Yuhan
Mei
a,
Fanglin
Che
b and
N. Aaron
Deskins
*a
aDepartment of Chemical Engineering, Worcester Polytechnic Institute, Worcester, Massachusetts 01609, USA. E-mail: nadeskins@wpi.edu
bDepartment of Chemical Engineering, University of Massachusetts Lowell, Lowell, Massachusetts 01854, USA
First published on 21st October 2024
The electrochemical environment present at surfaces can have a large effect on intended applications. Such environments may occur, for instance, at battery or electrocatalyst surfaces. Solvent, co-adsorbates, and electrical field effects may strongly influence surface chemistry. Understanding these phenomena is an on-going area of research, especially in the realm of electrocatalysis. Herein, we modeled key steps in the ethanol oxidation reaction (EOR) over a common EOR catalyst, Rh(111), using density functional theory. We assessed how the presence of electrical fields may influence important C–C and C–H bond scission and C–O bond formation reactions with and without co-adsorbed water. We found that electric fields combined with the presence of water can significantly affect surface chemistry, including adsorption and reaction energies. Our results show that C–C scission (necessary for the complete oxidation of ethanol) is most likely through CHxCO adsorbates. With no electric field or solvent present C–C scission of CHCO has the lowest reaction energy and dominates the oxidation of ethanol. But when applying strong negative fields (with or without solvent), the C–C scission of CH2CO and CHCO becomes competitive. The current work provides insights into how electric fields and water solvent affect EOR, especially when simulated using density functional theory.
Density functional theory (DFT) is a powerful tool for simulating electrochemical interfaces, which is the primary method used in the current study. There are various approaches to modeling electrochemical interfaces and describing the various components present at the interface (e.g., solvent molecules, electric fields, electron potential, etc.).14–16 A common technique to account for the electrode potential is to simulate electrocatalytic hydrogen/electron transfer at metal surfaces by adding energy adjustments based on the electron potential at the electrode surface, also known as the computational hydrogen electrode (CHE) approach.17 However, the widely used CHE method overlooks the effects of electric fields present near the electrode surface. Such fields can significantly alter the surface chemistry and affect adsorbate interactions. Furthermore, C–C bond cleavage does not involve hydrogen/electron transfer, and thus the electric field and solvent molecules near the electrode surface are expected to influence C–C bond cleavage more than the potential of the electrons themselves. Other methods exist for modeling electrochemical systems, such as the computational standard hydrogen electrode (SHE)18,19 method, which determines redox potentials using ab initio molecular dynamics (AIMD). Such calculations can be time-consuming, and controlling local electric fields with this method can be difficult. A related method is the constant-potential hybrid-solvation dynamic model20,21 which also uses AIMD and requires varying the number of electrons added to or removed from the system to maintain a constant applied potential. One prominent method to simulate the electric fields present at electrochemical systems is to introduce a dipole sheet into the vacuum, which creates an electric field in the simulation cell.22
Various DFT papers have examined the effect of an electrical field on surface chemistry.23–28 Electric fields can lead to remarkable behavior and variations in catalyst efficiency.23,24,29–34 It should be noted that it is possible to relate the electric field strength near the electrode surface to the electrode potential, as the electrode potential can be approximated as the double-layer thickness multiplied by the field strength, illustrated by Rossmeisl et al.23 A similar approach was used by Karlberg et al.31 Haruyama et al.35 also developed methods to relate electric fields to the electrode potentials. In other DFT studies on the oxygen reduction reaction,24,31,36 electric fields were incorporated to improve the simulations. Electric fields were also included in studies of methane conversion.25,37,38 Estejab et al.39 modeled methanol oxidation in the presence of an electric field. Regarding the study of electric fields in ethanol oxidation reactions, Jiang et al.26 have used molecular dynamics simulations to investigate the effect of external electric fields of different strengths on EOR (albeit in the gas phase without the presence of a catalyst). Their study shows that the application of an electric field not only changes the reaction rate in a nonlinear manner, but also modifies the reaction pathways for ethanol oxidation.
Previous studies have used molecular modeling approaches to better understand the role of electric fields in C–C and C–H bond cleavage (important for many reactions involving organic species). Investigations by Che et al. examined the effect of electric fields on C–H bond cleavage of CHx (x = 1–3) species over Ni,40,41 suggesting that negative external electric fields lower energy barriers while positive fields raise them. In recent work, Zhou et al.42 reported that for gas-phase pyrolysis of n-alkanes, electric fields can promote the breaking of C–C and C–H bonds. As for the C–C and C–H bond breakings in EOR, complementary studies using reactive force field (ReaxFF) molecular dynamics simulations have also been performed,26,27 analyzing the effects of external electric fields on the ethanol oxidation reaction mechanisms in the absence of a catalyst and in an O2 gas environment. These modeling efforts suggest that electric fields can shift reaction mechanisms and possibly open alternative reaction pathways for oxidation of alcohols like ethanol. However, the precise influence of an external electric field on surface-mediated reactions relevant to complete ethanol oxidation, which involves the breaking of both C–C and C–H bonds, remains an open question in the context of DFT simulations.
