catalytic activity of electrospun ag and ag/carbon composite fibres in partial methanol oxidation
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Shter, V. Gelman, D. M. Pesel, M. Mann-Lahav and G. S. Grader, Catal. Sci. Technol., 2014, DOI:
10.1039/C4CY01341G.
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Cite this: DOI: 10.1039/x0xx00000x
Received 00th January 2012,
Accepted 00th January 2012
DOI: 10.1039/x0xx00000x
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Catalytic activity of electrospun Ag and
Ag/carbon composite fibres in partial methanol
oxidation
V. Halperin, G. E. Shter, V. Gelman, D. M. Peselev, M. Mann-Lahav and G. S. Grader*,
We report on the catalytic activity of Ag metal fibres and composite Ag/carbon fibres synthesized by
electrospinning, in partial methanol oxidation (PMO) to formaldehyde. Uniform mats, containing fibres
with 300-600 nm in diameter were prepared from a stable suspension of Ag nanoparticles (NP), AgNO3,
PVA, water and ethanol. Thermal decomposition of the "green" mats was studied by TGA/DTA/MS in
inert, strongly and mildly oxidizing atmospheres. Special heat profiles were developed to obtain
metallic Ag as well as composite Ag/carbon (~10 wt. % carbon) fibre mats catalysts. The effect of
sintering conditions on the morphology and catalytic activity were studied. Using a catalyst weight of
45-70 mg and a methanol WHSV in the range of 60-90 h-1
, the highest conversion and selectivity for
metallic Ag fibres at 550°C were 94.2% and 82.4%, respectively. Under the same conditions, the
catalytic activity for Ag/carbon mats was found to improve yielding a conversion and selectivity of 95.8
% and 84.1 %, respectively. Large space time yields (STY) of 56 h-1
and 64 h-1
were obtained for metal
and metal/carbon cases, by optimizing the sintering conditions. A maximal WHSV and STY of 540 h-1
and 386 h-1
respectively were achieved with Ag/carbon composite catalyst at 95% conversion and 550°C.
In summary, we demonstrated the feasibility of electrospinning technology in producing highly active
catalysts containing Ag and composite Ag/carbon fibres for partial oxidation of organic molecules. We
also demonstrated the superior behaviour of the metal/carbon composite fibres over the metallic silver
fibre and powder analogues.
Introduction
Partial methanol oxidation to formaldehyde (PMO) is an
important industrial process with global annual production
(1996) estimated at 8.7∙106 metric tons1. Overall formaldehyde
consumption is expected to grow at annual rate of 5% in 2011-
20162. The most common catalyst used in PMO is silver.
Although the PMO process is not new, it is still the focus of
intense research as evidenced in recent publications3-7. Due to
the large formaldehyde production scale, one of the potential
routes to increasing the energy efficiency and catalyst lifetime
is reduction of the high temperatures (600-720°C) used
industrially1,2. Therefore, improvements in catalyst activity and
selectivity, as well as the possible lowering of the operating
temperatures will result in overall significant decrease in energy
consumption and production costs of this process.
In recent years much progress has been made in controlling
the phase composition, size and structure of nanometric
catalysts, allowing for highly selective and efficient catalysts8.
However, one of the obstacles of using micro-porous materials
in heterogeneous catalysis is the diffusion limitations inside the
pores. Diffusion coefficients decrease with decreasing pore
diameter and increasing molecular weight of both reactants and
products. For reactants or products molecules with
characteristic dimensions larger than pores diameter the
transport is limited. The deposition of either large molecules or
coking near the pore entrance during the reaction can deactivate
the whole pore8. One of the common ways to overcome these
limitations is the use of hierarchically porous materials. Fibrous
catalysts can be engineered to have hierarchical porosity,
ranging from micro-porous fibres to the meso- and macro-
porous structure of the fibrous mats.
Electrospinning of Ag containing fibres for catalysis
applications has been reported in the literature. Silver
nanoparticles (NP) dispersed in carbon fibres produced by
electrospinning of Ag nitrate and polymer containing precursor
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with subsequent reduction were tested for catalytic activity in
styrene epoxidation9,10. Electrospun polyacrylonitrile (PAN)
fibres were immersed in Ag nitrate solution followed by
reduction and tested in methylene blue reduction process11.
Silica fibres with dispersed Ag NP were prepared by either
electrospinning the Ag nitrate containing precursor12 or
immersing the activated electrospun silica nanotubes in Ag
nitrate solution with subsequent reduction13. The Ag NP/silica
fibres were tested in catalytic reduction of 4-nitrophenol13 and
methylene blue12. Additionally, Ag/NiO fibres were obtained
by using metal nitrates containing precursors followed by
calcination14. Finally, pure Ag fibres were produced by
impregnation of electrospun polymer fibres followed by their
thermal degradation and organics removal15.
