity and
selectivity. This decrease is in line with the decreasing metallic
surface area determined by H2 pulse chemisorption. Therefore,
20 wt % Ni loading is more appropriate.
Figure 7
Influence of Ni loading
on citral hydrogenation.
Influence of Ni loading
onn class="Chemical">citral hydrogenation.
The effect of the amount
of Ni/wFCC catalyst on the catalytic hydrogenation
of citral is investigated when the Ni loading, hydrogen pressure,
reaction temperature, and reaction time was 20 wt %, 4 MPa, 180 °C,
and 90 min, respectively. The results are shown in Figure . When the amount of catalyst
is less than 2.8%, the citralconversion rate is less than 61.4% (Figure ). Simultaneously,
the reaction control step is the adsorption of hydrogen molecules
on the active sites of the catalyst. The amount of catalyst and the
corresponding active sites are small, leading to the low conversion
and selectivity. As the amount of catalyst increases, the number of
active sites increases and the conversion and selectivity also increase.
When the amount of catalyst is greater than 5.6%, the conversion of
citral is close to 100% and the selectivity of citronellal does not
change. Therefore, the appropriate amount of catalyst is 5.6%.
Figure 8
Influence of
Ni/wFCC dosage on citral hydrogenation.
Influence of
Ni/wFCC dosage onn class="Chemical">citral hydrogenation.
The Ni loading, catalyst amount, reaction time, and hydrogen pressure
are 20 wt %, 5.6%, 90 min, and 4 MPa, respectively. The hydrogenation
reaction of citral at a reaction temperature of 160 to 200 °C
is studied. The results are shown in Figure . Figure shows that with the increase of the reaction temperature,
the surface reaction rate increases rapidly and the citralconversion
rate gradually increases. After 180 °C, the citralconversion
rate basically remains constant. The selectivity of citronellal is
the highest at 170 °C, reaching 88.7%, but with the increase
of temperature, the side reaction intensifies and the selectivity
of citronellal decreases significantly. Therefore, the suitable reaction
temperature was 180 °C.
Figure 9
Influence of reaction temperature on citral
hydrogenation.
Influence of reaction temperature on citraln class="Chemical">hydrogenation.
The Ni loading, amount of catalyst,
reaction temperature, and hydrogen
pressure are 20 wt %, 5.6%, 180 °C, and MPa, respectively. The
changes in the catalytic hydrogenation of citral with reaction time
are studied. The results are shown in Figure . As shown in Figure , as the reaction time increases, the conversion
gradually increases from 60 to 90 min. After 90 min, the citralconversion
stabilizes and the citronellal selectivity shows a slow downward trend.
The experimental results indicate that the conversion of citral has
been completed when the reaction time is 90 min. As time increases,
citronellalcontinues to react to form other substances. After GC–MS
analysis, citronellal further reacts to form isopulegol. Therefore,
the optimal reaction time is 90 min.
Figure 10
Influence of reaction time on citral
hydrogenation.
Influence of reaction time on citraln class="Chemical">hydrogenation.
The Ni loading, catalyst amount,
reaction temperature, and reaction
time are 20 wt %, 5.6%, 180 °C, and 90 min, respectively. The
effect of hydrogen pressure on the catalytic hydrogenation of citral
is studied when the hydrogen pressure is 2–4 MPa. The results
are shown in Figure . As shown in Figure , the hydrogen pressure increases from 2 to 3 MPa and the citralconversion rate increases significantly to 97.0% because increasing
the hydrogen pressure is equivalent to increasing the hydrogenconcentration,
which accelerates the reaction rate and further increases the citralconversion. After the hydrogen pressure is increased to 3 MPa, the
citralconversion slowly increases by 98.4%, whereas the citronellal
selectivity decreases from 87.7% at 2.5 MPa to 83.8%. When the hydrogen
pressure is greater than 3 MPa, the hydrogenconcentration in the
reaction solution tends to be saturated. Simultaneously increasing
the amount of hydrogen has little effect on the citralconversion
rate, but the supersaturated hydrogen molecules promote the hydrogenation
of other double bonds of citral, thereby reducing the selectivity
of citronellal. Therefore, the optimalhydrogen pressure is 3.0 MPa.
Figure 11
Influence
of hydrogen pressure on citral hydrogenation.
Influence
of hydrogen pressure onn class="Chemical">citral hydrogenation.
The Reusability of the Catalyst
After
studying the selective hydrogenation of citral catalyzed by Ni/wFCC,
the optimal reaction conditions were obtained: a Ni loading of 20
wt %, a catalyst amount of 5.6%, a reaction temperature of 180 °C,
a reaction time of 90 min, and a hydrogen pressure of 3.0 MPa. Moreover,
the stability test of Ni/wFCC was carried out under these conditions.
The experimental results are shown in Table . The activity of the Ni/wFCC catalyst had
no significant change during the first three-times recycle experiments,
and the slight difference between the values may be due to the analysis
and calculation process.
