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Electrodeposition of palladium nanoparticles at the liquid�/liquidinterface using porous alumina templates
Mark Platt a, Robert A.W. Dryfe a,1,*, Edward P.L. Roberts b
a Department of Chemistry, University of Manchester Institute of Science and Technology, P.O. Box 88, Manchester M60 1QD, UKb Department of Chemical Engineering, University of Manchester Institute of Science and Technology, P.O. Box 88, Manchester M60 1QD, UK
Received 1 October 2002; received in revised form 10 April 2003; accepted 10 April 2003
Electrochimica Acta 48 (2003) 3037�/3046
www.elsevier.com/locate/electacta
Abstract
Alumina membranes, with mean pore diameters of 100 nm, have been used as templates to control the electrodeposition of
palladium. Deposition occurs at the polarised water�/organic interface, leading to the formation of nanoparticles. The particles are
formed at the mouth of the alumina pores, the locus of their formation being dictated by the position of the organic�/water interface.
It is shown that the relative position of the liquid phases with respect to the alumina is controlled by the surface wetting properties of
the liquids, rather than gravity. This in turn controls the interfacial position and hence the size of the particles deposited. The
presence of the alumina membrane prevents agglomeration. Electrochemical and electron microscopy data are presented in support
of this proposed deposition mechanism.
# 2003 Elsevier Ltd. All rights reserved.
Keywords: Liquidjliquid interface; Deposition; Nanoparticle; Template; Controlled growth
1. Introduction
The controlled production of materials on micrometer
and sub-micrometer length scales is currently the focus
of intense scientific interest [1,2]. The physical properties
and chemical reactivity of small metallic nanoparticles
can become functions of particle size [3], while the high
surface area to volume ratio leads to important applica-
tions in fields such as catalysis. An important issue is the
‘‘protection’’ of nanoparticles, to their prevent agglom-
eration to form larger structures [4]. Electrochemical
methods have been employed widely for the production
of micro and nanostructured materials, such as alumina
from the anodic oxidation of aluminium [5,6]. Electro-
chemical deposition has also been used to fabricate
controlled metallic micro and nanostructures by using
materials such as porous g-alumina as overlayers on
electrode surfaces, where the dimensions of the porous
overlayer control those of the resultant deposits [7]. This
so-called electrochemical ‘‘templating’’ method has been
applied to the production of various substrates, includ-
ing silver [8], gold [9], cadmium [10] and conducting
polymers [11,12], while the templates employed have
been extended to other porous materials such as ‘‘track-
etched’’ polycarbonate membranes [7]. Non-electroche-
mical methods, such as pulsed laser deposition, have
also been applied to the template synthesis of nanos-
tructured materials [13].
An advantage of the use of porous alumina as a
template is that the alumina may be dissolved readily
[10], to free the deposited nanoparticles. Rather than
depositing nanostructures consisting of a single mate-
rial, the template method has also been applied to the
sequential deposition of multi-metallic layers, thus
creating ‘‘barcodes’’ designed for use in biological
assaying [14]. The obvious technological applications
of nanostructured metals are enhanced by the ability to
deposit metals within alumina templates, since alumina
is widely used as a support for metal particles in
heterogeneous catalysis [15].
Beyond the technological applications of the electro-
deposition of nanostructures, there is also interest in the
fundamental aspects of this phenomenon since tem-
* Corresponding author. Fax: �/44-161-200-4559.
E-mail address: [email protected] (R.A.W. Dryfe).1 ISE member.
0013-4686/03/$ - see front matter # 2003 Elsevier Ltd. All rights reserved.
doi:10.1016/S0013-4686(03)00373-6
plated deposition allows the process to be studied under
‘‘high resolution’’ conditions, giving insights into me-
chanistic aspects of electrodeposition. Electrodeposition
presents a unique way to follow the nucleation andgrowth of structures as a function of driving force [16],
however, the initial stages of electrodeposition on solid
substrates are often controlled by strong interactions
between the nucleated nanoparticles and the substrate,
manifested as under-potential deposition and epitaxial
growth [17,18]. Electrochemical deposition can also be
performed at the interface between water and an
immiscible organic phase. Efrima and co-workers [19]have reported dendritic structures formed from silver
deposition, induced by bringing an electrode close to the
water�/dichloromethane interface.
