1. Introduction
The dynamic view of the microscopic systems can be studied with the help of molecular dynamics (MD) simulations. The study of mass transport through nanoscale channels has gained much interest in recent times as it possesses a large application potential. Nanoscale materials such as nanotubes, nanopores and nanogaps have shown promising potential in the desalination process [1,2,3,4,5,6,7]. These nanoscale materials show better ion selectivity, high efficiency and low cost. Membrane desalination is considered to be more energy efficient than thermal desalination methods [8]. Additionally, the membrane desalination technique known as reverse osmosis (RO) is considered to be more environmentally friendly. The water flux across a membrane scales inversely to the thickness of the membrane. Hence, ultra-thin membranes promise better water transport. Graphene consists of sp2 carbon atoms arranged in a hexagonal honeycomb lattice, making it the ultimate ultrathin material. It also exhibits excellent mechanical, thermal and electronic properties [9]. Hence, the use of graphene in the desalination process has grabbed significant attention.
Water transport through single-layer graphene using molecular dynamics was first shown by Suk et al. [10]. Single-layer graphene membrane with hydrogenated and hydroxylated nanopores has shown fast water transport along with excellent salt rejection [8]. It has been reported that the desalination performances of pyridinic nitrogen-doped membranes exhibit higher water flux several orders of magnitude higher than polymeric reverse osmosis (RO) membranes [11]. The removal of heavy metal ions from water using functionalized graphene has been demonstrated using a molecular dynamics study [12]. In an experimental work conducted in 2015 to study the ionic transport through hydrophobic nanopores, the researchers found that there is a constant weak surface charge density for nanopore diameters greater than 3 nm [13].
Water is one of the most plentiful substances on planet earth and it is one of the most extensively studied substances [14,15]. Even though numerous studies have been carried out about it, our understanding of its behavior and its distinctive properties are incomplete [16]. To study water molecule and their interaction with other substances using molecular dynamics require accurate water models. Most of the studies in the MD use fixed-charge rigid non-polarizable water models due to their computational efficiency [17]. Rigid 3-point water models are the commonly used water models in atomistic MD simulations as they can reproduce many properties of water. Rigid 3-point water models represent water molecules as triatomic molecules with rigid bonds. simple point charge (SPC) [18], simple point charge-extended (SPC/E) [19] and transferable intermolecular potential 3P (TIP3P) [20] are the popular rigid 3-point water models. SPC water model is the oldest water model that is commonly in use today [21]. The 3-point optimal point charge (OPC3) model [17] is one of the new rigid 3-point water models which is comparable to or significantly better for simulations of divalent metal ions than the other 3-point water models [22].
Using molecular dynamics, numerous studies have been conducted to study the water transport properties of multilayered nanoporous graphene. In most of these simulation studies, water models such as transferable intermolecular potential 3 point (TIP3P) [23,24,25,26] and simple point charge-extended (SPC/E) [27,28,29,30,31] are widely used. In an MD study conducted in 2010, the interaction of the water molecules confined in between two graphene sheets showed that the results are qualitatively and semi-qualitatively equivalent for the TIP3P and SPC/E water models [32]. In a recent MD study in early 2022 carried out on water transport through carbon nanotubes, researches showed that the water models do not have any influence on the conductance trend as the diameter of the tube is increased [33]. In a study published in 2020, rotating graphene membranes were found to have almost 100% salt rejection, even with pores larger than hydrated ions, and to have high water permeability and ultra-selectivity simultaneously [34]. According to a recent study, fabricating distillation membranes with vertically aligned channels with a hydrophobicity gradient can be accomplished by removing imine bonds from covalent organic framework films, resulting in a threefold increase in water permeance over state-of-the-art membrane distillation [35]. The influence of water models on desalination performance in the single-layered system showed that the water flux variations are as high as 84% among different water models [36]. It appears that there has been no systematic study carried out on how the different water models influence water transport through multilayered nanoporous graphene.
In this study, we have performed molecular dynamics simulations on functionalized and non-functionalized nanoporous multilayered graphene using different water models. SPC (simple point charge) [18], SPC/E (extended simple point charge) [19], TIP3P-FB (transferable intermolecular potential with 3 points—Force Balance) [37], TIP3P-EW (transferable intermolecular potential with 3 points with Ewald summation) [38] and OPC3 (3-point optimal point charge) [17] are the different water models used in this study. The aim of this study is to find out the amount of variation in the number of water molecules transported across multilayered graphene, both functionalized and non-functionalized, using different water models. It also gives an overall picture of the key attributes that lead to the variation of the number of water molecules transported through the multilayered porous graphene membrane.
