Open Access Article
Sofia M. Johansson†
,
Josip Lovrić‡
,
Erik S. Thomson
,
Xiangrui Kong
* and
Jan B. C. Pettersson
*
Department of Chemistry and Molecular Biology, University of Gothenburg, 413 90 Gothenburg, Sweden. E-mail: kongx@chem.gu.se; janp@chem.gu.se
First published on 29th April 2026
Organic aerosol particles undergo phase transitions through water uptake and release, which directly influence their physicochemical properties and impact aerosol–cloud interactions, climate, and air quality. Here, we combine environmental molecular beam (EMB) experiments with molecular dynamics (MD) simulations to investigate water interactions with valeric acid (VA) as a model organic aerosol system. Water molecules colliding with VA surfaces are predominantly trapped, with only a minor inelastic scattering channel observed. Most trapped molecules are weakly bound and desorb rapidly (69–83%), while a smaller fraction occupies more strongly bound surface states, leading to desorption on millisecond timescales (7–16%) or longer-term accommodation (5–20%). The water sticking coefficient shows little temperature dependence over 160–260 K, but depends strongly on film thickness, i.e., molecularly thin VA coatings exhibit higher sticking probabilities than micrometer-thick layers. These results suggest that molecularly thin VA coatings may exhibit differences in molecular arrangement that could contribute to differences in hygroscopic behavior compared to bulk-like surfaces.
Carboxylic acids are one of the most common reaction products from oxidation of volatile organic compounds (VOCs).7,8 Small carboxylic acids are highly water-soluble and hygroscopic, and are therefore ubiquitous in aqueous aerosol particles. This makes them active participants in aerosol–cloud interactions, influencing hygroscopic growth and cloud droplet activation.9–11 High relative humidity (RH) has been confirmed to favor formation of secondary inorganic aerosol (SIA), which strongly relates to haze episodes in urban areas.12,13 The effects of RH on secondary organic aerosol (SOA) are, however, more complicated. Here water influences the interplay of multiple factors such as photochemistry, particle acidity, viscosity and phase state.10 At atmospheric conditions organic aerosols exist in a wide range of different states, like amorphous glassy solids, highly viscous semi-solids and liquids.14 By adsorbing and/or desorbing water from the surroundings, organic aerosol particles may transition between states,15,16 and these processes will in turn have direct feedbacks on the particles’ chemical and physical characteristics. Thus, in addition to providing fundamental insight, understanding mechanisms of water uptake by atmospheric organics affects our ability to resolve and model aerosol particles and the complex climate system. In the present work, valeric acid surfaces are used as well-defined model systems to probe elementary gas-surface interaction processes such as trapping, desorption, and accommodation. While such condensed surfaces are not direct analogues of liquid aerosol droplets, the interfacial region in both systems involves confined or partially coordinated water molecules. Studying these interactions therefore provides molecular-level insight into processes that are relevant for water uptake at organic aerosol interfaces.
Several short-chained carboxylic acids present in the atmosphere have been studied using molecular dynamics (MD) simulations focused on interactions with water at molecular levels.17–23 For example, the mixing state of formic acid and water is driven by the water content and temperature; where at cold and dry conditions water forms islands on top of the formic acid aggregate surface, and in contrast at warm conditions and high RH the mixing is more homogeneous.18 Similar behavior has been reported for other short-chain carboxylic acids, such as acetic and propionic acid, where hydrogen bonding and interfacial structuring govern water uptake and mixing.19,21,23 Recently, water on valeric acid (VA) was reported to form small water islands on the surface of VA aggregates at low RH, and to partially penetrate into the bulk, while at high RH the majority of the water remains on the surface.20 The VA is a product of fermentation and/or chemical transformation of lignocellulosic feedstocks, thus it is a common gas molecule during biomass energy conversion processes. These studies provide insight into water-carboxylic acid interaction motifs at the molecular level. In the present work, the solid VA surfaces are treated as simplified model interfaces and are not intended to directly represent the structure of atmospheric aggregates.