In addition to electric fields present at electrocatalyst surfaces, solvent molecules can also alter catalyst reactivity. In particular, the solvation environment can be instrumental in facilitating various surface reactions, including both oxidation and electrocatalytic processes. Several studies focused on solvation effects and bond dissociation reactions on metal surfaces. Investigations by Schweitzer et al.43 and Gu et al.44 have shown that accounting for water solvation can significantly alter the cleavage of C–C and C–H bonds in ethanol on a Pt(111) surface. Estejab et al. modeled methanol oxidation with explicit water molecules under an electric field. They indicated a dependency of both the solvation energy and the entropy on the strength and direction of an electric field, with the entropy of solvation being significantly impacted due to the orientation of water molecules.39 Complementary findings by Mei et al.45 highlighted the substantial role of a water solvent in modifying the dissociation of the C–C/C–H bonds on Rh(111). In a previous study, Guo et al.46 used DFT coupled with an implicit continuum solvation model to investigate the potential-dependent mechanism of EOR on Pd. They proposed a mechanism where C–C bond scission changed only slightly under different potentials. In light of these previous findings, the current study aims to unravel the interactive effects of both the explicit presence of water and electric fields on EOR.
We investigated the influence of electric fields on EOR using DFT to model the Rh(111) surface, which has been previously recognized as an effective catalyst for EOR.7,10,47–53 We calculated the reaction energies for key EOR steps: C–C and C–H bond cleavage and C–O bond formation. Although there are numerous computational strategies for simulating electric fields,54–61 our approach was to apply an external electric field following the methodology established by Neugebauer and Scheffler,22 where a dipole sheet is inserted into the vacuum layer. Given that our focus is primarily on examining the effects of local electric fields, the dipole sheet method is both sufficient and computationally less expensive than other methods. Thus, we can simulate the effect of an electric field on adsorbate-covered surfaces. In addition, our study incorporated a co-adsorbed water molecule from the solvent environment to determine its effect on the EOR. The inclusion of explicit water molecules is a more representative model of solvation than implicit solvent models, especially in the context of relevant EOR processes.43,45,52,62,63 Previous work39,55,58 has demonstrated how electric fields can be used in conjunction with explicit water molecules to understand electrochemical interfaces. Our work extends this to better understand the role of the electrochemical environment on EOR.
The Rh(111) surface was represented by a (3 × 3) four-layer slab (as shown in Fig. 1), with cell lengths of 8.15 Å and a 10 Å vacuum separation set in the z direction perpendicular to the surface. The bottom two layers of the slab were fixed. The lattice constant of bulk Rh was calculated to be 3.84 Å, which is in agreement with previous work.9,10,51,75 For the slab calculations, a Gamma-centered k-point grid of 4 × 4 × 1 was chosen to sample reciprocal space. Gas phase molecules were modeled in a 20 Å × 20 Å × 20 Å box cell, and the gas phase calculations used a Monkhorst Pack k-point grid of 1 × 1 × 1.
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Fig. 1 The slab model used in this work to represent the Rh(111) surface: (a) top view and (b) side view. The slab was a (3 × 3) slab with four layers, the bottom two layers being frozen. |
We modeled the adsorption of CH3CH2OH, CH3CH2O, CH2CH2O, CH2OH, CH2O, CH3CO, CH2CO, CHCO, CH3, CH2, CH, CO and H, as these species have been identified as key intermediates for the C–C and C–H bond breaking during ethanol oxidation/decomposition process.10,76,77 See also Fig. 2 for an illustration of various reactions and these species involved in EOR. In addition, we also modeled the adsorption of CH3COOH, CH3CO, and OH which are relevant for C–O bond formation. C–O bond formation can take place during incomplete EOR, and thus prevents complete EOR.12,13 Different initial geometries were considered in order to find stable configurations. Adsorbates were initially placed above the surface with atoms of the adsorbates at different fcc, hcp, top and bridge sites on the Rh(111) surface. The adsorption of larger molecules (e.g. CH3CH2OH, CH3CH2O, CH2CH2O, CH3CO, CH2CO, CHCO) can involve multiple interactions with the surface (e.g., *CH3CH2OH can have both of the C atoms interacting with Rh atoms). After geometry optimization, we took the structure with the lowest energy as the most stable configuration. For calculations in vacuum, geometries were first optimized without an external electric field, and then the most stable geometries were modeled in the presence of an external electric field in a range of −1.0 to 1.0 V Å−1, as discussed in the next section.
