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Simulation of clusters in vapour, alkanes and polyethylene Kim Bolton, Peter Ahlstrom, Lennart Joensson, Erik Johansson

To cite this version:

Kim Bolton, Peter Ahlstrom, Lennart Joensson, Erik Johansson. Simulation of water clusters in vapour, alkanes and polyethylene. Molecular Simulation, Taylor & Francis, 2009, 35 (10-11), pp.888- 896. ￿10.1080/08927020902787804￿. ￿hal-00515079￿

HAL Id: hal-00515079 https://hal.archives-ouvertes.fr/hal-00515079 Submitted on 4 Sep 2010

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For Peer Review Only Simulation of water clusters in vapour, alkanes and polyethylene

Journal: Molecular Simulation/Journal of Experimental Nanoscience

Manuscript ID: GMOS-2008-0250.R1

Journal: Molecular Simulation

Date Submitted by the 27-Jan-2009 Author:

Complete List of Authors: Bolton, Kim; University of Boraas, School of Engineering Ahlstrom, Peter; University of Boraas, School of Engineering Joensson, Lennart; University of Boraas, School of Engineering Johansson, Erik; University of Boraas, School of Engineering

Keywords: Gibbs Ensemble Monte Carlo, Water, Hydrocarbons, Polyethylene

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1 2 3 4 Simulation of water clusters in vapour, alkanes and polyethylenes 5 6 7 8 Kim Bolton*, Erik Johansson #, Lennart Jönsson and Peter Ahlström 9 10 11 University of Borås , SE-501 90, Borås, Sweden 12 13 14 15 * 16 [email protected] Peer Review Only 17 # 18 Present address: School of Chemical Engineering, University of KwaZulu-Natal, King 19 20 George V Avenue, 4041, Durban, South Africa 21 22 23 24 25 26 27 The Gibbs Ensemble Monte Carlo (GEMC) technique has been used to study the clustering of 28 29 30 water in vapour, alkanes and polyethylene, where the water clusters are in equilibrium with 31 32 liquid phase water. The effect of an external electric field and ionic impurities on the 33 34 clustering of water in the hydrocarbons (alkanes and polyethylene) has also been studied. 35 36 37 The simulations of water clustering in polyethylene were made more efficient by using a 38 39 connectivity altering osmotic Gibbs Ensemble method. It was found that trends in the size 40 41 42 distribution of water clusters in the hydrocarbons is similar to that found in the pure vapour, 43 44 but that fewer and smaller clusters are formed as the length of the hydrocarbon chain 45 46 increased. Also, large external electric fields decrease the of water in 47 48 49 hydrocarbons, whereas the presence of ionic species dramatically increases the solubility. 50 51 52 53 Keywords: Gibbs Ensemble Monte Carlo, Water, Hydrocarbons, Polyethylene 54 55 56 57 58 59 60

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1 2 3 1. Introduction 4 5 6 7 8 Water clusters are important in many environmental and industrial processes. For example, 9 10 the ’s heat budget is strongly influenced by the presence of water clusters in the 11 12 1 13 atmosphere , and stratospheric particles play a central role in the depletion of the ozone 14 15 layer that protects the earth from harmful ultraviolet radiation 2,3. There is also evidence that 16 For Peer Review Only 17 4,5,6 18 water in hydrophobic polymers may cluster , and hence these clusters play an important 19 20 role in the polymer’s barrier properties towards water . 21 22 23 24 25 Another process that involves water, and that provides the major motivation for the studies 26 27 presented here, is the formation of water trees in polyethylene sheaths used for high voltage 28 29 electric cable insulation 7. Water trees consist of water-filled voids in the polymer sheath, 30 31 32 where the voids form a tree- or bush-like structure. In severe cases the voids can form 33 34 channels that lead to breakdown of the insulation and electrical discharge. These trees only 35 36 grow in the presence of electric fields larger than ≈2x10 6 V/m (Ref. 7), which is lower than 37 38 7 8 39 the fields of 10 – 10 V/m that the insulation is typically exposed to. In addition, it appears 40 41 that ionic impurities, which are found in the polymer after manufacture and processing, play a 42 43 8 44 central role in the formation of water trees . 45 46 47 48 There are numerous experimental investigations of water clusters, water solubility in alkanes 49 50 51 and polyethylene, as well as the effect of external electric fields and ionic species on cluster 52 53 properties and water solubility. For example, far-infrared vibration-rotation-tunnelling and 54 55 infrared spectroscopic techniques have been used to study pure water vapour clusters ranging 56 57 9,10,11,12,13,14,15 16 17 58 from dimers to decamers . Economou and Tsonopoulos and Tsonopoulos 59 60 have compiled experimental data of water in alkanes and developed equations of

