Abstract
The solution-phase stability of the hydronium ion catalyst significantly affects the rates of acid-catalyzed reactions, which are ubiquitously utilized to convert biomass to valuable chemicals. In this work, classical molecular dynamics simulations were performed to quantify the stability of hydronium and chloride ions by measuring their solvation free energies in water, 1,4-dioxane (DIOX), tetrahydrofuran (THF), γ-valerolactone (GVL), N-methyl-2-pyrrolidone (NMP), acetone (ACE), and dimethyl sulfoxide (DMSO). By measuring the free energy for transferring a hydronium ion from pure water to pure organic solvent, we found that the hydronium ion is destabilized in DIOX, THF, and GVL and stabilized in NMP, ACE, and DMSO relative to water. The distinction between these organic solvents can be used to predict the preference of the hydronium ion for specific regions in aqueous mixtures of organic solvents. We then incorporated the stability of the hydronium ion into a correlative model for the acid-catalyzed conversion of 1,2-propanediol to propanal. The revised model is able to predict experimental reaction rates across solvent systems with different organic solvents. These results demonstrate the ability of classical molecular dynamics simulations to screen solvent systems for improved acid-catalyzed reaction performance.
Introduction
The catalytic upgrading of biomass (e.g., wood, crops, etc.) is a promising strategy to obtain valuable chemicals from renewable resources while limiting waste products (Huber et al., ; Stöcker, ; Tock et al., ; Shuai and Luterbacher, ; Nguyen et al., ; Walker et al., ). For example, cellulose, one of the primary components of lignocellulosic biomass, can be converted through a series of dehydration and hydrolysis reactions to form 5-hydroxymethylfurfural, a platform chemical for fuels and other commodity chemicals (Chheda et al., ; Corma et al., ; Román-Leshkov et al., ; Pagan-Torres et al., ; Mellmer et al., ; He et al., ). These reactions are typically performed in aqueous solution where extensive control over reaction kinetics and selectivity is available by tuning the temperature, catalyst, and solvent composition (Huber et al., ; Chheda et al., ; Román-Leshkov et al., ; Mellmer et al., ; Motagamwala et al., ; He et al., ; Won et al., ; Sener et al., ). Solution-phase biomass conversion reactions ubiquitously require an acidic proton catalyst (H+), which exists in solution as a hydronium ion (H3O+). In homogenous reactions, the catalyst is obtained from the addition of a Brønsted acid (He et al., ) and the reactions follow a specific catalysis mechanism since a protonated solvent is the catalyst. Figure 1A shows an example reaction for the acid-catalyzed dehydration of 1,2-propanediol to propanal, which is representative of acid-catalyzed reactions for biomass-derived model compounds (Mellmer et al., ; Walker et al., ). In these reactions, the hydronium ion catalyst (H3O+) protonates the reactant (R) to form a reactant/proton complex (RH+). The reaction proceeds to a charged transition state ([RH+]TS) and subsequently forms the product (P) with the hydronium ion reformed (Figure 1B). The relative stabilities of the reactant, transition state, and catalyst in solution are thus critical for determining reaction kinetics (Shuai and Luterbacher, ). Understanding how these solvent effects influence reaction kinetics is necessary to guide the optimization of solvent compositions and reactor conditions and maximize the productivity of biomass conversion reactions.
Figure 1
Previous studies have found that mixtures of water and organic, polar aprotic cosolvents (i.e., mixed-solvent environments) can increase or decrease the rates of Brønsted acid-catalyzed reactions depending on the stability of the acid catalyst (Mellmer et al.,
Building upon these studies, we hypothesized that acid-catalyzed reaction rates correlate with the formation of water-enriched local solvent domains because the catalyst is assumed to be stabilized by interactions with water and thus the formation of water-enriched local solvent domains would drive the partitioning of the catalyst to the reactant (Mellmer et al.,
It is experimentally difficult to directly measure the free energy of an isolated hydronium ion in solution since electroneutrality must be maintained (Reif and Hünenberger,
Herein, we use classical MD simulations to study the stability of a hydronium ion in six organic polar aprotic cosolvents: dioxane (DIOX), tetrahydrofuran (THF), γ-valerolactone (GVL), N-methyl pyrrolidine (NMP), acetone (ACE), and dimethyl sulfoxide (DMSO). We also study the stability of a chloride ion in the same solvents to calculate the effect of the conjugate base. We use previous literature values for the reaction rates of the acid-catalyzed conversion of 1,2-propandiol (PDO) as a model reaction to study the influence of the different cosolvents. Since our previous work found favorable agreement between MD simulation-derived descriptors with experimental reaction rates without mechanistic details of the reaction (Walker et al.,
Methods
Classical MD simulations were performed using GROMACS 2016 (Páll et al.,
We initialized simulation configurations using the protocol schematically depicted in Figure 2A. The initial simulation box containing water and cosolvent (if applicable) had dimensions of (6 nm)3 in all simulations and was equilibrated in a NPT simulation for 5 ns at T = 300 K and P = 1 bar with a velocity-rescale thermostat and Berendsen barostat. A single reactant or ion molecule (designated as “M” in Figure 2A) was then added to the system and equilibrated with the same barostat and thermostat for 500 ps. NPT production simulations were performed for all systems for 200 ns with a Parrinello-Rahman barostat and Nose-Hoover thermostat; simulations of the reactant, PDO, were performed at T = 433.15 K to match the experimental reaction temperature (Mellmer et al.,
Figure 2

(A) Schematic representation of simulation workflow for molecular dynamics and free energy simulations. M denotes either 1,2-propanediol, a hydronium ion, or a chloride ion. (B) Simulation snapshots of hydronium ion in pure water, 90 wt% DIOX, and 90 wt% DMSO. The hydronium ion is located at the center and only solvent molecules within a 5 Å radius is shown.