There is also considerable fundamental interest in the surface properties of organic compounds. The VA crystal structure deviates from those of other linear carboxylic acids.24 While carboxylic acids mostly form bilayer crystal structures, VA exhibits a zig-zag pattern inside the monolayer. Evidently, this induces a different surface organization compared to other carboxylic acids. In addition, many crystals undergo surface changes in terms of increased disorder and/or melting below the bulk melting point,25,26 but the importance of these processes for organic crystals and the associated effects on gas uptake is incompletely understood.
In this study, we focus on the water interactions with VA surfaces, by employing the environmental molecular beam (EMB) method,27,28 while conducting complementary MD simulations as investigative tools. The EMB technique has been used for detailed studies of dynamics and kinetics of gas–surface interactions, including several water-organics systems,29–35 water-bare ice36 and water-organic coated ice,37 water-graphite,38 as well as organic-graphite39 and organic–organic systems.40,41 The information from the EMB and MD methods are complementary and thus these methods have been combined beneficially in several recent studies.34,35,39,42 Here, they are used to investigate the water uptake and sorption kinetics and dynamics in a water-VA interfacial system.
During experiments, VA condensation and evaporation processes on the graphite substrate are monitored using helium and light (670 nm) scattering. Elastic scattering of helium is highly sensitive to initial surface coverage, while the light scattering provides information about layer thickness and morphology for thicker adsorbates. Once a VA layer coats the graphite substrate the leak valve can be adjusted to maintain steady state conditions throughout the measurements. From 160 K to 220 K, thick solid VA layers (≈ 1 µm thickness) can be stably adsorbed and maintained. At temperatures above ∼220 K, these thick layers become unstable under the experimental conditions, whereas molecularly thin VA coatings on graphite remain stable and can therefore be examined at higher temperatures. The latter is too thin to be observed with the optical method, but is detected by helium scattering. This suggests that a condensed phase consisting of one or a few molecular layers has properties that make it more stable than bulk VA. The bulk melting temperature Tm of solid VA is 239.6 K, suggesting that the thicker layers form a solid coating.43 During measurements the MB is directed onto the VA coated substrate and the QMS detects the outgoing molecular flux for 10 ms time windows after each beam pulse impacts the surface. Given that the beam source-to-surface and surface-to-detector distances are well known the resulting data takes the form of mass intensity as a function of arrival time or equivalently reformulated as Time-of-Flight (ToF) distributions. Between measurements the graphite substrate is cleaned by increasing its temperature to 600 K, typically for a period of >12 hours.
The ToF distributions generated during experiments are analyzed to gain information about the kinetics and dynamics of the interactions between water molecules in the beam and the condensed VA layers. The time-dependent water flux from the surface may be explained as a combination of three components: a fast component related to inelastic scattering (IS) and two thermal desorption (TD) components with significantly different rate coefficients. In the analysis procedure, a non-linear, least-squares minimization is used to identify the optimum convolution of the incident beam profile, the IS component, and the TD components that best represent the ToF data. In these VA studies it becomes obvious that one IS and one TD channel cannot sufficiently fit the experimental data, whereas two desorption components adequately explain the ToF data. The inelastic component may be described as a modified Maxwell–Boltzmann distribution,44
![]() | (1) |
is a free fitting parameter representing the average IS velocity, kB is the Boltzmann constant, m is the mass of the D2O molecule, and TIS is a free fitting parameter indicative of the velocity spread of the IS component. Here, TIS is an effective fitting parameter describing the velocity spread of the inelastically scattered molecules and does not represent the physical surface temperature, since these molecules have not fully equilibrated with the surface.
Molecules that are thermalized in the interactions with the surface spend a finite time on the surface before desorbing. Thermal desorption is best explained as a convolution of two distributions, one ITDa that relates desorption velocities to the surface temperature,
![]() | (2) |
| ITDb = Cje−kt. | (3) |
Here the desorption rate coefficient k serves as a fitting parameter, t is the molecular arrival time, and due to the convolution Cj is a degenerate scaling factor with that given in eqn (2).
Hence, the fits of experimental ToF distributions are carried out with 7 free parameters. These parameters are also restricted by the physics of the components that they are describing, which limits the flexibility of solutions. Nevertheless, the most sensitive part is the IS component, due to its low intensity and relatively high noise in the beginning of ToFs, which makes the fittings slightly vary depending on the initial guess values. The fitting procedure is constrained by the physical form of the IS and TD components, which limits parameter correlations and reduces fitting ambiguity. The IS component is most sensitive to noise and initial guesses due to its low intensity, whereas the TDfast and TDslow components are more robustly determined. Consequently, the extracted branching fractions are primarily governed by the TD components and are less sensitive to fitting uncertainties.
