Marin
Sapunar
a,
Mackenzie
Meyer
b,
Harindranath B.
Ambalampitiya
c,
Mark J.
Kushner
b and
Zdeněk
Mašín
*d
aDivision of Physical Chemistry, Ruđer Bošković Institute, Bijenička cesta 54, 10000 Zagreb, Croatia
bDepartment of Electrical Engineering and Computer Science, University of Michigan, Ann Arbor, MI 48109, USA. E-mail: maemeyer@umich.edu; mjkush@umich.edu
cQuantemol Ltd, 320 City Rd, London EC1V 2NZ, UK
dFaculty of Mathematics and Physics, Charles University, Institute of Theoretical Physics, V Holešovičkách 2, 18000 Prague, Czech Republic. E-mail: zdenek.masin@matfyz.cuni.cz
First published on 3rd October 2024
Plasma treatment of per- and polyfluoroalkyl substances (PFAS) contaminated water is a potentially energy efficient remediation method. In this treatment, an atmospheric pressure plasma interacts with surface-resident PFAS molecules. Developing a reaction mechanism and modeling of plasma–PFAS interactions requires fundamental data for electron–molecule reactions. In this paper, we present results of electron scattering calculations, potential energy landscapes and their implications for plasma modelling of a dielectric barrier discharge in PFAS contaminated gases, a first step towards modelling of plasma–water–PFAS intereactions. It is found that the plasma degradation of PFAS is dominated by dissociative electron attachment with the importance of other contributing processes varying depending on the molecule. All molecules posses a large number of shape resonances – transient negative ion states – from near-threshold up to ionization threshold. These states lie in the region of the most probable electron energies in the plasma (4–5 eV) and consequently are expected to further enhance the fragmentation dynamics in both dissociative attachment and dissociative excitation.
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Fig. 1 The molecules studied in this work. Top row from left to right: PFBA, PFOA. Bottom row from left to right: PFBS, PFOS. |
The mechanism of both PFOA and PFOS degradation through photochemical treatment is attributed to reactions initiated by the solvated electron (eaq−).7 The same species was also shown to be crucial for plasma treatment in liquid discharge reactors.6 However, the same study concluded that the primary step of the degradation is likely different in gas phase discharge reactors due to the possibility of interaction between free electrons or argon ions with PFAS molecules adsorbed at the gas–water interface. Wiens et al.8 studied the plasma degradation mechanism of these molecules in the gas phase to avoid the complications introduced by the solvent or gas–liquid interface environment on the molecules. Through their experiments, they quantified the charged products of PFBA (and, to a lesser extent, PFOA and PFOS) formed through reactions with Ar+ and dissociative electron attachment, but could not track neutral fragments formed.
The energy of electrons involved in plasma degradation processes is more than sufficient to electronically excite these molecules, but no studies of their excited state chemistry have been performed thus far. Here we perform the first step in understanding the excited state processes leading to degradation of these compounds by (1) identifying the likely initial states to which these molecules are excited through UV absorption or through inelastic scattering of low-energy electrons and (2) a systematic study of the excited state potential energy surfaces (PES) of these compounds to identify bonds where the initial steps of the degradation reaction can occur. The focus on pairs of molecules with the same functional group and different lengths of the carbon chain allows us to determine the effect of the chain length on the excited state chemistry of the molecules.
Neither experimental nor calculated electron collision data for the large polyfluoroalakyl molecules is available. For theory, the size of the molecules (both spatial and in terms of the number of electrons) presents a formidable challenge. We meet this challenge by employing our recently developed Born approach9 suitable for calculating optically-allowed transitions over a wide energy range. Additionally, due to the presence of strongly electronegative atoms and unoccupied virtual orbitals we can expect formation of a number of elastic and inelastic scattering resonances. Those transient negative ion states strongly influence internal dynamics of the molecule, including breakup. For that reason, characterization of resonances is key to understanding the electron attachment process. To characterize the resonances and to calculate cross sections for the optically-forbidden transitions in the low-energy region we use the ab initio R-matrix method for electron collisions with molecules10 and our recently developed method for direct localization of scattering resonances.11 To the best of our knowledge PFOS is one of the largest molecules for which an ab initio electron scattering calculation was attempted. Consequently, our calculations are limited to the simplest elastic scattering model and a very simple inelastic model. These models are designed to provide well-defined approximations to future accurate models and to reveal the number and basic parameters of the scattering resonances.
Many studies have investigated degradation of PFAS compounds in water due to atmospheric pressure plasma exposure.6,12–17 However, to our knowledge, no modelling of the plasma treatment of PFAS contaminated water has occurred as the complex chemistry occurring between the PFAS molecules and plasma-produced reactive species (in particular, electrons) poses a challenge for modelling studies. Using the recommended electron impact cross sections calculated in this work, we aim to provide a first step towards the modelling of PFAS contaminated water. To that end, the 0D plasma chemistry model GlobalKin is used to examine the decomposition in an Ar/PFAS system. As a first step, the chemistry is limited to gas phase reactions.