A more readily controllable approach is the direct
polarisation of the water�/organic interface by applica-
tion of a variable potential difference using methodol-
ogy that has become well established [20], as shown
schematically in Fig. 1. Interfacial electron transfer canbe induced (see Fig. 1(a)) and, if one of the couples is a
metal precursor, the electrodeposition of metallic parti-
cles at the water�/organic interface can ensue. Deposi-
tion of copper [21], gold [22] and palladium [23,24]
particles using this approach has been reported. The
lack of a solid substrate and associated preferential
nucleation sites offers a unique way to observe the
relationship between the driving force for particlegrowth and the form of the resultant particles. However,
the lack of solid substrate also means that the particles
deposited at the water�/organic interface are mobile and
thus tend to agglomerate [24], which complicates the
analysis of the form-driving force relationship.
In a recent preliminary communication [25], we have
reported initial results from a novel strategy developed
for nanoparticle electrodeposition. Essentially, thisstrategy involves the combination of the template and
water�/organic deposition approaches discussed above:
we have applied this method to the technologically
important formation of Pd nanoparticles dispersed in a
porous g-alumina substrate, a system of relevance in
catalysis and gas separation [15,26]. We are unaware of
any previous reports of palladium nanoparticle electro-
deposition using the membrane-templated approach.The application of the template approach to the
water�/organic interface is depicted schematically in
Fig. 1. The locus of particle deposition, the water�/
organic interface, is retained at the mouth of the
alumina pores and deposition is induced by application
of an interfacial potential difference. The preliminary
report demonstrated that deposition of discrete Pd
nanoparticles, with dimensions controlled by the radiiof the membrane pores (mean value of 50 nm), could be
achieved [25]. Here, more detailed findings are pre-
sented, which fully demonstrate this route to electro-
deposition of nanosized metal particles, combining the
electrochemical data under various conditions with
SEM and TEM analysis of the deposited materials.
2. Experimental
Voltammetric experiments were performed using a
PC-controlled EG&G Model 273 potentiostat (Prince-
ton Applied Research Corp., Princeton, NJ, USA)
operating in four-electrode mode. The aqueous refer-
ence electrode was a silver�/sulfate wire and the organic
reference electrode was a silver�/silver chloride wire,
both produced in-house by oxidation of a 1 mm
diameter silver wire in the appropriate electrolyte. Allpotentials are reported with respect to these reference
electrodes. The counter electrodes were constructed in-
house by spot welding an approximately 1 cm2 area of
platinum gauze (Advent, Eynsham, UK) to a length of
platinum wire (Advent). The standard current conven-
tion for liquid�/liquid electrochemistry was followed;
namely positive currents correspond either to the
transfer of a positive charge from the aqueous to organicphase, or of a negative charge in the reverse direction.
Commercial g-alumina membranes, with nominal mean
pore diameter of 100 nm (Whatman International Ltd,
Maidstone, UK) were sealed to a 5 mm inner diameter
glass tube with a silicone sealant (RS components,
Corby, UK). Membranes were washed in water before
use. Under some conditions (see below) the membranes
were also pre-treated with trimethylchlorosilane (Al-drich Co., Gillingham, UK) by soaking in the pure
liquid for 12 h prior to experimentation, but were
otherwise used as-received. Relevant properties of the
membranes employed are summarised in Table 1. It
should be noted that the pore diameter of the mem-
branes is not uniform along the length of the pore: the
value quoted in Table 1 is the ‘‘active’’ diameter, which
determines the membrane’s use in filtration. Only thefinal 0.5 mm length of the pore is of this diameter, the
remaining ‘‘support’’ layer is two to three times larger
than the diameter of the active pore [27,28].