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1 2 3 states that are valid over a large temperature interval and for alkanes ranging from pentane to 4 5 18,19 6 hexadecane. Sanchez and Lacombe have also developed an equation of state that can be 7 8 used for water solubility in alkane and that can also be extended to polyethylene systems. It is 9 10 known 20 that water is not very soluble in polyethylene between 298 and 333 K (30 ppm at 298 11 12 13 K) and that experimental investigations at higher temperatures can yield erroneous results 14 15 since water condenses on the polyethylene surface. 16 For Peer Review Only 17 18 19 20 The extensive work that has been done to understand water trees, including possible 21 22 mechanisms for tree formation and polymer degradation, has been discussed and reviewed 23 24 7,21 22 25 elsewhere . For example, a study by Radu et al . showed that the presence of water in 26 27 water trees leads to a local amplification of the electric field, and that this amplification can be 28 29 as much as 50% at the extremities of the trees. It was hypothesised that this, together with 30 31 32 defects in the material such as small conducting impurities, can cause the polymer 33 34 degradation. 35 36 37 38 39 These experimental studies are complemented by theoretical and computational investigations 40 41 which range from ab initio calculations of and small clusters 42 43 13,23 44 (such as minimum energy structures and dipole moments ) to larger systems where 45 24,25,26,27 46 analytic potential energy surfaces (PESs) are required to calculate interatomic forces 47 48 within a computationally tractable time. Water systems of intermediate size – or where a 49 50 28,29,30 51 small unit cell was used – have been studied using polarizable water models , direct 52 53 dynamics 31 and mixed quantum mechanics/ 32 methods. 54 55 56 57 58 Some results obtained from previous calculations and that are relevant to the work presented 59 60 here are summarised for the sake of completeness. (MD) and Monte

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1 2 3 Carlo (MC) studies of water clusters showed that the open (linear) cluster topologies are 4 5 25,33 6 preferred over the minimum-energy closed (ring) topologies at supercritical conditions . 7 8 These studies were based on the BJH 34 and TIP4P 27 models. Studies of vapour-liquid phase 9 10 equilibrium 35 that are based on the SPC 26 , SPC/E 36 and EP-637 models show that all three 11 12 13 models yield vapour phase densities that are in good agreement with experiment. Studies of 14 15 other properties, such as the radial distribution function 38 , indicate that the SPC/E model 16 For Peer Review Only 17 18 yields data that agrees with experiment as well as, if not better than, data obtained from other 19 39,40,41,42,43 20 simple water models . 21 22 23 24 25 Molecular simulations have also revealed that external electric fields can significantly affect 26 27 the properties of water and water clusters. For example, it has been seen that strong fields 28 29 induces freezing of liquid water (fields of 10 9 V/m were used to induce freezing in the 30 31 44 6 32 computational studies whereas fields as low as 10 V/m have been experimentally observed 33 34 to induce freezing 45 ). Gibbs Ensemble Monte Carlo 46 (GEMC) studies of vapour-liquid water 35 36 equilibrium have shown that fields of this magnitude lead to an increase in the liquid density 37 38 47 39 and a corresponding decrease in the vapour density , and extremely strong electric fields 40 41 (4x10 10 V/m) cause water molecules at 300 K to completely align along the field vector. It 42 43 48,49,50,51,52 8 9 44 has also been seen that application of fields of the order of 10 to10 V/m lead to 45 46 elongation of small water clusters (containing 3-64 molecules), with substantial alignment of 47 48 the water dipoles along the field vector. 49 50 51 52 53 Including an ion in the leads to packing of water molecules around the ion, 54 55 which can be seen as an increase in the local density of water near the ion 53 . Similarly to the 56 57 58 results discussed above for pure water clusters, exposing these ion-containing clusters to 59 60 strong electric fields leads to long range ordering of the water molecules54 .

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1 2 3 4 5 6 methods, such as the GEMC method, have also been used to study 7 8 water-hydrocarbon systems. Alkane-in-water and water-in-alkane solubilities for water- 9 10 methane and water-ethane systems that were obtained by combining the GEMC method with 11 12 55 13 the SPC/E model for water and TraPPE model for the alkanes are in good agreement with 14 15 experiment 56 . The Widom insertion method, using the EP6 models for water 37 and alkane 57 , 16 For Peer Review Only 17 18 was used to study the solubility of water in butane and hexane, but yielded results that were 19 56 20 lower than the experimental values . 21 22 23 24 58 25 Tamai et al . studied the solubility of water in polyethylene by combining MD with the 26 27 Widom insertion method. Their investigation was based on the SPC/E water and AMBER 59 28 29 alkane force fields and yielded a solubility of 22 ppm by weight, which is lower than 30 31 20 32 experiment (30 ppm). It is often assumed that the strong water-water hydrogen bonds will 33 34 lead to clustering of the dissolved water, and Zaikov et al. 60 used Brown’s equations 4 to 35 36 estimate that the average cluster size is 2.7 ± 0.2 water molecules at ambient conditions, 37 38 39 irrespective of the type of polymer. The tendency for water to cluster is supported by MD 40 41 studies by Fukuda 6 which showed that the diffusion of supersaturated water in polyethylene 42 43 44 occurs via the migration of water clusters, and hence cluster migration governs the polymer 45 46 barrier properties towards water. 47 48 49 50 61,62,63,64,65,66,67 51 Our studies are the first molecular level investigations that include all four 52 53 critical components for water treeing: water, polyethylene , electric field and ionic impurities. 54 55 After using the GEMC method to study water clustering in the vapour phase, in alkanes and 56 57 58 in polyethylene, we consider the effect of an external electric field and ionic impurities on 59 60 clustering in the alkanes and polyethylene . As described above, other investigators have

