Elsevier

Surface Science

Volume 432, Issue 3, 20 July 1999, Pages 279-290
Surface Science

Adsorption of the formate species on copper surfaces: a DFT study

https://doi.org/10.1016/S0039-6028(99)00605-6Get rights and content

Abstract

The density functional theory and the cluster model approach have been applied to study the interaction of the formate species with the copper (100), (110) and (111) surfaces. The short-bridge, long-bridge and cross-bridge sites of the copper surface have been modelled by Cu7 and Cu8 metal clusters after checking the validity of the results against those obtained with much larger clusters. The results show that the formate species is stabilized strongly on the short-bridge site of the surfaces considered and this is in agreement with available experimental data. For adsorption on the short-bridge site, and for the three surfaces considered, the CusurfO is close to 2.02 Å, the CO bond length is 1.26 Å and the OCO angle is 128°. On this adsorption site, formate is bridge-bonded with the two oxygens almost in a top position on two copper atoms. For the long-bridge site, the oxygen atoms of the adsorbate are not located above the two copper atoms. The two OC bonds are equivalent when formate is adsorbed on these two sites. On the cross-bridge site, the formate species is bonded to the surface in a monodentate conformation. The two OC bonds are different with two clearly different bond lengths. The difference is larger for adsorption on the Cu (100) surface. In this case, the bond lengths are typical of a bond order of one and two. The bonding to the surface is essentially ionic, and the total charge in the adsorbate is 0.75 ±0.05 e, approximately.

Introduction

The decomposition of formic acid on metal surfaces has been the subject of numerous experimental studies in recent years [1], [2], [3], [4], [5], [6], [7], [8], [9], [10], [11], [12], [13], [14], [15], [16], [17], [18], [19], [20], [21], [22], [23], [24], [25], [26], [27], due to the simplicity of the intermediates and products involved.

Formate is observed during the methanol oxidation reaction, and it is thought to be an intermediate in the methanol synthesis reaction. The most extensively studied surfaces are those directly related to the catalysis of these two reactions, i.e. copper and silver. In industry, a silver catalyst is used to obtain formaldehyde from methanol and a Cu/ZnO catalyst to produce methanol from syn-gas.

Surface formate is easily formed from formic acid by OH bond cleavage. It can undergo dehydrogenation to produce H2 and CO2 and dehydration to yield H2O and CO, depending on the metal surface. On copper surfaces, only dehydrogenation is observed [1], [8]. Formate has been studied by different experimental techniques on copper (100) [1], [2], [3], [4], [5], [6], [7], copper (110) [5], [6], [7], [8], [9], [10], [11], [12], [13], [14], [15], [16], [17], [18], [19], [20], [21], [22], copper (111) [23] and supported copper surfaces [23], [24], [25], [26], [27]. HCO2 has been identified by temperature-programmed reaction spectroscopy (TPRS) [8], [9], by electron energy loss spectroscopy (EELS) [1], high-resolution electron energy loss spectroscopy (HREELS) [1], [8], reflection absorption infra-red spectroscopy (RAIRS) [10], in-situ infra-red reflection absorption spectroscopy (IRAS) [10], [11], [23] and scanning tunnelling microscopy (STM) [12], [13], [14]. From the results obtained with these techniques, it was difficult to clarify how the formate species are chemisorbed on copper surfaces, if formate were bonded to the copper surfaces in a upright or tilted geometry or if it were bonded in a bidentate or monodentate geometry. This is due to the observation, or not, of the υas (OCO) band. More studies were performed using near-edge X-ray absorption spectroscopy (NEXAFS) [3], [4], [15], [16], and it was concluded that the formate species was oriented with its molecular plane normal to the metal surface. By means of surface extended X-ray absorption fine structure (SEXAFS) [3], [4], it was found that the HCO2 species was adsorbed on the Cu (100) surface on the cross-bridge site and later, in a data reanalysis [5], [6], that the diagonal atop site was the preferred adsorption site for formate adsorption. On the Cu (110) surface, the aligned atop site [5], [6], [15], [16] seemed to be the most favourable for HCO2 adsorption.

More recently and taking advantage of photoelectron diffraction (PhD) [7] and NEXAFS [17] techniques, it was found that the formate species are adsorbed on the short-bridge sites of the Cu (100) and on Cu (110) surfaces. The oxygen atoms are located at the same distance from the surface and with a CuO nearest-neighbour distance of 1.98±0.04 Å.

For the Cu (111) surface, as far as we know, a similar PhD study does not exist. In a recent study [23] using IRAS for HCO2/Cu (111), a bidentate structure was found with both oxygen atoms located at the same distance from the surface, thus possibly indicating adsorption of formate on the short-bridge site of the Cu (111) surface.

For low temperatures, it seems that this type of adsorption is preferred.

In the literature, only a few theoretical studies can be found on the adsorption of HCO2 on copper surfaces [28], [29], [30], [31], [32], [33]. These theoretical studies are 10 years old and use very poor methods (by today's standards) to evaluate chemisorption properties, with the exception of the recent studies of Casarin et al. [32] and Kakumoto et al. [33]. Casarin et al. [32] use a linear combination of atomic orbitals method within the local density approximation (LCAO–LDA) to study the chemisorption of formate on Cu (100). They studied the adsorption on the short-bridge and on the cross-bridge sites and concluded that the adsorption on the short-bridge site is the most favourable. Ab-initio MO calculations using the DFT method were presented by Kakumoto et al. [33] for the formate intermediate adsorbed on a [Cu2]+ bridge site. In this work, only the energy and geometry variation of the HCO2 species with the CuCu distance is calculated.

One of the goals of this paper is to compile theoretical results for the adsorption of the formate species on the Cu (100), (110) and (111) surfaces under the same conditions in terms of methodology and basis sets in order to compare the trends in the adsorption of this species.

This paper is organized as follows. In Section 2, the theoretical details are given for the computational method used and for the metal clusters used to describe the metal surface. In Section 3, the calculated results for HCO2 adsorption on Cu (100), (110) and on Cu (111) surfaces are presented and in Section 4, a summary of the main conclusions obtained with this work is given.

Section snippets

Method

In the present work, the interaction of the formate species with copper (100), (110) and (111) surfaces is studied. For that purpose, the density functional theory (DFT) approach was used. The Cu (100) and the Cu (110) metal surfaces are modelled by a Cu8 cluster and the Cu (111) surface by a Cu7 cluster as shown in Fig. 1. These two-layer clusters are a small section of the ideal Cu (100), Cu (110) and Cu (111) surfaces with a CuCu nearest-neighbour distance taken from the bulk and equal to

Free HCO2 and HCO2 species

Table 1 lists the computed geometry, energy and vibrational frequencies for the three different σ states of the HCOO radical, 2B2, 2A1 and 2A′ optimized at the DFT/6-31G∗∗ level. The calculations were made using as a starting point the geometry values obtained in previous work [45], [46], [47].

Depending on whether the oxygen atoms in HCO2 are identical or not, there are two possible symmetric types for the HCO2 species, C2v and Cs. The 2B2 and the 2A1 states belong to the C2v symmetric type,

Conclusions

The ab-initio cluster model approach has been applied to study the adsorption of the HCO2 species on the copper (100), (110) and (111) surfaces. Small metal clusters of seven and eight metal atoms have been chosen to model the short-bridge, long-bridge and cross-bridge sites in the three metallic surfaces as these have been shown to be trustworthy for studies of this type. In order to justify the use of these small clusters in this work, we have also studied HCO2 adsorption on the short-bridge

Acknowledgements

Financial support from the Fundação para a Ciência e Tecnologia (Lisbon) and project PRAXIS/PCEX/C/QUI/61/96 is acknowledged. J.R.B.G. thanks PRAXIS for a doctoral scholarship (BD/5522/95). We thank Professor Francesc Illas for helpful discussions.

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