The cell was set up as shown in Fig. 1. The aqueous
phase comprised of ammonium tetrachloropalladate
Table 1
Data in column 1 obtained from manufacturer (Ref. [27]), data in
column 2 quoted in Ref. [28]
Property Column 1 Column 2
Mean pore diameter of ‘‘active’’ layer
(cm)
1.0�/10�5 8.3�/10�6
Standard deviation of pore diameter
(cm)
Not avail-
able
9/2.5�/
10�6
Pore density (cm�2) 1.0�/109 5.1�/109
Pore fraction 0.40 0.29
Total thickness (cm) 6.0�/10�3 6.0�/10�3
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/30463038
(supplied by Fluka, Gillingham, UK), at concentrations
between 1�/10�3 and 2�/10�3 mol dm�3, lithium
chloride (5�/10�2 mol dm�3, Lancaster Synthesis,
Morecambe, UK) and lithium sulfate (5�/10�2 mol
dm�3, Aldrich, Gillingham, UK), dissolved in water
with a resistivity of 18 MV cm obtained from a Milli-Q
purification system (Millipore, Watford, UK). The
liquid�/liquid interface was formed with water and 1,2-
dichloroethane (DCE; HPLC grade, obtained from
Lancaster Synthesis). The organic electrolyte, bis(tri-
phenylphosphoranylidene) ammonium tetrakis(penta-
fluoro)phenylborate (BTPPA TPBF20), was prepared
according to a reported metathesis procedure [29] from
equimolar amounts of bis(triphenylphosphoranylidene)
ammonium chloride (BTPPACl; Lancaster, 97%) and
lithium tetrakis(pentafluoro)phenyl borate (Boulder
Fig. 1. (a) Schematic of the deposition at the liquid�/liquid interface: (i) electron transfer at the liquid�/liquid interface; (ii) metal deposition via
electron transfer at the liquid�/liquid interface and (iii) templated metal deposition at the liquid�/liquid interface. (b) The cell configurations used for
metal deposition at the alumina-templated liquid�/liquid interface: the upper cell (stable arrangement) has the organic phase above the aqueous
phase; in the lower cell (unstable arrangement), the positions of the phases are reversed.
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/3046 3039
Scientific, Boulder, CO, 98% pure). The concentration
of BTPPA TPBF20 in the DCE phase of all cells was 5�/
10�3 mol dm�3. During deposition experiments butyl-
ferrocene (BuFc, Lancaster, 98%) was added in concen-
trations between 5�/10�4 and 1�/10�3 mol dm�3. The
reference electrode for the organic phase was formed by
placing the silver�/silver chloride wire in an aqueous
solution of BTPPACl and lithium chloride (1�/10�3
and 1�/10�2 mol dm�3, respectively). The generic
composition of the cell is summarised above (Cell 1),
where the double bar denotes the polarised interface,
and the location of the alumina membrane:
The cell configurations employed are shown schema-
tically in Fig. 1(b). The upper configuration involved
placement of the DCE phase on the upper side of the
alumina membrane, with the higher density aqueous
phase on the underside. Due to the hydrophilic nature of
the alumina surface, this arrangement was stable, with
the gravitational instability being countered by the
surface effects. The alternative configuration (the lower
one in Fig. 1(b)) inverted the placement of these phases:
the aqueous phase quickly traversed the alumina
membrane, making the establishment of a stable
liquid�/liquid interface difficult. Under these conditions,
the rate of ingress of the aqueous phase could be
minimised by the treatment of the alumina surface
with trimethylchlorosilane. Electrochemical experiments
were performed at ambient temperature (between 20 and
25 8C). Certain experiments (see below) were performed
using a Grant GD100 water bath (Grant Instruments,
Cambridgeshire, UK) at 25 8C, which was able to
control the cell temperature to 9/0.1 8C.
Following electrodeposition, the membranes were
separated from the cell and affixed to 12 mm diameter
imaging studs with Araldite adhesive (Ciba-Geigy,
Cambridge UK), for analysis via scanning electron
microscopy (SEM) and energy dispersive X-ray analysis
(EDX) using a Philips XL30 Field Emission Gun SEM
and a Philips SEM525 fitted with an EDX DX4 system.