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1 2 3 successfully used the SPC and SPC/E water and TraPPE alkane force fields to model water- 4 5 6 hydrocarbon systems, and we also use these computationally cheap models in this study. This 7 8 contribution reviews this work and provides some new data and insights into the mechanism 9 10 of water cluster formation and water treeing. The new data presented here focuses mainly on 11 12 13 the validity of results obtained from both the SPC and SPC/E models for water systems 14 15 ranging from 200 to 1000 molecules, as well as entropy and enthalpy changes for cyclic to 16 For Peer Review Only 17 18 linear topological transformations of water tetramers and pentamers. However, the main aim 19 20 of this review is to give an overview of the effect of alkane , polyethylene matrices, 21 22 external electric fields and ionic impurities on the formation of water clusters, and how the 23 24 25 formation of water clusters can cause water treeing in polyethylene cables. 26 27 28 29 30 31 32 2. Methods 33 34 35 36 The simulation methods and potential models are presented elsewhere 61,62,62,64,65,66 and are 37 38 39 briefly discussed here for the sake of completeness. 40 41 42 43 44 2.1 Simulation techniques 45 46 46 The GEMC method was used to obtain equilibrium conditions for vapour-liquid water, 47 48 liquid-liquid water-alkane and liquid-melt water-polyethylene systems. Simulations were 49 50 51 typically performed within the NVT ensemble for water systems and the NPT ensemble for 52 53 combined water-hydrocarbon systems. The results presented here were obtained from 54 55 simulations using two boxes, one for each phase, with periodic boundary conditions applied 56 57 58 to each box. The method includes four possible (trial) actions – volume exchanges, particles 59 60 moves and rotations within a box, and particle swaps between boxes. Configurational bias 68

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1 2 3 where, after performing a trial move, one reconstructs the atom-by-atom according 4 5 6 to the usual Boltzman weighting criteria was also included for water and alkane molecules to 7 8 increase the efficiency of the simulations. 9 10 11 12 13 The polyethylene systems were studied at 450 K, which is above its melting temperature 14 15 (experimental melting point is ≈410 K 69 ) and hence ensures fully amorphous systems. The 16 For Peer Review Only 17 18 configurational bias method is inefficient for long hydrocarbon chains, so the polyethylene 19 20 matrix was modelled by five C 100 or ten C 300 chains using a new connectivity altering osmotic 21 22 Gibbs Ensemble method 66,70 . That is, the polyethylene molecules were modelled by chains 23 24 71 25 that contained on average C 100 or C 300 units, and where the end-bridging method was used to 26 27 vary the length of these chains by up to ±50 and ±150 carbon units, respectively. Changing 28 29 this parameter was not investigated, but the similarity of the results obtained from the C 100 30 31 32 and C 300 models indicates that they are insensitive to the chain length or variation in this 33 34 length. Also, since the alkane-water simulations showed that there is negligible solubility of 35 36 alkane in water for chains that are longer than decane, trial moves of polyethylene into the 37 38 39 water phase were not attempted. 40 41 42 43 44 As discussed below, the results presented here are not significantly affected whether 500 or 45 46 1000 water molecules are included in the simulations, so that 500 molecules were typically 47 48 used. In fact, after we had performed the simulations presented here, it was seen that using 49 50 51 200 water molecules with the minimum image convention (instead of the spherical truncation 52 53 used when simulating the larger systems) also yielded valid results. Some results from the 54 55 200 molecule simulations are also presented here. Monitoring of the average properties (e.g., 56 57 58 average densities and cluster sizes) over MC cycles (where each cycle contains the same 59 60 number of moves as molecules in the system) showed that equilibrium was typically obtained

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1 2 3 within 10 5 cycles for pure water systems and 10 6 cycles for water-hydrocarbon systems. 4 5 4 6 6 Equilibrium data was subsequently obtained from between 3x10 to 10 cycles, depending on 7 8 the temperature and system that was studied. This yielded standard deviations that are 9 10 typically smaller than the size of the data points shown in the figures. 11 12 13 14 15 The external electric field was modelled as a uniform field over both simulation boxes. This 16 For Peer Review Only 17 18 is reasonable due to the small, sub-microscopic sizes of the boxes. The total potential energy, 19 20 U, in a system with an external electric field ( E) is: 21 22 23 24 • 25 U = U0 – M E (1) 26 27 where U0 is the potential energy in the absence of an external field and M is the vector of the 28 29 30 molecular dipole moments. 31 32 33 34 When the simulations included a Na +--Cl - ion pair in the hydrocarbon matrix (see below), 35 36 + - 37 external fields that are parallel and antiparallel to the Na Cl ion pair field were simulated 38 39 to investigate the effect of enhancing or weakening this local field. Field strengths from 0 to 40 41 2x10 9 V/m were studied, which can be compared to fields of 10 7 – 10 8 V/m that polyethylene 42 43 9 44 cable insulation is typically exposed to, and 2.8x10 V/m that is found midway between the 45 46 Na +--Cl - ion pair when the ions are separated by a distance of 20 Å (typically used in our 47 48 simulations). 49 50 51 52 53 The presence of polyethylene -bound ionic impurities was modelled by a simple Na +--Cl - ion 54 55 56 pair. Hence, we do not attempt to model the specific impurities that are found in polyethylene 57 58 insulation (carbon black, etc) but perform the simulations to gain generic information of the 59 60 effect of ion pairs on the absorption of water into the polyethylene matrix. However, to