In general, most methods for electrospinning of composite
or metal Ag fibres above are based on precursors including
polymer and Ag-salt or Ag-complex or, alternatively,
metallization of polymer or ceramic electrospun fibres matrix.
The chosen model reactions for catalytic activity tests in most
above mentioned cases were conducted at low temperatures that
are insufficient for the PMO process discussed herein. Recent
studies by our group focused on nanostructured Ag based
materials with organic doping for enhanced catalytic properties,
including their deposition on nanofibrous TiO2 support16-18. The
hybrid catalyst consisting of thermally activated Congo-red
nanoparticles entrapped within Ag deposited on TiO2 fibres was
shown to considerably outperform other studied catalysts in
every parameter of PMO16.
In this study we describe the production of Ag and
composite Ag/carbon fibre mats and study their catalytic
activity in the PMO process. The fibre mats were produced by
electrospinning, using Ag nanoparticles suspension as a
precursor. This type of precursor is fundamentally different
from the precursors described earlier: firstly, it is heterogeneous
system including solid part of Ag-nanoparticles and liquid part
(polymer in solvents with small additives of salts). Secondly,
the skeleton of the final fibres was formed by relatively large
(~50nm) initial nanoparticles in contrast to very small
nanoparticles formed from salt solution during reduction. The
last factor prevents the formation of very large and non-uniform
Ag particles during sintering at high temperatures in this
catalytic application. In addition, this technique allowed
obtaining a high Ag loading (~70 wt.%) in the “green”
electrospun fibres. Further thermal treatment with varied
atmosphere and temperature regimes facilitated the synthesis of
fibrous catalytic material with desired structure and
composition. The high Ag loading used in this work has several
key advantages: firstly, the "green" fibres can be processed to
obtain either metal or composite metal/carbon fibres without
modification of electrospinning parameters or precursor
composition by varying only the thermal treatment conditions.
Secondly, the lower polymer content in fibres results with
significantly lower shrinkage during thermal treatment, hence it
allows retention of the fibrous morphology during sintering.
The main question addressed in this research is whether the
catalytic activity demonstrated thus far with Ag containing
fibres, can be improved using the highly Ag loaded electro-
spun fibres developed herein. In particular can residual carbon
intentionally preserved in the fibre matrix prevent Ag particle
aggregation and growth – that lead to degradation of the
catalytic activity? In this paper we demonstrate that Ag and
composite Ag/carbon fibres mats give rise to enhanced
performance in high temperature gas-phase PMO processes. In
addition, we show the interplay between the processing
parameters and the resulting morphology and catalytic activity.
Experimental
General description
The experimental work can be divided into 4 main parts: a)
preparation of liquid precursor for injection, b) the
electrospinning process resulting in "Green" Ag/polymer fibre
mats, c) thermal treatment of fibre mats under different
atmospheres (Air, Ar, O2/Ar) resulting in "white" Ag or
Ag/carbon fibre mats, and d) catalytic activity measurements in
partial methanol oxidation (PMO) using "White" Ag fibre mats
and "White" Ag/carbon composite mats as catalysts.
Throughout the paper the term "Green" mat designates the fibre
mat obtained after electrospinning and drying, while "White"
mat designates the electrospun fibre mats which were heated at
high temperature for organics burn-out and sintering.
Chemicals
AgNO3 - (99+%, Aldrich), Ag nanoparticles suspension -
(35 nm, 25%, IoLiTec Ionic Liquids Technologies GmbH,
Heilbronn, Germany), Polyvinyl alcohol (PVA) - (205000
g/mol, Aldrich), Ethanol - (Absolute, Carlo Erba), Methanol –
(Absolute, Bio-Lab ltd), Formaldehyde (A.G., Frutarom,
Israel), water – Milli-Q purified.
Precursor preparation
Precursor preparation procedure included the following
main steps:
1) A solution of 1.2 g PVA in 6 g of water was mixed with
magnetic stirrer at 70°C for 1 hour followed by homogenization
on roller at room temperature (RT) for 24 hours resulted in a
transparent high viscosity solution;
2) 7.2 g of this solution were mixed with 9.2 g of 28 wt.% Ag
nanoparticles suspension in ethanol and 0.8 g of 50 wt.%
AgNO3 water solution. The mixture was stirred on roller at RT
for 12 hours to yield a final precursor – stable
AgNP/AgNO3/PVA/Water/Ethanol suspension with weight
ratio Ag to PVA ~2:1.