2. Methods and Model
The nanoporous multilayered graphene used in this study is modeled in SAMSON (Software for Adaptive Modeling and Simulation of Nanosystems) software [39]. Minimization of the energy of the structure is carried out using the FIRE (Fast Inertial Relaxation Engine) algorithm [40]. The nanoporous multilayered graphene system consists of 5 layers of nanoporous graphene. These graphene layers are heavily stacked with an interlayer distance between the graphene sheets of 3.5 Å. The dimensions of the graphene sheets are 30 Å × 30 Å. Water molecules are placed on both sides of the nanoporous multilayered graphene structure. The simulation setup used in this study is illustrated in Figure 1.
The simulation box (30 Å × 30 Å × 160 Å) has a total of 2138 water molecules, of which 1710 water molecules are in the feed region and 428 water molecules in the permeate region. SPC, SPC/E, TIP3P-FB, TIP3P-EW and OPC3 are the different water models used in this study. The configurations of these water models are given in Figure 2.
The force field parameters of the water models used in this study are listed in Table 1.
AIREBO (adaptive intermolecular reactive bond order) potential [41] is used for the carbon atoms and the functionalized hydrogen atoms of the porous membrane. We used the Lorentz–Berthelot mixing rule to calculate the Lennard-Jones (L–J) interactions between the water molecules and the carbon and hydrogen atoms of the nanoporous multilayered graphene. A timestep of 1 femtosecond was used to simulate the simulations for 6 nanoseconds. We used pppm style (particle-particle particle-mesh) solver to calculate the long-range electrostatic interactions [42]. The cutoff for the L–J interaction used in this work is 10 Å. The simulations are carried out using LAMMPS software [43] and we used VMD (visual molecular dynamics) software for visualization [44]. The water molecules are kept constrained using the SHAKE algorithm [45]. Nosé-Hoover thermostat [46], along with the canonical ensemble NVT is used in this study. To simulate the pressure-driven flow, the desired pressure is applied onto the piston (graphene sheet) at the feed region, and ambient pressure to the piston at the permeate region is applied [47].
In this study, a pressure of about 150 MPa is applied to the piston at the feed region. Although a pressure of 150 MPa is significantly higher than the typical desalination system, which is around a few MPa, previous studies have shown that the results will be valid at low pressures as well since the time scales for flow scale linearly with pressure applied [8]. As mentioned earlier, we have employed both functionalized and non-functionalized porous graphene in this study. It should be noted that the effective pore size decreases as the pore is functionalized.
3. Cumulative Molecule Passage and Occupancy
Figure 3 shows the cumulative water molecules passed through the non-functionalized and functionalized multilayered graphene membrane. SPC water model and TIP3P-EW water models showed quite similar higher water molecule passage, while OPC3 and TIP3P-FB showed lower water molecule passage in the non-functionalized multilayered membrane system. SPC water model showed around a 55% increase in the number of water molecules when compared to the TIP3P-FB water model. In the membrane system containing the pores functionalized with hydrogen atoms, the SPC water model showed around 120 water molecules being filtered, whereas the OPC3 water model filtered only around 7 water molecules. In the functionalized membrane system modeled using the OPC3 water model, the pore remained empty most of the time. This could be visualized easily in Figure 4.
In the case of the non-functionalized pore, the TIP3P-FB and SPC/E showed better water occupancy. The occupancy of water molecules inside the channel is determined by the local excess chemical potential [48]. Even though SPC and TIP3P-EW sowed relatively lower water molecules occupancy, these water models favored better transport of the water molecules as they show the relatively lesser fluctuation of water molecules inside the pore. A large part of the variation in the number of molecules that are filtered can be attributed to the partial charges of the atoms used in the models of water. As mentioned in a previous study [38], this can be viewed clearly when we compare the SPC and SPC/E, water models. These two water models differ only in their partial charges, and they show a variation of 40% in the number of water molecules filtered. Another key factor that affects the water transport through the pore is the energy constant (ε). This can be understood clearly by comparing the number of water molecules filtered in a functionalized membrane between the OPC3 water model and TIP3P-FB water models. The TIP3P-FB water model has a lower energy constant (ε) and a larger Van der Walls radius when compared to the OPC3 water model. In the case of the functionalized pore, TIP3P-FB showed a greater number of water molecules filtered when compared to that of the OPC3 water model, suggesting that the energy constant (ε) also plays a key role when the pore is very confined.