In the VA experiments presented here, two TD components are identified and thus two independent ITDa and ITDb functions and convolutions must be constructed and further convoluted with the beam and IS components. Finally, a non-linear least squares fitting procedure uses numerical minimization to optimize the free fitting parameters. By comparing the fitting quality of one TD component fitting and two TD component fitting as shown in Fig. S1 in the SI, it is obvious that one TD component is insufficient to describe the desorption profiles. Confidence intervals presented in the results include propagated errors from the measurement and analysis procedure. Systematic errors, which dominate the displayed uncertainties, may arise from the QMS detection and beam intensity fluctuations during measurements. Non-systematic errors from unstable environmental chamber conditions during experiments are difficult to estimate, however, the experimental procedure is designed to minimize them.
The temperature dependence of the desorption rate coefficient can be extracted from the fitting procedure assuming Arrhenius type behavior,
![]() | (4) |
k versus 1/T, as illustrated by rearranging eqn (4),
![]() | (5) |
The angular flux for molecules leaving the substrate surface may generally be described by a cos(θ − θmax)n distribution, where θmax is the peak scattering angle with respect to the surface normal direction, θ is the observation angle also with respect to the surface normal, and n is a shape factor which either narrows or broadens the flux. Thermalized molecules lose their initial momentum in interactions with the surface and consequently desorb in all directions with no preference related to their incident direction. Thus, for the TD component, θmax = 0 and n = 1, resulting in a typical cos(θ) desorption distribution. This makes it easy to estimate the TD probability by observing the flux at any single scattering angle. The total integrated TD intensity IVATD is used to assess the absolute probability of thermal desorption of water molecules from the surface PTD. The PTD for D2O on a VA is retrieved by comparing IVATD with desorption from a clean graphite surface IGTD under similar conditions,
![]() | (6) |
The total integrated intensity for inelastic scattering IVAIS of water molecules from a VA surface is more difficult to estimate as it has a directed flow related to the MB incident angle. Thus IVAIS is quantified by assuming that scattering out of the plane, relative to the incident beam, has a similar angular profile as the in-plane scattering. A cos(θ − θmax)n function with θmax = 49–53° and n = 26–69 describes a narrow IS flux with a maximum close to the specular angle. The absolute inelastic scattering probability PIS is obtained by normalizing IVAIS to PTD. Molecules that are thermalized in the interaction with the surface and stay there for times longer than the experimental measurement time (10 ms) are assumed to be sticking on the surface. Thus a sticking coefficient α may be calculated from the absolute trapping desorption and inelastic scattering probabilities,
| α = 1 − PTD − PIS. | (7) |
The VA crystal lattice is modeled based on the structure characterized with X-ray diffraction.51 The crystal super cell is created by duplicating the unit cell in the x, y and z directions. After geometrical optimization, which removed all spurious contacts, the crystal is equilibrated in a NPT ensemble for 10 ns. In the next step, the slab surface is created by cutting the crystal in a given direction. Two alternative VA surfaces are chosen and energies are calculated to find a slab with the most energetically favorable surface, here determined to be a surface separating two monolayers. The simulation system consists of 4 352 atoms placed in a monoclinic box stretched by vectors sized 15.2 × 1.9 × 3.5 nm and having α, β and γ angles 90°, 39.59° and 90° respectively. The simulation box is extended 2 nm in the x direction (perpendicular to the surface) on each side to avoid image interactions between the slabs.