Electrospinning
The electrospinning system consisted of high voltage supply
(SL40P60, Spellman, Hauppauge, New York, USA), a
grounded vertical rotating aluminium collector with controller
(EP-613, O.Fi. electronics ltd., Haifa, Israel) and feed system
with syringe pump (KDS100, KD Scientific, Holliston, MA,
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USA) and injector. The precursor solution was fed at 0.5 ml/h
rate (SFR). The working distance between the needle and the
collector (WD) was 15-18 cm, while the applied voltage was in
the 20-25 kV range. Typical electrospinning duration was 6
hours. After electrospinning, the resulting "green" Ag/PVA
fibre mats were vacuum dried at 70°C for 12 hours in order to
remove the residual solvents.
Thermal treatment
"White" mats were obtained by thermal treatment of dried
"green" mats. The heating was performed in a horizontal tube
furnace (CTF, Carbolite). The gas atmosphere was adjusted by
flowing either air, or oxygen and Ar through mass flow
controllers to achieve desired O2 concentration. Gas was fed
into the furnace at a flow rate of 200 ml·min-1. Samples were
placed on dense alumina substrate. The gas mixture of 1.5
vol.% O2 in Ar was used to obtain “white” Ag metal fibre mats.
Argon gas was used to obtain “white” composite Ag/carbon
fibre mats. Stepwise profiles were based on TGA-DTA analysis
and are shown in Fig. 1a, b for both metal and composite
metal/carbon fibres.
Fig. 1 Thermal treatment profiles: a) in 1.5% O2 in Ar, b) in pure Ar
Catalytic Activity
The Experimental Setup for measurement of the PMO
process was described in detail earlier18. The catalytic reaction
was carried out at different temperatures, gradually decreasing
from 550 to 150°C, by employing the “methanol ballast
process” version, in which only air and pure methanol are fed
into the reactor without extra water in the reactant mixture. The
weight of Ag fibre mats as catalyst was typically 45-70 mg. To
keep constant catalyst bed volume of 1 ml, all the samples were
diluted with quartz powder. The CH3OH concentration in the
reaction mixture was kept constant at 500 mg L–1. The total
pressure in the reactors was held at 1.5 bar. The feed gas
mixture flow rate was 8.35 L·h–1, with corresponding methanol
WHSV in the range of 60-90 h-1. In the context of this study,
the WHSV (weight hourly space velocity) represents maximal
weight of methanol which can be converted to formaldehyde
during one hour per weight of catalyst at constant conversion.
The conversion and selectivity are defined in Eq.1 and Eq.2,
respectively.
Eq. 1 ���������� ��
����� ���������� 100%
Eq. 2 �������������
���������� ��� 100%
Conversion and selectivity determinations were carried out
after 2 h of continuous process at each reaction temperature to
ensure that the operating conditions of the reaction are
stationary. A full PMO run consisted of 6 steady state
measurements at different temperatures.
Thermal Analysis and material characterization
About 40 mg of samples were analysed by simultaneous
thermal gravimetric analysis (TGA) and differential thermal
analysis (DTA) at ambient pressure (Setsys Evolution 1750,
Setaram, Caluire, France). The TGA/DTA measurements were
carried out from 25 to 800 °C with a heating rate of 5°C/min
under Ar or air or Ar/O2 flow of 60 ml/min using a 100 µl
alumina crucible. The evolved gases were analysed on-line by a
quadrupole Mass Spectrometer (MS, ThermoStar GSD320,
Pfeiffer Vacuum, Asslar, Germany). The obtained data were
treated using the Calisto Processing software (AKTS and
Setaram). Morphology and microstructure were investigated by
high-resolution scanning electron microscopy (ULTRA plus;
Zeiss, Zurich, Switzerland). The catalytic system evolved gases
were analysed using a gas chromatograph (7890A, Agilent
Technologies, Santa Clara, CA, USA) with flame ionization
detector (FID) and Wcot fused silica column (Varian) kept at
40°C.
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Results and Discussion
Metallic fibres: preparation and characterization
Preparation of metallic fibre mats requires complete
removal of the organic species which make about 30 wt.% of
the "green" fibres. Specifically, during thermal treatment of the
"green" Ag/AgNO3/Polymer fibre mats in oxidative
atmosphere, polymer oxidation can be realized by two oxidants:
internal AgNO3 and external gaseous oxygen. Thermal analysis
experiments in air show minute water desorption of ~0.5% and
a small endothermic peak at 95°C (Fig. 2a).
Fig. 2 Thermal analysis of green fibres in air: a) TGA-DTA signals and b) MS signal
of effluent gas.
