Carlos
Busó-Rogero
,
Juan V.
Perales-Rondón
,
Manuel J. S.
Farias
,
Francisco J.
Vidal-Iglesias
,
Jose
Solla-Gullon
,
Enrique
Herrero
and
Juan M.
Feliu
*
Instituto de Electroquímica, Universidad de Alicante, Ap. 99 E-03080, Alicante, Spain. E-mail: juan.feliu@ua.es
First published on 27th February 2014
Thallium modified shape-controlled Pt nanoparticles were prepared and their electrocatalytic activity towards formic acid electrooxidation was evaluated in 0.5 M sulfuric acid. The electrochemical and in situ FTIR spectroscopic results show a remarkable improvement in the electrocatalytic activity, especially in the low potential region (around 0.1–0.2 V vs. RHE). Cubic Pt nanoparticles modified with Tl were found to be more active than the octahedral Pt ones in the entire range of Tl coverages and potential windows. In situ FTIR spectra indicate that the promotional effect produced by Tl results in the inhibition of the poisoning step leading to COads, thus improving the onset potential for the complete formic acid oxidation to CO2. Chronoamperometric experiments were also performed at 0.2 V to evaluate the stability of the electrocatalysts at constant potential. Finally, experiments with different concentrations of formic acid (0.05–1 M) were also carried out. In all cases, Tl-modified cubic Pt nanoparticles result to be the most active. All these facts reinforce the importance of controlling the surface structure of the electrocatalysts to optimize their electrocatalytic properties.
It is also known that the formic acid electro-oxidation reaction is very sensitive to the local surface structure.5,14,15 Concerning this point, it was shown that the Pt(100) electrode was the most active among platinum basal planes, while the activity was observed for Pt(111) for both routes.5 To modify the electrocatalytic activity and/or selectivity of bare substrates for the different routes, the presence of other species such as foreign atoms is a powerful strategy. In fact, many studies on modified single crystal Pt electrodes with Sb,16 Bi,17 Pb,18 Pd19 and Te20 show an improvement in the catalytic performance of these materials towards formic acid oxidation. These electrocatalytic improvements by foreign atoms are possible due to: (i) a third-body effect, where adatoms block neighboring sites required for COads formation;13 (ii) electronic effects, where the foreign adatoms modify the adsorption energy between the adsorbate and the substrate facilitating the oxidation reaction;12,13,21 and (iii) a bifunctional mechanism, where, in this case, the presence of foreign atoms can reduce the overpotential for COads oxidation providing easily activated oxygen-species at lower potentials than those on the corresponding bare substrate.22
From an applied point of view, the use of single crystal surfaces is not feasible and nanomaterials with a much higher surface to volume ratio are required. Since the development of methods to synthesize shape-controlled Pt nanoparticles23 and their first use in electrocatalysis,24 many studies have been focused on the evaluation of the electrocatalytic properties of these shaped Pt particles for oxidation reactions of promising fuels, such as formic acid.25,26 For this reaction, shape-controlled Pt nanoparticles have confirmed the structural electrocatalytic dependence related to the presence of facets with (100) and (111) symmetry. Thus, Pt nanoparticles rich in (100) facets are the most electroactive applicable system towards formic acid oxidation. Unfortunately, shaped Pt nanoparticles also show a high CO poisoning rate.26
As has been done with platinum single crystals, in order to increase the activity and/or to overcome the poisoning effect, Pt nanoparticles have been decorated with adatoms such as Pd,27,28 Bi,29,30 or Sb.31 In addition, Pt/Pd alloyed32 and PtBi intermetallic nanoparticles33 have also been tested. Based on the reported results in ref. 28 and 29 it can be proposed that the improvement in electrocatalytic activity seems to be mainly related to the geometry of the surface atoms of the shaped nanoparticles and the chemical nature of foreign adatoms.
Studies in the 1980s showed that thallium (Tl) UPD (under potential deposition) on both polycrystalline platinum and gold increases the rate of formaldehyde electro-oxidation.34,35 However, even considering these promising results, almost no studies have been devoted to the impact of Tl in the electrocatalysis of formic acid.36 For that reason, we report in this paper an electrochemical and spectroscopic (in situ FTIR – Fourier Transform Infrared) study on the electrocatalytic properties of Tl-decorated shape-controlled Pt nanoparticles towards HCOOH electrooxidation.