4. Free Energy of Occupancy Fluctuations
Figure 5 shows the occupancy fluctuation of the water molecules inside the non-functionalized and functionalized multilayered graphene pore. The detailed discussions regarding the free energy of occupancy fluctuations have been reported in many previous works [48,49,50]. In this work, we found that the maximum number of water molecules inside the channel is found in a non-functionalized membrane with a TIP3P-FB water model. In general, constant fluctuations of water molecules are seen in all cases. The constant fluctuation of the water molecules inside the channel shows that the average binding energy of water molecules inside the channel is unfavorable compared to bulk water. TIP3P-EW water model showed more fluctuations in the non-functionalized membrane. It also showed a very lower value of 15 for the most favorable number of atoms. The maximum value of 19 for the most favorable number of atoms is the TIP3P-FB water model. For the functionalized pore cases, most of the time, the pore remains empty. The maximum number of water molecules found in the functionalized pore is in the case of the SPC water model with 11 water molecules. The list of all water molecule occurrences and the instances inside the nanopore for both functionalized and non-functionalized cases using different water models is listed in Table 2.
5. Radial Distribution Function and Density
A particle’s probability of being found at a distance r away from a given reference particle is measured by RDF [51]. The radial distribution function inside the nanopore for the oxygen atoms to the first carbon atom of the pore is given in Figure 6. The RDF is computed for the same force cutoff distance used in the simulation. From Figure 6 of the non-functionalized pore, two atomic layers can be distinguished inside the channel from the two peaks in the radial distribution function plot [52]. The first distinctive peak occurs around 4 Å and the second distinctive peak occurs around 7.5 Å. For all water models, the position of peaks almost remains the same. The non-functionalized pore in Figure 6 also shows that the interaction between carbon atoms and oxygen atom of the TIP3P-EW water model is weak when compared to other water models. Hence, water molecules of the TIP3P-EW water model can slip freely through the multilayered graphene pore when compared to other water model cases.
The plot of the number density of the water molecules inside the nanopore is given in Figure 7. For the non-functionalized pore, we can see an increase in the density of the water molecules after the third layer of the porous graphene sheet. The water molecules enter the pore with large energy, this energy is subsequently lost as it crosses the third graphene layer, which results in the accumulation of a higher number of molecules in that region. Between the first and second layers of the multilayer, we can observe that molecules are mostly stagnated in the functionalized pore. It indicates that water molecules had difficulty overcoming the large energy barrier inside the pores.
6. Conclusions
In this study, we investigated the amount of variation in water molecules transported across functionalized and non-functionalized multilayered graphene using different water models. The five water models include the OPC3 water model, which claims to be more accurate in reproducing a comprehensive set of bulk properties when compared to water models of the same class such as TIP3P and SPC/E [5]. The other models are SPC, SPC/E, TIP3P-FB and TIP3P-EW. Different water models predict the different properties of water close to experimental results. So, in the transport of water through the nanopore, it is impossible to determine which water model best describes real water behavior [53]. However, based on the diffusion of water molecules in both functionalized and non-functionalized pores, TIP3P-FB predicts the diffusion of water molecules through multilayered porous graphene close to experimental results. For the non-functionalized pore water transport, we can say that the OPC3, TIP3P-FB and SPC/E water models predict close to real water diffusion. OPC3 and TIP3P-FB slightly predict the diffusion, while SPC/E slightly over-predicts the diffusion of water molecules. TIP3P-EW and SPC showed a similar higher number of transport of water molecules when compared with other water models used in this study. SPC and SPC/E water models that only differ in partial charges showed a 40% difference in the number of water molecules transported through the non-functionalized pore, which shows the significance of the water model’s partial charge. Additionally, by comparing OPC3 and TIP3P-FB in the functionalized pore, we can understand that the transport of water molecules in a very confined pore is affected by the value of the energy constant (ε) of the water model.
Conceptualization, C.P. and D.K.; data curation, C.P. and F.R.; formal analysis, C.P.; methodology, C.P.; project administration, D.K.; supervision, D.K.; validation, C.P. and F.R.; visualization, C.P. and F.R.; writing—original draft, C.P.; writing—review and editing, F.R. and D.K. All authors have read and agreed to the published version of the manuscript.
Not applicable.
Not applicable.
The data presented in this study are available on request from the corresponding author. The data are not publicly available due to privacy and ethical restrictions.
The authors declare no conflict of interest.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Figure 1. (a) Simulation domain, (b) porous graphene and (c) functionalized (hydrogenated) porous graphene.