Each solvation free energy was computed from a series of stochastic dynamics simulations (Figure 2A). Simulations were initialized using an equilibrated solvent system (as described above) with a hydronium or chloride ion added to the system. The total potential of the system was defined as a function of two parameters, λLJ and λelec, which scale the LJ and electrostatic potentials between the solute and solvent, as shown in Equation 1:
and are the LJ and electrostatic potentials between solute and solvent, and are intramolecular bonded and non-bonded potentials of the solute, and and are the bonded and non-bonded potentials between all solvent molecules (Shivakumar et al.,
Results
Comparison Between Experimental Reaction Rates and Preferential Exclusion Coefficient
In our previous study of solution-phase acid-catalyzed reactions (Walker et al.,
We first analyze the solvent environment around PDO by calculating the radial distribution function (RDF). The RDF quantifies the solvent density, normalized by the bulk solvent density, at a distance r away from a central point. Figure 3 shows the RDF between the center of mass of PDO and water for 90 wt% DIOX, 90 wt% DMSO, and pure water. In 90 wt% DIOX, the peak of the RDF is significantly higher than in pure water, indicating that water preferentially partitions to the local solvent domain around PDO in high concentrations of DIOX. Conversely, in 90 wt% DMSO, the first peak of the RDF is almost the same as in pure water and the RDF then drops below unity at ~0.60 nm, indicating the local depletion of water. The diminished water content near PDO in aqueous mixtures of DMSO is due to the cosolvent's high affinity for oxygen groups, resulting in a competition between water and DMSO for the hydroxyl groups of PDO (Vishnyakov et al.,
Figure 3

Radial distribution function between the center of mass of PDO and water in 90 wt% DIOX, 90 wt% DMSO, and pure water. Local and bulk domain cutoffs were determined as the value of r for which the RDF reaches unity. Bin widths for the RDFs were set to 0.02 nm.
Since RDFs are difficult to compare across different cosolvent concentrations, we previously computed the preferential exclusion coefficient (Γ), a molecular descriptor that quantifies the local domain composition around the reactant (Walker et al.,
nC and nW denote the number of cosolvent and water molecules, and superscripts L and B indicate molecules within the local and bulk domains, respectively. We define the boundary between local and bulk solvent domains as the value of r at which the RDF reaches unity (Figure 3), which occurs at r = 1.59 nm for both solvent systems. Positive Γ values indicate lower concentrations of cosolvent in the local solvent domain of the reactant compared to the bulk solvent domain. Therefore, positive Γ indicates the reactant has a higher affinity for water. Conversely, negative values of Γ indicate that the reactant has a higher affinity for the cosolvent.
We previously found that simulation-derived Γ correlates with experimental reaction rates quantified by the kinetic solvent parameter (σ) defined in Equation (3) (Walker et al.,
is the kinetic solvent parameter for the ith reaction and the subscript denotes the identity and composition (in jth mass fraction) of the organic solvent, is the apparent rate constant in aqueous mixtures with the organic phase, and is the apparent rate constant in pure water. For simplicity, we denote as σ. Positive σ values indicate that the reaction occurs more favorably in aqueous mixtures with organic solvents compared to pure water. Negative σ values indicate the converse. We take experimental reaction rates from Mellmer et al. (
Figure 4A compares values of simulation-derived Γ (filled lines) and experimentally measured σ (Mellmer et al.,
Figure 4

(A) Relationship between simulated preferential exclusion coefficient (Γ) and experimentally determined kinetic solvent parameters (σ) for aqueous mixtures of DIOX and DMSO. Experimental values were taken from Mellmer et al. (
Solvation Free Energy of the Hydronium Ion in Pure Solvent Systems
Previous studies have found that the hydronium ion is more stable in DMSO than water based on lower solvation free energies (Kelly et al.,
We calculated the solvation free energy of the hydronium ion in six organic, polar aprotic solvents (Figure 5A) and performed the same calculations for a chloride ion to determine the solvation free energy for a conjugate base. We selected polar aprotic solvents due to their relevance to acid-catalyzed biomass conversion processes, in which inclusion of these solvents has been found to enhance reaction performance (Mellmer et al.,
Figure 5

(A) Chemical structures of the organic solvents used in this study. (B) Thermodynamic cycle used to compute the free energy for transferring a hydronium or chloride ion from pure water to pure organic solvent. and are solvation free energies while is the transfer free energy computed from Equation 4. (C) Transfer free energies for six pure organic solvents. Cyan and purple bars indicate hydronium () and chloride (Cl−) ion transfer free energies, respectively. Dashed lines indicate the sum of the transfer energies. Error bars were computed from the standard deviation of two trials; the error is <1 kJ/mol and is not visible in the plot. The error is tabulated in Supplementary Table 4.