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Fig. 2 Schematic representation of possible pathways for complete ethanol oxidation/decomposition on Rh(111).2,10,76,78,79 Key reactions involve C–C and C–H scission. Not shown are pathways for incomplete oxidation, leading to acetaldehyde, acetic acid, and possible other products. Further discussion of reactions modeled in this work is found in the Methodology section. |
Adsorption energies (ΔEads(F)) were calculated using this equation:30
ΔE(F)ads = E(F)ads/slab − E(F)slab − E(F)ads(gas). | (1) |
To determine the impact of the electric field on surface reactions, we modeled several C–C and C–H bond breaking and C–O bond formation reactions over the Rh surface. We modeled C–C bond breaking involving CH3CH2OH, CH3CH2O, CH2CH2O, CH3CO, CH2CO, and CHCO. We also modeled C–H bond cleavage involving CH3CO and CH2CO. These reactions have been reported to be key reaction pathways in ethanol oxidation/decomposition.76,77,84,85 To calculate the reaction energies for C–C and C–H scission reactions (e.g., AB* → A* + B*), we used this formula:
ΔE(F)rxn = E(F)A/slab + E(F)B/slab − E(F)AB/slab − E(F)slab. | (2) |
We compared adsorption energies and reaction energies in vacuum (no water present) with results using explicit water. We also evaluated field effects by modeling solvated structures with applied electric fields. For these calculations, the adsorption energies were calculated with the following:92,93
ΔE(F)solads = E(F)(ads+H2O)/slab − E(F)H2O/slab − E(F)ads(gas). | (3) |
ΔE(F)solrxn = E(F)(A+H2O)/slab + E(F)(B+H2O)/slab − E(F)(AB+H2O)/slab − E(F)H2O/slab. | (4) |
We present the adsorption energies in the presence of an electric field for selected species in Fig. 3. The adsorption energies in the presence of an electric field for 15 different species are shown in Fig. S4 (ESI†). Analysis of the data from Fig. 3 and Fig. S4 (ESI†) reveals three distinct patterns of behavior. The first group of species (including CH3CH2OH, CH3CH2O, CH2CH2O, CH2OH, CH3CO, CH3, CH2, CH3COOH, and OH) exhibited a decrease in adsorption energies with increasing field strength (i.e., became more stable) or a negative slope in the adsorption energy versus electric field plot. In contrast, the second group of species (CHCO and CO) showed an increase in adsorption energies with increasing field strength, reflecting a positive slope in the adsorption energy versus the electric field profile. The third group of species (CH2O, CH, CH2CO, and H) showed a parabolic trend, with adsorption energies initially decreasing before reaching a minimum and then increasing. Notably, in the case of the parabolic plots, the adsorption energies of CH2O and CH reached their lowest values at slightly positive potentials, while the adsorption energies of CH2CO and H reached their minimum at or near 0 V Å−1. It should be noted that while we have identified three different patterns in these plots, those curves with positive or negative slope display curvature, such that parabolic behavior may be observed at much lower or larger potentials (well beyond −1 or 1 V Å−1).
Upon applying the electric fields, the optimized geometries of the adsorbates underwent only minor changes, with an example shown in Fig. S5 (ESI†). Changes in bond lengths within the adsorbates were less than 0.04 Å for all species studied when applying the electric field. In addition, we evaluated the structural fluxionality of these adsorbates following a similar approach discussed by Yang et al.,97 as described in the ESI.† This approach facilitated the comparison of adsorbate/surface geometries under electric fields with those without electric fields. The calculated structural fluxionality values, shown in Table S2 (ESI†), revealed negligible changes in geometry due to the electric fields. For example, the highest observed fluxionality value was only 0.02 Å for CH2OH at an electric field strength of 1 V Å−1.
In our study, we have investigated the variations of adsorbate–surface distances under different electrical potentials. Most of the adsorbates studied, such as CH3CH2OH, CH3CH2O, CH2CH2O, CH2OH, CH2O, CH2O, CH2O, CH2O, CH2O, CH2O, CH2O, CH2O, CH3CO, CH2CO, CH3, and OH, bonded to the surface mainly through Rh–O and Rh–C interactions. Our results showed that positive electric fields generally decreased the distances between these adsorbates and the surface, with Rh–O and Rh–C bond lengths shortened by up to 0.20 Å. Conversely, negative electric fields increased the distances. This phenomenon can be attributed to the polarization of the metal surfaces in a positive electric field, which induces a partial positive charge, increasing the attraction to negatively charged O atoms via electrostatic forces, as supported by the literature.30,41 Notably, CHCO and CO species also adsorbed through Rh–C bonds, while showing minimal distance reduction (0.03 Å) under negative potentials. In contrast, the distances for adsorbed CH2, CH and H atoms remained relatively unchanged, with bond length variations of only up to 0.01 Å. Thus, the most significant distance changes occurred for negatively charged adsorbates such as O at positive potentials, while other adsorbate distances were less affected by the applied potentials. Our results are consistent with previous studies. For example, the H adsorption energies, which increase at both positive and negative potentials, agree with the results of Che et al.40 on their investigations involving Ni(111) surfaces. This congruence extends to other species in their work as well; the adsorption energy profile of CH shows a parabolic shape, reaching optimal stability at a modest positive potential. In contrast, the adsorption energies for CH2 and CH3 show a monotonic decrease with increasing potential. The adsorption energy of CO, on the other hand, shows an upward trend with increasing potential, a trend that is also in good agreement with the findings of Che et al.,41 further validating our results by aligning with the established literature.
Fig. 3 illustrates the possible significant influence of an external electric field on the adsorption energies of reactive intermediates. The difference in adsorption energies between 1 V Å−1 and −1 V Å−1 reached up to 1 eV, with an average variation across these species of 0.44 eV. Our study also investigated the variation of adsorption energies under different potentials compared to the baseline (0 V Å−1), denoted as |E(0)ads| − |E()ads|. The maximum variance was observed for ethanol, with a value of 0.60 eV at −1 V Å−1. In Fig. 3 the largest deviations were typically observed at −1 or 1 V Å−1. The average maximum variance for all species was 0.29 eV. Some species showed significant deviations from 0 V Å−1 (e.g. ethanol, CH3CH2O, CH3COOH, OH), while others have smaller deviations (e.g. CH2CO, CHCO, CH2). For example, the adsorption energy range of CH2CO was 0.16 eV, suggesting a more limited influence of the electric potential on its adsorption.