Figure 2. Different water models used in this study. (a) OPC3; (b) SPC; (c) SPC/E; (d) TIP3P−EW; (e) TIP3P−FB.
Figure 2. Different water models used in this study. (a) OPC3; (b) SPC; (c) SPC/E; (d) TIP3P−EW; (e) TIP3P−FB.
Figure 3. Cumulative water molecule passage through (a) multilayered non-functionalized porous graphene and (b) multilayered functionalized porous graphene using different water models.
Figure 4. Number of water molecules inside the (a) multilayered non-functionalized porous graphene and (b) multilayered functionalized porous graphene using different water models at a given time.
Figure 5. Free energy of occupancy fluctuations of water molecules inside (a) multilayered non-functionalized porous graphene and (b) multilayered functionalized porous graphene using different water models.
Figure 6. Radial distribution function of oxygen atoms of the water molecules with that of the carbon atoms inside the multilayered non-functionalized porous.
Figure 7. Number density of water molecules inside (a) non−functionalized and (b) functionalized pore (grey dashed lines represent the initial location of graphene layers).
LJ parameters and atomic charges employed for water molecules in this work.
Water Model | σO (Å) | εO (kcal/mol) | qH (e) | qO (e) |
---|---|---|---|---|
SPC | 3.16557 | 0.1554 | 0.41 | −0.82 |
SPC/E | 3.16557 | 0.1554 | 0.4238 | −0.8476 |
TIP3P-FB | 3.178 | 0.15587 | 0.41722 | −0.84844 |
TIP3P-EW | 3.188 | 0.102 | 0.415 | −0.83 |
OPC3 | 3.17427 | 0.1634 | 0.447585 | −0.89517 |
List of water molecules and number of occurrences inside the pore for the 6 ns simulation.
Number |
Number of Occurrences | |||||||||
---|---|---|---|---|---|---|---|---|---|---|
Non-Functionalized Pore | Functionalized Pore | |||||||||
OPC3 | SPC | SPC/E | TIP3P-FB | TIP3P-EW | OPC3 | SPC | SPC/E | TIP3P-FB | TIP3P-EW | |
0 | 0 | 0 | 0 | 0 | 0 | 282 | 131 | 197 | 275 | 250 |
1 | 0 | 0 | 0 | 0 | 1 | 140 | 100 | 119 | 128 | 130 |
2 | 0 | 0 | 0 | 0 | 1 | 111 | 113 | 123 | 91 | 99 |
3 | 0 | 0 | 0 | 0 | 4 | 43 | 76 | 60 | 34 | 45 |
4 | 1 | 0 | 0 | 0 | 6 | 13 | 49 | 39 | 25 | 25 |
5 | 2 | 0 | 0 | 0 | 4 | 7 | 42 | 7 | 10 | 15 |
6 | 1 | 0 | 0 | 1 | 7 | 3 | 30 | 24 | 16 | 17 |
7 | 1 | 2 | 0 | 0 | 9 | 2 | 27 | 11 | 6 | 13 |
8 | 0 | 0 | 0 | 2 | 20 | 0 | 19 | 11 | 10 | 6 |
9 | 1 | 4 | 2 | 2 | 18 | 0 | 8 | 8 | 4 | 1 |
10 | 2 | 1 | 2 | 3 | 19 | 0 | 4 | 2 | 2 | 0 |
11 | 5 | 19 | 8 | 6 | 39 | 0 | 2 | 0 | 0 | 0 |
12 | 13 | 10 | 8 | 2 | 48 | 0 | 0 | 0 | 0 | 0 |
13 | 13 | 32 | 25 | 10 | 63 | 0 | 0 | 0 | 0 | 0 |
14 | 33 | 46 | 17 | 23 | 78 | 0 | 0 | 0 | 0 | 0 |
15 | 59 | 72 | 50 | 40 | 87 | 0 | 0 | 0 | 0 | 0 |
16 | 74 | 85 | 70 | 50 | 78 | 0 | 0 | 0 | 0 | 0 |
17 | 110 | 102 | 97 | 73 | 52 | 0 | 0 | 0 | 0 | 0 |
18 | 125 | 111 | 110 | 89 | 39 | 0 | 0 | 0 | 0 | 0 |
19 | 89 | 67 | 82 | 117 | 19 | 0 | 0 | 0 | 0 | 0 |
20 | 48 | 37 | 74 | 99 | 8 | 0 | 0 | 0 | 0 | 0 |
21 | 19 | 9 | 32 | 58 | 1 | 0 | 0 | 0 | 0 | 0 |
22 | 3 | 1 | 20 | 18 | 0 | 0 | 0 | 0 | 0 | 0 |
23 | 2 | 2 | 3 | 5 | 0 | 0 | 0 | 0 | 0 | 0 |
24 | 0 | 1 | 1 | 2 | 0 | 0 | 0 | 0 | 0 | 0 |
25 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 |
References