A multistep oxidative decomposition follows the water
desorption, with three main exothermic peaks up to 450oC. The
gaseous products of this oxidation stage were detected by on-
line mass spectrometry and MS profile included NO, N2O,
NO2, CO2 and water (Fig. 2b). Based on the evolution of NOx
gaseous by-products (Fig. 2b, m/z=30), polymer oxidation by
Ag nitrate occurred at 165°C, leading to an additional weight
loss of 4%. This reaction is apparently accelerated by PVA
melting and observed in narrow temperature range. The next
stages of polymer oxidation started around 210°C with a
dominant participation of external oxidant (O2 from air) and
characterized by several steps of weight loss (Fig. 2a) and
strong exothermic peaks. The largest weight loss was detected
in the range of 230- 375°C and the total loss was ~ 25.5%.
Mass spectrometry (MS) profiles reveal massive formation of
water and CO2 with only minor NO and NO2 contribution. At
the final oxidation stage in the range of 375 - 450°C (Fig. 2a)
the dominant evolving gas was CO2 (Fig. 2b) which indicated
the combustion of carbon or partially decomposed polymeric
residues. At 450°C the polymer was fully oxidized by internal
Ag nitrate and external oxygen with a 30% total weight loss.
The thermal treatment conditions of the “green” fibre mats
significantly affect the resulting "white" fibres morphology.
Fast polymer oxidation can have two main negative effects: a)
massive gas release can damage the fibrous morphology; b) fast
rates of heat generation can lead to local overheating, causing
aggressive fibres sintering along with undesired particles
growth leading to formation of large aggregates and non-
uniform structure. Therefore the attempts of thermal treatment
in air resulted in very non-uniform and agglomerated "white"
mats with undesired morphology. To avoid the above negative
effects, a stepwise treatment profile under Ar/oxygen gas
mixture with lower O2 content than air was implemented.
Fig. 3 Thermal analysis of green fibres under 1.5% O2 in Ar: a) TGA-DTA signals
and b) MS signal of effluent gas.
The TGA-DTA-MS analyses in air and in Ar with 1.5% O2
were significantly different. Firstly, the rate of weight loss in
Ar-1.5% O2 shown in Fig. 3a was substantially slower
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compared to the process in air (see Fig. 2a). Secondly, the
organic burnout under 1.5% O2 was incomplete even at 800 °C,
whereas under air the weight loss was over by 450 °C. In
addition, under 1.5% O2 the internal oxidation due to the
nitrates occurs at a higher temperature than in air (above
~200°C vs. 165 °C) as confirmed by MS data on release of
nitrogen containing gases (Fig. 3b). The above three factors are
important for preserving the desired nanostructure of the fibres
during thermal treatment. The developed profile of this process
shown in Fig. 1a includes three soaks at 200, 250 and 300°C
with heating rate of 150°C/h and cooling rate of 300°C/h under
gas mix flow of 200 ml·min-1. This gradual profile allowed
lowering of the residual carbon to values of 0.5-0.7 wt.% (by
TGA, EDS) and a slow release of gases, preserving the fibrous
structure in the sintered mats seen in the HRSEM images in
Fig. 4.
Fig. 4 The effect of sintering on the morphology of the fibres: (a, b, c) “green”
fibres, and (d, e, f) “white” fibres after sintering in 1.5% Oxygen atmosphere (1 h
at 300°C).
Based on Fig. 4, the diameter of the "green" fibres was in the
range of 300-600 nm. The diameter of the sintered "white"
fibres decreased significantly to value of 150-400 nm. In
summary, sintering the fibres in low oxygen pressure (1.5% O2
in Ar) allowed preservation of the fibre structure, giving rise to
well-connected Ag particles without visual organic binder.
Composite metal/carbon fibres: preparation and
characterization
One of the undesired phenomena during usage of
polycrystalline Ag fibres at high temperatures is particle growth
and formation of hard agglomerates. In the present case these
phenomena occur both at the stage of initial thermal treatment
and during the PMO catalytic process, leading to catalyst
deactivation. A key element of this research was to determine
whether separation of the Ag NP inside the fibres by a carbon
residue formed from the decomposed polymer, can inhibit the
sintering and grain growth, thereby preventing the associated
catalyst deactivation. As shown in the following section, the
benefits of composite Ag/carbon fibre mats were proven. In
addition, we believe that the mats with composite Ag/carbon
fibres would be more flexible and mechanically more stable
compared to pure metallic fibres mats.