For electrochemical and in situ FTIR measurements, the nanoparticles dispersed in water were deposited on a polished gold disk and dried under argon atmosphere. Thereafter, the nanoparticles were cleaned by CO (N47, Air Liquide) monolayer adsorption and stripping treatment before the experiments, avoiding high potential excursions to preserve surface order. The active area of platinum nanoparticles was calculated by measuring the charge involved in the so-called hydrogen UPD region after the subtraction of the conventional double-layer contribution in 0.5 M H2SO4 solution, using a reference value of 0.23 mC cm−2.40 A small quantity of nanoparticles (with an active area of ca. 0.05–0.1 cm2) was deposited in all the experiments in order to avoid/minimize transport problems of the reactant species to the surface of the nanoparticles.41
The deposition of Tl on Pt was performed using dilute concentrations of 10−4–10−5 M Tl2SO4 (Aldrich® 99.995%) in 0.5 M H2SO4 solution, cycling the electrode potential between 0.06 V and 0.90 V at 0.05 V s−1. The Tl coverage was monitored through the decrease of the hydrogen adsorption/desorption peaks, according to the equation:
A platinum wire was used as a counter electrode, and a reversible hydrogen (N50, Air Liquide) electrode (RHE) was employed as a reference electrode. All potentials used in this paper are referenced to the RHE. Experiments were carried out in 0.5 M H2SO4 (Merck KGaA Suprapur® 96%), prepared in ultrapure water (Elga PureLab Ultra 18.2 MΩ cm), and deareated with Ar (N50, Air Liquide). Formic acid (Merck KGaG 98%) oxidation experiments were performed in 0.5 M H2SO4.
For electrochemical measurements, cyclic voltammetry and chronoamperometry were employed using a waveform generator (EG&G PARC 175) together with a potentiostat (eDAQ EA161) and a digital recorder (eDAQ ED401).
In situ FTIR spectra were acquired using a Nicolet (Model 8700) spectrometer, equipped with an MCT (Mercury–Cadmium–Telluride) detector. The spectroelectrochemical cell was fitted with a prismatic 60° CaF2 window, as described previously.42 The spectra, obtained from the average of 100 interferograms using a resolution of 8 cm−1, were collected at intervals of 50 mV between 0.05 V to 0.90 V vs. RHE. For all experiments, p-polarized light was employed, which allows detecting changes in the concentration of active species on the electrode surface and electrolyte solution.42 Spectra are presented in absorbance units in which R2 and R1 are referred to as the reflectance values of the single beam spectra corresponding to the sample and the reference potentials, respectively. Positive bands in the spectra are related to species that have been formed at the sample potential whereas negative bands correspond to species consumed. All the experiments were performed at room temperature.
The positive going sweep voltammetric profiles of formic acid oxidation for the same Tl-modified Pt single crystal electrodes from Fig. 1 are presented in Fig. 2, using 0.1 M HCOOH in 0.5 M H2SO4 as test solution. As expected, very low currents are observed for the bare Pt(100) electrode as a consequence of the well-established CO poisoning process coming from the dehydration of formic acid, which is favored on Pt(100).11 With increasing amounts of Tl, the indirect path (through CO poisoning) is hindered. Then formic acid oxidation can take place through the direct path and oxidation currents increase very significantly. The results suggest an optimum Tl coverage at values close to 0.4. At higher coverages, the onset potential increases and the current diminishes.