In general, the application of a positive electric field resulted in a decrease of the adsorption energies for most of the intermediates. However, exceptions were observed for CH2CO, CH2O, CHCO, CH, CO, and H, where the adsorption energies increased in positive electric fields. This suggests that positive electric fields can stabilize many species on the surface, whereas negative fields tend to destabilize them. The implications of these field effects on the reaction energies of the steps involved in EOR are discussed later in the paper.
![]() | (5) |
This work | Literature | |||
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|![]() |
α | |![]() |
α | |
*CH3CH2OH | 0.37 | −0.44 | ||
*CH3CH2O | 0.33 | −0.17 | ||
*CH2CH2O | 0.20 | −0.18 | ||
*CH2OH | 0.22 | −0.03 | 0.1641 | −0.9341 |
*CH2O | 0.09 | −0.16 | 0.3041 | 0.0041 |
*CH3CO | 0.23 | −0.14 | ||
*CH2CO | 0.01 | −0.29 | ||
*CHCO | −0.14 | −0.08 | ||
*CH3 | 0.19 | −0.11 | 0.19;41 0.1940 | −0.02;41 −0.1540 |
*CH2 | 0.13 | −0.12 | 0.14;41 0.1440 | −0.02;41 −0.1640 |
*CH | 0.08 | −0.19 | 0.08;41 0.0840 | −0.19;41 −0.1940 |
*CO | −0.22 | −0.09 | −0.2141 | −0.0641 |
*H | −0.01 | −0.06 | −0.01;41 −0.0140 | −0.03;41 −0.0640 |
*CH3COOH | 0.47 | −0.05 | ||
*OH | 0.56 | 0.00 | −0.0941 | −0.0541 |
Species | Vacuum | Solvation method 1 | Solvation method 2 |
---|---|---|---|
*CH3CH2OH | −0.15/0.03/0.04 | −0.05/0.00/−0.01 | 0.40/−0.03/0.00 |
*CH3CH2O | −0.59/−0.40/−0.38 | −0.69/−0.46/−0.45 | −0.68/−0.43/−0.49 |
*CH2CH2O | −0.71/−0.51/−0.36 | −0.81/−0.63/−0.53 | −0.71/−0.57/−0.73 |
*CH2OH | −0.24/−0.06/0.06 | −0.28/−0.13/−0.04 | −0.34/−0.13/−0.14 |
*CH2O | −0.58/−0.40/−0.27 | −0.49/−0.46/−0.36 | −0.94/−0.52/−0.41 |
*CH3CO | −0.37/−0.17/−0.09 | −0.44/−0.28/−0.24 | −0.54/−0.28/−0.35 |
*CH2CO | −0.60/−0.40/−0.24 | −0.71/−0.55/−0.41 | −0.87/−0.55/−0.66 |
*CHCO | −0.47/−0.31/−0.13 | −0.63/−0.50/−0.35 | −0.69/−0.50/−0.84 |
*CH3 | −0.35/−0.18/−0.09 | −0.22/−0.20/−0.12 | −0.52/−0.20/−0.09 |
*CH2 | −0.44/−0.27/−0.18 | −0.30/−0.27/−0.21 | −0.78/−0.27/−0.71 |
*CH | −0.42/−0.27/−0.20 | −0.30/−0.32/−0.26 | −1.48/−0.32/−0.23 |
*CO | −0.42/−0.30/−0.20 | −0.51/−0.43/−0.34 | −0.63/−0.43/−0.15 |
*H | −0.25/−0.16/−0.14 | −0.17/−0.18/−0.16 | −0.19/−0.18/−0.15 |
*CH3COOH | −0.21/0.00/0.02 | −0.11/−0.08/−0.07 | −0.60/−0.07/−0.31 |
*OH | −0.63/−0.46/−0.40 | −0.55/−0.48/−0.44 | −0.59/−0.48/−0.47 |
We show in Fig. S7 (ESI†) a comparison of the adsorption energies and Bader charges of Rh atoms, which illustrates how adsorption energies of species bonding through negative atoms become stronger as Rh atoms become more positively charged. For species with positive effective dipole moments (such as CH3CH2OH, CH3CH2O, CH2CH2O, CH2OH, CH3CO, CH3, CH2, CH3COOH, and OH) negative electric fields weaken adsorption, while positive fields strengthen adsorption. Because more positive charges on Rh atoms (under positive fields) increases their attraction to negatively charged C and O atoms, adsorption is strengthened. Similarly, less positive charges (under negative fields) weaken adsorption. Species with negative effective dipole moments, such as CHCO and CO, show weaker binding under positive electric fields due to increased positive charge on both Rh and C atoms, resulting in decreased adsorption. For species with small effective dipole moments, such as CH2CO, CH, and H, there is a more complex relationship between Rh charges and charges of the adsorbate.
The second group of species, CHCO and CO, was found to adsorb onto the Rh surfaces via interactions involving both C atoms in CHCO and the C atom in CO, forming Rh–C bonds. The Rh atoms in these interactions were positively charged. In CHCO, one of the carbon atoms was positively charged and the other was negatively charged, as shown in Fig. S6 (ESI†). As the electric fields shift from negative to positive, the positively charged carbon atoms in CHCO became more positively charged, while the negatively charged carbon atoms became less negatively charged. This change results in increased repulsion or decreased attraction between the Rh and carbon atoms, leading to weaker adsorption in positive electric fields. Similarly, CO molecules bonded to the Rh surface through C–Rh bonds, where both the Rh and carbon atoms were positively charged. Therefore, in positive electric fields, the repulsion or weaker bonding between the Rh and carbon atoms was increased, reducing the strength of the adsorption. Indeed, Fig. S7 (ESI†) again shows that for these species more positive Rh atoms correlates with weaker adsorption.