Thermal treatment of “green” Ag/AgNO3/PVA material
under Ar was chosen as a way to obtain composite Ag/carbon
fibre mats for use as catalysts in the PMO process. To develop
an optimal profile of thermal treatment in Ar, a TGA/DTA test
in flowing Ar gas was run with "green" mats as shown in Fig. 5.
Fig. 5 The TGA and heat flow signals of “green” fibres vs. temperature under Ar.
Endothermic water desorption at ~90°C (WL= 0.8-0.85 %) and
a sharp exothermic PVA oxidation by Ag nitrate in the range
~160-190°C (WL=4.6%) were detected. These two effects were
also observed in TGA/DTA profiles under Air and Ar/1.5% O2
(Figs. 4, 5), however the data in Fig. 5 proves beyond doubt
that these effects are not dependent on the external oxygen. The
shallow endothermic effect at 211°C can be attributed to
AgNO3 melting and it was not found in TGA/DTA test under
oxidative atmosphere (Fig. 2, 3). In the previous case the
endothermic melting was masked by strong exothermic process
of organic oxidation by the external oxidant. The next
exothermic peak starting at ~295°C represents further polymer
oxidation by AgNO3 occurring after melting of both PVA and
AgNO3. This process leads to a dominant part of the weight
loss from 4.8 to 21% in the 210 – 450°C range. After ~450°C
the weight loss rate was slow and approximately constant up to
800 °C. Weight loss at 800°C was 22.4% - significantly lower
than was detected in the case of heating in air (30%, Fig. 2):
this difference was attributed to residual carbon, uniformly
distributed between the particles of Ag. The presence of carbon
was confirmed by EDS where its content was found in the
range of 10±3 wt.%. This weight is slightly larger from the
expected residual carbon content predicted from the TGA data
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of ~ 8%. The EDS data should be regarded as a qualitative
indicator rather than a quantitative measure.
Although the actual weight of residual carbon content is not
high, it is significant in terms of volume: for fibres with 8 wt.%
of carbon (based on the TGA data), the calculated carbon
volume is ~ 30 vol.%. This value justifies considering the final
fibres as a composite Ag/carbon material. On one hand, the
carbon serves as a physical barrier between the Ag particles that
prevents the Ag from aggregating and undergoing aggressive
sintering. On the other hand, the carbon may cover the active
sites on Ag surface and lower its catalytic performance in the
PMO process. Based on the TGA-DTA results above, the
heating profile included slow heating rates and 120°C and
300°C soaks for 30 and 6 min respectively, The morphology of
a composite fibre is presented in Fig. 6 a-d, where Ag particles
are coated and mostly separated by uniformly distributed
carbon. As mentioned above, the carbon residue of ~ 8 wt.% at
650°C, was effective in maintaining exceptionally small Ag
particle size, in the 50 nm range as seen in Fig. 6d.
Fig. 6 HRSEM images of composite Ag/carbon fibre mats after sintering at 650°C.
The carbon residue and the degree of Ag particle sintering
can be controlled with heating temperature and duration. It is
well known, that increase of either of these parameters results
in more active sintering. The TGA results in Fig. 5 for heating
in Ar clearly showed that carbon content in fibres decreased
with temperature. The morphology of the composite "white"
fibres obtained at different temperatures after a 1 h soak at 450
- 650 °C (see profile in Fig. 1b) is shown in Fig. 7.
Fig. 7 HRSEM images of composite Ag/carbon mats at sintering temperatures of
a) 450°C, b) 550°C and c) 650°C.
The temperature range was chosen from TGA data (Fig. 5) and
it corresponds to the stage when decomposition and
carbonization of polymer is completed. The two main
observations from these images are as follows: a) the absence
of Ag aggregates usually formed at high temperatures; b) a
similar average particle diameter of 110 nm over a significant
temperature range. It is direct evidence of the positive role of
the carbon as inhibitor of aggressive sintering and
agglomeration of the Ag particles. In the same time, the fibrous
structure with poorly sintered Ag particles was preserved, by
virtue of the carbon as good binder in the composite. Finally,
the composite fibre mats were found to be more flexible and
more robust during their handling.
Ag fibres - PMO catalytic activity
Methanol conversion and total selectivity towards
formaldehyde increased as a function of the reaction
temperature as shown in Fig. 8a.
Fig. 8 The PMO catalytic activity of “white” Ag mats after 2 h firing at 300°C in
1.5% O2: a) activity vs. temperature and b) activity at 550°C vs. the PMO run
number.
A sharp increase of the conversion and selectivity values
was measured in 250-500°C range, reaching a plateau above
550°C. The second run typically showed improved performance
compared to the first run, with the results slightly decreasing
during later runs as seen in Fig. 8b. This pattern can be
attributed to primary catalyst activation during the first cycle of
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the reaction. The maximal total selectivity and conversion of
82.4% and 94.2% respectively were found for 2nd and 3rd runs.