We computed the free energy of transferring the hydronium or chloride ion from water to solvent systems with organic solvents using Equation 4 (schematically illustrated in Figure 5B):
k denotes the solvent system of interest and j denotes either a hydronium or chloride ion. A negative value of indicates that the ion is thermodynamically stabilized in the kth solvent system compared to pure water. Figure 5C shows of the hydronium and chloride ions in each pure solvent. For the hydronium ion (cyan bars), is positive for DIOX, GVL, and THF, indicating that the hydronium ion is unfavorable in these solvents. These results support our prior assumption that the hydronium ion prefers water rather than the organic phase in these solvents, allowing us to correlate the formation of water-enriched local domains to reaction kinetics (Walker et al.,
Table 1
| Kamlet-taft Parameters | ||||||
|---|---|---|---|---|---|---|
| Solvent | Dielectric constanta | αb | βb | π*c | ∑ΔG | |
| DIOX | 2.20 | 0.00 | 0.37 | 0.49 | 184.6 | 389.85 |
| THF | 7.40 | 0.00 | 0.55 | 0.55 | 53.0 | 214.91 |
| GVL | 36.47 | 0.00 | 0.60 | 0.83 | 37.8 | 134.36 |
| Water | 78.50 | 1.17 | 0.47 | 1.14 | 0.0 | 0.00 |
| NMP | 32.16 | 0.00 | 0.77 | 0.92 | −4.3 | 101.25 |
| ACE | 20.70 | 0.08 | 0.43 | 0.62 | −11.2 | 99.55 |
| DMSO | 48.90 | 0.00 | 0.76 | 1.00 | −63.5 | 41.69 |
Dielectric constants and Kamlet-Taft parameters (α, β, π*) for pure solvents, tabulated according to decreasing transfer free energy of a hydronium ion () in these solvents. ∑ΔG was computed with Equation 5.
All solvation free energies are in units of kJ/mol.
Values are from Fowler et al. (
Values from Marcus (
Values from Laurence et al. (
Solvation Free Energy of the Chloride Ion in Pure Solvent Systems
While the solvation free energy of the hydronium ion alone quantifies catalyst stability, the effect of the solvent on acid dissociation equilibrium depends on the solvation free energy of the hydronium ion and its conjugate base (i.e., the chloride ion). Figure 5C shows that is positive for all pure organic solvent systems (purple bars), indicating that the chloride ion thermodynamically prefers water over each of these solvents. Furthermore, the solvation free energies for the chloride ion do not vary significantly for the different organic solvents, with the exception of DIOX and THF. The difference in the solvation of the hydronium and chloride ions is likely due to differences in hydrogen bonding capabilities: the hydronium ion can donate and accept hydrogen bonds while the chloride ion can only accept hydrogen bonds. Since water is the only solvent in this study that can donate hydrogen bonds, it is expected that the chloride ion is most stable in water.
The effect of the solvent on the solvation free energies of the hydronium and chloride ions relative to their solvation free energies in water is quantified via the term ∑ΔG, which we define in Equation 5 as:
We expect that positive values of ∑ΔG would reduce acid dissociation relative to pure water due to the decreased stability of the dissociated ions in the pure organic solvent. Figure 5C shows that ∑ΔG is positive for each organic solvent (black dashed lines). This result suggests that all of the polar aprotic solvents would decrease acid dissociation, leading to the reduced catalyst availability associated with weak acids based on experiments (Mellmer et al.,
Relationship Between Solvation Free Energies and Solvent Parameters
Given the computational expense of free energy calculations, we next sought to relate the transfer free energy results ( and ∑ΔG) to tabulated solvent properties to determine if these properties could accelerate solvent screening. Table 1 compares transfer free energy values to solvent dielectric constants and Kamlet-Taft parameters (α, β, π*). We use the dielectric constant to quantify the polarizability of the solvents and the Kamlet-Taft parameters to quantify hydrogen-bond donating ability (acidity, α), hydrogen-bond accepting ability (basicity, β), and polarity/polarizability (π*) (Kamlet and Taft,
These data suggest that typical solvent-specific parameters cannot easily describe the interplay of solute-solvent interactions and solvent reorganization that dictate the measured transfer free energies. We further computed the RDF between the hydronium ion and pure solvents (Supplementary Figure 7, Supplementary Material) to determine if solvent structure correlated with the transfer free energies, but we do not find a clear trend to explain the results found in Figure 5C. This data thus suggests that the free energy calculations are providing new information that can be used to predict the preference of the hydronium ion for either water or an organic solvent and quantify the effect of solvent composition on acid dissociation. It is also possible that the MD workflow is insufficiently accurate to predict these values, particularly given the classical model of the hydronium ion. However, the good agreement between the calculated solvation free energies of the hydronium and chloride ions in water with experimental data suggests that the model is reasonable. We also emphasize that DIOX, THF, and GVL have positive values of and lead to increased reaction rates in mixed-solvent systems when water is enriched near the reactant, while DMSO has a negative value of and leads to increased reaction rates in mixed-solvent systems when the cosolvent is enriched near the reactant. The distinct behavior of these cosolvents mirrors the difference in the sign of the calculated transfer free energies, suggesting that the transfer free energies are correctly capturing differences in the preference of the hydronium ion for bulk organic solvent.
Transfer Free Energies of the Hydronium and Chloride Ion in Mixed-Solvent Systems
Figure 6A shows the free energies for transferring either a hydronium or chloride ion to aqueous mixtures of DMSO and DIOX from pure water; these solvents represent extrema of low and high affinity cosolvents for the hydronium ion. In aqueous mixtures of DMSO, Figure 6A shows a monotonic decrease in the hydronium ion transfer free energy (i.e., an increase in hydronium ion stability relative to pure water) as the mass fraction of the organic phase increases. Since the free energy calculations in pure organic solvents (Figure 5C) show that pure DMSO stabilizes the hydronium ion more than water, these results agree with the expectation that increasing concentrations of DMSO results in improved stability of the hydronium ion. Figure 6B shows RDFs between the hydronium ion and both water and DMSO in 90 wt% DMSO. The peak of the ion-water RDF in 90 wt% DMSO is higher than in pure water, showing a local enrichment of water around the ion; however, there is also a cosolvent peak at ~0.38 nm, showing an enrichment in DMSO. Therefore, water and DMSO both favorable solvate the hydronium ion (visually shown in Figure 2C), leading to its increased stability relative to pure water. These results are consistent with experimental trends that find that increasing the concentration of DMSO monotonically increases basicity (Catalán et al.,
Figure 6

(A) Transfer free energies for transferring hydronium (, filled lines) and chloride (Cl−, dashed lines) ions from pure water to aqueous mixtures of dioxane (DIOX, blue lines) and dimethyl sulfoxide (DMSO, red lines). The sums of the transfer free energies (∑ΔG) are shown as green lines. Error bars are not shown; they range from 0 to 2.5 kJ/mol when averaging two trials and tabulated in Supplementary Table 5. (B) Radial distribution function (RDF) between the center of mass of the hydronium ion to water (top) and the organic solvent (bottom) in 90 wt% DIOX, 90 wt% DMSO, and pure water. Bin widths for the RDFs were set to 0.02 nm.