SEM images were also taken of the freed Pd particles,
following dissolution of the alumina over a 72 h period,
by dropping a continuous stream (approximately 0.2
cm3 s�1) of 1 M HCl over the membrane. In this case,
the membranes were placed on top of a polyester filter
membrane (Poretics, Livermore, CA), also with nominal
pore diameters of 100 nm, to retain the liberated
nanoparticles. Transmission electron microscopy
(TEM) was performed using a JEOL model JEM 2000
FX on Pd-loaded membranes, which had been pre-
viously sliced transversely to give sub-micron cross-
sections using an Ultracut Microtome (Leica Micro-
systems GmbH, Wetzlar, Germany) [7].
3. Results and discussion
In the absence of a membrane at the water�/DCE
interface, cyclic voltammetry of Cell 1 displayed theresponse denoted ‘‘a’’ in Fig. 2(a), when no organic
phase BuFc was present. A capacitative current region is
delimited by the onset of current corresponding to
background electrolyte transfer at �/0.25 and �/0.90
V. Introduction of the ferrocene derivative, which
functions as an electron donor, led to the observation
of a charge transfer at approximately �/0.7 V. On the
basis of earlier reports [23,24], the current observed isattributed to reduction of the aqueous phase palladinate
salt by the ferrocene derivative. Metallic palladium is
thus formed by electron transfer at the water�/DCE
interface, according to Eq. (1):
PdCl2�4 (aq)�2BuFc(DCE)
0 Pd0�4Cl�(aq)�2BuFc�(DCE) (1)
The palladium deposits were visible, following pro-longed electrolysis, as dark irregular particles.
The experiment was repeated with the g-alumina
‘‘templating’’ the water�/DCE interface, using the upper
(stable) configuration of the cells illustrated in Fig. 1(b).
Under these conditions, the voltammetry labelled ‘‘b’’ in
Fig. 2(a) was observed, with a characteristic nucleation
loop seen during the first few voltammetric runs at
positive potentials [23]. On prolonged electrolysis, thenucleation loop was swamped by an irreversible process
(response ‘‘c’’ in Fig. 2(b)). The results are consistent
with an electrodeposition process, with palladium
growth occurring at or near the pores of the alumina
membrane. Chronoamperometry was also performed at
the alumina-templated water�/DCE interface. A typical
response is shown in Fig. 2(c), which once again shows a
characteristic peaked response, indicative of a nuclea-tion event limiting the current at short times.
SEM images were obtained of the Pd-loaded mem-
branes, and compared against their ‘‘blank’’ (i.e., not
exposed to Pd) counterparts under a variety of condi-
tions. Figs. 3(a) and (b) show SEM images of the blank
alumina membranes, both face on and side on, the latter
obtained by fracturing the membrane. The images show
that the alumina surface is rough on the approximately10 nm scale, and suggest that the pore diameter and
distribution are in reasonable agreement with previously
quoted values (listed in Table 1). Also evident are white
spots of between 100 and 300 nm diameter, which
previous reports have identified as aluminium oxide
precipitate [30]. EDX analysis (Table 2) confirms that
the blank sample contains only Al, O and relatively low
amounts of P and S, the latter from traces of the acidsused in the oxidative preparation of the membranes [6].
The side-on image also clearly shows the transition of
the pores between the support and narrower active
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/30463040
layers, although the damage to the pores induced by the
fracturing process is also evident.
Fig. 4(a) shows an SEM image of a membrane
following Pd deposition through an initial electrolysis
at the water�/DCE interface. By comparison with Fig.