The VA crystal is gradually heated from 210 K to 270 K by performing simulated annealing in the NVT ensemble over 160 ns, and a simulated melting point is determined, Tm = 255 K. Subsequently, water interactions with the VA surface are investigated over a temperature range from 0.78Tm to 0.95Tm with simulations designed to resemble experimental conditions. Water is modeled with the SPC/E model52 where the choice of potential is motivated by previous work on carbohydrate interactions with water.53 Single water molecules are propagated towards the surface at a 45° angle with respect to the surface normal direction and an incident kinetic energy equal to 22.5 ± 0.5 kJ mol−1 (corresponding to a velocity of 1626 ms−1). Thenitial positions of water molecules are randomly chosen at a distance of 1 nm from the surface, and 5000 trajectories are propagated for 60 ps at each studied surface temperature. The water molecules are decoupled from the thermostat to avoid influencing the collision dynamics. The MD simulations are thus performed for single-water molecules under low-coverage, dry conditions and over short timescales, and therefore do not capture finite water coverage effects or the long-timescale desorption processes observed in the EMB experiments.
Inelastically scattered molecules typically lose 50–80% of their incident kinetic energy when colliding with the studied VA surfaces (Fig. 3). Within the experimental uncertainty, no clear trend is observed in the retained kinetic energy as a function of scattering angle. This is consistent with molecules that transfer energy efficiently both along and perpendicular to the surface plane, suggesting that water molecules interact with a relatively rough VA surface. The majority of the water molecules trap and thermalize on the studied VA surfaces, and reside there for some time (τ) before desorbing with a behavior that may be described with a temperature-dependent desorption rate coefficient (k). The water desorption observed from the VA surface is composed of two desorption components with distinct desorption rates. For TDfast the desorption rate is too fast to be experimentally resolved (τfast ≤ 10 µs), while for TDslow τslow ≈ 0.5–2.5 ms. The temperature-dependent desorption rate coefficient for the slow process is plotted in an Arrhenius fashion in Fig. 4. An activation energy for desorption and a pre-exponential factor are derived from the Arrhenius slope and intercept of the linear regression. The linear regression to the experimental data points in the Arrhenius plot yields Ea_slow = −3.8 kJ mol−1 and Aslow = 7.8 × 101 s−1. The low A and the negative Ea value indicate that the path to water desorption is a complex process involving more than one reaction step and the results do not provide direct information of a surface binding energy. The Arrhenius fit should therefore be regarded as an empirical description of the apparent TDslow kinetics rather than evidence for a single elementary desorption process. The derived Ea and A values are effective parameters reflecting a complex, multi-step process and should not be interpreted as direct adsorption energetics. This suggests that the slow desorption channel reflects a complex, multi-step process rather than a single elementary desorption event. The implications of this behavior for the underlying desorption mechanism are discussed in Section 4.
The impinging water molecules that are observed to remain on the surface for the entire experimental measurement time (10 ms), are defined as undergoing sticking on the surface. The sticking probability α eqn (7) on molecularly thin VA coatings on graphite and thick solid layers at different temperatures is presented in Fig. 5, together with the TDfast and TDslow fractions. The results are dominated (69–83%) by fast TD at all temperatures, with a minor contribution (7–16%) from slow TD, and no clear temperature dependence is observed. The same is true for the sticking probability α, that exhibits little variation with temperature. However, there is a small difference in α between thin VA coatings and thick solid VA layers, where more water is trapped on a thin layer (0.15 ≤ α ≤ 0.20) than on a thick layer (0.05 ≤ α ≤ 0.15). This phenomenon is contrary to observations reported in a recent study of the water/nopinone system.35 As described in Section 3.2, the VA molecules form dimers positioned horizontally along the multilayer surfaces, however, for the monolayer it seems that the carboxylic groups are more readily available on the surface, i.e. the dimer structure does not form or it is less stable compared to the bulk structure. The weak temperature dependence of α indicates that the structure of the molecularly thin VA layer does not undergo major changes in the investigated temperature range. This indicates that film thickness, rather than temperature, plays a more important role in determining water uptake under these conditions. This difference between thin and thick VA layers is discussed further in Section 4.
A lower limit for the activation energy of molecules undergoing sticking may be calculated from the experimental data and conditions. Assuming Arrhenius behavior at the maximum experimental temperature, a minimum surface residence time of 10 ms and a typical pre-exponential factor of 1013 s−1 for ordinary desorption,54 the activation energy for molecules undergoing sticking is estimated to be ≥55 kJ mol−1, representing a lower-bound value based on assumed Arrhenius behavior, a characteristic residence time, and a typical pre-exponential factor, rather than a direct measurement.