In aqueous mixtures of DIOX, Figure 6A shows a non-monotonic trend in the hydronium ion transfer free energy as the mass fraction of the organic phase increases. The transfer free energy is negative for all mixed compositions indicating that the hydronium ion is more stable than in either pure solvent. In the RDFs presented in Figure 6B, the peak of the ion-water RDF in 90 wt% DIOX is almost 10-fold larger than the peak in pure water, indicating a significant enrichment of water around the hydronium ion (visually shown in Figure 2B). In addition, the cosolvent RDF (Figure 6B, bottom) shows that DIOX is depleted near the hydronium ion up to distances of about 1 nm. These results together indicate that the hydronium ion nucleates a local domain of water molecules confined within the vicinity of the ion by the surrounding cosolvent. We attribute the decreased free energy of the hydronium ion in the mixed-solvent environment to the formation of this domain, which effectively sequesters water molecules to eliminate unfavorable water-cosolvent interactions that are not present in either pure solvent. Surprisingly, this data suggests that there should not be a driving force for hydronium ions to partition from bulk mixed-solvent environments to water-enriched domains near hydrophilic reactants as previously hypothesized because the solvation free energy of the ion in pure water is higher than in the mixed-solvent environment. This finding suggests that the stabilization of the charged transition state by confined water molecules in the water-enriched local domain might be the dominant factor leading to increased reaction rates. However, these calculations omit explicit modeling of the reactant, which could affect partitioning thermodynamics.
Finally, Figure 6A shows that the chloride ion is not favored in any mixed-solvent composition, resulting in positive and ∑ΔG values for all DIOX and DMSO mass fractions. These data again indicate that acid dissociation is preferred in pure water rather than any mixed-solvent environment and thus weak acids are less likely to dissociate, diminishing reaction performance.
Discussion
Screening Solvent Properties Using a Classical Hydronium Ion Model
Recent studies of acid-catalyzed biomass conversion reactions have illustrated that the stability of the hydronium ion catalyst in various mixed-solvent environments can dramatically affect reaction rates (Mellmer et al.,
In mixed-solvent environments, the solvation structure around the hydronium ion show that water-enriched local domains are formed, analogous to water-enrichment around hydrophilic reactants (Mellmer et al.,
In all solvent environments studied, the sum of the transfer free energies of the hydronium and chloride ions from water was positive. This result indicates that non-aqueous environments tend to suppress acid dissociation, leading to lower catalyst availability for weak acids that translates to lower reaction rates (Mellmer et al.,
Incorporation of Hydronium Ion Stability Into the Correlative Model of Reaction Rates
Figure 4 showed that the acid-catalyzed dehydration of PDO depends on the choice of cosolvent, with the experimentally measured kinetic solvent parameter (σ) correlating with the simulation-derived preferential exclusion parameter (Γ) in aqueous mixtures of DIOX and DMSO. This correlation is based on the physical understanding that catalytic hydronium ions preferentially partition to the water-enriched local domain around the reactant, increasing reaction performance and leading to a positive correlation between σ and Γ (Figure 4B). However, the correlation between σ and Γ is negative in DMSO, a solvent for which water depletion around the reactant is observed while reaction rates still increase. We hypothesized that the negative correlation may be because the hydronium ion preferentially interacts with DMSO rather than water and thus partitions to the water-depleted, DMSO-enriched local domain. This hypothesis is supported by the negative free energy for transferring a hydronium ion from water to DMSO as shown in Figure 5B. Thus, the correlation between Γ and σ must be adjusted to account for the stability of the hydronium ion in the local domain.
We include the sign of the hydronium ion transfer free energy between pure organic solvent to water, , as a correction term in the preferential exclusion coefficient (Γ′) by using Equation 6:
Equation 6 ensures that Γ′ and σ are positively correlated for aqueous mixtures of DMSO as shown in Figure 7A. We interpret Γ′ as quantifying the enrichment of the solvent (water or cosolvent) that preferentially stabilizes the hydronium ion, such that larger values of Γ′ suggest higher catalyst availability in the local domain of the reactant. Since Γ′ and σ are positively correlated for both aqueous mixtures of DIOX and DMSO, we can then write a correlative model for σpred that bridges these distinct solvents using Equation 7:
Figure 7

(A) Correlation between simulated preferential exclusion coefficient with solvation free energy correction term (Γ′), as expressed in Equation 7, and experimentally determined kinetic solvent parameters (σ) for aqueous mixtures of DIOX and DMSO. Experimental values were taken from Mellmer et al. (
A is a constant. Supplementary Figure 8 shows the correlation between σpred and σexp when combining results from both DIOX-water and DMSO-water mixtures, resulting in a best-fit slope of 0.25 (ideally this value should be unity), and a root-mean-square error (RMSE) between predicted and experimental values of 0.39. Similar to our previous work (Walker et al.,
Since acid-catalyzed reactions generally form a charged transition state after protonation of the reactant (Figure 1B), we interpret as a unitless metric that estimates transition state stability in mixed-solvent systems compared to pure water. In our prior work, the reactant-water hydrogen bonding lifetime was identified as a descriptor that quantified transition state stability (Walker et al.,
We combined Γ′ and using the multilinear regression model shown in Equation 9, where A, B, and C are coefficients. To enable comparison between the coefficients, we standardized Γ′ and by subtracting their mean and dividing by their standard deviations as described in Supplementary Section 5.2. All standardized variables are denoted by a hat accent.