3(a), which is on the same scale, grey shadows are visible
within approximately 5% of the pores, suggesting that
some Pd deposition has occurred. Importantly, the sizes
of the grey patches are of the order of the size of the
pores (mean diameter of 100 nm) and the underlying
structure of the alumina pores is always visible, indicat-
ing that deposition of approximately 100 nm particles
occurs at the mouth of the pores. The presence of
palladium within the membrane was confirmed by EDX
Fig. 2. (a) Initial cyclic voltammetric response obtained from Cell 1 at a scan rate of 0.1 V s�1. The organic phase was uppermost in the cell and x�/
1�/10�3 mol dm�3, where a: y�/0 and b: y�/5�/10�4 mol dm�3. (b) Cyclic voltammetric response of Cell 1 under the conditions of (a), but
following nine previous cycles with a: y�/0 and c: y�/5�/10�4 mol dm�3. (c) Initial chronoamperometric response of Cell 1, under the conditions of
(a), with applied potential difference stepped from �/0.45 to �/0.90 V.
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/3046 3041
(see Table 2). Prolonged electrolysis of the alumina-
modified water�/DCE interface, using a higher concen-
tration of organic phase electron donor, led to the
deposits such as those shown by SEM in Fig. 4(b). Most
of the pores appear to contain palladium, from theresolution of the SEM image (approximately 20 nm),
although close inspection shows that the underlying
structure of the alumina template is still apparent. A
side-on image of a fractured membrane would be
desirable to assess the depth of the particles deposited
within the pores. Attempts to obtain ‘‘side-on’’ SEM
images of the Pd-loaded membranes, comparable to that
shown in Fig. 3(b), were unsuccessful, in that the imageswere identical to those of the blank membranes. This is
presumably because the Pd nanoparticles were not
retained within the pores following the crude fracturing
process: this observation suggests that the interaction
between the alumina surface and the deposited particles
may be relatively weak.
An alternative approach to imaging was pursued by
using a microtoming method to prepare thin samples ofthe Pd-loaded membranes, to permit side-on imaging by
TEM. Higher resolution TEM images of Pd-loaded
alumina membranes are shown in Figs. 4(c) and (d).
Although the microtoming process has created more
local damage to the porous alumina structure, Pd
deposits are clearly visible in both images at the mouth
of the membrane pores. It is clear that the Pd present
within a given pore is discrete from metal withinneighbouring pores, as suggested by the SEM images.
Moreover, the depth of the Pd deposits (of the order of
100 nm) is also visible from TEM. Once more, EDX was
employed to confirm the presence of palladium. The
relative elemental abundances are given in Table 3. Note
that a higher percentage of palladium is observed when
compared against the EDX data of the SEM sample
(Table 2): the TEM sample has been subject to a moreprolonged electrolysis and the microtoming produces a
thinner sample, which is likely to contain a higher
percentage of palladium. It is difficult to conclude too
much about the form of the electrodeposited Pd, due to
Fig. 3. (a) Face-on SEM image of blank (i.e., prior to deposition) g-
alumina membrane. The scale bar is shown on the image. (b) Side-on
SEM image of fractured blank membrane.
Table 2
Composition, by weight percentage and by atom percentage of the
membranes shown in Fig. 4(b), as determined by EDX of the SEM
images
Sample Element Weight% Atom%
Blank membrane Oxygen 29.86 42.15
Aluminium 63.07 52.79
Phosphorus 3.04 2.22
Sulphur 4.04 2.84
Palladium-loaded membrane Oxygen 18.12 31.67
Aluminium 55.78 57.79
Phosphorus 2.56 2.31
Sulphur 3.37 2.94
Palladium 20.17 5.3
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/30463042
Fig. 4. (a) SEM image of alumina membrane following an initial deposition of palladium, under the conditions of Fig. 2(a), following five cyclic
voltammetric scans between �/0.30 and �/0.90 V at a scan rate of 0.1 V s�1. (b) SEM image of membrane following prolonged deposition of
palladium, with x�/1�/10�3 mol dm�3, y�/1�/10�3 mol dm�3, applying a potential difference of �/0.90 V continually for 1 h. (c) Side-on TEM
image of palladium-loaded sample, following exposure to conditions of (b). (d) Higher magnification of TEM image shown in (c).
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/3046 3043
the damage likely to have been induced by microtoming.
However, the appearance of the highest resolution TEM
image (Fig. 4(d)), suggests that the Pd deposits may not
be completely solid and, in fact, the Pd may show some
nanometre-scale porosity, particularly visible at the
outer edge of the particles.