The angular dependencies of the IS and TD components are calculated by integrating each component at all observation angles. In Fig. 6 angular distributions and polar plots that result from water interactions with a molecularly thin VA coating on graphite at 260 K and a thick solid VA layer at 220 K (Fig. 6a–d, respectively) are displayed. The inelastic components are minor parts of the total fluxes and their values are multiplied by a factor of ten to make them more visible. Inelastic scattering occurs predominantly in the forward direction with the peak of the distributions shifted slightly below the specular direction. Conversely, molecules that are thermalized in contact with the surface lose their incident momentum and desorb in random directions. The resulting TD profiles are typical cosine distributions relative to the surface normal, as expected for ordinary thermal desorption.
Most of the incoming water molecules are thermalized (see Fig. S2 in SI) and a fraction of them subsequently desorb from the surface. From the MD simulations we can directly see TDfast and IS. Molecules that undergo IS preserve ∼50% of their initial KE (e.g., 9 kJ mol−1 at 20° and 11 kJ mol−1 at 75° scattering angle, compared to the incident KE ≈ 22.5 kJ mol−1). In addition, binding energy distributions of the remaining fraction of water molecules on the VA surface hint at the existence of TDslow. Fig. 8 shows binding energy distributions experienced by adsorbed water monomers on VA for three different temperatures. At low temperatures the majority of molecules remain on the VA surface at the end of the 60 ps simulation run and are only weakly bound (−10 kJ mol−1), but with a fraction being able to find more strongly bound sites that could result in sticking on longer time scales. As temperature increases the probability of finding strongly bound molecules also increases, with a substantial change as the melting temperature is approached. This supports the presence of both weakly and more strongly bound states contributing to the observed desorption behavior. These findings are discussed in Section 4 in relation to the experimental desorption behavior.
Fig. 9 illustrates some of the typical adsorption scenarios of water molecules on VA surfaces. At low temperatures configurations with a water molecule adsorbed on top of the VA dimer dominate, and yield binding energies of ∼10 kJ mol−1 (Fig. 9a). However, some molecules become incorporated into the uppermost monolayer with binding energy of ∼40 kJ mol−1 (Fig. 9b). When the temperature is increased and approaches the melting point configurations with higher binding energies are favored (Fig. 9c).
The observed collision dynamics are typical for water interactions with organic surfaces where inelastically scattered molecules tend to lose a significant fraction (50–90%) of their incident kinetic energy in surface contact (Fig. 10a).29,31–35 Energy transfer between incoming water molecules and surface modes is highly efficient, which results in trapping probabilities close to unity. Any molecules that are nevertheless able to escape the surface by IS do so with a minor fraction of their initial kinetic energy. The final energy shows limited or no dependence on observation angle, and the results are consistent with efficient energy transfer both parallel and perpendicular to the surface plane. The scattered intensity as a function of angle is also qualitatively comparable for the studied systems (Fig. 10b), with the exception being water interactions with liquid n-butanol that results in a significantly wider distribution than observed for the solid surfaces.
![]() | ||
| Fig. 10 Experimental data from this and previous studies. Normalized (a) retained kinetic energy and (b) intensity distributions of inelastically scattered water molecules as a function of angle for VA (pink dots), nopinone (green hexagons),35 n-butanol (blue squares),34 n-hexanol (red triangle),31 acetic acid (yellow triangle)32 and methanol (red diamond)37 systems. Filled symbols and solid lines represent micrometer thick solid organic surfaces, and open symbols and dashed lines represent thin organic coatings on graphite. A liquid n-butanol surface is represented by crossed squares and a dotted line. | ||
Interestingly, no clear changes in the water trapping-desorption behavior are observed as the temperature of the solid VA layer is increased to 220 K. This is approximately 20 K below Tm and corresponds to 0.92Tm, and the results suggest that changes in surface properties do not play a major role for the desorption probability at this temperature. For comparison, Fig. 11 summarizes the observed trapping-desorption probability as function of temperature for several systems recently studied by the EMB method. The VA results are similar to data for other organic surfaces, with the exception being n-butanol where changes in surface structure influence water uptake well below the melting point (Fig. 11a). Similar conclusions can be drawn for molecularly thin layers of organic compounds on graphite (Fig. 11b), where methanol is the exception that displays a clear temperature dependence. Note that the melting point for these thin layers may deviate significantly from the bulk Tm indicated on Fig. 11.