1. Santhosh, C.; Velmurugan, V.; Jacob, G.; Jeong, S.K.; Grace, A.N.; Bhatnagar, A. Role of Nanomaterials in Water Treatment Applications: A Review. Chem. Eng. J.; 2016; 306, pp. 1116-1137. [DOI: https://dx.doi.org/10.1016/j.cej.2016.08.053]
2. Carpenter, A.W.; de Lannoy, C.-F.; Wiesner, M.R. Cellulose Nanomaterials in Water Treatment Technologies. Environ. Sci. Technol.; 2015; 49, pp. 5277-5287. [DOI: https://dx.doi.org/10.1021/es506351r]
3. Cohen-Tanugi, D.; Grossman, J.C. Water Desalination across Nanoporous Graphene. Nano Lett.; 2012; 12, pp. 3602-3608. [DOI: https://dx.doi.org/10.1021/nl3012853]
4. Daer, S.; Kharraz, J.; Giwa, A.; Hasan, S.W. Recent Applications of Nanomaterials in Water Desalination: A Critical Review and Future Opportunities. Desalination; 2015; 367, pp. 37-48. [DOI: https://dx.doi.org/10.1016/j.desal.2015.03.030]
5. Qu, X.; Alvarez, P.J.J.; Li, Q. Applications of Nanotechnology in Water and Wastewater Treatment. Water Res.; 2013; 47, pp. 3931-3946. [DOI: https://dx.doi.org/10.1016/j.watres.2012.09.058] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/23571110]
6. Savage, N.; Diallo, M.S. Nanomaterials and Water Purification: Opportunities and Challenges. J. Nanoparticle Res.; 2005; 7, pp. 331-342. [DOI: https://dx.doi.org/10.1007/s11051-005-7523-5]
7. Corry, B. Designing Carbon Nanotube Membranes for Efficient Water Desalination. J. Phys. Chem. B; 2008; 112, pp. 1427-1434. [DOI: https://dx.doi.org/10.1021/jp709845u]
8. Spiegler, K.S.; El-Sayed, Y.M. The Energetics of Desalination Processes. Desalination; 2001; 134, pp. 109-128. [DOI: https://dx.doi.org/10.1016/S0011-9164(01)00121-7]
9. Novoselov, K.S.; Geim, A.K.; Morozov, S.V.; Jiang, D.; Zhang, Y.; Dubonos, S.V.; Grigorieva, I.V.; Firsov, A.A. Electric Field Effect in Atomically Thin Carbon Films. Science; 2004; 306, pp. 666-669. [DOI: https://dx.doi.org/10.1126/science.1102896] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/15499015]
10. Suk, M.E.; Aluru, N.R. Water Transport through Ultrathin Graphene. J. Phys. Chem. Lett.; 2010; 1, pp. 1590-1594. [DOI: https://dx.doi.org/10.1021/jz100240r]
11. Chen, Q.; Yang, X. Pyridinic Nitrogen Doped Nanoporous Graphene as Desalination Membrane: Molecular Simulation Study. J. Membr. Sci.; 2015; 496, pp. 108-117. [DOI: https://dx.doi.org/10.1016/j.memsci.2015.08.052]
12. Kommu, A.; Namsani, S.; Singh, J.K. Removal of Heavy Metal Ions Using Functionalized Graphene Membranes: A Molecular Dynamics Study. RSC Adv.; 2016; 6, pp. 63190-63199. [DOI: https://dx.doi.org/10.1039/C6RA06817K]
13. Balme, S.; Picaud, F.; Manghi, M.; Palmeri, J.; Bechelany, M.; Cabello-Aguilar, S.; Abou-Chaaya, A.; Miele, P.; Balanzat, E.; Janot, J.M. Ionic Transport through Sub-10 Nm Diameter Hydrophobic High-Aspect Ratio Nanopores: Experiment, Theory and Simulation. Sci. Rep.; 2015; 5, 10135. [DOI: https://dx.doi.org/10.1038/srep10135]
14. Kale, S.; Herzfeld, J. Natural Polarizability and Flexibility via Explicit Valency: The Case of Water. J. Chem. Phys.; 2012; 136, 084109. [DOI: https://dx.doi.org/10.1063/1.3688228]