A slow deactivation process started during the subsequent runs
(Fig. 8b). The main contribution to catalyst deactivation
appears to be the sintering, grain growth and densification of
the fibrous structure.
The performance of prepared catalysts was compared in
terms of space-time yield (STY) which is defined by the mass
of formaldehyde produced in 1 hour (g h-1) per mass of Ag (g)
in the catalyst, as expressed by Eq. 3:
Eq. 3 ��� ����� !"#$%&#$
�'(∙*+,-./
The STY represents simultaneously the joint effect of
WHSV, conversion and selectivity and is therefore a practical
and convenient parameter for comparison of different catalysts
normalized by their weight. The effect of firing time at 300°C
on STY is shown in Fig. 9 for the for Ag mats during the
second PMO run. The optimal firing time was found to be 2
hours corresponding to an STY maximum of 56 h-1 in the PMO
process.
Fig. 9 The STY of Ag metal fibres at the second PMO run vs. the sintering soak
time at 300°C.
The effect of the PMO process on the morphology of the Ag
mats is seen in Fig. 10. The initial "white" mats morphology
(Fig. 10a), shows that the fibrous structure was retained after
firing for 1 hour at 300°C in 1.5% O2. However, during six
PMO runs the fibrous structure is completely transformed into a
porous yet strongly aggregated material with large primary
particles (Fig. 10b). Basic particle size is 5 to 15 µm that are
fused into a porous network. The formation of large connected
particles during the PMO runs is a result of the close proximity
of the Ag nanoparticles to each other in the original Ag mats,
which enables the massive diffusion and particle aggregation
seen in Fig. 10b.
To study the drastic change in morphology of the Ag fibre
mats during the PMO process (seen in. Fig. 10), we changed the
firing time of the soak at 300oC during the initial heat treatment
in 1.5% O2. The morphology of the Ag mats after 2 h and 5 h
firing is seen in Figs. 10c and 10e, respectively. The fibre
structure was lost in both cases, yet the particles formed after 2
h of firing are considerably smaller and more compact than
their 5 h analogue.
Fig. 10 The effect of firing time at 300°C in 1.5% O2 and PMO runs on the fibre
mat morphology : a) “White” mat after 1 hr and b) same mat after 6 PMO runs,
c) “White” mat after 2 hrs and d) same mat after 2 PMO runs, e) “White” mat
after 5 hrs and f) same mat after 2 PMO runs.
The grains in 5 h sample (Fig. 10e) have transformed into a
porous structure with particles of ~ 2-8 µm and relatively small
(20-30 µm) prolonged aggregates of 4-6 particles. The effect of
the PMO process on the two initial "white" mat structures is
shown in Figs. 10d and 10f. The structure formed after 5 h
firing limits the diffusion of the Ag during the PMO process
and leads to a lower sintering effect. So although some
aggregation is seen in Fig. 10f, the structure is relatively stable
compared to Fig. 10e.
The sample sintered for 2 hours at 300°C soak (which was
shown to be optimal in terms of STY) possesses high porous
mix structure: the fibres, the particles of 1-4 µm and small
aggregates of 2-3 particles (Fig. 10c). This structure has
transformed during the PMO reaction into a highly porous non-
fibrous morphology with relatively small both grains and linear
aggregates of 4-5 particles (Fig. 10d). It is important to point
out that all structure elements of this material are significantly
smaller compared to those in 5 h analogue described above.
The larger contact area arising from the smaller aggregates in
the 2 h case (Fig. 10d) can explain the better catalytic
performance as evidenced by the larger STY (Fig. 9). The
lower performance of the mats sintered with soak at 300°C for
less than 2 h can be attributed also to polymer residues. They
might hinder the reaction in few different ways: decreasing the
catalyst active surface area, consuming the oxygen from the
reagents mixture, generating local overheating and thus
promoting undesired grain growth.
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View Article OnlineDOI: 10.1039/C4CY01341G
ARTICLE Journal Name
8 | J. Name., 2012, 00, 1-3 This journal is © The Royal Society of Chemistry 2012
Composite Ag/carbon fibres - PMO catalytic activity
In the process with composite Ag/carbon catalyst, the
selectivity and conversion as a function of reaction temperature
are shown in Fig. 11 a,b. The general trends are very similar to
those observed in the metal fibres seen in Fig. 8 a,b with a
sharp rise in conversion and selectivity above 250°C and
activity stabilization after the first run.