In Section 2 we outline the theoretical methods and the parameters used in the calculation. This is followed in Section 3 by results for the fragmentation pathways of all molecules and by results of the electron scattering calculations in both the Born approximation and using the R-matrix approach. In Section 3.6 the electron impact data are combined with a comprehensive modelling of plasma degradation of PFAS molecules in Ar, followed by discussion of the role of the individual processes in Section 4 and Conclusions in Section 5.
Cuts along all likely dissociation pathways on the PESs of the molecules were studied. Geometries along the cuts were obtained through constrained optimisations of the S0 state at the PBE0/def2-SVPD level and (for the most likely channels of PFBA) of the S1 and T1 surfaces at the ADC(2)/aug-cc-pVDZ level with constraints on the bond being extended and the C–O–H angle in the case of hydrogen dissociation curves (to prevent the hydrogen jumping to other oxygen atoms). A low convergence threshold was used for the optimisations to reduce computational time. Single point calculations along all scans were performed at the ADC(2)/aug-cc-pVDZ level. The method employed here is a single-reference method and is thus unable to accurately describe dissociation curves. However, the results should be accurate for distances large enough to estimate the relative feasibility of the various pathways.
The target electrons were described with the cc-pVDZ atomic basis set while the unbound electron was described using Gaussian-only continuum bases22 centered on the center of mass with angular momenta up to lmax = 6. The R-matrix radius was 15 bohr with exception of the PFOS molecule for which we used radius of 18 bohr and a continuum basis with lmax = 4. The molecular integrals were computed in quad precision which prevents linear dependency issues between the target and continuum Gaussians and allowed us to retain all functions in the continuum basis.
To the best of our knowledge the PFOS molecule is the largest molecule treated by the R-matrix method so far which goes with the corresponding computational demands: the largest part of the calculation was the computation of the molecular integrals. The rest of the calculation was computationally simple due to the choice of small scattering models.
Two types of scattering models were employed: elastic static-exchange (SE model) and inelastic close-coupling with CASSCF target wavefunctions (CAS model). The static-exchange (SE) scattering model10 employs Hartree–Fock orbitals and doesn't include any effects of electron correlation beyond the exchange interaction of all electrons in the system. The L2 functions for the SE model have the form of the Hartree–Fock ground state coupled to virtual orbitals. In this case all available virtual orbitals were used. In case of the CAS models we included the standard set of configurations of this model:10
For all molecules, except for PFOS, we included in the calculation all molecular orbitals generated by the atomic basis. In case of PFOS we included, due to computational limitations, only a subset of 355 instead of the full set of 455 molecular orbitals.
PFBA | PFOA | |||||
---|---|---|---|---|---|---|
ADC(2) | PBE0 | CASSCF | ADC(2) | PBE0 | CASSCF | |
S1 | 5.48 | 5.46 | 6.48 | 5.34 | 5.45 | 5.33 |
S2 | 7.40 | 7.81 | 9.14 | 7.44 | 7.83 | 9.24 |
S3 | 8.00 | 7.96 | 9.39 | 7.92 | 7.91 | 10.02 |
S4 | 8.55 | 8.58 | 10.86 | 8.53 | 8.16 | 10.83 |
S5 | 8.58 | 8.78 | 11.28 | 8.59 | 8.31 | 10.92 |
S6 | 9.20 | 8.86 | 12.79 | 8.61 | 8.40 | 12.53 |
S7 | 9.28 | 9.02 | 13.09 | 8.99 | 8.69 | 12.76 |
S8 | 9.33 | 9.29 | 9.22 | 8.82 | ||
S9 | 9.57 | 9.55 | 9.42 | 8.98 | ||
S10 | 9.72 | 9.63 | 9.49 | 9.08 | ||
T1 | 5.02 | 4.86 | 6.12 | 5.00 | 4.85 | 5.00 |
T2 | 6.06 | 5.61 | 6.50 | 6.05 | 5.60 | 5.75 |
T3 | 7.45 | 7.36 | 8.90 | 7.45 | 7.40 | 9.20 |
T4 | 8.13 | 7.90 | 9.81 | 8.14 | 7.82 | 9.37 |
T5 | 8.40 | 8.26 | 10.36 | 8.39 | 8.04 | 10.72 |
T6 | 8.59 | 8.40 | 10.79 | 8.41 | 8.12 | 10.81 |
T7 | 9.07 | 8.69 | 12.65 | 8.88 | 8.27 | 12.39 |
T8 | 9.16 | 8.74 | 14.62 | 9.00 | 8.49 | 14.05 |
T9 | 9.43 | 9.09 | 9.11 | 8.58 | ||
T10 | 9.47 | 9.22 | 9.21 | 8.68 |
PFBS | PFOS | |||||
---|---|---|---|---|---|---|
ADC(2) | PBE0 | CASSCF | ADC(2) | PBE0 | CASSCF | |
S1 | 7.58 | 7.74 | 8.58 | 7.57 | 7.76 | 8.41 |
S2 | 7.78 | 7.86 | 8.95 | 7.77 | 7.87 | 8.88 |
S3 | 8.04 | 8.23 | 9.16 | 8.02 | 8.21 | 9.18 |
S4 | 8.24 | 8.39 | 9.70 | 8.21 | 8.35 | 9.22 |
S5 | 8.32 | 8.45 | 10.09 | 8.30 | 8.42 | 9.65 |
S6 | 8.49 | 8.57 | 10.45 | 8.48 | 8.55 | 9.80 |
S7 | 8.58 | 8.63 | 11.05 | 8.55 | 8.61 | 10.48 |
S8 | 8.60 | 8.66 | 8.58 | 8.64 | 11.39 | |
S9 | 8.76 | 8.79 | 8.71 | 8.74 | ||
S10 | 8.99 | 8.87 | 8.95 | 8.75 | ||
T1 | 7.19 | 7.11 | 8.23 | 7.16 | 7.09 | 8.22 |
T2 | 7.43 | 7.39 | 8.57 | 7.42 | 7.39 | 8.44 |
T3 | 7.62 | 7.61 | 8.67 | 7.60 | 7.59 | 8.63 |
T4 | 7.77 | 7.66 | 8.91 | 7.76 | 7.64 | 8.82 |
T5 | 7.91 | 7.81 | 9.02 | 7.89 | 7.80 | 8.91 |