15. Tu, Y.; Laaksonen, A. The Electronic Properties of Water Molecules in Water Clusters and Liquid Water. Chem. Phys. Lett.; 2000; 329, pp. 283-288. [DOI: https://dx.doi.org/10.1016/S0009-2614(00)01026-5]
16. Stillinger, F.H. Water Revisited. Science; 1980; 209, pp. 451-457. [DOI: https://dx.doi.org/10.1126/science.209.4455.451]
17. Izadi, S.; Onufriev, A.V. Accuracy Limit of Rigid 3-Point Water Models. J. Chem. Phys.; 2016; 145, 074501. [DOI: https://dx.doi.org/10.1063/1.4960175]
18. Berendsen, H.J.C.; Postma, J.P.M.; van Gunsteren, W.F.; Hermans, J. Interaction Models for Water in Relation to Protein Hydration. Intermolecular Forces, Proceedings of the Fourteenth Jerusalem Symposium on Quantum Chemistry and Biochemistry Held in Jerusalem, Israel, April 13–16, 1981; Pullman, B. Springer: Dordrecht, The Netherlands, 1981; pp. 331-342. [DOI: https://dx.doi.org/10.1007/978-94-015-7658-1_21]
19. Berendsen, H.J.C.; Grigera, J.R.; Straatsma, T.P. The Missing Term in Effective Pair Potentials. J. Phys. Chem.; 1987; 91, pp. 6269-6271. [DOI: https://dx.doi.org/10.1021/j100308a038]
20. Jorgensen, W.L.; Chandrasekhar, J.; Madura, J.D.; Impey, R.W.; Klein, M.L. Comparison of Simple Potential Functions for Simulating Liquid Water. J. Chem. Phys.; 1983; 79, pp. 926-935. [DOI: https://dx.doi.org/10.1063/1.445869]
21. Kadaoluwa Pathirannahalage, S.; Meftahi, N.; Elbourne, A.; Besford, A.; McConville, C.; Padua, A.; Winkler, D.; Gomes, M.; Greaves, T.; Le, T. et al. Systematic Comparison of the Structural and Dynamic Properties of Commonly Used Water Models for Molecular Dynamics Simulations; ACS Publications: Washington, DC, USA, 2021; [DOI: https://dx.doi.org/10.33774/chemrxiv-2021-0dt3n]
22. Sengupta, A.; Li, Z.; Song, L.F.; Li, P.; Merz, K.M. Parameterization of Monovalent Ions for the OPC3, OPC, TIP3P-FB, and TIP4P-FB Water Models. J. Chem. Inf. Model.; 2021; 61, pp. 869-880. [DOI: https://dx.doi.org/10.1021/acs.jcim.0c01390]
23. Sahu, S.; Zwolak, M. Ionic Selectivity and Filtration from Fragmented Dehydration in Multilayer Graphene Nanopores. Nanoscale; 2017; 9, pp. 11424-11428. [DOI: https://dx.doi.org/10.1039/C7NR03838K] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/28767109]
24. Zhang, H.; Liu, B.; Wu, M.-S.; Zhou, K.; Law, A. Transport of Salty Water through Graphene Bilayer in an Electric Field: A Molecular Dynamics Study. Comput. Mater. Sci.; 2017; 131, pp. 100-107. [DOI: https://dx.doi.org/10.1016/j.commatsci.2017.01.039]
25. Chen, Y.; Zhu, Y.; Yang, R.; Zhao, N.; Liu, W.; Zhuang, W.; Lu, X. Molecular Insights into Multilayer 18-Crown-6-like Graphene Nanopores for K+/Na+ Separation: A Molecular Dynamics Study. Carbon; 2018; 144, pp. 32-42. [DOI: https://dx.doi.org/10.1016/j.carbon.2018.11.048]
26. Yang, J.; Shen, Z.; He, J.; Li, Y. Efficient Separation of Small Organic Contaminants in Water Using Functionalized Nanoporous Graphene Membranes: Insights from Molecular Dynamics Simulations. J. Membr. Sci.; 2021; 630, 119331. [DOI: https://dx.doi.org/10.1016/j.memsci.2021.119331]
27. Soleimani, E.; Foroutan, M. Multilayer Graphene with a Rippled Structure for Water Desalination. J. Mol. Liq.; 2018; 265, pp. 208-215. [DOI: https://dx.doi.org/10.1016/j.molliq.2018.04.155]