Figure 7B shows the correlation between σpred and σexp when using Equation 9 and combining results from both DIOX-water and DMSO-water mixtures. The best-fit slope is 0.91, close to the ideal value of unity, and the RMSE between predicted and experimental values is 0.13, which is comparable to experimental error (Walker et al.,
Conclusions
We performed classical molecular dynamics simulations and solvation free energy calculations to quantify the stability of hydronium and chloride ions in six organic, polar aprotic solvents. We found that the hydronium ion is favorably solvated in pure NMP, ACE, and DMSO solvents, but unfavorably solvated in pure DIOX, THF, and GVL solvents. In mixed-solvent environments, the inclusion of water with DIOX stabilizes the hydronium ion more than their pure solvent counterparts. We attribute this increased stabilization to the formation of water-enriched local solvent domains around the hydronium ion. In aqueous mixtures of DMSO, the hydronium ion is further stabilized with increasing concentration of the organic phase. Conversely, the chloride ion is destabilized in all pure organic solvents and mixed solvent systems, inhibiting acid dissociation. By quantifying the stability of the hydronium ion in organic solvents, we obtained a new cosolvent-specific descriptor that quantifies acid catalyst stability. We incorporated this descriptor into a correlative model for 1,2-propanediol dehydration reaction rates to demonstrate that the solvation free energy results can be used to bridge reaction rate predictions across different cosolvent systems. Incorporating information about the acid catalyst stability in different solvent mixtures represents an important step toward the rational design of mixed-solvent environments for acid-catalyzed reaction schemes and has the potential to alleviate time-intensive experimentation that accompanies the optimization of biomass conversion reactions for maximum productivity.
Statements
Data availability statement
All datasets generated for this study are included in the manuscript and/or the Supplementary Files.
Author contributions
AC designed, performed, and analyzed the molecular dynamics simulations. AC and RV conceived of the simulations, interpreted the results, and wrote the manuscript.
Funding
The authors acknowledge support from the Department of Chemical and Biological Engineering at the University of Wisconsin-Madison and the Wisconsin Alumni Research Fund. This work used the Extreme Science and Engineering Discovery Environment (XSEDE), which is supported by National Science Foundation grant number ACI-1549562. This work also used the computing resources and assistance of the UW-Madison Center for High Throughput Computing (CHTC) in the Department of Computer Sciences. The CHTC is supported by UW-Madison, the Advanced Computing Initiative, the Wisconsin Alumni Research Foundation, the Wisconsin Institutes for Discovery, and the National Science Foundation, and is an active member of the Open Science Grid, which is supported by the National Science Foundation and the U.S. Department of Energy's Office of Science.
Acknowledgments
The authors would like to thank Benginur Demir for sharing the 1,2-propanediol dehydration experimental data.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fchem.2019.00439/full#supplementary-material
References
1
BerendsenH. J. C.GrigeraJ. R.StraatsmaT. P. (1987). The missing term in effective pair potentials. J. Phys. Chem.91, 6269–6271. 10.1021/j100308a038
2
BestR. B.ZhuX.ShimJ.LopesP. E.MittalJ.FeigM.et al. (2013). Optimization of the additive CHARMM all-atom protein force field targeting improved sampling from the backbone and side chain and dihedral angles. J. Chem. Theory Comput.8, 3257–3273. 10.1021/ct300400x
3
BeutlerT. C.MarkA. E.VanschaikR. C.GerberP. R.VangunsterenW. F. (1994). Avoiding singularities and numerical instabilities in free-energy calculations based on molecular simulations. Chem. Phys. Lett.222, 529–539. 10.1016/0009-2614(94)00397-1
4
BonthuisD. J.MamatkulovS. I.NetzR. R. (2016). Optimization of classical nonpolarizable force fields for OH- and H3O+. J. Chem. Phys.144:104503. 10.1063/1.4942771
5
BuhvestovU.RivedF.RafolsC.BoschE.RosesM. (1998). Solute-solvent and solvent-solvent interactions in binary solvent mixtures. Part 7. Comparison of the enhancement of the water structure in alcohol-water mixtures measured by solvatochromic indicators. J. Phys. Org. Chem.11, 185–192.