SEM images were also taken of the Pd particles
obtained following chemical dissolution of the alumina
template. The Pd-loaded membrane was supported on a
polyester membrane (see Section 2) to retain the
liberated nanoparticles. Fig. 5 shows the resultant Pd
deposits, retained on the polyester membrane. Although
some agglomeration of the Pd nanoparticles is likely to
have occurred in solution following template dissolution
[24], it is clear from the magnification of the Pd deposits
shown in the inset, that some spherical structure is
retained in the particles, visible as ‘‘bulbs’’. The approx-
imate diameter of these bulbous intergrowths is 100 nm,
confirming that the dimensions of the alumina template
control those of the resultant nanoparticles, and hence
suggesting that growth does take place at the mouth of a
pore.A comparison was made between the form of the Pd
deposits obtained at the alumina-templated water�/DCE
interface, and those obtained at the bare water�/DCE
interface. A representative SEM image of Pd deposits
from the latter interface is shown in Fig. 6(a). Once
more, agglomerated particles are obtained, although
there is no single characteristic dimension of the
Table 3
Composition, by weight percentage and by atom percentage of the
membranes shown in Fig. 4(b), as determined by EDX of the TEM
images
Sample Element Weight% Atom%
Palladium-loaded membrane Oxygen 34.68 63.37
Aluminium 23.11 25.05
Palladium 42.21 11.60
Fig. 5. SEM image of palladium particles retained, using a polyester
membrane, following dissolution of alumina. The palladium was
prepared using the conditions of Fig. 4(b): the inset shows a
zoomed-in segment from the centre of the image.
Fig. 6. (a) SEM images of palladium particles obtained on electro-
deposition at the bare liquid�/liquid interface. Concentrations were
(see Cell 1) x�/1�/10�3 mol dm�3, y�/5�/10�4 mol dm�3. Twenty-
five cyclic voltammetric scans were performed between �/0.30 and �/
0.90 V at 0.1 V s�1. The deposited palladium was visible to the eye,
following this period. Palladium particles were collected by suction and
washed by filtration using the polyester membrane to retain the
particles. (b) SEM image of palladium deposited under thin layer
conditions, by inverting the order of the solution phases (see Fig. 1(b)).
The concentrations were (see Cell 1) x�/1�/10�3 mol dm�3, y�/5�/
10�4 mol dm�3. Fifteen cyclic voltammograms were performed
between �/0.30 and �/0.90 V at 0.1 V s�1.
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/30463044
spherical structures that compose each agglomerate.
Some agglomerates (e.g., in the far left of the image)
contain structures approximately 50 nm in diameter,
while those in the right of the image are closer to 200 nm
in diameter. The observations support the conclusion
previously inferred that agglomeration, following de-
position, affects particle growth at the liquid�/liquid
interface [24], and thus underline the utility of the
templated approach to deposition reported herein.
Moreover, these images are the first reported, to our
knowledge, of palladium nanoparticles grown at theliquid�/liquid interface: a previous report included a low
resolution SEM image of gold deposited at the water�/
DCE interface [22].
Palladium deposition was also performed in cells
where the positioning of the organic and aqueous phases
has been inverted (see Section 2 and the lower cell of
Fig. 1(b)). In such cases, a steady flow of the aqueous
phase through the alumina membrane was observed,making deposition experiments impossible. However,
prior treatment of the alumina with trimethylchlorosi-
lane rendered the membrane surface more hydrophobic
and slowed the rate at which the aqueous phase
traversed the membrane. Deposition experiments were
performed under these conditions: a typical SEM image
of deposited palladium is shown in Fig. 6(b). It is clear
that the palladium has ‘‘grown out’’ from the aluminasurface: the underlying structure of the alumina (and its
consequent influence on the deposited metal) has been
lost, hence there is no regularity in the dimensions of the
metallic growth. The similarity between the deposits
obtained in Fig. 6 suggests that the membrane has had
no influence on palladium growth in Fig. 6(b). The form
of the metal in the case of the inverted alumina-
templated interface implies that the aqueous phase hastraversed the membrane, albeit slowly, and formed a
‘‘thin layer’’ between the underside of the membrane
and the organic phase, from where deposition has
proceeded.