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1 2 3 reproduce the conditions found in insulating cable we fix the Na + and Cl - ionic positions so 4 5 6 that they do not migrate in the polyethylene matrix. Separations between 15 and 25 Å were 7 8 studied here (in fact, these separations increased by ≈0.05 Å during the simulations since 9 10 water was absorbed into the polyethylene simulation box thereby increasing the box volume, 11 12 13 but this does not affect the results reported here). 14 15 16 For Peer Review Only 17 18 19 20 2.2 Potential energy surface 21 22 The SPC 26 and SPC/E 36 models were used to describe the water intermolecular interactions. 23 24 25 These are rigid, three centre models with effective dipole moments of 2.27 D (SPC) and 2.35 26 27 D (SPC/E). These dipoles are between that of a water molecule in a minimum energy cyclic 28 29 hexamer (2.70 D) 13 and that of an isolated water molecule (1.85 D) 72 . Since they are larger 30 31 32 than the dipole of isolated water molecules they may lead to the formation of clusters that are 33 34 too large. However, it is expected that these models give the correct trends in cluster size 35 36 (e.g., with increasing temperature) which is the focus of this contribution. The validity of this 37 38 39 model is supported by the fact that it gives the same trends obtained from other models and ab 40 41 initio theory 23,25,33,73,74 . 42 43 44 45 55 46 The TraPPE united atom was used to describe the alkane and polyethylene 47 48 intermolecular interactions. As mentioned in the Introduction, this force field has 49 50 51 successfully been used by other workers to simulate hydrocarbon and water-hydrocarbon 52 53 systems. 54 55 56 57 58 The hydrocarbon-water intermolecular interactions were described by Lennard-Jones (12,6) 59 60 functions, where the diameter, σ, and energy, ε, parameters were obtained from the SPC (or

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1 2 3 SPC/E) and TraPPE models using the simple Lorentz-Berthelot mixing rules. However, these 4 5 6 rules did not yield satisfactory results for water solubility in alkanes and, as described below, 7 8 they were altered for the present simulations. 9 10 11 12 + - 13 Simulating the systems that contained the Na --Cl ion pair was done using the Dang 14 15 models 75 . These models were developed to be used with the SPC/E model, which was 16 For Peer Review Only 17 18 therefore also the used for these systems. Interactions between the ions and 19 20 hydrocarbons are determined using the Lorentz-Berthelot mixing rules. 21 22 23 24 25 The cut-off distance for Lennard-Jones interactions was typically 2.84 times larger than the LJ 26 27 diameter ( σ), tail corrections were used for distances longer than the cut-off and Ewald 28 29 summation was used for electrostatic interactions. 30 31 32 33 34 2.3 Definitions 35 36 The size of a water cluster may well depend on the way that the cluster is defined. To 37 38 39 investigate this we performed our cluster analyses using two definitions, both of which are 40 41 based on those that have been used previously 76,77 . In the first definition a water molecule is 42 43 44 considered to be part of a cluster if its (O) centre is within 4 Å of another oxygen 45 46 centre (O) that belongs to the cluster. This O-O distance was used since the peak in the 47 48 vapour phase water radial distribution function is less than 4 Å (it is 2.79 and 2.83 at 350 and 49 50 62 51 600 K, respectively) . Hence all molecules that are within the first (and only) peak in the O- 52 53 O radial distribution function are included in this definition. Clusters that are analysed using 54 55 this definition are referred to as ‘physical’ clusters. 56 57 58 59 60

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1 2 3 The second definition 77 takes account of hydrogen-bonding (H-bonding) in a simple way. In 4 5 6 this case two molecules belong to the same cluster (i.e., they are H-bonded) if the H centre on 7 8 one molecule is within 2.4 Å of the O centre of a neighbouring molecule, and the 9 10 intermolecular energy between these two molecules is less than -10 kJ/mol. It can be noted 11 12 13 that the results presented here are not sensitive to moderate changes of this energy criterion 14 15 (e.g., increasing the energy cut-off to -5.45 kJ/mol does not change the trends reported here). 16 For Peer Review Only 17 18 Clusters that are analysed using this definition are called ‘H-bonded’ clusters. 19 20 21 22 23 24 25 3. Results and discussion 26 27 28 29 The trends of water clustering that are presented here are not dependent on the definition used 30 31 32 to define a cluster, whether 200, 500 or 1000 water molecules are used in the simulation or 33 34 whether the SPC or SPC/E model is used to describe the water intermolecular interactions. 35 36 For example, Fig. 1 shows that the shape of the density-temperature phase diagrams, 37 38 39 especially for the gas phase studied here, are the same irrespective of the number of water 40 41 molecules or potential model used in the simulation. In addition, they are all in qualitative 42 43 44 agreement with experimental data. It can also be noted that similar trends for found for other 45 78 79 80 37 46 water models such as TIP4P , TIP5P , MSPC/E and EP-6 . 47 48 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 For Peer Review Only 17 18 19 20 21 Figure 1 . Density-temperature phase diagrams obtained from simulations using i) 500 water 22 23 24 molecules with the SPC model (stars), ii) 1000 water molecules with the SPC model (filled 25 26 circles), and iii) 500 water molecules with the SPC/E model (open squares). Experimental 27 28 data 81 are shown as a solid line. 29 30 31 32 33 34 35 Although the SPC and SPC/E give similar trends, they give quantitatively different (liquid 36 37 38 and) vapour phase densities that are not apparent on the scale used in Fig. 1. Fig. 2 is a plot of 39 40 the temperature dependence of the vapour phase densities using an expanded scale, and shows 41 42 43 that for temperatures below 500 K the SPC model yields densities that are in better agreement 44 45 with experiment. As can be seen in Fig. 1, the SPC/E results converge with, and eventually 46 47 are smaller than, the experimental vapour temperatures with increasing density (the SPC 48 49 50 model yields lower temperatures than the SPC/E model at all vapour densities). The results 51 52 also show that these data are not dependent on the number of molecules used in the 53 54 simulation. In spite of the difference seen in Fig. 2, we stress that both models yield the 55 56 57 correct trends, which is the focus of the work presented here. 58 59 60