The third set of species, including CH2O, CH2CO, CH and H, showed adsorption characteristics different from the previous two groups, having parabolic adsorption curves (see Fig. 3 and Fig. S4, ESI†). CH2O and CH species bound to the surface through Rh–O and Rh–C bonds, respectively, while CH and H bound through Rh–C and Rh–H bonds, respectively. In CH2O and CH2CO, O atoms were negatively charged while carbon atoms were positively charged. Rh atoms bound to CH2O and CH2CO were positively charged. In positive electric fields, the charges on the oxygen atoms decreased, reducing the attraction between the negatively charged oxygen and the positively charged Rh. Conversely, in negative fields, the Rh atoms bound to oxygen became less positively charged, weakening the Rh–O bond. Thus, electric fields modulated the charges and interactions between oxygen and Rh atoms, affecting the adsorption energy profiles of CH2O and CH2CO. For CH, the carbon atom exhibited reduced negative charge in both negative and positive fields. This weakened the interaction between negatively charged carbon and positively charged Rh as reflected in the adsorption energy behavior of CH. Adsorbed H atoms were always negative upon adsorption, and in negative fields, negatively charged Rh atoms decrease the Rh–H interaction, while in positive fields, despite Rh being more positively charged, the reduced charge on H led to weaker adsorption. We note that similar negative charges for H interacting with metals were observed by others.100–102 Overall, the Bader charge analysis elucidates how external electric fields significantly influence charge transfer and ionic interactions between adsorbates and metal surfaces, altering the adsorption behavior of various intermediates.
For C–H bond cleavage, as shown in Fig. 5, both the reaction energies of CH3CO and CH2CO increased with increasing potential. The reaction energies increased by 0.37 and 0.38 eV for CH3CO and CH2CO, respectively, between −1 V Å−1 and 1 V Å−1. C–O bond formation in an electric field was more complicated. The results show that both negative and positive potentials favored C–O formation. In negative electric fields, the reaction energy decreased by up to 0.029 eV, while in positive electric fields, the reaction energy decreased by up to 0.056 eV. Thus, negative potentials favored the C–H bond cleavage and C–O bond formation reactions in EOR, while positive potentials favored only C–O bond formation. However, the effect of a potential on C–O formation was rather small.
Our results indicate that the presence of an external electric field has a significant effect on the reaction energies for selected C–C/C–H bond cleavage and C–O bond formation reactions. Negative electric fields could significantly lower the reaction energies of certain C–C and C–H bond cleavages. On the other hand, positive electric fields had minimal effect in lowering the reaction energies and significantly increased the reaction energies for some species. Both negative and positive electric fields favored the formation of the C–O bond, although the effect was small. Therefore, it appears that negative electric fields are likely to have the most beneficial effect in increasing the rate of the EOR reaction steps, at least in the absence of water. This finding correlates well with the experimental results that ethanol decomposes on Rh surfaces at negative onset potentials via C–H bond cleavage to form intermediates such as acetic acid and acetaldehyde, and C–C bond cleavage to form CO or CO2.106–109
In Fig. 6 we show the adsorption energies of selected species in the presence of an electric field and water. Fig. S10 (ESI†) shows similar adsorption energies for 15 different species. Unlike the vacuum calculations, the adsorption energy–potential plots for most species are parabolic, increasing with increasing/decreasing potential. Exceptions are CH3COOH and OH, which have negative slopes. The lowest adsorption energies do not always occur at 0 V Å−1, but can occur at weak positive potentials (CH3CH2O, CH2CH2O, CH2OH, CH3CO, and CH2) or weak negative potentials (CHCO, CO). Some species had their lowest adsorption energies near 0 V Å−1 (CH3CH2OH, CH2O, CH2CO, CH3, CH, and H). In the case of CO, a recent paper39 showed favorable interactions between water and CO at moderately negative potentials. We observed a similar effect where CO adsorption energies with water also decreased at moderate negative potentials.
In this study, as discussed in Section 2, we started with different initial geometries at 0 V Å−1 and chose the most stable structures as the initial geometries for further calculations in electric fields (i.e. Method 1). When we started with several possible initial geometries and then applied an electric field (i.e. Method 2), the adsorption energies, as shown in Fig. 6, could be quite different for some species. In general, the adsorption energies using Method 2 followed a trend similar to that of Method 1, but the adsorption energies decreased by −0.04 eV on average. The highest increases and decreases in adsorption energy were 0.17 eV (CH3 at 1.0 V Å−1) and 0.35 eV (CH3CH2OH at −0.6 V Å−1), respectively. CH2O also had significantly lower adsorption energies with Method 2 compared to Method 1 by an average of 0.12 eV. Fig. 6 shows that the differences in adsorption energies between Methods 1 and 2 are often most pronounced at larger potentials (e.g. near 1 V Å−1 or −1 V Å−1): CH, OH, CH3, CH2, CH2CH2O, etc.