Fig. 11 The PMO catalytic activity of “white” Ag/carbon mats after 1 h firing at
550°C in Ar: a) activity vs. temperature and b) activity at 550°C vs. the PMO run
number.
The optimal catalyst thermal treatment condition was found by
measuring the STY as a function of temperature. As shown in
Fig. 12, a sharp maximum in the STY of 64 h-1 was achieved
with mats sintered in Ar for 1 h at 550°C.
To explain the STY behaviour in composite fibres the
complex effect of carbon on the catalytic performance must be
discussed. The direct and immediate effect of carbon is to block
the active sites on some of the Ag surface and lower the
catalytic performance. Another effect is the possible carbon
exothermic oxidation in the reaction mixture, lowering effective
reactant concentration and leading to local overheating.
Fig. 12 Composite Ag/carbon fibre mats STY vs. the sintering temperature.
A third important effect of carbon is maintaining a physical
barrier between Ag particles in fibres, preventing aggregation
and sharp particle growth and, in turn, delaying the sintering-
related deactivation. Surely, other effects of carbon in the
vicinity of the Ag catalyst grains such as the "adsorb and
shuttle"19 or “spillover”20,21 mechanisms may play a role here as
well. These multiple opposing effects give rise to the maximum
in STY as function of sintering temperature seen in Fig. 12. As
seen in the TGA data for fibres heated in Ar (Fig. 5), the mass
monotonically drops with temperature above 450°C due to
carbon loss. Therefore, as the amount of carbon in composite
mats decreases with increasing sintering temperature, more
active Ag sites are exposed for catalysis, potentially leading to
an increase in catalytic activity. So what causes the sharp drop
in the STY values from 64 h-1 at 550°C to 35 h-1 at 650°C in
Fig. 12? This phenomenon may be due to the dynamics of pore
formation and their behaviour during thermal treatment and
subsequent PMO process. The morphology of the Ag/carbon
composite fibres after 2 PMO runs is shown in Fig. 13 for
fibres that were sintered at 450°C, 550°C and 650°C.
Fig. 13 HRSEM images after 2 runs of PMO of composite Ag/carbon fibre mats
treated at: a) 450°C, b) 550
°C and c) 650
°C.
Unlike the previous case of Ag metal fibres, where the original
fibre structure was totally lost in the PMO process (Fig. 10),
remnants of the original fibre structure are clearly visible in this
case due to the carbon acting as a sintering inhibitor (Fig. 7). As
the gaseous products of polymer decomposition evolve from
the treated fibres, a porous carbon mass is created. So long as
there is sufficient carbon to prevent the Ag massive particle
growth and aggregation, the STY increases with increased
exposure of the Ag catalytic centres. However, as the
temperature rises, the carbon content may drop below a critical
level, where the Ag particles are free to grow. This in turn can
lead to decreased porosity and smaller exposed surface that
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Journal Name ARTICLE
This journal is © The Royal Society of Chemistry 2012 J. Name., 2012, 00, 1-3 | 9
give rise to an overall lower catalytic activity (Fig. 12) at higher
temperatures. Clearly, the structure obtained after PMO of the
650°C mat (Fig. 13c), is more dense and compact than that from
the mats treated at lower temperatures.
The weight hourly space velocity (WHSV) measurements
(Fig. 14a) were conducted in the 400-550°C temperature range
during the second run.
Fig. 14 Comparison of the a) WHSV and b) STY of CR@Ag powder
16, Ag deposited
on TiO2 nanofibres16
, 1.67 % CR@Ag deposited on TiO2 nanofibres16
and
Ag/carbon fibre mat sintered at 550°C.
Methanol conversions were kept constant at intermediate 70%
(at 400°C) and close to maximal 95% (at 500°C and 550°C)
values by varying the feed rates. The WHSV values achieved
were 140 h-1 for 95% conversion at 500°C, 370 h-1 for 70%
conversion at 400°C and, finally, 540 h-1 for 95% conversion at
550°C and flow rate of initial gas mix of 807.9 normal ml·min-1
(mcat=0.045 g). Comparison of these results with submicron
powder of CR@Ag, investigated earlier17,18, shows a significant
advantage of composite Ag/carbon fibre mats, with 17.5-22.5
fold increase in WHSV. The corresponding STY values were
97.5 h-1 for 95% conversion at 500°C, 129 h-1 for 70%
conversion at 400°C and, finally, 386 h-1 for 95% conversion at
550°C. These values are also significantly higher in comparison
to powder-like catalyst (Fig. 14b).