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1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 For Peer Review Only 17 18 19 20 21 22 23 24 Figure 2 . Temperature dependence of the vapour phase densities using the SPC (stars, 200 25 26 molecules and triangles, 500 molecules) and SPC/E models (squares). Experimental data 81 is 27 28 shown as a solid line. 29 30 31 32 33 Fig. 3 shows the percentage of clusters that have two or more water molecules as a function of 34 35 temperature (i.e., water molecules are considered as clusters with one water molecule, and 36 37 38 Fig.3 shows the change in percentage of clusters that contain more than one water molecule). 39 40 It is clear that there is a larger percentage of clusters with at least two water molecules with 41 42 43 increasing temperature. In addition to the increase in fraction of clusters that contain at least 44 45 two water molecules, the average cluster size (number of water molecules in the cluster) also 46 47 increases with increasing temperature 62 . Hence the number of water molecules included in 48 49 50 clusters with more than one molecule also increases with increasing temperature. This is 51 52 expected since, under equilibrium conditions, and increase in temperature is accompanied by 53 54 an increase in (vapour) pressure. Similarly to the discussion with reference to Fig. 2, the same 55 56 57 trends are observed for the SPC and SPC/E models. It is also clear from the figure that these 58 59 trends do not depend on whether the H-bonded or physical definition of the cluster is used 60

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1 2 3 (although there are always fewer molecules included in H-bonded clusters due to the more 4 5 6 stringent conditions in this definition). 7 8 9 10 11 12 13 14 15 16 For Peer Review Only 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 Figure 3. Percentage of clusters containing at least two water molecules as a function of 32 33 temperature. Physical clusters are shown by open symbols and hydrogen bonded clusters by 34 35 36 filled symbols. Results obtained from 200 molecule simulations using the SPC model are 37 38 shown in circles, and those using the SPC/E model with 200 and 500 water molecules are 39 40 41 shown as diamonds and triangles, respectively. 42 43 44 45 46 47 48 The simulations also allowed for the analysis of the most favoured cluster topologies at all 49 50 temperatures. Since the number of possible topologies increases dramatically with increasing 51 52 cluster size, the analysis was restricted to clusters containing three, four and five molecules, 53 54 55 where the number of possible topologies is two, six and twenty, respectively. Analysis of 56 57 these trimer, tetramer and pentamer clusters 62 shows that open (linear) topologies are favoured 58 59 at temperatures above approximately 400 K whereas closed (cyclic) topologies are 60 energetically preferred at low temperatures (for both the SPC and SPC/E models).

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1 2 3 4 5 6 The change in enthalpy, H, and entropy, S, for cyclic linear transformation can be 7 8 analysed by plotting the (logarithm of the) relative abundances of these topologies as a 9 10 function of inverse temperature. In accordance with standard chemical thermodynamics 82 , 11 12 13 and since H and S only have small temperature dependences , this plot yielded the straight 14 15 line 16 For Peer Review Only 17 18 19 20 lnK = S/R – H/RT (2) 21 22 23 24 25 For example, analysis for the cyclic linear tetramer for the SPC/E model yielded H = 28 26 27 kJ/mol and S = 74 J/(mol K). This change in enthalpy is very similar to the energy required 28 29 to break the SPC/E , which is 30 kJ/mol. As seen from the data in Table 1, 30 31 32 results from the tetramer and pentamer cyclic linear isomerisation are similar (data of the 33 34 SPC pentamer not presented since the lack of sufficient numbers of pentamer cluster in the 35 36 simulations makes the analysis statistically unreliable). 37 38 39 40 41 Table 1 Change in enthalpies and entropies for cyclic linear isomerisation of trimer, 42 43 44 tetramer and pentamer clusters for the SPC and SPC/E models. 45 46 Type trimers tetramers pentamers: 47 48 49 SPC/E SPC SPC/E SPC SPC/E 50 51 ∆H 13 20 28 21 36 52 (kJ/mol) 53 54 ∆S 48 62 74 68 93 55 56 (J/molK) 57 58 Ttrans (K) 260 307 377 317 387 59 60