6
CaratzoulasS.VlachosD. G. (2011). Converting fructose to 5-hydroxymethylfurfural: a quantum mechanics/molecular mechanics study of the mechanism and energetics. Carbohydr. Res.346, 664–672. 10.1016/j.carres.2011.01.029
7
CatalánJ.DíazC.García-BlancoF. (2001). Characterization of binary solvent mixtures of DMSO with water and other cosolvents. J. Org. Chem.66, 5846–5852. 10.1021/jo010415i
8
ChhedaJ. N.HuberG. W.DumesicJ. A. (2007). Liquid-phase catalytic processing of biomass-derived oxygenated hydrocarbons to fuels and chemicals. Angew. Chem. Int. Ed. 46, 7164–7183. 10.1002/anie.200604274
9
CormaA.IborraS.VeltyA. (2007). Chemical routes for the transformation of biomass into chemicals. Chem. Rev.107, 2411–2502. 10.1021/cr050989d
10
DuignanT. T.BaerM. D.SchenterG. K.MundyC. J. (2017). Real single ion solvation free energies with quantum mechanical simulation. Chem. Sci.8, 6131–6140. 10.1039/C7SC02138K
11
FawcettW. R. (1993). Acidity and basicity scales for polar-solvents. J. Phys. Chem.97, 9540–9546. 10.1021/j100139a045
12
FowlerF. W.KatritzkyA. R.RutherfordR. J. (1971). Correlation of solvent effects on physical and chemical properties. Chem. Soc. B Phys. Org.460–469. 10.1039/j29710000460
13
HeJ. Y.LiuM. J.HuangK. F.WalkerT. W.MaraveliasC. T.DumesicJ. A.et al. (2017). Production of levoglucosenone and 5-hydroxymethylfurfural from cellulose in polar aprotic solvent-water mixtures. Green Chem. 19, 3642–3653. 10.1039/C7GC01688C
14
HessB.BekkerH.BerendsenH. J. C.FraaijeJ. G. E. M. (1997). LINCS: a linear constraint solver for molecular simulations.J. Comput. Chem.18, 1463–1472.
15
HorinekD.MamatkulovS. I.NetzR. R. (2009). Rational design of ion force fields based on thermodynamic solvation properties. J Chem. Phys.130:124507. 10.1063/1.3081142
16
HuberG. W.IborraS.CormaA. (2006). Synthesis of transportation fuels from biomass: chemistry, catalysts, and engineering. Chem. Rev.106, 4044–4098. 10.1021/cr068360d
17
HunenbergerP.ReifM. (2011). Single-ion solvation: experimental and theoretical approaches to elusive thermodynamic quantities. Single-Ion Solvation: Experimental and Theoretical Approaches to Elusive Thermodynamic Quantities (Cambridge: Royal Society of Chemistry, 1–664.
18
IzvekovS.VothG. A. (2005). Ab initio molecular-dynamics simulation of aqueous proton solvation and transport revisited. J. Chem. Phys.123:044505. 10.1063/1.1961443
19
JessopP. G.JessopD. A.FuD. B.PhanL. (2012). Solvatochromic parameters for solvents of interest in green chemistry.Green Chem.14, 1245–1259. 10.1039/c2gc16670d
20
KamletM. J.AbboudJ. L.TaftR. W. (1977). The solvatochromic comparison method. 6. The.pi.* scale of solvent polarities. J. Am. Chem. Soc.99, 6027–6038. 10.1021/ja00460a031
21
KamletM. J.AbboudJ. L. M.AbrahamM. H.TaftR. W. (1983). Linear solvation energy relationships. 23. A comprehensive collection of the solvatochromic parameters, pi-star, alpha and beta, and some methods for simplifying the generalized solvatochromic equation.J. Org. Chem.48, 2877–2887. 10.1021/jo00165a018
22
KamletM. J.TaftR. W. (1976). The solvatochromic comparison method. I. The.beta.-scale of solvent hydrogen-bond acceptor (HBA) basicities. J. Am. Chem. Soc.98, 377–383. 10.1021/ja00418a009
23
KangM.SmithP. E. (2007). Preferential interaction parameters in biological systems by Kirkwood-Buff theory and computer simulation. Fluid Phase Equilib.256, 14–19. 10.1016/j.fluid.2006.11.003
24
KellyC. P.CramerC. J.TruhlarD. G. (2007). Single-ion solvation free energies and the normal hydrogen electrode potential in methanol, acetonitrile, and dimethyl sulfoxide. J. Phys. Chem. B111, 408–422. 10.1021/jp065403l
25
KlimovichP. V.ShirtsM. R.MobleyD. L. (2015). Guidelines for the analysis of free energy calculations. J. Comput. Aided Mol. Des.29, 397–411. 10.1007/s10822-015-9840-9
26
KoppelI. A.PalmV. A. (1972). The influence of the solvent on organic reactivity, in Advances in Linear Free Energy Relationships, eds ChapmanN. B.ShorterJ. (Boston, MA: Springer US: Boston, MA). p., 203–280. 10.1007/978-1-4615-8660-9_5
27
LaurenceC.NicoletP.DalatiM. T.AbboudJ. L. M.NotarioR. (1994). The empirical-treatment of solvent solute interactions - 15 years of Pi. J. Phys. Chem.98, 5807–5816. 10.1021/j100074a003
28
MarcusY. (1993). The properties of organic liquids that are relevant to their use as solvating solvents. Chem. Soc. Rev.22, 409–416. 10.1039/cs9932200409
29
MarxD. (2006). Proton transfer 200 years after von Grotthuss: insights from ab initio simulations. Chemphyschem7, 1848–1870. 10.1002/cphc.200600128
30
MarxD.TuckermanM. E.HutterJ.ParrinelloM. (1999). The nature of the hydrated excess proton in water. Nature397, 601–604. 10.1038/17579
31
McGibbonR. T.BeauchampK. A.HarriganM. P.KleinC.SwailsJ. M.HernándezC. X.et al. (2015). MDTraj: a modern open library for the analysis of molecular dynamics trajectories. Biophys. J.109, 1528–1532. 10.1016/j.bpj.2015.08.015
32