![]() | ||
| Fig. 11 Experimental data from this and previous studies. Trapping desorption probability from (a) microscopically thick organic layers and (b) thin coatings on graphite of VA (pink dots), nopinone (green hexagons),35 n-butanol (blue squares),34 n-hexanol (red triangles),31 acetic acid (yellow triangles)32 and methanol (red diamonds, as a function of temperature relative to the bulk melting point (Tm).37 | ||
The negative temperature dependence of the desorption rate constants (Fig. 4) observed for TDslow is intriguing. Generally, molecules that are trapped in a weakly bound state desorb with a higher rate as temperature is increased. Absent changes in surface structure with increasing temperature, this increased desorption will allow molecules less time to diffuse to sites with higher binding energies. However, it is unlikely that over a significant temperature range a surface layer will remain unaffected by an increasing temperature. Instead changes in surface structure and breaking hydrogen bonds within the VA surface layer can be expected to provide increased opportunities for forming strong surface bonds with water molecules. This is illustrated by the MD simulations as the temperature approaches the melting point (Fig. 9). Adding complexity to the situation is the fact that the MD simulations are carried out under “dry” conditions with single water molecules interacting with the VA surface. The MD simulations are thus performed for single-water molecules under low-coverage, dry conditions and over short timescales (60 ps), and therefore do not capture finite water coverage effects or the long-timescale desorption processes observed in the EMB experiments. Conversely, in the EMB experiments, a low but finite surface coverage of water may build up and provide additional opportunities for water–water interactions and the formation of relatively strong hydrogen bonds. These competing processes may affect the experimentally observed temperature dependence.
This study illustrates the complexity of molecular-level processes at the interface between gas and condensed organic phases. An interesting detail is the observed differences between solid organics and thin coatings. In particular graphite with its smooth surface character appears to have a significant impact on the properties and behavior of adsorbates. The stability of the thin organic coatings is significantly higher than the micrometer thick layers, which indicates that they are structurally different. EMB experiments show that trapping desorption probabilities for water on thin methanol coatings have a clear temperature dependence with decreasing desorption as one goes from high to low temperatures and Tm is approached (Fig. 11b).29 Such trends are absent for water desorbing from thin coatings of nopinone35 and VA. However, the melting temperatures of thin coatings are likely to deviate from those of the bulk, as is the case for methanol coatings that have a substantially lower melting temperature (135 K) compared to the bulk (175.4 K).29 The weak temperature dependence of the PTD for thin VA and nopinone coatings (Fig. 11b) may signify that the thin layer melting points differ significantly from the bulk Tm.
The observed difference in sticking probability on thin coatings compared to thick adsorbed layers also indicates a difference in surface properties. This has previously been seen for organics such as n-hexanol,31 acetic acid32 and nopinone.35 However, the observed higher uptake on thin VA coatings relative to micrometer thick layers is opposite to the trend seen in the previously mentioned studies.31,32,35 Further studies will be required to elucidate the underlying structural and dynamic differences responsible for the observed trends.
The surface state of the condensed layers is of central importance for the water uptake processes. The results obtained from these EMB experiments and MD simulations are not indicative of VA surface melting at temperatures up to 0.92Tm. This is an important finding because in the atmospheric context surface state highly influences mass transfer, surface chemistry, and other physicochemical properties of aerosol particles.
The observed water sticking coefficients are also observed to have only weak temperature dependencies in the investigated range. However, we do observe a discontinuity between the uptake on molecularly thin VA layers on graphite versus thicker VA layers. This suggests that the thin VA coating on graphite may have a different molecular arrangement compared to micrometer thick layers that may contribute to a higher possibility for water accommodation.
The employed EMB and MD methods contribute to the molecular-level understanding of organic systems of atmospheric importance. The investigated surfaces are proxies for the organic mixtures that can be expected to be found under atmospheric conditions, and further studies of increasingly complex systems are needed to build a modelling framework for atmospheric applications.
Footnotes |
| † Now at: Renova AB, 401 22 Gothenburg, Sweden. |
| ‡ Now at: AstraZeneca, 431 83 Mölndal, Sweden. |
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