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1 2 3 As mentioned in the Methods section, the TraPPE model was used to describe the 4 5 6 hydrocarbon intermolecular interactions. Interactions between the SPC water molecules, i, 7 8 and TraPPE hydrocarbons, j, were determined from 9 10 11 12 σ + σ 13 i j σ = (3) 14 ij 2 15 16 For Peer Review Only 17 18 19 and 20 21 22 23 24 ε = ε + ε ij B i j (4) 25 26 27 28 29 where σ and ε are the Lennard-Jones parameters of the SPC (subscript i) and TraPPE (j) 30 31 32 models. When B=1.0 these equations are the Lorentz-Berthelot mixing rules. As exemplified 33 34 in Fig. 4 for decane, these mixing rules (with B=1.0) underestimate the solubility of water in 35 36 hydrocarbons. The agreement was greatly improved when increasing the value of B to 1.68, 37 38 39 but this led to the formation of a single phase system at 550 K, which is well below the 40 41 critical temperature of water (which is 647 K 81 and 587-596 K 80 for SPC water). As a 42 43 44 compromise B=1.3 was used since this gave good agreement with the experimental 45 63 46 solubilities of water for a variety of hydrocarbons , while still maintaining a two phase 47 48 system at the temperatures studied in this work. 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 For Peer Review Only 17 18 19 20 21 22 23 24 25 26 27 28 29 30 Figure 4. Solubility of water in decane (g water/kg decane) as a function of temperature for 31 32 33 B=1.0 (stars), 1.2 (circles), 1.3 (triangles) and 1.4 (squares) where B is the parameter in Eq. 34 35 (4). Experimental results from Tsonopoulos 17 are shown as a solid curve. The insert shows 36 37 38 the corresponding solubility of decane in water (no decane was dissoved in water below 440 39 40 K). The pressure is 20 MPa at 550 K, 6 MPa at 500 K and 3 MPa at all other temperatures. 41 42 43 44 45 46 47 The insert to Fig. 4 shows the solubility of decane in water for the values of B used in Fig. 4. 48 49 It is clear that one cannot obtain good water-in-decane and decane-in-water solubilities with 50 51 52 the same value of B. It is probable that more elaborate mixing rules (and perhaps even more 53 54 elaborate water and hydrocarbon models) are required to achieve simultaneous improvement 55 56 in water-in-decane and decane-in-water solubilities. However, this work focuses exclusively 57 58 59 on the trends of water solubility and clustering in hydrocarbons, and developing a more 60 accurate force field is beyond the scope of this study.

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1 2 3 4 5 6 Fig. 5 shows the solubility of water in hydrocarbons as a function of chain length (using 7 8 B=1.3 in Eq. (4)). The increase in the number of water molecules that are included in clusters 9 10 containing at least two water molecules, and the increase in the average size of clusters with 11 12 62 13 temperature, that are observed for pure water vapour are also seen for water in the 14 15 hydrocarbon phase. However, there is a decrease in the density of clusters and cluster size 16 For Peer Review Only 17 18 with increasing carbon chain length. This is probably due to the increase in hydrocarbon 19 20 density with increasing chain length. Fig. 5 also shows that there are fewer water molecules 21 22 for each carbon atom as the length of the chain increases. 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 Figure 5 47 . Solubility of water in hydrocarbons (g/kg) as a function of chain length at 450 K 48 17 49 and 30 bar. The stars show experimental data and the circles are calculated from the 50 51 Sanchez-Lacombe equation of state 83 . 52 53 54 55 56 Fig. 5 shows that, in agreement with experiment, the solubility of water in polyethylene is 57 58 low. This will hinder the formation of water trees. As mentioned in the Introduction, 59 60 formation of water trees in polyethylene insulators requires an alternating current (which

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1 2 3 leads to external fields that change direction on the 50 – 60 Hz frequency scale) and 4 5 6 impurities in the polyethylene matrix. If sufficiently strong, the external electric field will 7 8 cause the water molecules dipole moments to align with the field84 , which can lead to an 9 10 increase in the density of the water and change its solubility in the polyethylene . Fig. 6 shows 11 12 6 7 13 that the presence of electric fields that are typical for electric cables (10 -10 V/m) does not 14 15 significantly affect the water solubility in polyethylene. Far larger electric fields (> 10 8 V/m), 16 For Peer Review Only 17 18 that may occur locally due to nanoscale protrusions from the conducting metal or the presence 19 20 of impurities, reduce the water solubility since a larger energy gain is obtained when the water 21 22 molecules align in the liquid water phase (and hence water molecules are lost from the 23 24 25 polyethylene matrix). Hence, large external electric fields reduce water solubility in pure 26 27 polyethylene. 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 Figure 6. Solubility of water in polyethylene at 450 K and 30 bar as a function of the applied 53 54 electric field (stars). The effect of the Na +--Cl - ion pair when the ion-ion separation is 20 Å is 55 56 + - 57 also shown (the external field enhances the local Na Cl ion field). 58 59 60