T6 | 8.02 | 7.92 | 9.25 | 8.01 | 7.91 | 9.06 |
T7 | 8.16 | 7.97 | 9.40 | 8.15 | 7.93 | 9.09 |
T8 | 8.39 | 8.22 | 10.13 | 8.37 | 8.18 | 9.68 |
T9 | 8.45 | 8.26 | 8.42 | 8.24 | 9.80 | |
T10 | 8.52 | 8.35 | 8.50 | 8.33 |
At the CASSCF level, the lowest lying states are well described by an active space of 8 electrons in 8 orbitals (8,8) and the aug-cc-pVDZ basis set. In terms of the orbital composition, the only noticeable difference is the σ orbital which is the dominant contribution to the S3 state at the CASSCF level and is significantly more delocalized in the S4 state at the ADC(2) level. Without the diffuse basis functions, at the CASSCF(8,8)/cc-pVDZ level 3p Rydberg type orbitals are not sufficiently described by the basis set so only the five lowest states are accurately described. Comparing the energies of the states at the ADC(2), CASSCF and CASPT2 levels of theory, we see that CASSCF(8,8)/aug-cc-pVDZ (Table S1, ESI†) offers surprisingly accurate excitation energies which are only marginally improved by CASPT2. On the other hand, energies computed at the CASSCF(8,8)/cc-pVDZ level are significantly higher and are improved substantially by including the dynamical correlation with CASPT2.
Turning next to the sulfonic acids, the hole and particle NTOs with the largest contribution to the lowest excited states of PFBS and PFOS are shown in S3 and S4. The sulfo group, unlike the carboxyl group, does not contain any π orbitals and thus, no low-lying bright states. Instead, starting from approximately 7.5 eV, PFBS and PFOS exhibit a dense manifold of nσ* and nRyd transitions, all of which have oscillator strengths an order of magnitude or more lower than the bright ππ* state of PFBA. The σ* orbital which is the particle orbital for the three lowest transitions exhibits nodes on both the C–S and S–OH bonds indicating that these bonds are the most easily broken. At the CASSCF level, we see that the nσ* and the nRyd(s) states are qualitatively correct even when using the smaller (cc-pVDZ) basis set and a smaller active space of 10 electrons in 8 orbitals (Table S2 and Fig. S5, ESI†). This basis set is not adequate to describe states involving 3p Rydberg orbitals.
The CASSCF representation is accessible in the molecular R-matrix codes and we have used it in inelastic electron scattering models to complement the data calculated using the Born approach. Cross sections for impact excitation of both singlet and triplet states were calculated. Most importantly, R-matrix calculations produce a structured continuum including the presence of resonances which strongly affects all types of cross sections. Despite the drawbacks of using the more compact basis set for the description of the excited states of the target molecule, the R-matrix calculations were performed only with the cc-pVDZ basis due to the computational demands that would be required for the diffuse basis calculations: a larger R-matrix sphere and consequently a larger basis of continuum functions. While calculations for highly diffuse targets have been made in the past for small molecules and would be in principle possible even for the present targets using a mixed B-spline/Gaussian basis,10 the number of the continuum functions required implies hugely expensive integral calculations: the limited benefit of the diffuse target basis doesn't justify such effort, see Section 3.3 for details.
Next, we look at potential energy surface cuts along the possible dissociation pathways. Looking first at the dissociation curves optimized on the S0 surface of PFBA (Fig. 2 and 3), we see that dissociation of the –OH group and the fluorine atoms closest to the functional group are energetically favorable both from the singlet and the triplet manifold. On the other hand, dissociation of the C–C bond appears unlikely in the singlet manifold. However, this pathway becomes significantly easier in the triplet manifold where one state is quickly stabilised along the pathway and the barrier along the T1 state is even lower than the one for –OH dissociation. Results for analogous scans of PFOA are nearly identical (Fig. S6, ESI†). Relaxing the scans on excited state surfaces instead of on the ground state surface results, as expected, in curves with significantly lower barriers (Table 3). In these cuts, all barriers are shown to be below the vertical excitation energy, proving that all dissociation paths are feasible after electronic excitation of the molecules. However, many of the scans relaxed on the excited state surfaces, most notably the C–C bond dissociations, involve larger structural rearrangements. In these scans, the molecule is trapped in a local minimum until the bond is significantly extended at which point a large rearrangement of the molecular backbone occurs and the potential energy drops suddenly. While these pathways are open energetically, the large structural changes involved in the process suggest that they would be less likely than the more direct dissociations due to entropy considerations.