28. Pan, J.; Xiao, S.; Zhang, Z.; Wei, N.; He, J.; Zhao, J. Nanoconfined Water Dynamics in Multilayer Graphene Nanopores. J. Phys. Chem. C; 2020; 124, pp. 17819-17828. [DOI: https://dx.doi.org/10.1021/acs.jpcc.0c04897]
29. Suk, M.E.; Aluru, N.R. Molecular and Continuum Hydrodynamics in Graphene Nanopores. RSC Adv.; 2013; 3, pp. 9365-9372. [DOI: https://dx.doi.org/10.1039/c3ra40661j]
30. Cicero, G.; Grossman, J.C.; Schwegler, E.; Gygi, F.; Galli, G. Water Confined in Nanotubes and between Graphene Sheets: A First Principle Study. J. Am. Chem. Soc.; 2008; 130, pp. 1871-1878. [DOI: https://dx.doi.org/10.1021/ja074418+]
31. Konatham, D.; Yu, J.; Ho, T.A.; Striolo, A. Simulation Insights for Graphene-Based Water Desalination Membranes. Langmuir; 2013; 29, pp. 11884-11897. [DOI: https://dx.doi.org/10.1021/la4018695]
32. Falk, K.; Sedlmeier, F.; Joly, L.; Netz, R.R.; Bocquet, L. Molecular Origin of Fast Water Transport in Carbon Nanotube Membranes: Superlubricity versus Curvature Dependent Friction. Nano Lett.; 2010; 10, pp. 4067-4073. [DOI: https://dx.doi.org/10.1021/nl1021046]
33. Mejri, A.; Mazouzi, K.; Herlem, G.; Picaud, F.; Hennequin, T.; Palmeri, J.; Manghi, M. Molecular Dynamics Investigations of Ionic Conductance at the Nanoscale: Role of the Water Model and Geometric Parameters. J. Mol. Liq.; 2022; 351, 118575. [DOI: https://dx.doi.org/10.1016/j.molliq.2022.118575]
34. Zhang, Z.; Li, S.; Mi, B.; Wang, J.; Ding, J. Surface Slip on Rotating Graphene Membrane Enables the Temporal Selectivity That Breaks the Permeability-Selectivity Trade-Off. Sci. Adv.; 2020; 6, eaba9471. [DOI: https://dx.doi.org/10.1126/sciadv.aba9471]
35. Zhao, S.; Jiang, C.; Fan, J.-C.; Hong, S.; Mei, P.; Yao, R.; Liu, Y.; Zhang, S.; Li, H.; Zhang, H. et al. Hydrophilicity Gradient in Covalent Organic Frameworks for Membrane Distillation. Nat. Mater.; 2021; 20, pp. 1551-1558. [DOI: https://dx.doi.org/10.1038/s41563-021-01052-w] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/34294883]
36. Prasad, K.V.; Kannam, S.K.; Hartkamp, R.; Sathian, S.P. Water Desalination Using Graphene Nanopores: Influence of the Water Models Used in Simulations. Phys. Chem. Chem. Phys.; 2018; 20, pp. 16005-16011. [DOI: https://dx.doi.org/10.1039/C8CP00919H]
37. Wang, L.-P.; Martinez, T.J.; Pande, V.S. Building Force Fields: An Automatic, Systematic, and Reproducible Approach. J. Phys. Chem. Lett.; 2014; 5, pp. 1885-1891. [DOI: https://dx.doi.org/10.1021/jz500737m] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/26273869]
38. Price, D.J.; Brooks, C.L. A Modified TIP3P Water Potential for Simulation with Ewald Summation. J. Chem. Phys.; 2004; 121, pp. 10096-10103. [DOI: https://dx.doi.org/10.1063/1.1808117]
39. OneAngstrom; SAMSON: Zorah, Nahal Sorek, 2020.
40. Bitzek, E.; Koskinen, P.; Gähler, F.; Moseler, M.; Gumbsch, P. Structural Relaxation Made Simple. Phys. Rev. Lett.; 2006; 97, 170201. [DOI: https://dx.doi.org/10.1103/PhysRevLett.97.170201]
41. Stuart, S.J.; Tutein, A.B.; Harrison, J.A. A Reactive Potential for Hydrocarbons with Intermolecular Interactions. J. Chem. Phys.; 2000; 112, pp. 6472-6486. [DOI: https://dx.doi.org/10.1063/1.481208]