The comparison of achieved WHSV and STY using
Ag/carbon mats as catalyst with values recently published for
Ag/TiO2 and CR@Ag/TiO2 nanofibres16 is also presented in
Fig, 14a,b. While the results obtained in the present work are
comparable with those in16 at temperatures 400-500°C, the
considerable advantage of Ag/carbon mats was found for
550°C: STY of 386 h-1 vs 320 h-1 and 273 h-1 for doped silver
and undoped silver deposited on TiO2 nanofibres. In addition, it
should be noted that the fabrication technique using
electrospinning is much simpler and more scalable than the
nanofibres preparation in the above publication16.
Finally, all above STY values (97.5, 129, 386 h-1) in
temperature range of 400 - 550°C were found higher than a
corresponding STY value of 23 h-1 calculated from a reported
results for the industrial process conducted at 700°C with
commercial Ag powder catalyst22. This significant difference is
probably due to the larger Ag surface accessible for catalysis in
the present work.
Conclusions
This paper summarizes the synthesis of Ag metal fibres and
composite Ag/carbon fibres by electrospinning and their
catalytic activity in a partial methanol oxidation (PMO) process
to produce formaldehyde. Uniform mats, containing fibres with
300-600 nm in diameter were prepared from a stable
suspension of Ag NP/AgNO3/PVA/water/ethanol. Thermal
decomposition of the "green" mats was studied by thermal
analysis (TGA/DTA) and mass spectrometry (MS) in different
atmospheres: inert (Ar), strongly oxidizing (air) and mildly
oxidizing (Ar/1.5% O2). Based on the thermal analysis data,
specific heat treatment profiles were devised to obtain metallic
Ag fibre mats as well as composite Ag/carbon fibre mats that
were subsequently used in the catalytic testing.
Metallic fibre mats were obtained under mild oxidation
conditions at an optimal temperature of 300°C at various
soaking times. The morphology of the Ag mats changed
dramatically with time from highly porous with sub-micron
fibres at 1 hour at 300°C, to porous network of fused Ag
particles at 2 hours and finally, to a strongly sintered large Ag
aggregates at 5 hours. The highest catalytic activity at methanol
WHSV in the range of 60-90 h-1 was found for samples treated
for 2 hours: the methanol conversion and selectivity towards
formaldehyde were 94.2% and 82.4%, respectively. A large
space time yield (STY) of 56 h-1 was obtained.
Alternatively, thermal treatment in Ar was used to prepare
the composite Ag/carbon fibrous mats. For treatment in inert
atmosphere, the maximal sintering temperature was varied from
350 to 650°C, for 1 h. The residual carbon content in composite
fibres was on the order of 10 wt.%, consistent with the TGA
data. The presence of uniformly distributed carbon prevented
aggressive sintering during heat treatment and PMO process.
The composite mats sintered at 550°C showed the highest
catalytic activity. The achieved WHSV values were 140 h-1 for
Page 9 of 11 Catalysis Science & Technology
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ARTICLE Journal Name
10 | J. Name., 2012, 00, 1-3 This journal is © The Royal Society of Chemistry 2012
95% conversion at 500°C, 370 h-1 for 70% conversion at 400°C
and, finally, 540 h-1 for 95% conversion at 550°C. The
corresponding STY values of 97.5 h-1, 129 h-1 and 386 h-1 at the
above three temperatures.
These results demonstrate a considerable improvement over
the previously published laboratory results obtained with
submicron Ag powder17,18, undoped and doped Ag
nanoparticles deposited on the TiO2 nanofibres16 as well as
commercial Ag powder catalyst22.
In summary, we demonstrated the effectiveness of
electrospinning technology in producing highly active catalysts
containing Ag and composite Ag/carbon fibres for oxidation
processes as demonstrated on partial methanol oxidation.
Acknowledgements
Supported by a Tashtiot Infrastructure grant of the Israel
Ministry of Science (Grant 3-6474), and by joint grant from the
Committee for Planning and Budgeting of the Council for
Higher Education and by the Center for Absorption in Science
(Israel) under the KAMEA program. Authors acknowledge the
support of Russell Berrie Nanotechnology Institute (Technion,
Israel), the Grand Technion Energy Program (GTEP) and the
Adelis Foundation for renewable energy research.
Notes and references * Department of Chemical Engineering, Technion –Israel Institute of
Technology, Haifa, 32000, Israel. Fax: +972-4- 8295099, Tel: +972-4-
8292008, E-mail: [email protected].
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View Article OnlineDOI: 10.1039/C4CY01341G
A feasibility of electrospinning in producing of highly active Ag and Ag/carbon fibres based
catalysts is demonstrated in methanol partial oxidation process (PMO).
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View Article OnlineDOI: 10.1039/C4CY01341G