MejiasJ. A.LagoS. (2000). Calculation of the absolute hydration enthalpy and free energy of H+ and OH-. J. Chem. Phys.113, 7306–7316. 10.1063/1.1313793
33
MellmerM. A.AlonsoD. M.LuterbacherJ. S.GalloJ. M. R.DumesicJ. A. (2014a). Effects of gamma-valerolactone in hydrolysis of lignocellulosic biomass to monosaccharides. Green Chem.16, 4659–4662. 10.1039/C4GC01768D
34
MellmerM. A.GalloJ. M. R.AlonsoD. M.DumesicJ. A. (2015). Selective production of levulinic acid from furfuryl alcohol in THF solvent systems over H-ZSM-5. ACS Catal.5, 3354–3359. 10.1021/acscatal.5b00274
35
MellmerM. A.SanpitaksereeC.DemirB.BaiP.MaK. W.NeurockM.et al. (2018). Solvent-enabled control of reactivity for liquid-phase reactions of biomass-derived compounds. Nat. Catal.1, 199–207. 10.1038/s41929-018-0027-3
36
MellmerM. A.SenerC.GalloJ. M. R.LuterbacherJ. S.AlonsoD. M.DumesicJ. A. (2014b). Solvent effects in acid-catalyzed biomass conversion reactions. Angew. Chem. Int. Ed. 53, 11872–11875. 10.1002/anie.201408359
37
MorroneJ. A.TuckermanM. E. (2002). Ab initio molecular dynamics study of proton mobility in liquid methanol. J. Chem. Phys.117, 4403–4413. 10.1063/1.1496457
38
MotagamwalaA. H.WonW. Y.MaraveliasC. T.DumesicJ. A. (2016). An engineered solvent system for sugar production from lignocellulosic biomass using biomass derived gamma-valerolactone. Green Chem.18, 5756–5763. 10.1039/C6GC02297A
39
NguyenT. Y.CaiC. M.KumarR.WymanC. E. (2017). Overcoming factors limiting high-solids fermentation of lignocellulosic biomass to ethanol. Proc. Natl. Acad. Sci. U.S.A.114, 11673–11678. 10.1073/pnas.1704652114
40
Pagan-TorresY. J.WangT. F.GalloJ. M. R.ShanksB. H.DumesicJ. A. (2012). Production of 5-Hydroxymethylfurfural from glucose using a combination of lewis and bronsted acid catalysts in water in a biphasic reactor with an alkylphenol solvent. ACS Catal.2, 930–934. 10.1021/cs300192z
41
PállS.AbrahamM. J.KutznerC.HessB.LindahlE. (2015). Tackling exascale software challenges in molecular dynamics simulations with GROMACS, in Solving Software Challenges for Exascale: International Conference on Exascale Applications and Software, EASC 2014, eds MarkidisSLaureE. (Cham; Stockholm: Springer International Publishing: Cham). p. 3–27. 10.1007/978-3-319-15976-8_1
42
PliegoJ. R. (2003). Thermodynamic cycles and the calculation of pK(a). Chem. Phys. Lett. 367, 145–149. 10.1016/S0009-2614(02)01686-X
43
PliegoJ. R.RiverosJ. M. (2000). New values for the absolute solvation free energy of univalent ions in aqueous solution. Chem. Phys. Lett.332, 597–602. 10.1016/S0009-2614(00)01305-1
44
PliegoJ. R.RiverosJ. M. (2001). The cluster-continuum model for the calculation of the solvation free energy of ionic species. J. Phys Phys. Chem. A105, 7241–7247. 10.1021/jp004192w
45
ReifM. M.HünenbergerP. H. (2011). Computation of methodology-independent single-ion solvation properties from molecular simulations. IV. Optimized Lennard-Jones interaction parameter sets for the alkali and halide ions in water. J. Chem. Phys.134:144104. 10.1063/1.3567022
46
Román-LeshkovY.BarrettC. J.LiuZ. Y.DumesicJ. A. (2007). Production of dimethylfuran for liquid fuels from biomass-derived carbohydrates. Nature447, 982–U5985. 10.1038/nature05923
47
RyckaertJ. P.CiccottiG.BerendsenH. J. C. (1977). Numerical-integration of cartesian equations of motion of a system with constraints - molecular-dynamics of N-alkanes. J. Comput. Phys.23, 327–341. 10.1016/0021-9991(77)90098-5
48
SagnellaD. E.LaasonenK.KleinM. L. (1996). Ab initio molecular dynamics study of proton transfer in a polyglycine analog of the ion channel gramicidin A. Biophys. J.71, 1172–1178. 10.1016/S0006-3495(96)79321-9
49
SchneiderC. P.TroutB. L. (2009). Investigation of cosolute - protein preferential interaction coefficients: new insight into the mechanism by which arginine inhibits aggregation investigation of cosolute - protein preferential interaction coefficients: new insight into the mechanism by. J. Phys. Chem. B113, 2050–2058. 10.1021/jp808042w
50
SenerC.MotagamwalaA. H.AlonsoD. M.DumesicJ. A. (2018). Enhanced furfural yields from xylose dehydration in the gamma-valerolactone/water solvent system at elevated temperatures. ChemSusChem11, 2321–2331. 10.1002/cssc.201800730
51
ShirtsM. R.ChoderaJ. D. (2008). Statistically optimal analysis of samples from multiple equilibrium states. J. Chem. Phys.129:124105. 10.1063/1.2978177
52
ShivakumarD.WilliamsJ.WuY.DammW.ShelleyJ.ShermanW. (2010). Prediction of absolute solvation free energies using molecular dynamics free energy perturbation and the OPLS force field. J. Chem. Theory Comput.6, 1509–1519. 10.1021/ct900587b
53
ShuaiL.LuterbacherJ. (2016). Organic solvent effects in biomass conversion reactions. ChemSusChem9, 133–155. 10.1002/cssc.201501148
54
ShuklaD.TroutB. L. (2011). Preferential interaction coefficients of proteins in aqueous arginine solutions and their molecular origins. J. Phys. Chem. B115, 1243–1253. 10.1021/jp108586b