We discuss a specific example of how the optimization approach affects the final geometries. Fig. 7 and Section 7 of the ESI† both provide details on the geometries of CH3CH2O using Methods 1 and 2. When using both Method 1 and Method 2, the orientation of the water molecule adopts one of two configurations, either facing the surface as H-down (see Fig. 7 using Method 1 at −1 V Å−1), or lying flat as H-up (see Fig. 7 using Methods 1 and 2 at 0 V Å−1). However, it was observed that the water molecule preferred the H-down position towards the metal surface only under the influence of strong electric fields when Method 1 was applied. Conversely, in Method 2, the configurations of the water molecules were more complex, exhibiting both surface-facing and flat positions at different electric fields without following a consistent pattern. These patterns align with previous studies suggesting that varying electric fields significantly affect water molecule orientations and interactions on the metal surface.30,39,118 It is noteworthy that in the case of *CH3CH2O, the water favored an H-down orientation at −1.0 V Å−1 using Method 1. However, using Method 2, the H-up orientation was found to be the most energetically favorable at the same electric field. Conversely, at −0.4 V Å−1, the H-up orientation was preferred using Method 1, while the H-down configuration was energetically preferred using Method 2. This difference in geometric preferences can be attributed to the different approaches used in Method 2, where both H-up and H-down configurations were initially modeled for geometry optimization and energy calculations at various electric fields. Therefore, the Method 2 configurations shown in Fig. 7 represent the most energetically favorable results of these calculations.
Table 2 also shows that for the ethanol-related intermediates, Methods 1 and 2 yield similar Bader charges under positive electric fields and no electric field conditions. However, under strong negative electric fields at −1.0 V Å−1, pronounced differences in Bader charges are observed for species such as *CH3CH2OH, *CH2O, *CH2, *CH, and *CH3COOH. In these cases, Method 1 tends to favor the H-down configuration of the water molecules, while Method 2 shows a preference for the H-up configuration. This difference in water molecule orientation results in significant Bader charge discrepancies (greater than 0.45 e−) between the two methods, underscoring the influence of solvent interactions and molecular orientation on electronic properties.
Hydrogen bond distances at different potentials are also given in Table S3 (ESI†). As previously discussed, the differences in the most energetically favorable configurations of the intermediates between Method 1 and Method 2 can be substantial, especially under different external electric fields, mainly due to fluctuations in the orientation of the water molecules (either H-up or H-down). Consequently, these orientation differences affect the hydrogen bonding distances between water molecules and adsorbates. For example, in the case of CH3CH2O, the interaction between the water molecule and the adsorbate exhibits weak hydrogen bonding, with average bond distances of 2.75 Å for Method 1 and 2.50 Å for Method 2, showing notable differences in the most energetically stable configurations between the two methods (Fig. 7). Conversely, there are cases where the most energetically favorable structures remain consistent using both methods. To illustrate, we also provide examples such as CH2CH2O and CO, where the interaction between water molecules and adsorbates involves strong hydrogen bonding, with average bond distances of 1.49 Å for Method 1 and 1.46 Å for Method 2 in CH2CH2O, and 1.93 Å for Method 1 and 1.94 Å for Method 2 in CO. The most energetically stable geometries for CH2CH2O and CO are consistent between Method 1 and Method 2 (see Fig. S12 and S13, ESI†). In summary, Methods 1 and 2 may give similar geometries and energies for some species. But our results have also shown that simply using the most stable geometries from potential-free calculations (i.e., Method 1) may not yield the most stable geometries under an applied potential and that the initial geometries may strongly affect the geometry optimization. Care must be taken to ensure that the correct geometries are used for calculations with an electric field.
Fig. 3 shows the adsorption energies in vacuum, while Fig. 6 shows adsorption energies in the presence of water. We also show a comparison of adsorption energies in vacuum and water in Fig. S15 (ESI†). The adsorption energies decreased significantly in some cases in the presence of an electric field without a water molecule present, as indicated by the negative slope of the adsorption energy curves. However, the lowest adsorption energies tended to occur near 0 V Å−1 in the presence of water, while this was not the case with no water molecule present. Adsorption energies tended to increase in water compared to vacuum for several species: CH3CH2O, CH3, and CH2, CH. The largest increase in adsorption energy in water compared to vacuum occurred with CH3, having an increase of 0.46 eV at 1.0 V Å−1. The average adsorption energy increases in water versus vacuum are 0.14, 0.13, 0.08 and 0.08 eV for CH3CH2O, CH3, CH2, CH, respectively. However, the adsorption energies in water decreased compared to vacuum for several species: CH3CH2OH, CH2CH2O, CH2O, CH2CO, CHCO, CO, H, and OH. The average decreases in adsorption energy were −0.13, −0.16, −0.10, −0.12, −0.29, −0.16, −0.01, and −0.24 eV for CH3CH2OH, CH2CH2O, CH2O, CH2CO, CHCO, CO, H, and OH, respectively. The largest decrease was −0.42 eV for OH.
In conclusion, in the presence of water, the adsorption of several adsorbates could be significantly affected by an electric field. Water interactions with an adsorbate resulted in adsorption behavior that was significantly different from that in vacuum for many adsorbates. Adsorption energy curves in the presence of water tended to be parabolic, while adsorption energy curves in vacuum tended to be more linear, with positive or negative slopes. Adsorption energies decreased for some species in the presence of water (compared to vacuum calculations) due to the formation of intermolecular hydrogen bonds. Some species were destabilized with water compared to vacuum. In addition, relying solely on vacuum-optimized geometries to guide solvent calculations (Method 1) may not yield the most stable geometries at the applied potential. To ensure that the most stable geometries are obtained, several initial geometries should be considered (Method 2). This effect of water on adsorption energies can have an impact on reactivity, which will be discussed further in the next section.