Fig. 2 Positive sweep voltammetric profiles for 0.1 M formic acid oxidation in 0.5 M H2SO4 with and without Tl for (a) Pt(100) and (b) Pt(111) single crystals. Scan rate: 0.02 V s−1. |
However, in the case of the Pt(111) electrode (Fig. 2b), for which it is well-established that the CO poisoning is almost negligible,11 the addition of Tl does not provide significant changes in the electrooxidation process. These results seem to indicate that Tl acts as a third body preventing the dehydration reaction. For the Pt(111) electrode, owing to the almost negligible CO formation rate,5 the presence of Tl does not improve its catalytic activity. The current diminution for this electrode is just the result of the diminution of the Pt free sites. On the other hand, the increase of activity for the Pt(100) electrode can be related to the diminution of the COads coverage which leads to an increase of the oxidation through the active intermediate reaction path. However, electronic effects cannot be discarded for this electrode. It should be noted that the onset for the direct oxidation reaction in the absence of poison on the Pt(100) electrode is 0.30 V (see ref. 43), whereas in the presence of Tl the onset is ca. 0.20 V. This diminution of the onset potential at a Tl coverage of ca. 0.4 suggests the possible presence of an electronic effect. These results also point out the importance of controlling the surface structure of the Pt substrate, the Pt(100) square structure being much more convenient than the hexagonal Pt(111). Thus, in terms of the particle shape, it would be preferable to use cubic Pt nanoparticles in which the number of {100} surface sites is maximized.44
Fig. 3 Voltammetric profiles for increasing amounts of Tl coverages on (a) (100)Pt and (b) (111)Pt nanoparticles in 0.5 M H2SO4 + 10−4–10−5 M Tl2SO4. Scan rate: 0.05 V s−1. |
Fig. 3 also shows the voltammetric responses of the (100)Pt and (111)Pt nanoparticles after partial and maximum deposition of Tl. The evolution of the voltammetric profiles is similar to those previously reported for Pd and Bi on shape-controlled Pt nanoparticles28,29 or after deposition of Bi(III), Te(IV) and Se(IV) on stepped Pt surfaces.46 In addition, the Tl adsorption process does not produce appreciable changes in the charge density on the so-called double layer region until high thallium coverages are reached. As described in the experimental section, the Tl coverage can be calculated considering the expression θTl = 1 − θH, where θTl and θH are the thallium and hydrogen coverages, respectively. However, at the maximum thallium coverage on both Pt nanoparticles, Fig. 3, an important increase of the double layer region is observed. This fact prevents an accurate determination of the Tl coverage for highly covered surfaces that cannot be properly calculated. For that reason, the maximum coverage for each sample will be referred to as “maximum” and no numeric value will be given. In addition, it is important to note the absence of additional voltammetric features at high coverages and remark that only a small broad peak is visible at about 0.70 V, particularly in the preferential (111)Pt nanoparticles. This feature can be linked to the thallium desorption from {111} terrace sites, as pointed out for Tl UPD in Pt(111) reports.47,48
For the (111)Pt nanoparticles, Fig. 4b, a similar effect on the onset potential is observed after surface decoration with Tl. Taking into account that (i) the {111} domains do not suffer the same strong CO poisoning effect as that observed with the {100} domains,11 (see Fig. 2), and (ii) the {111} domains have a low catalytic activity for the direct oxidation,5 the electrocatalytic enhancement observed is lower than that reported for the (100)Pt nanoparticles. Anyhow, the onset potential diminishes when θTl increases, decreasing to around 0.1 V at the maximum coverage (blue line). Also, the onset for the formic acid oxidation observed for the Tl modified nanoparticles at high coverages is ca. 0.2–0.3 V lower than the onset for the direct oxidation route in the unmodified nanoparticles.26
Finally, with the aim of comparing the activity of both samples in the whole potential range, Fig. 5 displays the HCOOH activity ratio between the bare and Tl modified (maximum coverage) Pt nanoparticles. From Fig. 5, it is evident that the “improvement factor” due to the presence of Tl for the (100)Pt nanoparticles is larger than that obtained with the (111)Pt nanoparticles in the entire potential range. In fact, the highest ratio between both activities is observed at ca. 0.3 V, the potential at which the {100} domains have the greatest activity, in agreement with the large catalytic activity of Tl on the {100} domains (Fig. 2a). In addition, in terms of maximum currents, the electrooxidation activity of the Tl-modified (100)Pt nanoparticles is always higher (about 1.5 times) than that of the (111)Pt nanoparticles, Fig. 6.