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Fig. 3 Scan of the PES of PFBA along the C1–C2, C2–C3, C3–C4, C2–F1, C3–F3 and C4–F5 dissociation coordinates at the RI-ADC(2)/aug-cc-pVDZ level relaxed on the S0 surface. See Fig. 2 for the legend. |
Scan | State | –OH | –H | C1–C2 | C2–C3 | C3–C4 | C2–F1 | C3–F3 |
---|---|---|---|---|---|---|---|---|
S0 | S1 | 6.38 | 6.92 | — | — | — | 5.69 | 5.75 |
S0 | T1 | 6.24 | 6.66 | 6.40 | 5.90 | 6.48 | 5.34 | 5.41 |
S1 | S1 | 4.52 | 5.21 | 5.12 | 5.51 | — | 4.82 | 5.64 |
T1 | T1 | 4.27 | 5.16 | 4.34 | 4.76 | 6.24 | 4.67 | 5.42 |
In summary, from these static calculations it is not possible to give an accurate estimate of the branching ratios for PFBA and PFOA where many pathways are open and there is no clear indication that any one of these would dominate. This is especially true for the higher lying excited states where nonadiabatic effects are more important.
For the sulfonic acids (Fig. 4, and Fig. S8 and S9, ESI†) we see that dissociation of the sulfo group is energetically the most favourable pathway, as expected from the unconstrained optimizations. However, we also see that the dissociation curve for the OH group is not very different, making it another likely option. All other pathways for the sulfonic acids appear significantly less probable at low energies. Again, there do not appear to be any significant differences between PFBS and PFOS.
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Fig. 4 Scan of the PES of PFBS along the sulfo, OH, H, C1–F1, C2–F3 and C3–F5 dissociation coordinates at the RI-ADC(2)/aug-cc-pVDZ level relaxed on the S0 surface. See Fig. 2 for the legend. |
Altogether, upon electronic excitation even to the lowest excited states these molecules will have more than enough energy to access multiple deactivation pathways which are likely to occur on a femtosecond time scale. However, for a quantitative description of the deactivation pathways, nonadiabatic dynamics simulations would need to be performed to account for the coupling between excited states.
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Fig. 6 Elastic scattering cross sections and Siegert (Resonant) states in PFBS and PFOS. Indicated in the legend is the maximum continuum partial wave lmax included in each calculation. |
We present results for scattering energies up to 20 eV for which the continuum basis is sufficiently reliable. Presenting results for energies higher than 20 eV would be in principle possible (even with the GTO-only continuum basis) but our calculations suffer from lack of convergence of the continuum partial wave expansion. Therefore we deem data beyond 20 eV significantly inaccurate and not converged with respect to continuum angular momentum. This is true even for the results with lmax = 6 and it is evident from the comparison for PFOA between the calculations with lmax = 4 and lmax = 6, shown in Fig. 5. The lack of partial wave convergence is especially severe in case of the PFOS molecule, see Fig. 6, where its elastic cross section drops down below that of PFBS at 9 eV. The lack of convergence of the Siegert states for energies above approx. 11 eV is evident even in the calculations with lmax = 6. Our tests show that the angular momentum convergence is poor not only due to the polar character of the molecules but mostly due to their geometric size which makes scattering at distances relatively far away from the center of mass still appreciable.
Nevertheless, given the large computational demands of the integral calculations we regard our chosen combination of atomic and continuum bases as sufficient to obtain realistic values for the inelastic cross sections and estimates of the positions and widths of the shape resonances. Both of these are less sensitive to convergence of the partial-wave expansion compared to the elastic cross sections.
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Fig. 7 PFBA isomers. Left: Heptafluorobutyric acid, right: perfluorobutyric acid. The molecule on the left is the one studied in this work. |
The SE calculations represent the first quantitative estimate of elastic cross sections for these large molecules. Nevertheless, all the molecules are polar which implies the need to include higher partial waves in the calculation. This is commonly done by estimating their contribution using the Born approximation24,25 which can enhance the elastic cross section by an order of magnitude.26 However, the goal of the present calculations is not to present accurate magnitudes of elastic cross sections but to identify shape resonances which can further enhance the dissociative processes: for this purpose the SE model is sufficient. While this model does not include correlation/polarization effects and therefore overestimates resonance positions25 it is a well defined reference model which can be used for comparisons against different approaches. To provide an estimate of the resonant shifts we performed exploratory SE calculations for a related molecule, perfluoroisobutyronitrile,9 for which experimental positions of the lowest-lying resonances are known.27 We have found that the resonances from the SE model would have to be shifted by at least 2 eV to match the positions of the corresponding lowest-lying resonances in the experiment. On the basis of this analogy we estimate that the SE resonance positions in the PFAS molecules would have to be shifted down by at least the same amount. Additionally, the shift is not linear and a larger shift would be required for the higher-lying resonances. We conclude tentatively that the resonant positions from the SE model are approx. 2–5 eV higher than in experiment.