Fig. 9 shows CDD plots for CH3CH2OH, while Fig. S9 (ESI†) shows CDD plots for CH2CO and CHCO. In vacuum CH3CH2OH has the most stable adsorption energy at positive potentials. Fig. 9 shows that in vacuum there are more electron density changes between the adsorbate and surface at 1 V Å−1, compared to the other CDD plots under vacuum, and thus is consistent with the adsorption energy behavior. Unsurprising, when water is present there are significant changes in electron density in the vicinity of the water molecule, as the water molecule interacts with both the surface and the adsorbate. Fig. 6 indicates that Method 2 geometries are the most stable for CH3CH2OH, and that adsorption energies are most stable near 0 eV, increasing under any electric field. This is consistent with the CDD plots. The CDD plots of CH3CH2OH using Method 2 have the largest electron density changes at 0 V Å−1. See for instance the region around the water molecule for these pronounced changes. Method 1 has the smallest electron density changes at −1 V Å−1, and noticeably the water molecule is farthest from the Rh surface. Similar patterns can be seen for the other molecules. CHCO, for instance, has the most stable adsorption energy in vacuum at negative potentials, and the greatest electron density changes in vacuum are seen at −1 V Å−1 for CHCO (see Fig. S9, ESI†).
For C–H bond cleavage (Fig. 11), the effect of an electric field was very similar for the vacuum and water cases. The reaction energies increased with increasing potential, although CH3CO showed a slight increase at very negative potentials when using Method 2. The reaction energies between Method 1 and 2 had an increase of up to 0.10 eV for the cleavage of the CH3CO C–H bond at −1.0 V Å−1, and a decrease of 0.10 eV at 1.0 V Å−1 for the cleavage of the CH2CO C–H bond. The average reaction energy changes were 0.01 eV for C–H scission in CH3CO and −0.03 eV for C–H scission in CH2CO. Methods 1 and 2 gave similar C–H scission reaction energies except at low potentials with CH3CO and high potentials with CH2CO. For C–O bond formation with water, the reaction energy curves were parabolic (concave) as in the vacuum calculations. Negative electric fields decreased the reaction energy by up to 0.30 eV, while positive electric fields decreased the reaction energy by up to 0.34 eV.
Fig. 4, 5, 10 and 11 show the reaction energies in vacuum and with water. We also show a comparison of these energies in Fig. S16 and S17 (ESI†). Comparing the reaction energies with water (Method 2) to the vacuum calculations, the reaction energies of C–C bond cleavage in CH3CH2O, CH3CO, and C–H bond cleavage in CH3CO and CH2CO were on average lower in water than in vacuum. The average energy decreases of these reactions were −0.10, −0.04, −0.14, and −0.18 eV, respectively. The largest energy decrease was −0.27 eV for the C–H bond cleavage in CH2CO. However, the reaction energies of C–C bond scission of CH3CH2OH, CH2CH2O, CH2CO, and CHCO became more endothermic in water compared to vacuum by 0.26, 0.14, 0.04, and 0.21 eV, respectively. The largest energy difference was 0.48 eV for CH3CH2OH. The C–O bond formation energies were more endothermic in water than in vacuum, with an average difference of 0.28 eV. These changes in reaction energy are due to strong adsorption of reactant intermediates (e.g., *CH2CH2O, *CH2CO) or weak adsorption of product intermediates (e.g., *CH2, *CH). The results are consistent with our previous solvation work,45 in that explicit water solvation favors C–C scission of CH3CH2O, CH3CO; and C–H scission in CH3CO and CH2CO. However, our current and previous work also showed that water inhibited the C–C scission of CH2CH2O, CH2CO and CHCO and C–O bond formation.
In summary, our results show that the application of an external electric field significantly affects the energies involved in the cleavage of C–C and C–H bonds with co-adsorbed water. This effect varies between reactions occurring under vacuum conditions and those with water, as shown in our results (as shown in Fig. 4, 5 and 10, 11). The choice of initial geometric configurations (Methods 1 and 2) yielded different results. In particular, C–C bond cleavage in molecules such as CH3CH2OH, CH3CH2O, CH3CO, along with C–H bond cleavage in CH3CO and CH2CO, showed more favorable (exothermic) reaction energies in the presence of water compared to vacuum scenarios. Conversely, certain reactions involving C–C bond cleavage (as in CH2CH2O, CH2CO, and CHCO) and C–O bond formation showed less favorable (more endothermic) results in water. In addition, the influence of electric fields on the reaction energy changes for most of the C–C bond cleavages studied typically showed a parabolic trend, with negative electric fields more likely to promote C–H bond cleavages and C–C cleavages in CH2CO. We do note that previous work46 examined C–C cleavage under potential, although only cleavage of CH3CO was studied using implicit solvation. In this work reaction energies only changed slightly with potential, possibly due to the use of implicit solvation and a different metal (Pd).