Table 2
Results of Parallel
Experiments
running time
citral conversion/%
citronellal selectivity/%
1#
97.9
85.9
2#
98.3
86.5
3#
98.5
86.6
Conclusions
The characterization results show that the wFCC sample is in an
amorphous state and consists of Al2O3, ZSM-5,
and Y-type zeolites. After loading the Ni metal, the surface impurities
of the particles are reduced and the zeolite framework structure does
not change significantly. The optimalconditions for the selective
hydrogenation of citral catalyzed by Ni/wFCCare as follows: a Ni
loading of 20 wt %, a catalyst dosage of 5.6%, a reaction temperature
of 180 °C, a reaction time of 90 min, and a hydrogen pressure
of 3.0 MPa. Under the optimal reaction conditions, the conversion
of citral is 98.5% and the selectivity of citronellal is 86.6%.
Experimental Materials and Methods
Materials
Citral, C10H16O (99.13%, neral 50.92% + geranial
48.21%), with AR was purchased
from Xilong ChemicalCo., Ltd. Waste FCC catalysts were provided by
CNPC Guangxi Tiandong PetrochemicalComplex Co., Ltd. Nickelnitrate
(NiN2O6·6H2O) with AR was purchased
from Shanghai Haiqu ChemicalCo., Ltd. Canned hydrogen with 99.9%
H2 and H2/N2 mixed gas with 5% H2 were purchased from Guangxi Nanning Air Separation Gas Co.,
Ltd. Deionized water was self-made by three-effect evaporation. Solvent
oil with a boiling point of 140–180 °C was purchased from
Shanghai Subang Plastic Technology Co., Ltd.
Preparation
of Waste FCC Catalyst Supported
Ni
The equal volume impregnation method assisted by ultrasound
was adopted to prepare the waste FCC catalyst (wFCC) supported Ni
catalyst (Ni/wFCC), and the steps are as follows: a certain amount
of wFCC was roasted at 500 °C for 4 h, and after cooling, wFCC
was removed through a 160 mesh sieve before use. The required mass
of NiN2O6·6H2O and volume of
H2O were calculated on the required Ni loading of the experiment
(the water absorption rate of wFCC was 0.7 mL/g). wFCC, NiN2O6·6H2O, and H2O were mixed
and stirred ultrasonically for 15 min and then immersed for 12 h;
the impregnated catalyst was dried at 110 °C for 8 h and calcined
at 500 °C for 8 h to obtain the oxidized wFCC-supported Ni precursor
(NiO/wFCC), which was reduced by H2/N2 mixed
gas at 550 °C for 2.5 h to prepare the wFCC-supported Ni catalyst
(Ni/wFCC).
Citral Catalytic Hydrogenation
Reaction
The reaction was carried out with a magnetically
stirred high-pressure
microreactor (Hotong Instrument/HT-50FJ). The effective volume of
the reactor was 50 mL. The design temperature was under 300 °C,
and the design pressure was 20.7 MPa. The reactor was equipped with
a magnetic coupling mechanical stirrer, charge and discharge gas valve,
safety valve, and temperature controller. A certain amount of citral
(1:1 ratio to solvent oil) and Ni/wFCC catalyst were poured into the
reactor; the reactor was sealed and replaced with N2 gas
three times. The pressure was maintained, and the reactor was checked
for leaks. When no leak was found, the reactor was emptied and filled
with a small amount of hydrogen, and the pressure was maintained for
10 min. Then, the experiment temperature and speed were set, and the
temperature increased. When the temperature increased to the required
temperature, H2 was charged at a certain pressure. The
reaction began, and the reaction time was recorded. After the reaction
was completed, it was cooled to room temperature. After the pressure
was released, the reaction sample was removed, filtered, and analyzed
by gas chromatography–mass spectrometry (GC–MS).
Catalyst Characterization
The morphology
of the sample was analyzed using a Zeiss EVO 80 scanning electron
microscope (Germany). Structural analysis was performed using a Bruker
D8 Advance X-ray diffractometer (Germany), with a Cu Kα source
(k = 1.541 Å) at 40 and 200 kV, and 200 mA in
the air, and the sample was scanned at the Bragg angle (2θ)
ranging from 5 to 80°, with a scanning speed of 7°/min.
FT-IR was analyzed using a PerkinElmer-65 spectrometer with 4000–400
cm–1 KBr. H2-TPR experiments were performed
with an AutoChemII 2910 instrument (USA) to evaluate the reduction
behavior of NiO/wFCC. 10 mg of NiO/wFCC powder was pretreated under
a 30 mL/min flow of Ar at 200 °C for 2 h to remove the adsorbed
moisture and then cooled down to 50 °C and heated up to 900 °C
using a rate of 10 °C/min under a 30 mL/min flow of 10% H2/Ar. The effluent gas was forced into a thermalconductivity
detector (TCD) to detect the hydrogenconsumption. Hydrogen pulse
chemisorption was performed with the same instrument to measure the
metal dispersion, the metallic surface area, and the cubic crystallite
cize.[22,23] The experiment was conducted at 50 °C
under a 30 mL/min flow of 10% H2/Ar using 0.1 mL pulses.
Before each experiment, the samples were reduced at 600 °C for
2.5 h under a 10 mL/min flow of 10% H2/Ar.
Authors: Cristiane de Bona da Silva; Sílvia S Guterres; Vanessa Weisheimer; Elfrides E S Schapoval Journal: Braz J Infect Dis Date: 2008-02 Impact factor: 1.949