A. Basile et al. / Electrochimica Acta 56 (2011) 2895–2905
2905
If the silver deposition is carried out in [C mPyr][TFSI] that has
that the uptake of atmospheric water in the IL resulted in a change
in the electrodeposition mechanism to progressive nucleation and
growth. This is in agreement with studies carried out in aque-
ous solution that also demonstrated the same electrodeposition
mechanism. Interestingly, continuous exposure of the silver salt/IL
solution to atmospheric conditions resulted in the extensive for-
mation of silver nanoparticles that interfere with electrodeposition
experiments by adhering to the glassy carbon electrode. Overall it
has been demonstrated from these studies that the water content
of ionic liquids can significantly influence metal electrodeposition
processes and under controlled conditions may offer a route to
tuning the morphology of the resulting deposits.
4
been allowed to absorb atmospheric H O, the SEM images (Fig. 7g
2
and h) show significant differences to the dry case. The SEM images
show a random distribution of spherical particles from sub micron
sized upwards. All of the larger structures are layered on top of an
underlying layer of sub-micron sized spherical particles similar to
the case of [BMIm][BF ]. The particle size distribution behaviour is
4
consistent with the proposed change in mechanism from instanta-
neous to progressive nucleation and growth as suggested by the CA
data. The effect of water in this system can clearly have a significant
effect on the deposition morphologies.
XRD studies were carried out to investigate if the morphology
of the electrodeposits was related to any preferred crystallographic
orientation of the silver particles. For silver electrodeposited from
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2
BMIm][BF ] at a potential of −0.80 V characteristic peaks at
4
◦
◦
◦
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Significantly, for the case of [C mPyr][TFSI], it was demonstrated
4