Closed | Occupied | Max. CSFs | |
---|---|---|---|
PFBA | 48 | 56 | 2352 |
PFOA | 97 | 103 | 189 |
PFBS | 68 | 76 | 1512 |
PFOS | 117 | 125 | 2352 |
The CAS states were ordered in energy and a total of 25 lowest-lying states of both singlet and triplet character, including the ground state, were employed in the CAS scattering calculations. The results for the 5 lowest-lying CASSCF states are shown in Fig. 8. The complete set of R-matrix results is plotted in Fig. S11 (ESI†).
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Fig. 8 R-Matrix CAS inelastic cross sections for PFBA, PFOA (top row), PFBS, PFOS (bottom row). For clarity results only for the lowest 5 states calculated on the CAS level are shown. |
The inelastic cross sections contain many structures which is a complexity to be fully expected for molecules of this size.26,28 Some of them are associated with the shape resonances but core-excited and Feshbach resonances are expected to be formed too29 although we have made no attempt to rigorously characterize the peaks also in the view of the limited accuracy of the R-matrix calculations. Some of the peaks at energies exceeding the energy of the highest included state will be unphysical pseudoresonances, a typical feature of close-coupling calculations.25
In case of the sulfo-containing molecules PFBS and PFOS the cross sections for the various transitions have a comparable magnitude, while for PFBA and PFOA there are a few dominant transitions. This trend is consistently confirmed by the Born calculations, see below.
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Fig. 9 Inelastic cross sections for excitation into the lowest 20 singlet excited states of PFBA (left) and PFOA (right) calculated at the ADC(2)/aug-cc-pVDZ level using the Born approximation. |
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Fig. 10 Inelastic cross sections for excitation into the lowest 20 singlet excited states of PFBS (left) and PFOS (right) calculated at the ADC(2)/aug-cc-pVDZ level using the Born approximation. |
Fig. 11 shows a comparison between the cross sections calculated for PFBA using the two methods (Born and R-matrix) but with the same electronic structure description (CAS). The purpose of this figure is to show the impact of the structured continuum on the cross sections: the role of resonances, state coupling, correlation and electron exchange which are all the effects omitted on the Born level. Despite its simplicity the Born cross sections have a similar magnitude as the R-matrix ones. In some cases and energy ranges the results differ from each other by more than 100% but at higher energies approaching 20 eV the magnitude of the R-matrix and Born cross sections becomes similar. Nevertheless, for reasons explained above neither of the methods can be regarded as an accurate reference result that we could use to rescale results from the other method. For that reason we can provide only a tentative educated guess to estimate the actual uncertainty of the recommended cross sections to be in the range 50–100%.
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Fig. 11 Comparison of the R-matrix (solid lines) and Born (dashed lines) inleastic cross sections for PFBA for the seven lowest-lying singlets in the energy range up to 20 eV. |
On the other hand, the differences in the Born cross sections between Fig. 9 and 11 are exclusively due to the different description of the excited states of PFBA at the ADC(2)/aug-cc-pVDZ and CASSCF/cc-pVDZ levels. While these two results appear significantly different at first glance, the main feature seen in both cases originates from the same ππ* transition. In the ADC(2) calculation, this transition is mixed with the nRyd(s) transition to form the S2 and S3 states, with the S3 state having the greater involvement of the ππ* transition and thus having a significantly higher cross section. These same transitions are present at the CASSCF level as states S2 and S4, but here the transitions are split almost evenly between the two states and thus the cross sections of the two states are similar.
• Born cross sections for impact excitation of the singlet states for the energy range 0–50 eV from Fig. 9 and 10.
• R-matrix cross sections for impact excitation of the triplet states for the energy range 0–20 eV from Fig. 8.
The full set of our recommended inelastic cross sections for all molecules is plotted in Fig. S10 (ESI†). The advantage of the Born singlet cross sections lies in much more accurate threshold energies: the CAS thresholds cannot be trusted beyond the first few lowest-lying states, cf.Tables 1 and 2. Additionally, the Born cross sections don't suffer from angular momentum convergence issues, particularly at higher impact energies. This is due to the momentum-space formulation of the Born calculation. On the other hand the singlet Born cross sections miss all features associated with the many shape resonances and background scattering, i.e. structured continuum. It can be expected that the R-matrix triplet excitation cross sections would be less sensitive to lack of angular momentum convergence since the transition dipole is zero: the excitation process is not dominated by the long-range dipole interaction as is the case for the singlet–singlet transitions but by electron exchange and correlation.