A final observation is that the intermediate stage of
templated deposition using the standard cell (upper cell
in Fig. 1(b)), between the initial growth pictured in Fig.
4(a) and the prolonged electrolysis of Fig. 4(b), led todeposits typified by the SEM image shown in Fig. 7(a).
The image shows that the palladium deposits, although
still separate, have tended not to grow in isolation.
Islands, consisting of regions of neighbouring pores that
have become blocked with palladium, are evident. The
diameters of these islands are between 500 and 700 nm.
Their appearance is surprising as nucleation of indivi-
dual nanoparticles ought to be a statistical event, andhence a random particle distribution would be expected.
Repetition of the experiment under thermostatic condi-
tions, by immersion of the cell within a water bath, gave
rise to the deposits shown in Fig. 7(b). Comparison of
Figs. 7(a) and (b) shows that a similar fraction of metal
has been deposited in each case, although the distribu-
tion of the metal is more even in the thermostatic case.
This observation may indicate that the palladium islandsresult from the presence of fluid instabilities, such as
local convection cells, within the solution phase. Particle
growth is dependent on the supply of reactants from
both the aqueous and organic phases, hence it is
Fig. 7. (a) SEM image of the islands of palladium deposited within the
alumina membrane from Cell 1 with x�/1�/10�3 mol dm�3, y�/5�/
10�4 mol dm�3, following a potential step from �/0.45 to �/0.90 V for
1 h at ambient temperature. (b) SEM image of palladium deposits
formed using the water bath to control the temperature of the system.
Cell 1 was employed with x�/1�/10�3 mol dm�3, y�/5�/10�4 mol
dm�3, following a potential step from �/0.45 to �/0.90 V for 20 min at
25.0 8C.
M. Platt et al. / Electrochimica Acta 48 (2003) 3037�/3046 3045
conceivable that natural convection in a given phase
may influence local transport and hence the growth of
palladium nanoparticles.
4. Conclusions
Electrodeposition at the template-modified liquid�/
liquid interface has been shown to be a viable route to
the controlled production of nanostructures. Dissolu-
tion of the alumina template, as well as SEM and TEM
imaging of the resultant palladium nanoparticles, con-
firm that particle growth occurs at the mouths of
template pores. Tuning of the pore size can be used to
tune the dimensions of the particles obtained. The
deposition voltage, electrolysis time or reactant concen-
tration (in either phase) can be used to control the
charge passed, and hence dimensions of the resultant
deposits. Many issues concerning the mechanism of this
interfacial deposition process remain to be clarified, and
such studies are in progress. For example, deposition
here has been performed under conditions reproduced
from previous works at the bare liquid�/liquid interface
where neither reactant was in excess (i.e., in terms of Cell
1, x :/y ) [23,24]. Quantitative analysis of the chron-
oamperometric response of the cell will be facilitated by
performing experiments under conditions where one
reactant is in excess, i.e., x �/y , or y �/x . We suggest
that the weak interaction observed between the pore
walls and the deposited particles is evidence that
nucleation is initiated at the liquid�/liquid interface,
rather than the surface of the alumina, although further
work is required to test this hypothesis. The TEM
images of the palladium deposits suggest that the
deposits themselves may display some porosity: we are
presently using other techniques (such as probe micro-
scopy methods) to investigate the structure of the
deposits further. Finally, we note that the deposition
process may effectively ‘‘freeze’’ the liquid�/liquid inter-
face and hence may be treated as a method by which
interfacial structure can be probed with nanometre
resolution.
Acknowledgements
The authors thank the EPRSC for financial support.
We are extremely grateful to Mr. I. Brough (Manchester
Materials Science Centre) and Dr. B. Bethune (UMIST
Corrosion & Protection Centre) for their assistance with
the SEM and TEM imaging, respectively.
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