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1 2 3 Fig. 6 also shows the solubility of water in polyethylene when a Na +--Cl - ion pair is included 4 5 + - 6 in the polyethylene matrix. Results are included for Na --Cl separations of 20 Å and in the 7 8 absence and presence of electric fields, where the external field enhances the local Na +Cl - 9 10 ion field. It is clear that the presence of Na +--Cl - ion pairs leads to a dramatic increase in the 11 12 13 water solubility. This is because water forms rod-like structures between the ion pairs when 14 15 they are sufficiently close. For sufficiently small Na +--Cl - separations (15 and 20 Å studied 16 For Peer Review Only 17 18 here), the local electric field between the ions induces the formation of the water cluster even 19 20 in the absence of an electric field, and hence increases the solubility in the polyethylene 21 22 matrix. When the ions are far apart (25 Å studied here) the local field is not sufficiently 23 24 25 strong to support the rod-like structure, and separate water clusters form around each ion. 26 27 This leads to a decrease in water solubility compared to that obtained for separations of 15 28 29 and 20 Å. Typical structures for Na +--Cl - separations of 15, 20 and 25 Å, when there is no 30 31 64 32 external electric field, are shown in Ref. . 33 34 35 36 As seen in Fig. 6, the presence of external fields that enhance the local field between the ions 37 38 39 leads to a further increase in the water solubility. In fact, the presence of sufficiently large 40 41 electric fields (e.g., 2x10 9 V/m) induces the formation of rod-like structure between ions that 42 43 44 have large separation. For example, Fig. 7 shows that a cluster is induced between when the 45 + - 46 Na and Cl ions are separated by 25 Å where, as discussed above, there is no rod-like cluster 47 48 in the absence of a field. This leads to a large increase in solubility for these ion-pairs. 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 For Peer Review Only 17 18 19 20 Figure 7 . A typical water clusters for a Na +--Cl - separation of 25 Å in the presence of an 21 22 9 23 enhancing electric field of 2x10 V/m. The polyethylene matrix is not shown for the sake of 24 25 clarity. 26 27 28 29 30 31 32 In summary, we have combined the GEMC method with the bridge-ending method to study 33 34 35 the solubility and clustering of water molecules in a polyethylene matrix. It was found that 36 37 the presence of ionic impurities in the matrix dramatically increases the water solubility, and 38 39 the presence of an external electric field that enhances the local field between the ions leads to 40 41 42 a further increase in the water uptake. These results allow us to hypothesise a possible 43 44 mechanism for water tree formation in polyethylene electric cable insulation: The presence of 45 46 an external field that enhances the local field between positive  negative pairs of ion 47 48 49 impurities leads to the formation of rod-like water clusters between the ions, and this cluster 50 51 creates a cavity in the polymer matrix. Switching of the (AC) current leads to a change in the 52 53 direction of the electric field, which weakens the local positive  negative field but enhances 54 55 56 the field between a nearby negative  positive ion pair. This leads to a reduction (or 57 58 removal) of the original water cluster and the formation of a new cluster, and hence a new 59 60 cavity in the polymer matrix between the negative  positive ion pair. Since typical AC

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1 2 3 switching rates (typically 50 – 60 Hz) are far faster than polymer relaxation rates, the cavities 4 5 6 induced by the formation of water clusters are not removed between AC cycles. This allows 7 8 for continued growth of the cavity so that channels of water can be formed in the polymer 9 10 matrix. 11 12 13 14 15 16 For Peer Review Only 17 18 4. Conclusion 19 20 21 22 The GEMC technique has been used to study the clustering of water in vapour, alkanes and 23 24 25 polyethylene, where the water clusters are in equilibrium with liquid phase water. The 26 27 simulations of water clustering in polyethylene were made more efficient by using a new 28 29 connectivity altering osmotic Gibbs Ensemble technique. It was seen that, for water vapour in 30 31 32 equilibrium with liquid phase water, an increase in temperature leads to the formation of more 33 34 and larger water clusters. In addition, entropic effects favour the formation of open cluster 35 36 topologies compared to the minimum-energy closed topologies. These trends are also found 37 38 39 for water clustering in alkanes and polyethylene, although fewer and smaller clusters are 40 41 formed as the length of the hydrocarbon chain increases. Also, large external electric fields 42 43 44 decrease the solubility of water in the hydrocarbons. However, the presence of pairs of 45 46 oppositely charged ions in the hydrocarbon matrix dramatically increases the water solubility, 47 48 which is further increased in the presence of an external field that enhances the local field 49 50 51 between the ions. 52 53 54 55 56 57 58 59 60