The recommended excitation cross sections shown in Fig. S10 (ESI†) can be summed to estimate the cross sections for dissociative excitation into triplet and singlet states. This estimation was done on the assumption that the excited levels are dissociative which is further justified by the repulsive PES scans for the corresponding dissociative coordinates shown in Fig. 2–4. In the plasma modelling, we used the 20 separate singlet cross sections and the 12 or 13 separate triplet cross sections computed, as opposed to the sum of the singlet and triplet cross sections. In addition, the ionization cross sections were also computed via the binary encounter Bethe30 model which is conveniently implemented in Quantemol's electron scattering (QEC) interface.31
The decomposition of PFBA, PFOA, PFBS, and PFOS was examined in a repetitively pulsed Ar plasma at atmospheric pressure in a configuration corresponding to a dielectric barrier discharge. Plasmas containing each PFAS molecule were examined individually (Ar/PFBA, Ar/PFOA, Ar/PFBS, and Ar/PFOS) with the ratio Ar/PFAS = 99.5/0.5. The species in the reaction mechanism include Ar, H2O, O2, CO2, F2, CxFy (x ≤ 3), HSO3, and their dissociation fragments and radicals, excited states, and ions. The Ar/H2O/O2 reaction mechanism is based on Van Gaens and Bogaerts,33 and the fluorocarbon mechanism is from Vasenkov et al.34 The PFAS species and their dissociation products, including CxFy (x ≥ 4), were added to the mechanism.
The decomposition reactions of the PFAS molecules are listed in Table 5. The mechanism includes dissociative ionization (DI), charge-exchange (CEX), dissociative attachment (DA), and dissociative excitation transfer (DET) from Ar excited states. Note that only ions with an ionization potential greater than the PFAS ionization potentials can participate in CEX reactions. (PFAS ionization potentials were taken from Wiens et al.8) The DA rate coefficients reported in Wiens et al.8 are thermally attaching rate coefficients, neglecting resonances at higher electron energies. The rates of DET were estimated from rates of DET with other fluorocarbons.34 The cross sections from Section 3.5 were implemented in GlobalKin allowing for electron impact dissociative excitation to singlet or triplet states. Note that each individual singlet or triplet cross section was used for the plasma modelling. For the carboxylic acids (PFBA, PFOA), excitation to singlet states removes an OH from the acid head group, while excitation to triplet states breaks the C–C chain, forming a shorter-chain PFAS molecule (TFA) and a fluoroalkane. For the sulfonic acids (PFBS, PFOS), excitation to either the singlet or triplet states removes the HSO3 acid group. Further study is needed to determine the precise products of dissociation from each individual singlet and triplet state. The reaction mechanism was constructed to decrease the C–C chain in the PFAS molecules by 2 C atoms at a time. Therefore, all reactions that occur for PFBA, PFOA, PFBS, and PFOS are assumed to occur with the same rate coefficient or cross section for TFA, PFHxA, PFES, and PFHxS, respectively. While VUV photons could degrade the PFAS molecules,35 they were not included in the present reaction mechanism. However, we expect the inclusion of these reactions would only increase the rate of degradation of the PFAS molecules. As many of the rates and products of the PFAS decomposition reactions are estimated, the results of GlobalKin should be regarded as qualitative.
Dissociative excitation to singlet states | e + PFBA → C3F7CO + OH + e | This work |
e + PFOA → C7F15CO + OH + e | This work | |
e + PFBS → HSO3 + C4F9 + e | This work | |
e + PFOS → HSO3 + C8F17 + e | This work | |
Dissociative excitation to triplet states | e + PFBA → C2F4 + TFA + e | This work |
e + PFOA → C6F12 + TFA + e | This work | |
e + PFBS → HSO3 + C4F9 + e | This work | |
e + PFOS → HSO3 + C8F17 + e | This work | |
Dissociative ionization (DI) | e + PFBA → C2F+4 + TFA + e | Binary encounter Bethe |
e + PFOA → C2F+4 + PFHxA + e | Binary encounter Bethe | |
e + PFBS → C2F+4 + PFES + e | Binary encounter Bethe | |
e + PFOS → C2F+4 + PFHxS + e | Binary encounter Bethe | |
Charge-exchange (CEX) | M+ + PFBA → HCOO+ + C3F7 + M | 8 |
M+ + PFOA → C3F+5 + CO2 + HF + C4F9 + M | 8 | |
M+ + PFBS → C2F+5 + C2F4 + HSO3 + M | Assumed from PFBA8 | |
M+ + PFOS → C3F+5 + C5F12 + HSO3 + M | Assumed from PFOA8 | |
Dissociative attachment (DA) | e + PFBA → C3F6HCOO− + F | H–F elimination8 |
e + PFOA → C7F14HCOO− + F | H–F elimination8 | |
e + PFBS → C4F9SO−3 + H | Assumed from PFBA8 | |
e + PFOS → C8F17SO−3 + H | Assumed from PFOA8 | |
Dissociative excitation transfer (DET) | Ar* + PFBA → HCOO+ + C3F7 + Ar + e | Estimated |
Ar* + PFOA → C3F+5 + CO2 + HF + C4F9 + Ar + e | Estimated | |
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Estimated | |
Ar* + PFBS → C2F+5 + C2F4 + HSO3 + Ar + e | Estimated | |
Ar* + PFOS → C3F+5 + C5F12 + HSO3 + Ar + e | Estimated | |
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Estimated |
The decomposition of the PFAS molecules was examined in a pulsed nanosecond dielectric barrier discharge operating at atmospheric pressure. The power pulse ramps up for 15 ns and stays constant to 82 ns. The power then decreases to 1% of the peak value at 115 ns. 5.8 mJ cm−3 is deposited in the plasma for each pulse, and the peak power deposition is 68 kW cm−3. The pulse repetition frequency is 10 kHz, corresponding to a pulse every 0.1 ms. The evolution of the plasma is tracked over 20 pulses.
As shown in Fig. 12a for Ar/PFOA, the electron density rapidly increases as the power ramps up. The reactivity in the plasma is driven by the hot electrons either directly through electron impact processes or indirectly through the formation of positive ions and excited states that react with the PFAS molecules through CEX or DET. While the electron temperature ranges from 4–5 eV (average electron energy of 6–7.5 eV), the electrons in the tail of the energy distribution have energies above the thresholds for electron impact processes with Ar and PFAS molecules. While the plasma remains quasi-neutral, the dominant negative charge becomes the negative ions within the first 2 ns as DA with the PFAS molecules forms negative ions. During the plasma pulse, the positive and negative ion densities are over an order of magnitude larger than the electron density, and the electron temperature is around 4 eV. As the power decreases, the electron density decreases rapidly due to DA and recombination with positive ions. The positive and negative ion densities decrease over a longer timescale, as the dominant consumption mechanism is ion–ion neutralization which proceeds at heavy particle rates (as opposed to electron rates). The plasma properties, and in particular the electron density depend on the PFAS molecule. The electron density is lower for Ar/PFBA and Ar/PFBS (7–8 × 1011 cm−3) than Ar/PFOA (7 × 1012 cm−3) at the time the power begins to ramp down, while the electron density is higher for Ar/PFOS (1013 cm−3) than Ar/PFOA. However, the positive and negative ion densities are less affected by the PFAS molecule, ranging from 1.9 × 1014 cm−3 for Ar/PFOA to 2.5 × 1014 cm−3 for Ar/PFOS.
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Fig. 12 (a) Electron, positive ion, and negative ion densities in the Ar/PFOA plasma over the first pulse. (b) Decomposition of PFBA, PFOA, PFBS, and PFOS over 20 pulses. |
The decomposition of PFBA, PFOA, PFBS, and PFOS over 20 pulses is shown in Fig. 12(b). The initial concentrations of the PFAS molecules are 1.2 × 1017 cm−3. Most of the PFAS degradation occurs during the plasma pulse as the species that react with the PFAS molecules (electrons, positive ions, and excited states) are most prevalent during the pulse. There are few reactions between pulses that decompose the PFAS molecules. PFOS exhibits the largest degradation, reaching 7.2 × 1016 cm−3 (40% of PFOS degraded) at 2 ms. PFBA has the lowest degradation, reaching 8.5 × 1016 cm−3 (30% of PFBA degraded) at 2 ms. Two trends can be identified: the sulfonic acids (PFBS, PFOS) decompose at faster rates than the carboxylic acids (PFBA, PFOA), and the long-chain compounds (PFOA, PFOS) decompose at faster rates than the short-chain compounds (PFBA, PFBS). These trends have been observed in previous work on plasma degradation of PFAS molecules. PFOS has been observed to decompose at a faster rate than PFOA,17 and short-chain compounds have been shown to decompose at slower rates than long-chain compounds.12 While these studies were performed with PFAS molecules solvated in water, the results for gas phase decomposition presented here reproduce the observed trends.
The roles of the different processes listed in Table 5 in degrading the PFAS compounds were examined. The rates of these processes are shown in Fig. 13 over the first pulse for PFBA, PFOA, PFBS, and PFOS. While the rates of DA are similar for all of the PFAS molecules, the rates of other decomposition reactions change depending on the PFAS molecule. CEX has a higher rate for the short-chain molecules than for the long-chain molecules. The short-chain species have higher concentrations of the species able to participate in CEX reactions. DI has higher rates for the sulfonic acids than for the carboxylic acids due in part to lower threshold energies for the sulfonic acids. DET occurs at higher rates for the long-chain species, driven by the additional DET reaction with for the long-chain species compared to the short-chain species. Dissociative excitation to singlet and triplet states occurs at a higher rate in the long-chain versus the short-chain species, driven by an increased electron density in the long-chain cases.
To explicitly demonstrate the effect of the dissociative excitation to singlet and triplet states, these processes were removed from the model. The resulting degradation percentages decreased by less than 5% of the initial PFAS molecule, with the largest difference seen for PFOA. When removing the dissociative excitation to singlet and triplet states, the rates of the other degradation reactions do not remain constant; instead, they increase. CEX and DET play a larger role as the densities of the ions and Ar excited states increase when dissociative excitation reactions are removed. The rates of DA and DI also increase when dissociative excitation reactions are removed as the electron density increases. This is more prominent in the long-chain species compared to the short-chain species.