![]() | ||
Fig. 12 A comparison of C–C bond breaking reaction energies using the various approaches of this study. Indicated are the reactants for C–C scission, with reaction energies at different potentials. |
Our results show that at no applied potential (0 V Å−1), C–C scission was easiest for CHCO (i.e. the lowest reaction energy), followed by CH2CO and then CH3CO, regardless of whether water was present. The reaction energies decrease at negative potentials for CH3CO and CH2CO (positive slope), but increase for CHCO (negative slope), again regardless of whether water is present. Reaction energy changes for C–C scission of CHCO between −1 V Å−1 and 1 V Å−1 were 0.05 eV (vacuum), 0.03 eV (Method 1), and 0.07 eV (Method 2). These small numbers indicate that the applied field had only a small effect on the C–C scission of CHCO. On the other hand, the reaction energy changes for C–C scission of CH3CO between −1 V Å−1 and 1 V Å−1 were 0.46 eV (vacuum), 0.56 eV (Method 1), and 0.47 eV (Method 2). Reaction energy changes for C–C scission of CH2CO between −1 V Å−1 and 1 V Å−1 were 0.22 eV (vacuum), 0.22 eV (Method 1), and 0.12 eV (Method 2). Clearly, the electric field has a much larger effect on the scission of CH3CO and CH2CO. We note that while CHCO has the most exothermic reaction energies, at very low negative potentials the scission of CH2CO can become competitive with CHCO scission due to close reaction energies. For example, the reaction energies for CH2CO scission at −1 V Å−1 are −0.74 eV (vacuum) and −0.64 eV (Method 2), while the reaction energies for CHCO scission at −1 V Å−1 are −0.95 eV (vacuum) and −0.74 eV (Method 2). Our results thus show that negative potentials can open new reaction pathways for C–C scission involving CH2CO, and that the competition becomes more pronounced in the presence of water. This conclusion could not be reached without considering the electrochemical environment present during EOR.
We further examined the reaction data to understand and rationalize the observed trends. The reaction energy at a potential can be expanded as in the following series:119
![]() | (6) |
Vacuum | Method 1 | Method 2 | ||||
---|---|---|---|---|---|---|
|Δ![]() |
Δαrxn | |Δ![]() |
Δαrxn | |Δ![]() |
Δαrxn | |
*CH3CH2OH | 0.0376 | −0.0414 | −0.026 | −0.2772 | −0.0333 | −0.346 |
*CH3CH2O | −0.0475 | −0.0878 | −0.0696 | −0.2804 | −0.1038 | −0.4754 |
*CH2CH2O | 0.0206 | −0.0398 | −0.0602 | 0.208 | 0.0901 | −0.1394 |
*CH3CO | −0.2314 | −0.0842 | −0.287 | −0.1164 | −0.2269 | −0.3832 |
*CH2CO | −0.109 | 0.0076 | −0.1229 | 0.0356 | −0.063 | 0.005 |
*CHCO | 0.0288 | −0.0672 | 0.0173 | 0.0358 | 0.0354 | −0.0786 |
We do acknowledge the limitations of our results. All our calculations have essentially been static calculations, focused on reaction energies. This approach has been used previously to study EOR.45,46 Activation energies would provide more insight into the nature of these reaction steps. However, such calculations are time-consuming and complicated, especially when incorporating solvation and electric fields. Such calculations may be the topic of future work. Scaling relationships do indicate that often activation energies are proportional to reaction energies, and linear scaling relationships have been applied to the study of C–C breaking of ethanol over various metals (albeit with no electric fields or solvent molecules present).77,103 Related work37 on methane steam reforming over Ni showed linear scaling relationships changed only slightly in the presence of both positive or negative electric fields. Thus, we expect lower reaction energies to correspond to lower activation energies. We also point out that modeling the dynamic nature of electrochemical reactions is an ongoing area of research. For instance, kinetic Monte Carlo calculations have been used to simulate electrocatalytic systems as they change over time120,121 or ethanol decomposition.76 Certainly applying such methods to study the EOR would provide valuable insights, and again may be the topic of future work.
We also examined how electric fields and the presence of water impact ethanol oxidation on Rh(111). We employed two methods to incorporate water molecules into our calculations. In Method 1 the initial geometries were taken from converged structures involving no electric fields. In Method 2 four different initial geometries were used at each electric field strength. Method 2 is a more robust process to explore possible structures, but also more time-consuming. These approaches yielded different geometries and energy profiles for several species, emphasizing the importance of a comprehensive exploration of possible geometries in electrochemical systems. The presence of water altered the adsorption energy trends, causing them to generally become more parabolic under an electric field. It also enhanced C–C and C–H bond cleavage by up to −0.27 eV but could inhibit C–O bond formation by about 0.28 eV. Electric fields, especially negative fields, favor the cleavage of C–H and specific C–C bonds such as CH2CO, while most C–C bond cleavages become more parabolic under an electric field in the presence of water. We also found that C–C bond cleavage is most likely to occur in CHCO, followed by CH2CO and CH3CO. Although electric fields have minimal effect on C–C bond cleavage in CHCO, they significantly affect CH2CO C–C cleavage. Under strong electric fields C–C scission through CHCO and CH2CO become competitive, demonstrating the potential of electric fields to manipulate chemical reaction pathways. Overall, our study illuminates the significance of electric fields and solvent molecules in electrochemical ethanol oxidation, showcasing their impact on adsorption processes and reaction pathways.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4cp02765e |
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