Fig. 5 Ratio between the HCOOH oxidation current densities obtained using the bare and Tl-decorated (maximum coverage) shape-controlled Pt nanoparticles. Data taken from Fig. 4. |
Fig. 6 Ratio between the HCOOH oxidation current densities obtained using Tl-modified (maximum coverage) (100) and (111)Pt nanoparticles. Data taken from Fig. 4. |
In order to better evaluate the activity as well as the stability of the Tl-modified samples, current transient responses for each modified electrode were recorded at 0.2 V, (Fig. 7), a reasonably low potential value. In these experiments, a pretreatment consisting of a potential step at 0.85 V for 10 s prior to the potential step at 0.2 V was performed in order to oxidize all the possible CO blocking surface sites.26 Current transients for the bare nanoparticles are not reported, as current densities for both samples are almost zero. This is due to the fact that the CO formation rate is very high and the surface is immediately covered by CO after the cleaning step. For Tl modified (100)Pt nanoparticles (Fig. 7a), the current densities after 600 s are 0.002, 0.010 and 0.014 mA cm−2 at Tl coverages of 0.25, 0.48 and the maximum one, respectively. For Tl modified (111)Pt nanoparticles (Fig. 7b), reactivity is lower and current densities of 0.002, 0.004 and 0.006 mA cm−2 were obtained at coverages of 0.43, 0.57 and the maximum one, respectively. These results indicate that Tl adsorbed on the surface successfully hinders the CO adsorption through the poisoning pathway, and this effect increases with the Tl coverage.
Fig. 8a displays the spectra for formic acid oxidation on (100)Pt bare nanoparticles. From 0.2 V to 0.6 V, the spectra show the linearly adsorbed CO band between 2050 and 2060 cm−1.42 At 0.2 V, the band frequency is around 2052 cm−1, whereas at 0.6 V the frequency shifts to 2060 cm−1, likely due to the Stark effect.50 Between 0.4 and 0.5 V, the band shows a slightly bipolar character, meaning that adsorbed CO was present in the reference potential (0.05 V).42 At around 0.2 V, a new band at 2343 cm−1 appears, which is associated with the start of CO2 formation.42 The spectra do not show any signal band that could be attributed to bridge adsorbed CO, which should appear at around 1820 cm−1 as was observed for formic acid oxidation in ATR-SEIRA (Attenuated Total Reflection – Surface Enhanced Infra-Red Absorption) experiments on thin-film polycrystalline platinum electrodes at 0.35 V vs. RHE.9
Fig. 8b shows the spectra for formic acid oxidation on Tl-modified (100)Pt nanoparticles. The band for CO2 can be clearly observed at 0.1 V, and the COads band is absent for all the spectra, pointing out that Tl enhances the electrocatalytic activity (Fig. 4a) by hindering the poisoning pathway thus allowing formic acid oxidation to proceed through the direct pathway, which also explains why CO2 is formed at low potentials.
Additional evidence on that is found in the chronoamperometric responses after 600 s of reaction at 0.2 V for both nanoparticles at maximum Tl coverage at different formic acid concentrations (Fig. 10). In the case of (100)Pt nanoparticles (Fig. 10a), there is nearly no clear difference between the final current density for 0.05 M and 0.1 M (around 0.015–0.020 mA cm−2), but for the other concentrations, current density increases with the amount of formic acid in solution, increasing up to 0.145 mA cm−2 for 1 M formic acid concentration. A similar behavior was observed for (111)Pt nanoparticles in Fig. 10b, with a final current density of 0.049 mA cm−2 for 1 M formic acid. As for voltammetric curves, chronoamperometric currents become higher when the concentration of formic acid increases. Fig. 11 summarizes the differences observed for the final current density after 10 min at 0.2 V for both samples at maximum coverage, clearly indicating that the Tl-modified (100)Pt nanoparticles are much more active than the (111)Pt nanoparticles in the range of HCOOH concentration under study (0.05–1 M HCOOH). Currents recorded after 10 minutes reflect a nearly stationary situation. For the currents at 10 min the reaction order is similar to that measured by voltammetry, which reinforces the fact that the reaction mechanism through the active intermediate is complex.
Fig. 10 Current transients for (a) (100)Pt and (b) (111)Pt nanoparticles with maximum Tl coverage recorded at 0.20 V for different formic acid concentrations in 0.5 M H2SO4. |
Fig. 11 Comparison between formic acid concentrations and current densities obtained after 10 minutes at 0.2 V. Data extracted from Fig. 9 for (a) (100)Pt and (b) (111)Pt nanoparticles. |
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