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1 2 3 5. Acknowledgement 4 5 6 7 8 We are grateful for valuable discussions with Prof. Doros Theodorou, National Technical 9 10 University of Athens, Greece. This work has been funded by the Swedish Graduate School in 11 12 13 Materials Science and the simulations were performed on a Beowulf computer sponsored by 14 15 Stiftelsen FöreningsSparbanken Sjuhärad. 16 For Peer Review Only 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 Word count: 6384 4 5 6 7 8 The manuscript is for a special edition ‘Frontiers of Molecular Simulation’ 9 10 11 12 13 Editor handling the manuscript: Jerome Delhommelle 14 15 16 For Peer Review Only 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 Table 4 5 6 Table 1 Change in enthalpies and entropies for cyclic linear isomerisation of trimer, 7 8 tetramer and pentamer clusters for the SPC and SPC/E models. 9 10 11 Type trimers tetramers pentamers: 12 13 14 SPC/E SPC SPC/E SPC SPC/E 15 ∆H 13 20 28 21 36 16 (kJ/mol) For Peer Review Only 17 18 19 ∆S 48 62 74 68 93 20 (J/molK) 21 22 T (K) 260 307 377 317 387 23 trans 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 Figure captions 4 5 6 Figure 1 . Density-temperature phase diagrams obtained from simulations using i) 500 water 7 8 molecules with the SPC model (stars), ii) 1000 water molecules with the SPC model (filled 9 10 circles), and iii) 500 water molecules with the SPC/E model (open squares). Experimental 11 12 81 13 data are shown as a solid line. 14 15 Figure 2 . Temperature dependence of the vapour phase densities using the SPC (stars, 200 16 For Peer Review Only 17 81 18 molecules and triangles, 500 molecules) and SPC/E models (squares). Experimental data is 19 20 shown as a solid line. 21 22 Figure 3. Percentage of clusters containing at least two water molecules as a function of 23 24 25 temperature. Physical clusters are shown by open symbols and hydrogen bonded clusters by 26 27 filled symbols. Results obtained from 200 molecule simulations using the SPC model are 28 29 shown in circles, and those using the SPC/E model with 200 and 500 water molecules are 30 31 32 shown as diamonds and triangles, respectively. 33 34 Figure 4. Solubility of water in decane (g water/kg decane) as a function of temperature for 35 36 B=1.0 (stars), 1.2 (circles), 1.3 (triangles) and 1.4 (squares) where B is the parameter in Eq. 37 38 17 39 (4). Experimental results from Tsonopoulos are shown as a solid curve. The insert shows 40 41 the corresponding solubility of decane in water (no decane was dissoved in water below 440 42 43 44 K). The pressure is 20 MPa at 550 K, 6 MPa at 500 K and 3 MPa at all other temperatures. 45 46 Figure 5 . Solubility of water in hydrocarbons (g/kg) as a function of chain length at 450 K 47 48 and 30 bar. The stars show experimental data 17 and the circles are calculated from the 49 50 83 51 Sanchez-Lacombe equation of state . 52 53 Figure 6. Solubility of water in polyethylene at 450 K and 30 bar as a function of the applied 54 55 electric field (stars). The effect of the Na +--Cl - ion pair when the ion-ion separation is 20 Å is 56 57 + - 58 also shown (the external field enhances the local Na Cl ion field). 59 60

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1 2 3 Figure 7 . A typical water clusters for a Na +--Cl - separation of 25 Å in the presence of an 4 5 9 6 enhancing electric field of 2x10 V/m. The polyethylene matrix is not shown for the sake of 7 8 clarity. 9 10 11 12 13 14 15 16 For Peer Review Only 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

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1 2 3 4 5 6 References 7

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1 SPC 2 3 Exp 4 SPC/E 1000 5 600 6 For Peer Review Only SPC/E 500 7 8 9 10 11 12 500 13 14 15 16

17T(K) 18 19 400 20 21 22 23 24 25 26 27 300 28 29 30 31 32 33 34 200 35 0 200http://mc.manuscriptcentral.com/tandf/jenmol 400 600 800 1000 36 37 3 38 Density (kg/m ) 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 600 Page 32 of 37

1 Exp 2 3 SPC/E 500 4 SPC 500 5 6 For Peer Review Only SPC 200 7 8 9 500 10 11 12 13 14 15 16

17T(K) 18 19 20 400 21 22 23 24 25 26 27 28 29 30 31 300 32 33 34 35 0.1http://mc.manuscriptcentral.com/tandf/jenmol1 10 36 37 3 38 Density (kg/m ) 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 Page20 33 of 37

1 2 3 4 5 For Peer Review Only 6 7 15 8 9 10 11 12 13 14 15 16 10 17 18 19 20Percentage 21 22 23 24 25 5 26 27 28 29 30 31 32 33 0 34 http://mc.manuscriptcentral.com/tandf/jenmol 35 350 400 450 500 550 36 37 Temperature (K) 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 Page 34 of 37

1 1e-02 2 3 For Peer Review Only 4 5 6 100 1e-04 7 8 9 10 11 12 1e-06 13 14 15 440 500 560 16 17 18 19 20 21

22 decane g water/kg 23 24 1 25 26 27 28 29 30 31 32 33 http://mc.manuscriptcentral.com/tandf/jenmol 34 300 350 400 450 500 550 35 36 T/K 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 Page20 35 of 37

1 This work 2 3 Tsonopoulos 4 5 For Peer Review OnlySanchez-Lacombe EOS 6 Experimental 7 15 8 9 10 11 12 13 14 15 16 10 17 18 19 20 21 22

23kg alkane / g water 24 25 5 26 27 28 29 30 31 32 33 0 34 http://mc.manuscriptcentral.com/tandf/jenmol 35 6 8 10 16 100 300 36 37 Chain length in carbon units 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 25 Page 36 of 37

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1 2 3 4 5 6 7 For Peer Review Only 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 http://mc.manuscriptcentral.com/tandf/jenmol 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60