55
ShulginI. L.RuckensteinE. (2007). Local composition in the vicinity of a protein molecule in an aqueous mixed solvent. J. Phys. Chem. B111, 3990–3998. 10.1021/jp066353n
56
StöckerM. (2008). Biofuels and biomass-to-liquid fuels in the biorefinery: catalytic conversion of lignocellulosic biomass using porous materials. Angew. Chem. Int. Ed47, 9200–9211. 10.1002/anie.200801476
57
TaftR. W.KamletM. J. (1976). The solvatochromic comparison method. 2. The.alpha.-scale of solvent hydrogen-bond donor (HBD) acidities. J. Am. Chem. Soc.98, 2886–2894. 10.1021/ja00426a036
58
TawaG. J.TopolI. A.BurtS. K.CaldwellR. A.RashinA. A. (1998). Calculation of the aqueous solvation free energy of the proton.J. Chem. Phys.109, 4852–4863. 10.1063/1.477096
59
TockL.GassnerM.MarechalF. (2010). Thermochemical production of liquid fuels from biomass: thermo-economic modeling, process design and process integration analysis. Biomass Bioenergy34, 1838–1854. 10.1016/j.biombioe.2010.07.018
60
TuckermanM.LaasonenK.SprikM.ParrinelloM. (1995a). Ab-initio molecular-dynamics simulation of the solvation and transport of hydronium and hydroxyl ions in water. J. Chem. Phys.103, 150–161. 10.1063/1.469654
61
TuckermanM.LaasonenK.SprikM.ParrinelloM. (1995b). Ab-Initio molecular-dynamics simulation of the solvation and transport Of H3o+ and Oh- ions in water. J. Phys. Chem.99, 5749–5752. 10.1021/j100016a003
62
TuckermanM. E.LaasonenK.SprikM.ParrinelloM. (1994). Ab-initio simulations of water and water ions. J. Phys. Cond. Matter6, A93–A100. 10.1088/0953-8984/6/23A/010
63
TuckermanM. E.MarxD.KleinM. L.ParrinelloM. (1997). On the quantum nature of the shared proton in hydrogen bonds. Science275, 817–820. 10.1126/science.275.5301.817
64
TunonI.SillaE.BertranJ. (1993). Proton solvation in liquid water - an abinitio study using the continuum model. J. Phys. Chem.97, 5547–5552. 10.1021/j100123a016
65
UosakiY.KawamuraK.MoriyoshiT. (1996). Static relative permittivities of water plus 1-methyl-2-pyrrolidinone and water plus 1,3-dimethyl-2-imidazolidinone mixtures under pressures up to 300 MPa at 298.15 K. J. Chem. Eng. Data41, 1525–1528. 10.1021/je960236b
66
VanommeslaegheK.HatcherE.AcharyaC.KunduS.ZhongS.ShimJ.et al. (2009). CHARMM general force field: a force field for drug-like molecules compatible with the CHARMM all-atom additive biological force fields. J. Comput. Chem.31, 671–690. 10.1002/jcc.21367
67
VargheseJ. J.MushrifS. H. (2019). Origins of complex solvent effects on chemical reactivity and computational tools to investigate them: a review. React. Chem. Eng.4, 165–206. 10.1039/C8RE00226F
68
VishnyakovA.LyubartsevA. P.LaaksonenA. (2001). Molecular dynamics simulations of dimethyl sulfoxide and dimethyl sulfoxide-water mixture. J. Phys. Chem. A105, 1702–1710. 10.1021/jp0007336
69
WalkerT. W.ChewA. K.LiH. X.DemirB.ZhangZ. C.HuberG. W.et al. (2018). Universal kinetic solvent effects in acid-catalyzed reactions of biomass-derived oxygenates. Energy Environ. Sci.11, 617–628. 10.1039/C7EE03432F
70
WalkerT. W.MotagamwalaA. H.DumesicJ. A.HuberG. W. (2019). Fundamental catalytic challenges to design improved biomass conversion technologies. J. Catal, 369, 518–525. 10.1016/j.jcat.2018.11.028
71
WohlfarthC. (2015). Static dielectric constant of γ-valerolactone, in Static Dielectric Constants of Pure Liquids and Binary Liquid Mixtures: Supplement to Volume IV/17, ed LechnerM. D. (Berlin: Springer Berlin Heidelberg), 91–91. 10.1007/978-3-662-48168-4
72
WonW. Y.MotagamwalaA. H.DumesicJ. A.MaraveliasC. T. (2017). A co-solvent hydrolysis strategy for the production of biofuels: process synthesis and technoeconomic analysis. React. Chem. Eng.2, 397–405. 10.1039/C6RE00227G
73
YuW.HeX.VanommeslaegheK.MacKernellA. D. (2012). Extension of the CHARMM general force field to sulfonyl- containing compounds and its utility in biomolecular simulations. J. Comput. Chem.33, 2451–2468. 10.1002/jcc.23067
Summary
Keywords
acid-catalyzed reactions, solvent effects, biomass conversion, hydronium ion, classical molecular dynamics simulation, solvation free energy
Citation
Chew AK and Van Lehn RC (2019) Quantifying the Stability of the Hydronium Ion in Organic Solvents With Molecular Dynamics Simulations. Front. Chem. 7:439. doi: 10.3389/fchem.2019.00439
Received
13 February 2019
Accepted
28 May 2019
Published
19 June 2019
Volume
7 - 2019
Edited by
Moisés Canle, University of A Coruña, Spain
Reviewed by
Valerije Vrcek, University of Zagreb, Croatia; Arturo Santaballa, University of A Coruña, Spain
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© 2019 Chew and Van Lehn.
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*Correspondence: Reid C. Van Lehn vanlehn@wisc.edu
This article was submitted to Green and Sustainable Chemistry, a section of the journal Frontiers in Chemistry
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