Finally, the carbon containing products of the PFAS decomposition were assessed. The products, grouped by number of C atoms they contain, are shown in Fig. 14. For Ar/PFBA (Fig. 14(a)), species with 1, 3, and 4 C atoms dominate. The dominant C compound is CO, formed from spontaneous decomposition of the radical C3F7CO → C3F7 + CO36 and electron recombination with HCOO+. The dominant C3 compound is C3F7, formed from decomposition of C3F7CO and a direct product of CEX with PFBA. The dominant C4 compound is C3F6 HCOO, a H–F elimination product formed from ion–ion neutralization of the DA product C3F6HCOO−. Note that C3F6HCOO is a terminal species in the mechanism. For Ar/PFOA (Fig. 14(b)), the C products dominate. The 2 most prevalent C products are CO2, formed from DET and electron recombination with HCOO+, and CO, from spontaneous decomposition of C7F15CO and electron recombination with HCOO+. For Ar/PFBS (Fig. 14c), 1, 2, and 4 C atom species are the dominant products. The dominant C2 product is C2F3, formed by dissociative ion–ion neutralization of C4F9SO−3 and C2F+5. C2F+5 is formed directly through CEX or DET with PFBS. The dominant C4 product is C4F9, formed directly through dissociative electron impact excitation to singlet and triplet states and through ion–ion neutralization of C4F9SO−3. Note that C4F9 is a terminal species in this mechanism. The dominant C product is CF4, formed from three-body recombination of CF3 and F. CF3 is formed from ion–ion neutralization of C4F9SO−3 and C2F+5. For Ar/PFOS (Fig. 14(d)), the C8 species have the largest concentration. The dominant C8 product is C8F17, formed directly from dissociative electron impact excitation to singlet and triplet states as well as dissociative ion–ion recombination of C8F17SO−3. Note that C8F17 is a radical, but in this mechanism, it is a terminal species as reactions and their corresponding rate coefficients with other species are not known.
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Fig. 14 Carbon containing decomposition products for (a) PFBA, (b) PFOA, (c) PFBS, and (d) PFOS. Products are grouped by the number of C atoms they contain. |
The role of DA however is expected to be even more important since our mechanism includes only the DA rates from Wiens et al.8 which cites values only up to temperatures of 600 K while ideally, we would require DA cross sections up to 10–15 eV of electron energy which are currently not available. Crucially, our electron scattering calculations reveal a large number of shape resonances from near-threshold energies up to approx. 10 eV which are expected to further enhance the contribution of DA through generation of molecular fragments other than neutral F and H which dominate at low energies. The role of resonances can be especially important since the electron temperature in our simulations is 4–5 eV which lies in the middle of the resonant region.
As the plasma degradation takes place in dielectric barrier discharge an increased degradation of PFAS can be expected when VUV photoionduced processes are also included.35
The high level challenge that this work aims to contribute to is plasma-based treatment of PFAS-contaminated water. The plasma modelling described here considers only gas phase processes and is a first step towards modelling the more complex plasma–liquid interactions that occur with water containing PFAS molecules. While the results presented in Section 3.6 are based on several assumptions, the results demonstrate the variety of reactive species (electrons, ions, Ar*) that contribute to PFAS decomposition. The PFAS molecules are often preferentially found at the plasma–liquid interface due to their surfactant nature. Reactions between PFAS molecules and gas phase reactive species can occur at the plasma–liquid interface. In particular, the reactions with electrons can occur before the electrons solvate.6 Once the electrons solvate into the liquid, they react within tens of nm of the interface. The reactions at the interface are particularly sensitive to the surface activity of the PFAS species, determining the concentration of the PFAS species at the interface. Since long-chain species have larger surface activities than short-chain species, direct electron impact processes and processes involving solvated electrons would contribute to increased rates of degradation of the long-chain species. Other reactions not considered in this work become important in a solvated context, including the proposed decarboxylation–hydroxylation–elimination–hydrolysis (DHEH) process initiated by solvated electrons to shorten the C–C chain in carboxylic acids.37,38 It has also been observed that PFOS degrades to PFOA, perhaps through the intermediate C8F17, formed by removal of the sulfonic acid group by solvated electrons, participating in a hydroxylation–elimination–hydrolysis process.17
To provide the data required to model electron impact dissociative excitation we calculated both electron-impact elastic and inelastic cross sections using well-defined models and performed calculations of the likely fragmentation dynamics that would occur following excitation into singlet and triplet states.
The elastic cross sections show that all PFAS molecules investigated here posses a large number of shape resonances spanning near-threshold region up to the ionization potential. The electron impact cross sections are strongly enhanced by these resonances. The role of resonances is expected to be important as the plasma simulations show that electrons responsible for dissociative collisions with PFAS molecules have average energies of 4–5 eV. However, little data on dissociative attachment to PFAS are presently available for this energy region except for the low-energy data derived from the experiments of Wiens et al.8
The importance of electron impact dissociative excitation varies depending on the molecule. A more detailed assessment of this process will require subsequent calculations of nuclear dynamics including non-adiabatic dynamics and consideration of the environment. In the current work we have performed an extensive exploration of the potential energy surfaces of these molecules and have shown that (1) the computational cost required for a reasonable description of the excited states of the smaller molecules is low enough to allow mixed quantum-classical simulations of the dissociative excitation process, and (2) that the excited state potential energy surfaces of PFOA and PFOS are close enough to those of, respectively, PFBA and PFBS that results for the smaller molecules could be generalized to the larger ones. With such calculations branching ratios (in addition to cross sections) could be provided for plasma modelling which would complete the ab initio treatment for dissociative excitation.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4cp01911c |
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