42. Hockney, R.W.; Eastwood, J.W. Computer Simulation Using Particles; CRC Press: Boca Raton, FL, USA, 1988.
43. Thompson, A.P.; Aktulga, H.M.; Berger, R.; Bolintineanu, D.S.; Brown, W.M.; Crozier, P.S.; in’t Veld, P.J.; Kohlmeyer, A.; Moore, S.G.; Nguyen, T.D. et al. LAMMPS—A Flexible Simulation Tool for Particle-Based Materials Modeling at the Atomic, Meso, and Continuum Scales. Comput. Phys. Commun.; 2022; 271, 108171. [DOI: https://dx.doi.org/10.1016/j.cpc.2021.108171]
44. Humphrey, W.; Dalke, A.; Schulten, K. VMD: Visual Molecular Dynamics. J. Mol. Graph.; 1996; 14, pp. 33-38. [DOI: https://dx.doi.org/10.1016/0263-7855(96)00018-5]
45. Ryckaert, J.-P.; Ciccotti, G.; Berendsen, H.J.C. Numerical Integration of the Cartesian Equations of Motion of a System with Constraints: Molecular Dynamics of n-Alkanes. J. Comput. Phys.; 1977; 23, pp. 327-341. [DOI: https://dx.doi.org/10.1016/0021-9991(77)90098-5]
46. Evans, D.J.; Holian, B.L. The Nose–Hoover Thermostat. J. Chem. Phys.; 1985; 83, pp. 4069-4074. [DOI: https://dx.doi.org/10.1063/1.449071]
47. Chogani, A.; Moosavi, A.; Bagheri Sarvestani, A.; Shariat, M. The Effect of Chemical Functional Groups and Salt Concentration on Performance of Single-Layer Graphene Membrane in Water Desalination Process: A Molecular Dynamics Simulation Study. J. Mol. Liq.; 2020; 301, 112478. [DOI: https://dx.doi.org/10.1016/j.molliq.2020.112478]
48. Hummer, G.; Rasaiah, J.C.; Noworyta, J.P. Water Conduction through the Hydrophobic Channel of a Carbon Nanotube. Nature; 2001; 414, pp. 188-190. [DOI: https://dx.doi.org/10.1038/35102535]
49. Robinson, F.; Shahbabaei, M.; Kim, D. Deformation Effect on Water Transport through Nanotubes. Energies; 2019; 12, 4424. [DOI: https://dx.doi.org/10.3390/en12234424]
50. Robinson, F.; Park, C.; Kim, M.; Kim, D. Defect Induced Deformation Effect on Water Transport through (6, 6) Carbon Nanotube. Chem. Phys. Lett.; 2021; 778, 138632. [DOI: https://dx.doi.org/10.1016/j.cplett.2021.138632]
51. Azamat, J.; Khataee, A.; Joo, S.W.; Yin, B. Removal of Trihalomethanes from Aqueous Solution through Armchair Carbon Nanotubes: A Molecular Dynamics Study. J. Mol. Graph. Model.; 2015; 57, pp. 70-75. [DOI: https://dx.doi.org/10.1016/j.jmgm.2015.01.008]
52. Abbaspour, M.; Akbarzadeh, H.; Abroodi, M. A New and Accurate Expression for the Radial Distribution Function of Confined Lennard-Jones Fluid in Carbon Nanotubes. RSC Adv.; 2015; 5, pp. 95781-95787. [DOI: https://dx.doi.org/10.1039/C5RA16151G]
53. Liu, L.; Patey, G.N. Simulations of Water Transport through Carbon Nanotubes: How Different Water Models Influence the Conduction Rate. J. Chem. Phys.; 2014; 141, 18C518. [DOI: https://dx.doi.org/10.1063/1.4896689]
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
© 2022 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.
Abstract
The water transport through nanoporous multilayered graphene at 300k is investigated using molecular dynamics (MD) simulation with different water models in this study. We used functionalized and non-functionalized membranes along with five different 3-point rigid water models: SPC (simple point charge), SPC/E (extended simple point charge), TIP3P-FB (transferable intermolecular potential with 3 points—Force Balance), TIP3P-EW (transferable intermolecular potential with 3 points with Ewald summation) and OPC3 (3-point optimal point charge) water models. Based on our simulations with two water reservoirs and a porous multilayered graphene membrane in-between them, it is evident that the water transport varies significantly depending on the water model used, which is in good agreement with previous works. This study contributes to the selection of a water model for molecular dynamics simulations of water transport through multilayered porous graphene.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer