separation of fluid mixtures in nanoporous membranes.pdf
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MOLECULAR SIMULATION OF THE STRUCTURE, TRANSPORT, AND
SEPARATION OF FLUID MIXTURES IN NANOPOROUS MEMBRANES
UNDER SUBCRITICAL AND SUPERCRITICAL CONDITIONS
by
Mahnaz Firouzi
A Dissertation Presented to the FACULTY OF THE GRADUATE SCHOOL
UNIVERSITY OF SOUTHERN CALIFORNIA In Partial Fulfillment of the
Requirements for the Degree DOCTOR OF PHILOSOPHY
(CHEMICAL ENGINEERING)
December 2005
Copyright 2005 Mahnaz Firouzi
UMI Number: 3219811
32198112006
Copyright 2005 byFirouzi, Mahnaz
UMI MicroformCopyright
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by ProQuest Information and Learning Company.
Dedication I would like to dedicate this thesis to my husband Dr. Babak Fayyaz-Najafi for his
understanding, support, and love, my parents for their support, boundless faith, and
prayers.
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Acknowledgements
I am grateful to many individuals who have contributed towards shaping this thesis. I
would like to express my deepest appreciation and sincere gratitude to Professor
Muhammad Sahimi and Professor Theodore T. Tsotsis for their advice during my
doctoral research. As my advisors, they constantly assisted me to remain focused on
achieving my goal. Their intelligent observations and comments helped me to
establish the overall direction of the research and to move forward with the
investigations in depth.
I wish to extend my appreciation to Professor Chi H. Mak for being my Ph.D.
committee member, and Professor Katherine S. Shing and Professor C. Ted Lee for
being my Qualifying committee members. They all gave me a lot of useful
suggestions and support. I would like to thank Dr. Lifang Xu for her help during the
initial stage of my research. I sincerely appreciate the help of Ms. Karen Woo and
Mr. Brendan Char of the Department of Chemical Engineering, and thank them for
their assistance and help. I would also like to acknowledge National Science
Foundation, the Department of Energy, the Petroleum Research Fund, and Media &
Process Technology for providing the financial support for this work, and the
University of Southern California and San Diego Supercomputer Center for
providing computational facilities.
Finally, special thanks go to Dr. Babak Fayyaz Najafi, my husband, for his
continuous support, patience, and understanding during my graduate studies.
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Table of Contents
Dedication ii
Acknowledgements iii
List of Tables vi
List of Figures vii
Abstrat xxii 1 Introduction 1
1.1 Nanoporous Membranes ….…………………..…………………….. 1 1.2 Models of Transport Processes in Membranes ………..................…. 6 1.3 The Potential Energy ……………………………………………… 10 1.4 Molecular Dynamics ……...……….….…………………………… 14
1.4.1 Equilibrium Molecular Dynamics …….……...............…… 19 1.4.2 Non-equilibrium Molecular Dynamics ……………………. 20
1.5 Monte Carlo and Grand Canonical Monte Carlo ………………..… 24 1.6 Thesis Outline ……………………...……………………………… 27
2 Transport and Separation of Supercritical Fluid Mixtures in a
Single Carbon Nanopore 29 2.1 Introduction ……………………………………………………...… 29 2.2 The Pore Model ………………………………………………….... 35 2.3 The DCV-GCMD Method ………………………………………… 37 2.4 Potential Models of the Molecules and the Walls ……………....… 40 2.5 Molecular Dynamics Simulations …………………………………. 41 2.6 Results and Discussions …………………………………………… 43 2.7 Summary …………………….………………………………….…. 53
3 Transport and Separation of Carbon Dioxide-Alkane Mixtures in Carbon Nanopores 74 3.1 Introduction ….…………………………………………………….. 74 3.2 Model of Carbon Nanopore ………………….……………………. 75 3.3 Molecular Models of the Gases and the Interaction Potentials ….... 76 3.4 Configurational-Bias Monte Carlo Method ……………………….. 78 3.5 Configurational-Bias Grand-Canonical Monte Carlo Method …..... 81 3.6 Nonequilibrium Molecular Dynamics Simulations ……………..… 82 3.7 Experimental Study ……………………………………………..… 85
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3.8 Results and Discussions ……………………………..………......… 86 3.8.1 Methane-Propane Mixtures ………………………..……… 86 3.8.2 Methane-Butane Mixtures ………………………….....…... 92 3.8.3 Carbon Dioxide-Propane Mixtures ………………….......… 94
3.9 Modeling of Long n-Alkane Chain Mixtures and their Transport and Separation in CMSM …………………………...… 98 3.10 Summary ……………………………………..………..….……….. 99
4 Sub- and Supercritical Fluids in Nanoporous Materials: Direction- Dependent Flow Properties 126 4.1 Introduction ……………………………………………………..... 126 4.2 Asymmetric Pore Models …………….………..……………….... 128 4.3 Adsorption and Transport in Asymmetric Pore ………...……...… 131 4.4 Molecular Dynamics Simulations in Asymmetric Pore………..… 132 4.5 Results and Discussions ……………………………………..…… 136 4.6 Summary …………………………………………….…………… 147
5 Transport and Separation of Carbon Dioxide-Alkane Mixtures in a
Carbon Pore Network under Sub- and Supercritical Conditions 176 5.1 Introduction ………………………………………………………. 176 5.2 Pore Network Modelof CMSMs ………………….…………...…. 178 5.3 NEMD Simulation in CMSM Pore Network ...………................... 184 5.4 Molecular Models of the Fluid and the Interaction Potentials …... 185 5.5 Results and Discussions …………..…….………………………... 187
5.5.1 Methane-Carbon Dioxide Mixtures …………………….... 187 5.5.2 Carbon Dioxide-Propane, Methane-Propane, and Methane-Butane Mixtures …………………………..…… 193
5.6 Asymmetric Pore Network Model ……..………………………… 197 5.7 Summary ……………………………………………...………….. 199
6 Bibliography 235
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List of Tables
2.1 The conversion between the reduced and the actual units. Subscript 1 referes to the value of the parameters for CH4 ………………….….…… 36
3.1 Values of the molecular parameters used in the simulations. kB is the B
Boltzmann’s constant ……………………………………………...….… 77
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List of Figures
1.1 The 12-6 Lennard-Jones potential for particles i and j (Eq.1.3). The potential energy is in units of ε and the distance between i and j is in units of δ . When is positive, the interactions for the pair of particles are repulsive. When is negative, their interactions are
ijU
ijU attractive …............................................................................................… 12
2.1 Schematics of the slit pore used in the simulations. The h and l regions represent the high- and low-pressure control volumes respectively……... 55
2.2 Dimensionless temperature distribution in the pore containing an
equimolar mixture of CO2 and CH4. The upstream pressure in both cases is 120 atm, while the downstream pressures are 90 atm (top) and 20 atm (bottom). The pore size is 1.67 1σ . Dashed lines indicate
the boundaries of the pore region …………………………..…………… 56
2.3 Time-averaged density profiles in the transport direction x in a pore of size 5 1σ , containing an equimolar mixture of the two components at T = 40°C. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (open triangles), 50 atm (open circles), 70 atm (solid triangles), and 100 atm (solid circles). Dashed lines indicate the
boundaries of the pore region ……...………………...………………….. 57
2.4 The distribution of CO2 (circles) and CH4 (triangles) in a pore of size 5 1σ , containing an equimolar mixture at T = 40°C. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top),
70 atm (middle) and 100 atm (bottom) ………………..………………… 58
2.5 Time-averaged density profiles in the transport direction x in a pore of size 5 1σ , containing a mixture of CO2 and CH4 with a CO2 mole fraction of x2 = 0.9 at T = 40°C. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (open triangles), 50 atm (circles), and 70 atm (solid triangles. Dashed lines indicate the
boundaries of the pore region …………………………………………… 59
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2.6 Comparison of the density profiles of CO2 (top) and CH4 (bottom), computed after 3.5 million times steps (dashed curves) and 5 million time steps (solid curves). All other parameters of the system are the same as those in Figure 2.3. The upstream and downstream pressure are, respectively, 120 atm and 90 atm. Dashed lines indicate the
boundaries of the pore region ………………………….………………... 60
2.7 Time-averaged density profiles between the upper and lower walls, in three different regions of a pore of size 5 1σ , containing an equimolar mixture of CO2 (dashed curve) and CH4 (solid curve) at T = 40°C. The upstream and downstream pressures are, respectively, 120 atm and 70 atm. Also shown is the distribution of the molecules in the pore. The
arrows indicate the boundaries of the pore region ……………….……… 61
2.8 Same as in Figure 2.7, except that the upstream and downstream pressures are, respectively, 3 atm and 1 atm ……………………………. 62
2.9 Same as in Figure 2.7, except that the upstream and downstream pressures are, respectively, 120 atm and 1 atm ….…………...…...…….. 63
2.10 Same as in Figure 2.7, except that the mole fraction of CO2 in the mixture is x2 =0.9 ……………………………………..…………………. 64
2.11 The distribution of the molecular clusters after 5 × 105 (top), 106
(middle) and 1.5 × 106 (bottom) time steps, in a pore of size 5 1σ , containing an equimolar mixture of CO2 and CH4 at T = 40 °C. The upstream and downstream pressures are both 120 atm. Numbers
indicate the size of the clusters ……………………...…………………... 65
2.12 Time dependence of the size of the largest clusters in a pore of size 5 1σ (left) and 1.67 1σ (right), containing an equimolar mixture of CO2 and CH4 at T = 40°C. The upstream and downstream pressures are,
respectively, 120 atm and 70 atm ………………………..……………… 66
2.13 Time-dependence of the size distribution of the molecular clusters. All the parameters are the same as those in Figure 2.12. Numbers next to
the curves indicate the size of the clusters ……………..…………..……. 67
2.14 Cluster size distribution ns(t) in a pore of size 5 1σ , containing an equimolar mixture of CO2 and CH4 at T = 40 °C. The results are for
times 5.1 × 106 (◊), 5.2 × 106 ( ), 5.4 × 106 (ο), and 5.5 × 106 (Δ) …….. 68
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2.15 The dependence of the flux and permeance of CO2 and CH4, and the corresponding separation factor, on the pressure drop PΔ applied to a pore of size 1.67 1σ at T = 40°C. The mixture is equimolar, with the
upstream pressure being 120 atm ……………………………..………… 69
2.16 Same as in Figure 2.15, but for a pore of size 5 1σ ……………….….….. 70
2.17 Same as in Figure 2.15, but for a pore of size 5 1σ and CO2 mole fraction of 2x = 0.9 …………………………...………………..………… 71
2.18 Dependence of the permeance of CO2 (solid curves) and CH4 (dashed
curves), and the corresponding separation factors, on the mole fraction of CO2 in the feed, in a pore of size 1.67 1σ at T = 40°C (circles) and 100°C (triangles). The upstream and downstream pressures are,
respectively, 120 atm and 20 atm …...………………………...……….... 72
2.19 Temperature-dependence of the permeance of CO2 (solid symbols) and CH4 (open symbols), and the corresponding separation factors, for a pore of size 1.67 1σ and downstream pressures of 90 atm (squares) and 110 atm (triangles). The upstream pressure is 120 atm, and the mixture
is equimolar ……………………………………………...…………….... 73
3.1 Dimensionless temperature distribution in a pore of size H* = 5 and the two control volumes, containing mixtures of CH4 and C3H8 with methane mole fraction in the feed being 0.7 (top) and 0.5 (bottom).
Dashed lines indicate the boundaries of the pore region …………….… 101
3.2 Snapshot of the pore containing CH4 (triangles) and C3H8 (chains), at steady state. The mole fraction of CH4 in the feed is 0.9, and the pore
size is H*= 5 ……………………………………………….…………... 102
3.3 Time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transverse direction (perpendicular to the walls), measured near the pore’s center at T = 50°C. The pore size is H* = 5, while the mole fraction of CH4 in the feed is 0.5 (top) and 0.9
(bottom) …………………………………………………………. 103
3.4 Comparison of the time-averaged density profiles of CH4 (solid curves) and C3 H8 (dashed curves) in the transverse direction (perpendicular to the walls), measured near the pore’s center at T =
50°C, in three pores. The mole fraction of CH4 is 0.7 ………………..... 104
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3.5 Time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transport direction x in a pore of size H* = 5, in which the methane mole fraction in the feed is 0.7 (top) and 0.5 (bottom), and T = 50°C. Dashed lines indicate the boundaries of the
pore region ……………………………………………..……………… 105
3.6 Time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transport direction x in a pore of size H* = 5 in which the CH4 mole fraction is 0.9. The upstream and downstream pressures are, respectively, 3 atm and 1 atm (top), and 30 atm and 10 atm (bottom). Dashed lines indicate the boundaries of the pore
region …….………………………………………………....………….. 106
3.7 Time-averaged density profiles of CH4 (solid curve) and C3H8 (dashed curve) in the transport direction x in a pore of size H* = 3. The CH4
mole fraction in the feed is 0.7, and T=50°C ……………….......……… 107
3.8 Comparison of the simulation results for the permeance of CH4 (open triangles) and C3H8 (open circles) with the corresponding experimental data (solid symbols). The mole fraction of CH4 in the feed in the upper Figure is 0.7, while T = 50°C in the lower Figure. The pore size is
H* = 5 ..……………………………………………………...…………. 108
3.9 Comparison of the computed separation factors (open circles) with the experimental data (solid circles) for a CH4/C3H8 mixture. The mole fraction of CH4 in the feed in the upper Figure is 0.7,while T = 50°C in
the lower Figure ………………………………………………………... 109
3.10 The effect of pore size on the permeances of CH4 and C3H8 and the corresponding separation factors in a binary mixture in which the CH4
mole fraction in the feed is 0.7, and T = 50°C ……………….......…….. 110
3.11 A snapshot of the pore containing CH4 (triangles) and C4H10, at steady state in a pore of size H* = 5 at T = 50°C. The CH4 mole fraction in
the feed is 0.9 …………………………………………….………….…. 111
3.12 Time-averaged density profile of CH4 (solid curve) and C4H10 (dashed curve), between the upper and lower walls of a pore of size H* = 5 at T = 50°C. The profiles were calculated in the middle of the pore, and
CH4 mole fraction in the feed is 0.9 ………………...…………………. 112
3.13 Same as in Figure 3.12, but in the transport direction x. Dashed vertical lines indicate the boundaries of the pore region ………….…… 113
x
3.14 The computed permeances of CH4 (triangles) and C4H10 (circles). The mole fraction of CH4 in the feed in the upper Figure is 0.9, while T =
50°C in the lower Figure …..……………………………..….………… 114
3.15 The effect of pore size on the permeances of CH4 (triangles) and C4H10 (circles), and the corresponding separation factors at T = 50°C. The
CH4 mole fraction in the feed is 0.7 …………………………..……..… 115
3.16 Time-averaged temperature distribution in a pore of size H* = 5 and the two CVs that contain a binary mixture of CO2 and C3H8. The mole fraction of CO2 is 0.7 (top) and 0.5 (bottom). Dashed vertical lines
indicate the boundaries of the pore ………………………………….…. 116
3.17 Distribution of CO2 (triangles) and C3H8 chains in a pore of size H* = 5 at T = 50°C, obtained at steady state. The CO2 mole fraction in the
feed is 0.9 …………………………………….………………………… 117
3.18 Density profiles of CO2 (solid curves) and C3H8 (dashed curves) between the upper and lower walls of a pore of size H* = 5, computed at the pore’s center and obtained at steady state. The CO2 mole fraction in the feed is 0.5 (top) and 0.9 (bottom), and T =
50°C ……………………………………………….………………..….. 118
3.19 Same as in Figure 3.18, but in the transport direction x. The CO2 mole fraction in the feed is 0.7 (top) and 0.5 (bottom), and T = 50°C.
Dashed vertical lines indicate the boundaries of the pore ……………... 119
3.20 Comparison of the computed permeances of CO2 (open triangles) and C3H8 (open circles), for a pore of size H* = 5, with the corresponding experimental data (solid symbols). The CO2 mole fraction in the feed
in the upper Figure is 0.7, while T = 50°C in the lower Figure ……...… 120
3.21 Comparison of the computed separation factors of CO2/C3H8 binary mixtures (open circles), for a pore of size H* = 5, with the experimental data (solid circles). The CO2 mole fraction in the feed in
the upper Figure is 0.7, while T = 50°C in the lower Figure ...............… 121
3.22 The effect of the pore size on the permeances of CO2 (triangles) and C3H8 (circles), and the corresponding separation factors at T = 50°C.
The CO2 mole fraction in the feed is 0.7 ………………………………. 122
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3.23 Time-averaged density profiles of CO2 (solid curves) and C6H14 (dashed curves) between the upper and lower walls, in three different regions of a pore of size H* = 2. The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The CO2 mole fraction in the feed is 0.9 and T = 50°C. Also shown is the distribution of the CO2 (triangles) and C6H14 (chains) in the pore. The arrows indicate the
boundaries of the pore region ………………………………………….. 123
3.24 Snapshot of the pore containing CO2 (triangles) and C6H14 (chains) with the same parameters as figure 3.23 ……………………….………. 124
3.25 Time-averaged density profile (top) of CO2 (solid curves) and C6H14
(dashed curves) and temperature profile (bottom), in the transport direction x in a pore of size 5* =H in which the CO2 fraction is 0.9 and T=200°C. The upstream and downstream pressures are, respectively, 20 atm and 5 atm. Dashed lines indicate the boundaries
of the pore region ……………………………………………………..... 125
4.1 Asymmetric pore model with CVs inside the pore ……...…..…..…..…. 130
4.2 Asymmetric pore model with CVs outside the pore ………..…..…….... 130
4.3 Snap-shots and density profiles of CO2 in supercritical – subcritical conditions. The upstream and downstream pressures are, respectively, 82.63 (1200 psig) and 5 atm (59 psig), and temperature is 35 °C, (a) the upstream pressure is on the macro side, obtained after 1,500,000 time steps, (b) the upstream pressure is on the nano side, obtained after 4,000,000 time steps. Vertical lines indicate the boundaries of the
pore ……..............................................................................................… 149
4.4 Snapshots of the pore containing pure CO2 in 3D. The upstream and downstream pressures are, respectively, 82.63 atm (1200 psig) and 5 atm (59 psig), and temperature is 35 °C. The upstream pressure is on
the macro side (top) and nano side (bottom) ………………………...… 150
4.5 Density profiles of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.63 atm (1200 psig) and 5 atm (59 psig), and temperature is 35 °C. The upstream pressure is on
the macro side ………………………………………...………………... 151
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4.6 Density profiles of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.63 atm (1200 psig) and 5 atm (59 psig), and temperature is 35 °C. The upstream pressure is on
the nano side ……………………………………….………………...… 152
4.7 Density and temperature profiles of pure CO2 along the pores for subcritical - subcritical conditions. The upstream and downstream pressures are, respectively, 21.4 atm (300 psig) and 11.2 atm (150 psig), and temperature is 35 °C, (a) the upstream pressure is on the macro side, (b) the upstream pressure is on the nano side. Dashed
vertical lines indicate the boundaries of the pore ……………………… 153
4.8 Density profiles and number of the molecules of pure CO2 along the pores for subcritical - subcritical conditions. The upstream and downstream pressures are, respectively, 41.8 atm (600 psig) and 4.4 atm (50 psig), and temperature is 35 °C, (a) the upstream pressure is on the macro side, (b) the upstream pressure is on the nano side.
Dashed vertical lines indicate the boundaries of the pore ...…...………. 154
4.9 Snapshot of the pore containing equimolar mixture of CH4 (triangles) and CO2 (circles) under supercritical - subcritical conditions obtained after 4,000,000 time steps. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top)
and macro side (bottom) .……………………..................…...…….……155
4.10 Time-averaged density profiles of both CH4 (solid curves) and CO2 (dashed curves) in the transport direction x in the pore with the same parameters as Figure 4.9. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the
boundaries of the pore ……………………………….……...…………..156
4.11 Time-averaged temperature distribution along the pore with the same parameters as Figures 4.9 and 4.10. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate
the boundaries of the pore ……………….………………………………157
4.12 Snapshot of the pore containing CO2 under subcritical - subcritical conditions. The upstream and downstream pressures are, respectively, 62.2 atm (900 psig) and 28.2 atm (400 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) obtained after 3,125,000 time steps, and macro side (bottom) obtained after
3,410,000 time steps ………………………………………………….... 158
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4.13 Time-averaged density profiles of pure CO2 in the transport direction x in the pore with the same parameters as Figure 4.12. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed
vertical lines indicate the boundaries of the pore ………...........………. 159
4.14 Time-averaged temperature distribution of pure CO2 along the pore with the same parameters as Figures 4.12 and 4.13. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed
vertical lines indicate the boundaries of the pore ……………...…..…... 160
4.15 Snapshot of the pore containing CO2 under supercritical - subcritical conditions. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 48.6 atm (700 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) and macro side
(bottom) ……………………………………………………………...… 161
4.16 Time-averaged density profiles of pure CO2 in the transport direction x in the pore with the same parameters as Figure 4.15. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed
vertical lines indicate the boundaries of the pore …………...…………. 162
4.17 Time-averaged temperature distribution of pure CO2 along the pore with the same parameters as Figures 4.15 and 4.16. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed
vertical lines indicate the boundaries of the pore ………...……………. 163
4.18 The dependence of the permeability and molar flow of pure CO2 on the upstream pressure at T=35°C, when PΔ =500 psi is applied in the two opposite directions. Continuous and dashed curves show, respectively, the results when the upstream pressure is applied on the
macropore and nanopore ……………..………………………………… 164
4.19 Snapshot of the pore containing CO2 under supercritical - subcritical conditions. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 11.2 atm (150 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) obtained after 770,000 time steps, macro side (bottom) obtained after 810,000 time
steps ………............................................................................................. 165
4.20 Time-averaged density profiles of pure CO2 in the transport direction x in the pore with the parameters as Figure 4.19. The upstream pressure is on the nano side (top), macro side (bottom). Dashed
vertical lines indicate the boundaries of the pore ……….………...….... 166
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4.21 Snapshot of the pore containing equimolar mixture of CH4 (triangles) and CO2 (circles) under supercritical - subcritical conditions. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream
pressure is on the nano side (top) and macro side (bottom) ………....... 167
4.22 Time-averaged density profiles of both CH4 (solid curves) and CO2 (dashed curves) in the transport direction x in the pore with the same parameters as Figure 4.21. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the
boundaries of the pore ………………………………………………..... 168
4.23 Time-averaged temperature distribution along the pore with the same parameters as Figures 4.21 and 4.22. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate
the boundaries of the pore ……..………………………...….………….. 169
4.24 Density profiles of an equimolar mixture of CH4 (solid curves) and CO2 (dashed curves) in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on
the macro side ……...……………….……………….………...…......… 170
4.25 Density profiles of an equimolar mixture of CH4 (solid curves) and CO2 (dashed curves) in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on
the nano side ………………………………………................………… 171
4.26 Density profiles of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 96.2 atm (1400 psig) and 48.6 atm (700 psig), and temperature is 35 °C. The upstream pressure
is on the macro side ……………………………..………………...…… 172
4.27 Density profile of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 96.2 atm (1400 psig) and 48.6 atm (700 psig), and temperature is 35 °C. The upstream pressure is on
the nano side …………………………………………………………… 173
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4.28 The dependence of the permeabilities and molar flows of CO2 (circles) and CH4 (triangles) on the upstream pressure in an equimolar mixture at T=35°C, when PΔ =700 psi is applied in the two opposite directions. Continuous and dashed curves show, respectively, the results when the upstream pressure is applied on the macropore and
nanopore …………....................................................................…..….... 174
4.29 The dependence of the permeabilities and molar flows of CO2 (circles) and CH4 (triangles) on the pressure drop in an equimolar mixture at T=35°C, when the upstream pressure is 1400 psig. Continuous and dashed curves show, respectively, the results when the upstream
pressure is applied on the macropore and nanopore …...………..………175
5.1 Two-dimensional representation of a porous membrane ………………. 176
5.2 A two-dimensional Voronoi network ……………………….…………. 181
5.3 Computed pore size distribution (PSD) for the model CMSMs. On the top is the PSD for a system in which the pores are selected randomly. On the bottom is the PSD for a system in which the pores are
generated according to their sizes, starting from the largest size …....… 182
5.4 Computed PSD for the model CMSMs for different porosities. The pores are generated according to their sizes, starting from the largest
size ........................................................................................................... 183
5.5 PSD of the membrane used in the experiments ………………………... 183
5.6 Time-averaged density profiles of both components of an equimolar mixture of CO2 (dashed curves) and CH4 (solid curves) at T=40°C in the transport direction x . The upstream pressure is 120 atm, while the downstream pressures are 20 atm, 50 atm, and 90 atm. Dashed lines
indicate the boundaries of the pore network region …………….... 201
5.7 Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.6. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore
network region ………………………...…………………………….…. 202
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5.8 The dependence of the flux and permeability of CO2 (dashed curves) and CH4 (solid curves), and the corresponding separation factor, on the pressure drop ΔP applied to the pore network at T=40°C. The mixture
is equimolar, with the upstream pressure being 120 atm …………....…. 203
5.9 Time-averaged density profiles of both components of a mixture of CO2 (dashed curves) and CH4 (solid curves) with a mole fraction of 90% CO2 and 10% CH4 at T=40°C in the transport direction x . The upstream pressure is 120 atm, while the downstream pressures are 20 atm, 50 atm, and 90 atm. Dashed lines indicate the boundaries of the
pore network region ................................................................................. 204
5.10 Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.9. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore
network region …………………………………….……..………….…. 205
5.11 The dependence of the flux and permeability of CO2 (dashed curves) and CH4 (solid curves), and the corresponding separation factor, on the pressure drop ΔP applied to the pore network at T=40°C, in a mixture in which the mole fraction of CO2 is 0.9 and the upstream pressure is
fixed at 120 atm ....................................................................................... 206
5.12 Snapshot of the pore network containing an equimolar mixture of CH4 (circles) and CO2 (asterisks) at T=40°C, obtained after 2,220,000 time steps. The upstream and downstream pressures are, respectively, 120
atm and 90 atm ………………………………….……………..…..….... 207
5.13 Snapshot of the pore network containing CH4 (circles) and CO2 (asterisks) at T=40°C, obtained after 1,740,000 time steps. The CO2 mole fraction in the feed is 0.9. The upstream and downstream
pressures are, respectively, 120 atm and 90 atm ………...........……….. 208
5.14 Time-averaged density profiles of both components of an equimolar mixture of CO2 (dashed curves) and CH4 (solid curves) at T=40°C in the transport direction x . The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore network region ………………...……………...…….………..…………….......... 209
xvii
5.15 Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.14. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore network region ………………….………………………..…...….…...... 210
5.16 Snapshot of the pore network containing an equimolar mixture of CH4
(circles) and CO2 (asterisks) at T=40°C obtained after 2,650,000 time steps. The upstream and downstream pressures are, respectively, 120 atm and 20 atm ………………………….………..……………....…….. 211
5.17 The dependence of the flux and permeability of CO2 (dashed curves)
and CH4 (solid curves) in an equimolar mixture on the pressure drop ΔP applied to the pore network at T=40°C. The upstream pressure is fixed at 120 atm ……………………………………….……………...... 212
5.18 Snapshot of the pore network containing CH4 (circles) and CO2
(asterisks) at T=40°C obtained after 2,315,000 time steps. The CO2 mole fraction in the feed is 0.7. The upstream and downstream pressures are, respectively, 120 atm and 20 atm ……………………..... 213
5.19 Time-averaged density profiles of both components of CO2 (dashed
curves) and CH4 (solid curves) at T=40°C in the transport direction x . The upstream and downstream pressures are, respectively, 120 atm and 20 atm. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.9 (bottom). Dashed lines indicate the boundaries of the pore network region ………………………………………...……………….. 214
5.20 Time-averaged temperature profiles of mixture of CO2 and CH4 with
the same parameters as Figure 5.19. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.9 (bottom). Dashed lines indicate the boundaries of the pore network region …….......………………..……... 215
5.21 The dependence of the flux and permeability of CO2 (dashed curves)
and CH4 (solid curves), and the corresponding separation factor, on the mole fraction of CO2 in the feed at T=40°C. The upstream and downstream pressures are, respectively, 120 atm and 20 atm …………. 216
5.22 Time-averaged density profiles of both components of CO2 (dashed
curves) and CH4 (solid curves) in the transport direction x at different temperatures. The upstream and downstream pressures are, respectively, 120 atm and 90 atm, and the mixture is equimolar. Dashed lines indicate the boundaries of the pore network region ……... 217
xviii
5.23 Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.22. Temperature is fixed at 20°C (top), 100°C (middle), and 140°C (bottom). Dashed lines indicate the boundaries of the pore network region …………...……..……………... 218
5.24 Time-averaged density profiles of both components of CO2 (solid
curves) and C3H8 (dashed curves) in the transport direction x at different temperatures. The upstream and downstream pressures are, respectively, 3 atm and 1 atm and the mole fraction of CO2 in the feed is 0.7. Dashed lines indicate the boundaries of the pore network region …………………………………………………………………... 219
5.25 Time-averaged temperature profiles of mixture of CO2 and C3H8 with
the same parameters as Figure 5.24. Temperature is fixed at 25°C (top), 50°C (middle), and 75°C (bottom). Dashed lines indicate the boundaries of the pore network region …...………………..…….…….. 220
5.26 The dependence of the flux and permeability of CO2 (solid curves) and
C3H8 (dashed curves), and the corresponding separation factor, on the temperature. The upstream and downstream pressures are, respectively, 3 atm and 1 atm, and the mole fraction of CO2 in the feed is 0.7 ………………………………………………………………..…... 221
5.27 Time-averaged density profiles of both components of CO2 (solid
curves) and C3H8 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.85 (bottom). Dashed lines indicate the boundaries of the pore network region ……………………………………………..…. 222
5.28 Time-averaged temperature profiles of mixture of CO2 and C3H8 with
the same parameters as Figure 5.27. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.85 (bottom). Dashed lines indicate the boundaries of the pore network region …...………...…..……………… 223
5.29 The dependence of the flux and permeability of CO2 (solid curves) and
C3H8 (dashed curves), and the corresponding separation factor, on the mole fraction of CO2 in the feed at T=50°C. The upstream and downstream pressures are, respectively, 3 atm and 1 atm ……….…..… 224
xix
5.30 Distribution of CO2 (triangles) and C3H8 chains in a pore network at T=50°C, obtained after 4,000,000 time steps. The CO2 mole fraction in the feed is 0.85. The upstream and downstream pressures are, respectively, 3 atm and 1 atm …………...………………...……...……. 225
5.31 Time-averaged temperature and density profiles of both components of
CH4 (solid curves) and C3H8 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The mole fraction of CH4 in feed is 0.7. Dashed lines indicate the boundaries of the pore network region ……………………………………….………………...……...… 226
5.32 Time-averaged density profiles of both components in an equimolar
mixture of CO2 (solid curves) and C3H8 (dashed curves) (top), and in an equimolar mixture of CH4 (solid curves) and C3H8 (dashed curves) (bottom), at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 30 atm and 10 atm. Dashed lines indicate the boundaries of the pore network region …………...… 227
5.33 Time-averaged temperature and density profiles of both components of
CO2 (solid curves) and C3H8 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 120 atm and 20 atm. The mole fraction of CO2 in feed is 0.9. Dashed lines indicate the boundaries of the pore network region ………………………………………………………..….……… 228
5.34 The dependence of the flux and permeability of CO2 (solid curves) and
C3H8 (dashed curves), and the corresponding separation factor, on the pressure drop ΔP applied to the pore network at T=50°C, in a mixture in which the mole fraction of CO2 is 0.9 and the upstream pressure is fixed at 120 atm ....................................................................................... 229
5.35 Time-averaged temperature and density profiles of both components of
CH4 (solid curves) and C4H10 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The mole fraction of CH4 in feed is 0.7. Dashed lines indicate the boundaries of the pore network region ………………………………………………………...………… 230
5.36 A three-dimensional asymmetrical Voronoi network. Poisson points
are shown in top figure and the pore polyhedra are shown in bottom figure ........................................................................................................ 231
xx
5.37 Time-averaged density profiles of CH4 (solid curves) and CO2 (dashed curves) in an equimolar mixture at T=40°C in the transport direction x . The upstream pressure is fixed at 120 atm, in left CV (top) and right CV (bottom), and the downstream pressure is 20 atm. Dashed lines indicate the boundaries of the pore network region ….………………… 232
5.38 Dimensionless temperature distribution in a pore network and the two
control volumes, containing CH4 and CO2 in an equimolar mixture at T=40°C. The upstream pressure is fixed at 120 atm, in left CV (top) and right CV (bottom), and the downstream pressure is 20 atm. Dashed lines indicate the boundaries of the pore network region ……………………………………………………..……...….…. 233
5.39 Snapshot of the pore network containing an equimolar mixture of CH4
(circles) and CO2 (asterisks) at T=40°C. The upstream pressure is fixed at 120 atm, in left CV (top) and right CV (bottom), and the downstream pressure is 20 atm ………………………..…....………….. 234
xxi
Abstract
The goal of this dissertation is to study the transport and separation properties of
fluid mixtures confined in enclosing media, i.e., by pores. In particular, molecular
dynamics simulations are carried out to study the adsorption, transport, permeation
and separation properties of fluid mixtures in nanoporous carbon molecular-sieve
membranes at the atomic scales. Molecular modeling represents a valuable tool for
the study of nanoporous membranes, and of the transport processes that take place in
their pore space. My research is intended to provide a better understanding of the
effect of confinement on the behavior of the fluids. The result of these studies will
allow the chemical and petrochemical industries to improve the design of membrane
separation technology.
Non-equilibrium molecular dynamics simulations are implemented in order
to study the behavior of the system on which an external chemical potential or
pressure gradient has been imposed. Extensive simulations are carried out to study
the effect of the pore structure and the imposed external potential on the quantities of
interest, such as the fluids' distributions in the system, transport properties and the
separation factor for broad ranges of conditions. We examine the behavior of the
fluid mixtures under both subcritical and supercritical conditions.
It is shown that under supercritical conditions, which represent a high
pressure and relatively low temperature, the fluids form dynamic molecular clusters
that travel the pore space. Their sizes vary with the time in a seemingly oscillatory
xxii
manner. We study the dynamic behavior, and the size distribution of the clusters as it
evolves with the process time. The confined structure of the pores gives rise to
adsorption and transport phenomena, as well as dynamic evolution of the fluid
clusters, that are completely absent in the same pores under subcritical conditions.
The fluid mixtures we study are the binary mixtures of carbon dioxide and n-
alkanes, as well as mixtures of n-alkanes chains. The united atom model, in which
CH2 and CH3 groups are considered as one interaction site, are used to model n-
alkane chains. Bending and torsion potentials are included, and the bond lengths are
kept constant using the RATTLE algorithm. Configurational-bias Monte Carlo
technique is used for the efficient generation of molecular model of the n-alkanes.
Two models have been used to represent the nanoporous membrane, which
are a slit pore composed of parallel planar carbon walls, and the model represented
by a three-dimensional pore space, generated, atomistically by the Voronoi
tessellation of the space, using tens of thousands of atoms. The Voronoi model
contains interconnected pores of various sizes and shapes, which is a realistic model
for the membrane and allows us to investigate the effect of morphology of the pore
space, i.e., its pore size distribution and pore connectivity, on the transport and
separation properties of fluid mixtures in a nanoporous membrane.
In addition, the possibility of asymmetry in the permeation properties of fluid
mixtures in carbon molecular-sieve membranes is investigated under sub- and
supercritical conditions. To do so, we carry out extensive nonequilibrium molecular
dynamics simulations of flow and transport of a pure fluid, as well as a binary
xxiii
mixture, through a porous material composed of a macro-, a meso-, and a nanopore,
in the presence of an external pressure gradient. We find that under supercritical
conditions, unusual phenomena occur that give rise to direction- and pressure-
dependent permeabilities for the mixture's components. Hence, the classical models
of fluid flow and transport through porous materials that are based on single-valued
permeabilities that are independent of the direction of the applied pressure gradient
are completely in error. The simulations are in qualitative agreement with the
experimental data gathered in our laboratory and provide a rational explanation for
them in terms of a non-linear flow regime, coupled with adsorption.
xxiv
Chapter 1 Introduction 1.1 Nanoporous Membranes
low, transport and behavior of fluids and their mixtures in confined media are
currently of fundamental and practical interest (Sahimi, 1993, 1995, 2003;
Torquato, 2002). Examples of such confined media include nano- and mesoporous
materials, such as catalysts, adsorbents, skin and biological tissue, and nanoporous
thin films (e.g., silica aerogels) that are utilized as low-dielectric constant
composites, optical coatings, sensors and insulating films.
F
An important class of such materials consists of nanoporous membranes,
such as biological or synthetic membranes (e.g., carbon molecular-sieve and silicon
carbide membranes). The former play a fundamental role in biological activities of
living organisms, while the latter, are under active investigations, both
experimentally and by computer simulations, for separation of fluid mixtures into
their constituent components, and for sensors that can detect trace amounts of certain
chemical compounds. These materials, depending on their pore space morphology,
contain a range of pore sizes, from nano- to meso- to macropores. However, the main
resistance to any transport process in the pore space of these materials is offered
1
mainly by the interconnected nano- and mesopores. Thus, studies of flow and
transport processes in such materials have focused on this range of pore sizes.
Here, we briefly explain what constitute meso- and nanopores, since pore
dimensions play an important role in the overall transport and thermodynamic
properties of an adsorbed fluid and, therefore, their distinction is important.
A mesopore is any pore whose diameter is on the order of 10-6 meters, which
is large compared to the size of an adsorbed fluid layer (whose size is on the order of
angstroms). In a mesopore, the fluid molecules are uniformly distributed in the pore
volume, as in the bulk fluids, and individual fluid molecules can then be ignored, i.e.
the fluid can be treated as a continuum and the fluid properties, such as density or
velocity, can be obtained by dividing the fluid into volume elements that are large at
the molecular level, but small at the macroscopic level. A nanopore is one whose
diameter is on the order of 10-9 meters, which is comparable to the size of the
molecules it adsorbs. In this type of pores, except for a small percentage of fluid
molecules at the pore center, the fluid density varies greatly over molecular distances
and the fluid molecules experience strong interactions with the pore walls over most
of the pore volume. Hence, there is no meaningful way to ignore individual
molecules and divide the fluid into molecularly large volume elements. Therefore,
the continuum approximation fails. Consequently, the molecular-level details of a
fluid confined at the nanoscale must be taken into account, making theoretical
predictions more difficult (Hansen and McDonald, 1991). Nanopores, have
diameters which are less than ten fluid diameters. Therefore, in such pores all the
2
adsorbed molecules are within five fluid diameters of the pore walls and even some
adsorbed molecules simultaneously experience strong interactions with more than
one pore wall. In this case, confinement restrictions on adsorbed fluid molecules are
extreme, and small changes in the pore geometry or in the wall interaction strength
can profoundly affect fluid properties. Therefore, the theoretical predictions of fluid
properties in a nanopore are more difficult than in a larger sized micropore.
Some of the phenomena that occur in the pore space of nanoporous material
include adsorption of gases, flow and transport of fluids, separation of a mixture of
fluids, and several other phenomena. Among these phenomena, flow, adsorption and
transport of fluids in the pore space of a nanoporous material are of particular
importance. The significance of studying flow and transport of fluids in nanoporous
materials is due to three reasons. (1) In a confined fluid, the energy dissipated by
friction can induce chemical transformations and phase transitions that are very
different from those under bulk conditions, as well as cause drastic changes in the
fluid's static and dynamical properties – phenomena that are all of fundamental
importance. (2) From a practical viewpoint, it is clearly important to understand how
flow or transport processes occur in the pore space of nanoporous materials
(Pinnavaia and Thorpe, 1995; Sahimi, 1993, 1995, 2003; Torquato, 2002; Unger et
al., 1988) so that their morphology can be optimized for such applications as
separation, purification, and storage of gases in the pore space. (3) Even when
transport through the solid matrix of nanoporous materials is of prime importance, as
is the case, for example, during electrical conduction in low-dielectric constant
3
nanoporous materials and similar composites, understanding transport and adsorption
in the materials is still critical to characterization (Pinnavaia and Thorpe, 1995;
Sahimi, 1993, 1995, 2003; Torquato, 2002; Unger et al., 1988) of their pore space,
the morphology of which greatly influences the transport and optical properties of
the solid matrix and the materials as a whole.
Much research has been carried out, both experimentally and theoretically, to
determine the principal features which govern the adsorption and transport properties
of fluids in nanoporous membranes. Current models for macroporous membranes
are sufficiently reliable for design purposes. However, in many cases, the size of the
membrane pores is commensurate with the size of the fluid molecules and significant
hindrance effects are observed. Frequently, molecular size permselectivity is highly
desirable as, for example, in heterogenous catalysis using zeolites or passive
transport in biological membranes. With their complicated geometric structure,
many factors are involved in actual nanoporous membranes, including pore size
distribution, degree of interconnectivity, and pore cross-sectional shape. In addition
to structural effects, other factors which must be taken into consideration are the
concentration, temperature, and pressure-dependence of the properties of the fluid.
The presence of adsorption force fields also significantly influences equilibrium and
transport, particularly when the fluid is a gas or vapor and to a lesser extent when the
fluid is a liquid.
Therefore, due to the exceedingly small sizes of the pores of nanoporous
materials, the behavior of fluids and their mixtures in their pore space is typically
4
different from that observed in the bulk. It has been shown experimentally (Horn
R.G., 1981), computationally (Lane and Spurling, 1979; Liu et al., 1974; Magda et
al., 1985; Snook and Van Megen, 1980; Subramanian and Davis, 1979) and
theoretically (Bratko et al., 1989; Curtin and Ashcroft, 1985; Fischer and Methfessel,
1980; Johnson and Nordholm, 1981; Tarazona, 1985) that fluid molecules near solid
surfaces exhibit collective ordering due to fluid-substrate interactions. For example,
near a flat surface, fluid molecules line up so that they are adsorbed as layers parallel
to the surface. Far from the surface, these layers are less pronounced and diminish at
a distance of five fluid molecular diameters (Israelachvili, 1985).
Owing to the complexity of these interacting effects, the principles which
govern transport properties of fluids in membrane containing pores of molecular
dimensions have not yet been firmly established. For example, since the average
pore size of many membranes and nanoporous material is typically of the order of a
few angstroms, the traditional continuum approach cannot be used for modeling such
phenomena. This is due to the fact that the pores’ small sizes imply that the
molecular interactions between the diffusing and/or flowing fluids themselves, and
between them and the pores’ walls, are important and cannot be ignored. Hence, one
must resort to molecular modeling of such phenomena and a more detailed
understanding at a molecular level has become increasingly necessary and important
in guiding experimental work and improving engineering design. The goal in any
molecular dynamics simulation of nanoporous material is to describe the material
and the phenomena that occur in it, the practical consequences of which are at
5
macroscopic length scales, by the molecular dynamics method which considers a
system at atomic scales and provide insights into the phenomena.
1.2 Models of Transport Processes in Nanoporous Membranes Membranes have gained an important place in the chemical industry and are used in
a broad range of applications. There is a great interest in developing membranes for
separation of gas and liquid mixtures by selective adsorption and permeation.
Among them, inorganic membranes, such as alumina, silica, and carbon membranes
are of special interest compared with organic membranes, due to their favorable
characteristics in terms of thermal, mechanical and structural stability, and chemical
resistance. Carbon molecular-sieve membranes (CMSMs) have been used as model
systems by many groups (Acharya et al., 1997; Afrane and Chimowitz, 1993, 1996;
Chen and Yang, 1994; Jones and Koros, 1994a, 1994b, 1995a, 1995b; Koresh and
Sofer, 1983; Linkov, Sanderson and Jacobs, 1994; Linkov, Sanderson and Rychkov,
1994; Naheiri et al., 1997; Petersen et al., 1997; Rao and Sircar, 1993a, 1993b, 1996;
Shiflett and Foley, 1999; Shusen et al., 1996; Sircar et al., 1996; Steriotis et al.,
1997), as well as our own group (Sedigh et al., 1998, 1999, 2000), in studies
involving separation of subcritical fluid mixtures. Beyond their potential practical
significance, these membranes allow one to carry out steady-state transport
investigations, thus significantly simplifying the burden of data analysis and
interpretation. In addition, these membranes can be prepared with well-controlled
6
porosity and a narrow pore size distribution. Nanoporous membranes are used to
perform separations on a molecular level. Models that have been developed for
nanoporous membranes can be divided into two groups.
(i) In one group, the membrane is represented by a single nanosize pore. The
motivation for doing so is the fact that in some membranes the pores are more or less
parallel to each other and, therefore, studying the phenomena of interest in a single
pore may suffice for understanding them in a nanoporous membrane. Many pore
shapes have been used, ranging from cylindrical and slit pores to much more
complex shapes (Düren et al., 2003).
(ii) In the second class are those that model the nanoporous membrane by a
2D or 3D network of interconnected pores. Many different types of such molecular
pore networks have been developed. In one group, the pore network is generated
based on geometrical and topological considerations, without any regards for the
physico-chemical process that generates the nanoporous membrane and, therefore,
the chemical and energetic details of creating the nanopores are ignored. As an
example, consider pillared clays (PCs), nanoporous materials that were originally
developed as a new class of catalytic materials, although it is currently believed that
their greatest potential use may be as membrane materials for separation processes,
especially separating CO2 from a mixture of gases. Hence, in recent years a number
of investigators have studied gas adsorption in PCs. As a second example, consider
CMSMs. These membranes are prepared by pyrolysis of a polymeric precursor. If
the pyrolysis of the polymeric precursor is done at high enough temperatures, the
7
resulting solid matrix of the porous material will have a structure similar to graphite.
Thus, one begins the molecular simulations of these materials with a 3D cell of
carbon atoms with a structure corresponding to graphite. We will explain this method
in details in Chapter 5.
Here, we briefly describe some of the molecular simulation and modeling
methods for adsorption, transport and separations of fluids which have been used in
nanoporous membranes.
The thermodynamic properties of simple fluids in graphitic slit-shaped pores
have been studied extensively at the molecular level via the statistical mechanical
Density Functional Theory (DFT), Monte Carlo (MC), and molecular dynamics
(MD) computer simulations (Jiang et al., 1993; Rhykerd et al., 1991). These studies
have revealed many differences between the structural and dynamical properties of
confined fluids and the corresponding bulk fluids of the same composition. In a slit-
shaped pore, for instance, simple Lennard-Jones fluids tend to organize in layers near
the impenetrable pore walls, resulting in oscillations in the average density within the
pore, in the solvation force acting between the opposing surfaces, and in the
effective, or pore-averaged, diffusion coefficient describing mass transport parallel to
the pore walls (Magda et al., 1985; Schoen et al., 1988; Somers and Davis, 1992).
More recent studies of fluid mixtures in graphitic slit-like pores have begun to
examine complex phenomena, such as the selective adsorption of one of the
molecular components (Cracknell et al., 1993; Klochko et al., 1996; Sokolowski and
Fischer, 1990). In these studies, however, the individual fluid components are still
8
modeled as Lennard-Jones particles. In addition, these simulations have, so far, been
limited to the study of the thermodynamic properties of adsorbed mixtures, whereas
separation of many mixtures, including supercritical (SC) mixtures, that are of
interest in this thesis (Chapter 2), is expected to be transport-dominated.
Other types of pore shapes, and random pore structures, which are of more
relevance to the CMS materials, have so far received only scant attention. A few
studies on triangular pores (Bojan et al., 1992), of carbon nonotubes (Maddox and
Gubbins, 1995; Takaba et al., 1995, 1996), and of a random pore space created by
stacked disks (Segarra and Glandt, 1994) have appeared. A significant advance has
been in combining experimental adsorption isotherms and DFT (Lastoskie et al.,
1993) or grand-canonical MC (GCMC) simulations to obtain realistic pore size
distributions (PSD), thus providing a bridge between the behavior at the
molecular/single pore-scale and that at the macroscopic/pore network-scale. Samios
et al. (Samios et al., 1997), for example, employed slit-shaped graphite pores to
simulate the adsorption of CO2 and assumed the microporous structure to consist of
parallel, non-intersecting pores of various sizes having a postulated PSD. On the
basis of comparison of sorption isotherms obtained by simulation and experiments,
they derived the desired PSD function. Seaton and co-workers (Liu et al., 1992,
1993; Lopez-Ramon et al., 1997; Seaton et al., 1989, 1991, 1997) and Gusev et al.
(Gusev et al., 1997) proposed a similar technique. Their novel contribution was in
using percolation theory (Sahimi, 1994), which allowed them to estimate the
connectivity of the pore network. They used this approach to study the molecular
9
sieving mechanism of carbon molecular sieves, by combining equilibrium MD
(EMD) simulations of transport of single species in slit-shaped pores, and pore
network and percolation theory. Though simple in its inception, the study showed
how powerful the combination of MD simulations and network modeling can be in
describing important aspects of kinetic separation obtained with networks having a
range of pore sizes.
1.3 The Potential Energy Adsorption, diffusion and transport properties are modeled in molecular simulations
on a molecular scale, i.e. the molecules of the fluid mixture and the atoms of the pore
walls of the adsorbents or membranes are considered individually. In order to do this,
we need to calculate the interaction energies throughout the system. The quantum
effects are normally neglected; i.e. the system is modeled as a collection of N
classical particles interacting with each other via an intermolecular potential.
Moreover, there may be external potentials which are acting on the system. Then, the
total potential energy is:
(1.1) External ParticleU U U= +
For fluid atoms adsorbed in a pore, the first term in Eq. (1.1) is due to
interactions between the fluid molecules and the pore walls or structure. The second
term is due to interactions of fluid molecules with each other, which can occur
between pairs, triplets and larger groups of molecules. The fluid interactions beyond
10
pairs of molecules are usually ignored since the potential calculations are
computationally costly when interactions between large groups of atoms are
accounted. Using this simplifying assumption, the fluid interactions are pairwise
additive, and the total potential energy due to particle interactions for a system of N
particles can be written as:
(1.2) 1
1 1( )
N NParticle
iji j i
U−
= = +
= ∑ ∑ u r
where is the pair potential between the particles i and j that are separated by )( ijru
222222 )()()( jijijiijijijij zzyyxxzyxr −+−+−=++= , and are the
particle coordinates. The indices in the double summation of Eq.(1.2) show that each
pair is counted once, which means that only distinct particle pairs contribute to the
total potential energy.
),,( iii zyx
In many MD simulations the interaction potential between a pair of particles,
the center of which are a distance apart, is represented by the classical Lennard-
Jones (LJ) 12-6 potential (Allen and Tildesley, 1987):
ijr
12 6
( ) 4ijij ij
u rr rδ δε
⎧ ⎫⎛ ⎞ ⎛ ⎞⎪ ⎪= −⎜ ⎟ ⎜ ⎟⎨ ⎬⎜ ⎟ ⎜ ⎟⎪ ⎪⎝ ⎠ ⎝ ⎠⎩ ⎭ (1.3)
given here for a like pair of particles i and j. This potential is shown in Fig. 1.1. The
terms ε and δ in Eq. (1.3) are the Lennard-Jones parameters of the fluid, where ε
is the energy parameter of the potential (the maximum energy of attraction between a
pair of molecules), or the LJ well depth, and δ is the size parameter (or the distance
at which the LJ potential passes through zero and the potential sharply rises to
11
repulsive values), also called the collision diameter. Note that δ is not the same as
molecular diameter of the molecules, although the two quantities are usually close to
each other. In Eq. (1.3) the term represents a hard-core or repulsive potential,
while the term is the attractive part. The simulation results are usually reported
in units of
12−ijr
6−ijr
ε (energy), δ (length), and m (the mass of a fluid particle).
Figure 1.1: The 12-6 Lennard-Jones potential for particles i and j [Eq. (1.3)]. The potential energy is in units of ε and the distance between i and j is in units of δ . When is positive, the interactions for the pair of particles are repulsive. When
is negative, their interactions are attractive. ijU
ijU
12
When the particles i and j in Eq. (1.3) are of different type, we needs to
approximate the Lennard-Jones parameters, δ and ε . One commonly used
approximation is the Lorentz-Berthelot mixing rules:
and 2
i jij i j ij
δ δε ε ε δ
+= = (1.4)
given here for particles of type i and j.
In order to reduce the number of interactions calculated in a molecular
simulation, the interaction potential is truncated and shifted to zero at a cut-off
distance, rcut-off )( cr . In practice, what is done in most cases is cutting the interactions
off at a distance . Typically, is set to be a multiple of the effective molecular
diameter of the largest atom in the simulations and, therefore, it is usually smaller
than half the system’s linear size. If this approach is taken, then at every step of the
integration one must check, for any particle i, the distances of all other particles from
i to see whether they are at a distance larger or smaller than . We must point out,
however, that cutting off the interaction potentials violates energy conservation,
although if is selected carefully, the effect will be small. Moreover, by shifting the
interaction potentials one can avoid violation of energy conservation altogether by
writing
cr cr
cr
cr
0 0 ij
ij
( ) ( ), if r( )
0 if r > ij c c
ijc
u r u r ru r
r
− ≤⎧⎪= ⎨⎪⎩
(1.5)
where represents the original interaction potential to be used. However, this
shift does not affect the force resulting from the shifted potential; it remains
)(0 ijru
13
discontinuous at . In order to make the force also continuous at the cutoff point, we
write
cr
00 0
( )( ) ( ) ( ) if r( )
0 if r
cc c r r
c
du ru r u r r r ru r dr
r
=⎧ − − − ≤⎪= ⎨⎪ ⟩⎩
c (1.6)
This algorithm was first suggested by Stoddard and Ford (Stoddard and Ford, 1973).
The actual number of interacting particles (i.e., those that are within a sphere of
radius , centered at the center of a given particle) is a function of the molecular
density and this method is much more efficient than a full N−body calculation. The
cut-and-shift procedure cannot be used if electric and gravitational forces are
operative in the system, since they decay only as
cr
r1 .
1.4 Molecular Dynamics Over the past two decades, MD simulations, in which atoms and molecules are
treated as classical particles and quantum-mechanical effects are neglected, have
become an important tool for investigating and predicting various static as well as
dynamical properties of materials. Knowledge of transport properties of
multicomponent gases and oil is of great economical importance in planning of
transport and in dimensioning of industrial plants and reservoir modeling. For
mixtures that consist of molecules of dissimilar sizes, shapes and polarity, traditional
prediction methods for thermal conductivity and viscosity need experimental data to
14
fit mixing rules (Monnery et al., 1995), whereas for diffusion the few existing
prediction methods deviate up to almost an order of magnitude (Helbaek et al.,
1996). One possible route to obtained better predictions is to use MD simulations
that can predict thermophysical properties from models of molecular interactions
only. We will simply mention below a few key papers appeared in the 50s and in the
60s that can be regarded as milestones in molecular dynamics.
The first paper reporting a molecular dynamics simulation was written by
Alder and Wainwright (Alder and Wainwright, 1957) in 1957, who studied a system
with only a few hundreds hard-sphere particles and discovered a fluid-solid phase
transition. The article Dynamics of radiation damage by J.B. Gibson, A. N. Goland,
M. Milgram and G. H. Vineyard , from Brookhaven National Laboratory, appeared
in 1960 (Gibson et al., 1960), is probably the first example of a molecular dynamics
calculation with a continuous potential based on a finite difference time integration
method. The calculation for a 500-atoms system was performed on a IBM 704, and
took about a minute per time step. Aneesur Rahman at Argonne National Laboratory
was well known as a pioneer of molecular dynamics. In his famous 1964 paper
correlations in the motion of atoms in liquid argon (Rahman, 1964), he studied a
number of properties of liquid Ar, using the LJ potential on a system containing 864
atoms and a CDC 3600 computer. Loup Verlet calculated in 1967 (Verlet,
1967,1968) the phase diagram of argon using the LJ potential, and computed
correlation functions to test theories of the liquid state. The bookkeeping device
which became known as Verlet neighbor list was introduced in these papers.
15
Moreover the “Verlet time integration algorithm” was used. Phase transitions in the
same system were investigated by Hansen and Verlet a couple of years later (Hansen
and Verlet, 1969).
We call molecular dynamics a computer simulation technique where the time
evolution of a set of interacting atoms is followed by integrating their equations of
motion. One uses the MD technique to obtain the dynamic properties for a collection
of classical particles. In molecular dynamics we follow the laws of classical
mechanics, and most notably Newton’s law. For a system of size N, this involves
solving a set of 3N second order differential equations (Newton’s equations of
motion):
2 2 2
2 2 2, , i 1,2,...Ni i i
i i ix i y i z i
x y zF m F m F mt t t
∂ ∂ ∂= = = =
∂ ∂ ∂ (1.7)
where is the force exerted on the ii
Fβth particle in the β direction, mi is the particle
mass, and t represents time.
The force on the ith particle is related to the potential energy by:
( )
i
ij ijx
j i ij ij
x u rF
r r≠
∂= −
∂∑ (1.8)
where the summation is over all other particles in the system. If present, forces due
to external interactions are also added to Eq.(1.8). Similar relations hold for the y and
z directions. Therefore in contrast with the MC method, molecular dynamics is a
deterministic technique: given an initial set of positions and velocities, the
subsequent time evolution is, in principle, completely determined. In more pictorial
terms, atoms will “move” into the computer, bumping into each other, wandering
16
around (if the system is fluid), oscillating in waves in concert with their neighbors,
perhaps evaporating away from the system if there is a free surface, and so on, in a
way pretty similar to what atoms in a real substance would do. Therefore, the MD
method is a way of simulating the behavior of a system as it evolves with time since,
unlike the MC method, in the MD simulations the system moves along its physical
trajectory. The main advantage of the MD method over the MC technique is that, not
only does it provide a method for computing the static properties of a system, but
also allows one to calculate and study the dynamical properties of many nanoporous
materials that are of interest to us in this thesis.
The computer calculates a trajectory in a 6N-dimentional phase space (3N
positions and 3N momenta). However, such trajectory is usually not particularly
relevant by itself. Molecular dynamics is a statistical mechanics method. Like Monte
Carlo, it is a way to obtain a set of configurations distributed according to some
statistical distribution function, or statistical ensemble. An example is the
microcanonical ensemble, corresponding to a probability density in phase space
where the total energy is a constant E:
( )H Eδ ⎡ ⎤Γ −⎣ ⎦ (1.9)
Here, is the Hamiltonian (the total energy), and ( )ΓH Γ represents the set of
positions and momenta. δ is the Dirac function, selecting out only those states
which have a specific energy E. Another example is the canonical ensemble, where
the temperature T is constant and the probability density is the Boltzmann function:
17
( )exp BH k T⎡ ⎤− Γ⎣ ⎦ (1.10)
According to statistical physics, physical quantities are represented by
averages over configurations distributed according to a certain statistical ensemble.
A trajectory obtained by molecular dynamics provides such a set of configurations.
Therefore, a measurement of a physical quantity by simulation is simply obtained as
an arithmetic average of the various instantaneous values assumed by that quantity
during MD run.
Statistical physics is the link between the microscopic behavior and
thermodynamics. In the limit of very long simulation times, one could expect the
phase space to be fully sampled, and in that limit this averaging process would yield
the thermodynamics properties. In practice, the runs are always of finite length, and
one should exert caution to estimate when the sampling may be good (“system at
equilibrium”) or not. In this way, MD simulations can be used to measure
thermodynamics properties and, therefore, evaluate, say, the phase diagram of a
specific material. Molecular simulation allow conducting computer experiments, i.e.,
by studying the system on a molecular scale it is possible to measure macroscopic
thermodynamic properties, such as adsorption isotherms or diffusion coefficients at
various process conditions. It is possible to easily change the process conditions,
such as the temperature, and to predict both pure and multicomponent adsorption
isotherms. Furthermore, molecular simulations yield much more detailed information
about the system studied than available from conventional experiments. As the
position of every molecule in the system is known explicity, it is, for example,
18
possible to measure local density profiles and to visualize how the special
distribution of heterogeneities on the pore surface influences the distribution of the
adsorbate molecules in the pore. Molecular dynamics is especially useful for
calculating the dynamic properties, such as the self-diffusion and mutual diffusion
coefficients (Jaccucci and Mcdonald, 1975; Jolly and Bearman, 1980; Schoen and
Hoheisel, 1984) for mixtures. Beyond this “traditional” use, MD is also used for
other purposes, such as studies of non-equilibrium processes, and as an efficient tool
for optimization of structures overcoming local energy minima (simulated
annealing).
We consider here a few important phenomena that occur in the pores of a
nanoporous membranes, two of which, adsorption of a single gas or a mixture of
gases (an equilibrium phenomenon), and flow and transport of fluids in the pore
space under the influence of an external potential gradient (a non-equilibrium
phenomenon), have been studied extensively using molecular modelling. In what
follows we describe atomistic modelling of both types of phenomena.
1.4.1 Equilibrium Molecular Dynamics
Equilibrium MD (EMD) is an important way to study the structure, adsorption and
thermodynamic properties of fluids near a wall surface and inside pores. One of the
most important equilibrium phenomena that can occur in the pore space of a
nanoporous membrane is adsorption of gases. There are several computational
19
techniques for molecular modeling of adsorption phenomena in the pore space of
such materials. One can naturally use the equilibrium molecular dynamics method
for simulating adsorption (Xu et al., 2001). Such simulations are typically done in
the microcanonical ensemble, i.e., one in which the total number of particles, N, the
total volume of the system, V, and its energy, E, are held fixed, which is why it is
usually referred to as the (NVE) ensemble. For example, chemical potential of
adsorbed gas on graphite (Cheng and Steel, 1990; Cracknell et al., 1995) has been
calculated using iso-kinetic MD method.
The self diffusion coefficient Ds , which is an important dynamic property, can
also be calculated by the EMD method, either from an integral over the velocity
autocorrelation function (the Green-Kubo relation), or from the time evolution of the
mean square displacement (the Einstein relation). Pressure is calculated from the
virial theorem. Temperature is also calculated from the kinetic theory:
( )2
13 1
N
i i Bi
T m v N=
= ∑ k− (1.11)
1.4.2 Non-equilibrium Molecular Dynamics
Much attention is paid to studies of membrane separation mechanisms at a molecular
level, since high performance inorganic membranes suitable for gas separations have
been developed during the past two decades. Gas permeation is essentially a non-
equilibrium phenomenon since it occurs when different pressures are applied on two
20
sides of a membrane. Equilibrium MD (EMD) simulations are applicable to systems
that, at least in principle, are amenable to treatment by statistical mechanics.
However, if we are to compute the effective flow and transport properties of fluids in
nanoporous materials, such as the permeability, diffusivity, shear viscosity, and
thermal conductivity, then EMD is not an effective tool. For example, as is well-
known, by calculating the velocity correlation functions for every distinct pair of
species in the system, one can obtain information about the microscopic motion of
the molecules. However, since the velocity correlation function decays as the size of
the system increases, use of EMD is not feasible for estimating the transport
properties of a mixture of molecules in a system which is under the influence of an
external potential gradient - a situation which is encountered in a very large number
of practical problems. One can use the velocity autocorrelation function, but this
quantity can only be used for predicting the tracer or self-diffusivity sD of a species
(that is, when the system is very dilute) via the Green-Kubo equation:
[ ]0
1
1 ( ) . (0) 3
N
s i ii
D v t vN
∞
=
= ∑∫ dt (1.12)
where is the velocity of particle i. The self-diffusivity is, however, completely
different from the transport diffusivity because tracer diffusion ignores the effect of
the collective motion of other molecules, especially in systems with a moderate or
high density. As such, EMD is not suitable for investigation of a transport process in
a system on which an external potential (pressure, voltage, chemical potential,
concentration, etc.) gradient has been imposed. Direct MD simulation of membrane
iv
21
permeation, therefore, requires two regions at different pressures or densities, which
create a driving force for molecular transport across the membrane. This technique
involves the creation of stationary chemical potential gradients between two control
volumes. The grand canonical ensemble Monte Carlo (GCMC) method is suitable
for maintaining a region to be at constant chemical potential or a constant density.
The specification of two sub-regions at different chemical potentials (or densities)
yields a new type of non-equilibrium MD (NEMD) method: the dual control-volume
grand canonical ensemble MD (DCV-GCMD) method proposed by Heffelfinger and
Swol (Heffelfinger and Van Swol, 1994), a grand canonical MD (GCMD) method by
MacElroy (MacElroy, 1994), a GCMD method by Cracknell, Nicholson and Quirke
(Cracknell, Nicholson and Quirke, 1995), and the grand canonical ensemble NEMD
( VTμ -NEMD) method by Furukawa et al. (Furukawa et al., 1996; Furukawa and
Nitta, 1997). Such NEMD simulation methods represent practical alternatives to
EMD for those systems for which the velocity correlation function is difficult, or
meaningless, to measure. They are particularly ideal for the practical situation in
which an external driving force is applied to the system. These methods have been
widely used. In particular, the GCMD method (Cagin and Pettitt, 1991; Lupkowski
and Van Swol, 1991; Sun and Ebner, 1992) combines the MC and MD simulations,
and the DCV-GCMD has also been used for studying many non-equilibrium
phenomena.(Cracknell, Nicholson and Quirke, 1995; Düren et al., 2002; Firouzi et
al., 2003, 2004; Ford and Heffelfinger, 1998; Furukawa et al., 1997; Heffelfinger
and Van Swol, 1994; Heffelfinger and Ford, 1998; Kjelstrup and Hafskjold, 1996;
22
MacElroy, 1994; Maginn et al., 1993; Nicholson et al., 1996; Pohl and Heffelfinger,
1999; Sokhan et al., 2002; Sunderrajan et al., 1996; Supple and Quirke, 2003;
Thompson et al., 1998; Xu et al., 1998, 1999; Xu, Sahimi et al., 2000; Xu, Sedigh et
al., 2000).
The DCV-GCMD method has become an effective tool for studying systems
that are under the influence of an external potential gradient. We will describe this
method in details in Chapter 2. In this method, the simulation box is divided into
three sections: two control volumes maintained at constant chemical potential, μ1 and
μ2 correspondingly, connected by a "transport region," where there is a net flux of
molecules due to the potential gradient generated by the difference μ1 - μ2. The
transport coefficients that describe the steady-state, non-equilibrium transport under
the influence of a chemical potential gradient, are obtained by directly monitoring
the net flux of molecules through the transport region of the simulation cell. This
technique has been applied in the study of the transport of mixtures in graphitic slit-
shaped micropores (Cracknell, Nicholson and Quirke, 1995; Ford and Glandt, 1995;
Ford and Heffelfinger, 1998; Furukawa et al., 1996, 1997; Furukawa and Nitta,
1997; Heffelfinger and Van Swol, 1994; Heffelfinger and Ford, 1998; Kjelstrup and
Hafskjold, 1996; Nicholson et al., 1996; Pohl et al., 1996; Pohl and Heffelfinger,
1999; Sun and Ebner, 1992; Sunderrajan, 1996; Thompson et al., 1998; Xu et al.,
1998, 1999; Xu, Sedigh et al., 2000).
Although the DCV-GCMD has been used extensively during recent years, the
systems studied did not constitute realistic models of transport of gaseous mixtures
23
through porous materials under typical experimental conditions. In most of these
studies the physical conditions of the system did not correspond to an actual
experimental situation and, therefore, no direct comparison with experimental data
was possible. Our group (Ghassemzadeh et al., 2000; Xu et al., 1998, 1999; Xu,
Sedigh et al., 2000; Xu, Sahimi et al., 2000; Xu et al., 2001) initiated the study of the
transport and separation of fluid mixtures in CMSMs under realistic chemical
potential gradient, by both experiments and DCV-GCMC simulations.
1.5 Monte Carlo and Grand Canonical Monte Carlo
In the MC simulation technique, random system perturbations are accepted or
rejected according to the theory of statistical thermodynamics (Allen and Tildesley,
1987; Hill, 1986; McQuarrie, 1976). The resulting set of fluid configurations spans
the phase space of a chosen statistical ensemble. Since, the particle trajectories are
generated at random, unlike in MD, dynamic properties of the system are not
normally calculated in MC.
In the standard MC technique of Metropolis et al. (Metropolis et al., 1953),
the equilibrium properties of a fluid at fixed temperature (T), number of particles (N)
and system volume (V) is simulated as a Markov chain of states. Each state is
generated by perturbing the preceding state. Specifically, a randomly chosen particle
undergoes a randomly sized displacement. Once the new state is produced, one
24
compares the total potential energies in the new and old states. The new state is
accepted into the Markov chain if its energy is lower than that of the old state.
Otherwise, it is accepted with probability:
expiB
Upk T
⎛ ⎞−Δ= ⎜
⎝ ⎠⎟ (1.13)
where is the difference between the total potential energy in the
new and old states, and is the Boltzmann’s constant. The quantity in Eq. (1.13) is
the ratio of the Boltzmann factor
oldnew UUU −=Δ
Bk
( )[ ]TkU B−exp
)
in the new and old states.
Consequently, the states in the Markov chain resulting from an MC simulation
belong to the canonical ensemble, and averages of properties (e.g., energy and
density distribution) over the states correspond to the mean properties of a fluid at
constant temperature, volume and number of particles.
The main advantage of the MC technique is that it is straightforward to
simulate a fluid in different ensembles; i.e., other than for fixed temperature, volume
and number of particles. For instance by modifying the Metropolis algorithm, one
can perform simulations at constant temperature, system volume and chemical
potential (μ . In this case, the ensemble sampled is the grand canonical ensemble
and the simulation technique is aptly named grand canonical Monte Carlo (GCMC).
In a grand-canonical ensemble, both the energy and density are allowed to fluctuate,
hence making GCMC a suitable technique for computing equilibrium properties of
single- and multicomponent mixtures. In particular, it has been used extensively for
25
computing the adsorption isotherms of gases and their mixtures in models of various
types of nanoporous materials (Cracknell and Gubbins, 1993; Cracknell and
Nicholson, 1993, 1994; Cracknell, Nicholson and Gubbins, 1995; Gale et al., 1990;
Ghassemzadeh et al., 2000; Ghassemzadeh and Sahimi, 2004; June et al., 1990,
1992; Keldsen et al., 1994; Maddox and Gubbins, 1994; Mezei, 1980; Miller et al.,
1987; Percus, 1986; Peterson and Gubbins, 1987; Plee et al., 1985; Skipper et al.,
1989; Yi et al., 1995, 1996, 1998). The method was first used in studies of bulk
fluids (Adams, 1975), and was then extended to adsorbed systems (Van Megen and
Snook, 1982, 1985). The GCMC method is based on utilizing a Markov chain for
generating a series of molecular configurations by determining whether to accept a
configuration into the Markov chain using the same criteria as in canonical MC. In a
GCMC simulation the new configuration is generated by the following three steps:
(1) A particle is chosen at random and given a displacement with a probability given
by Eq. (1.13).
(2) A position is chosen at random, and a particle is added at that position with a
probability
min exp( / ),11
i ci
i
Z VpN
+BU k T
⎧ ⎫= −Δ⎨ ⎬+⎩ ⎭
(1.14)
Here, is the absolute activity, 3exp( / ) /i i BZ k Tμ= iΛ iμ is the chemical potential of
component i, TkB1=β and Tkmh Bii 2π=Λ is the de Broglie wavelength (h is
26
Plank’s constant). and are the volume of the CV and the number of atoms of
component i in CV, respectively.
cV iN
(3) A particle is chosen at random and is removed from the system with a probability
min exp( / ),1ii
i c
Np UZ V
−Bk T
⎧ ⎫= −Δ⎨ ⎬
⎩ ⎭ (1.15)
In order to guarantee irreducibility of the Markov chain (i.e., each state in the chain
can be reached from any other state), which is critical to maintaining ergodicity in
the system, the second and third GCMC perturbations are attempted with equal
probability (Allen and Tildesley, 1987). For simulation of multi-component fluids,
care must be taken to attempt insertion and deletion steps for each component with
equal probability. The dimensionless form of Z can be written as:
( )( )
(33
expexp cZ
βμ )σ βμσ
= =Λ
(1.16)
Where cμ is called the configurational potential.
1.6 Thesis Outline The aim of this thesis is to further the understanding of the transport and separation
of gas mixtures in carbon molecular sieve-membranes (CMSM), modeled either as a
single slit pore, a composite pore model, or as a three-dimensional pore network with
interconnected pores. Non-equilibrium molecular dynamics simulations are used for
27
investigating the transport and separation of binary mixtures of n-alkanes, as well as
mixtures of CO2 and n-alkanes, as well as pure CO2. The effect of important factors,
such as the temperature of the system, the applied pressure gradient, feed
compositions, pore size, pore interconnectivity, and interaction of the molecules with
each other, on their adsorption, permeation, and separation through CMSM will be
investigated. The results are compared with the experimental data generated in our
laboratory. Better understanding of these phenomena will permit the tailoring of
membranes for optimum sorption or separation performance.
The thesis is divided into the following five chapters. Chapter 2 presents the
results of extensive NEMD simulations of the transport and separation properties of
supercritical binary fluid mixtures consisting of CH4 and CO2 in a slit carbon
nanopore. In Chapter 3 contains the results of NEMD simulations of transport and
separation of binary mixtures of n-alkanes, as well as mixtures of CO2 and n-alkanes,
in a slit carbon nanopore. We present in Chapter 4 the results for the composite pore
model and address whether the permeation properties of CO2 and binary mixtures of
CH4 and CO2 in the system, under sub- and supercritical conditions exhibit any
asymmetry. The results of transport and separation of binary mixture of n-alkanes, as
well as mixtures of CO2 and n-alkanes, in a carbon pore network under sub- and
supercritical conditions are presented in Chapter 5.
28
Chapter 2 Transport and Separation of Supercritical Fluid Mixtures in a Single Carbon Nanopore 2.1 Introduction
lmost all the previous theoretical and computer simulation studies of
transport of fluid mixtures in confined media have been carried out under the
condition that the fluids that enter the nanopore space are in a thermodynamic state
below their critical points. On the other hand, supercritical fluids (SCFs) – those that
are in a thermodynamic state above their critical temperature and/or pressure – have,
in recent years, attracted much attention. They are attractive media for chemical
reactions because of their unique properties. Many of the physical and transport
properties of SCFs are intermediate between those of a liquid and a gas. Such fluids
and their transport and separation properties are the focus of this chapter.
A
Consider, for example, supercritical fluid extraction (SCFE) for adsorbent
regeneration, which appears to be a promising technology. Spent adsorbents are
currently being incinerated, landfilled, or subjected to harsh thermal regeneration.
With disposal costs rapidly increasing, attention is progressively placed on more
efficient regeneration processes, and SCFE certainly shows great potential in this
area. For example, SCFE may be used for clean-up of contaminated soils. The
29
advantage of SCFE over conventional liquid extraction is that in the SC region,
where density becomes liquid-like, viscosity and diffusivity remain between gas and
liquid values and surface tension effects are negligible, thus making it easier under
such conditions to access the soil's internal pore structure, and resulting in enhanced
mass transport.
SCFE utilizing CO2 has received considerable attention in recent years (Kiran
and Sengers, 1994; Sengers and Sengers, 1986). The potential utility of this process
has been investigated for the removal of contaminants from water (Brignole et al.,
1987; Gamse et al., 1997; Meguro et al., 1996; Roop et al., 1988; Shing et al., 1988),
sludge (McGovern et al., 1987), soils (Akgerman and Yao, 1993; Brady et al., 1987;
Dooley and Knopf, 1987; Dooley et al., 1987; Erkey et al., 1993; Firus et al., 1997;
Hall et al., 1990; Liu et al., 1991; Pang et al., 1991), spent catalysts (Silva et al.,
1993), aerogels (Novak and Knez, 1997; Wawrzyniak et al., 1998), and adsorbents,
such as activated granular carbon (De Filippi et al., 1980, 1983; Macnaughton and
Foster, 1995; Tan and Liou, 1989; Tomasko et al., 1993, 1995). They are also used
for preparing nanosize particles for drug delivery. Though other compounds, such as
propane, butane, and various fluorocarbons might be better solvents under SC
conditions (especially for low volatility solutes), CO2 is generally preferred in
environmental applications because it is non-toxic and non-flammable. In addition,
SCFE by CO2 leaves no solvent residue on the contaminated soil. Compared with
thermal incineration, SCFE is less energy intensive, leaves the soil's internal
30
structure and nutrients relatively intact, and can handle far higher concentrations of
toxic components than bioremediation.
Perhaps the most promising SCFE method is one that combines a SC fluid with
another separation medium, such as a nanoporous membrane, which will
preferentially and continuously extract the solute, leaving behind a solute-depleted,
recyclable SC solvent stream, hence promising significant reductions in the cost of
the energy intensive compression/re-compression cycle, typically associated with
SCFE. Several recent studies have investigated the use of various membranes with
SC fluids (Afrane and Chimowitz, 1993, 1996; Chimowitz and Afrane, 1996; Fujii et
al., 1996; Kelley and Chimowitz, 1990; Muller et al., 1989; Nakamura et al., 1994;
Ohya et al., 1993; Sarrade et al., 1996; Semenova et al., 1992b,1992a; Tokunaga et
al., 1997), and reported several complex phenomena. For example, hysteresis in the
permeability isotherms was observed at some temperatures but not at others. The
permeabilities also exhibited a maximum as a function of the temperature, which
also depended on the pressure. Solute rejection was found to be positive or negative,
depending on the membrane type and the solutes used. Such complex behavior is
generally attributed to the combined effects of sorption of the SC fluid, their
tendency to aggregate and form clusters, and the variation of the pore structure and
surface characteristics due to membrane type and preparation procedures, as well as
the competition between equilibrium- and transport-dominated processes. There is
currently little fundamental knowledge on the transport of SC mixtures in
membranes, due to the complexities that arise as the result of the interactions
31
between the highly nonideal, compressible SC mixtures and the complex pore space
of a nanoporous membrane. Moreover, in addition to being of practical importance,
these phenomena have also raised a number of fundamental issues related to the
solvation structure and dynamics of the solutes under SC conditions.
The fundamental understanding of the behavior of fluids under SC conditions
in microporous systems, such as adsorbents, membranes and catalysts, is in general
very limited. The early studies focused on the adsorption of single gases in carbon
molecular sieves (Bojan et al., 1992; Matranga et al., 1992), in micropores (Van
Slooten et al., 1994), and in pores with structured surfaces (Cascarini de Torre et al.,
1996; Nicholson, 1994). These studies provided valuable information about such
systems. For example, Nicholson's study of adsorption of N2 in a slit-shaped pore
with corrugated potential (to represent surface heterogeneity) indicated that, the
transition associated with corrugations are likely to be suppressed in micropores in
comparison with the corresponding phenomena observed with planar surfaces.
Afrane and Chimowitz (Afrane and Chimowitz, 1996) reported on experimental
studies of SC fluids during separation processes in inorganic membranes.
Studies of the sorption of mixtures under SC conditions have only recently
appeared (Chimowitz and Afrane, 1996). Nitta (Nitta et al., 1993; Nitta and Yoneya,
1995) and Shingetta (Shigeta et al., 1996) studied the sorption of dilute benzene/SC
CO2, and butane/SC CO2 mixtures in slit-shaped graphitic pores using MC
techniques. The kinetic properties of mixtures in pores and membranes, such as the
rates of mutual diffusion, remain unexplored and little understood. Only a few
32
modeling studies (Sedigh et al., 1998; Xu et al., 1998), of direct relevance to non-
equilibrium transport in porous carbons have been published. The first study is by
Cracknell et al. (Cracknell et al., 1993), who studied simple LJ spheres in graphite
slit-shaped nanopores. More recently, Furukawa et al. (Furukawa et al., 1996, 1997;
Furukawa and Nitta, 1997) reported a study of the transport of a mixture of two LJ
spheres through a slit-shaped nanopore, followed by studies of the effect of surface
heterogeneity. A somewhat related study is by Takaba et al. (Takaba et al., 1996),
who investigated the effect of sorption affinities on CO2 separation from a CO2/N2
mixture in a slit-shaped inorganic membrane pore, using MD simulation of the
transient uptake process.
Although work is ongoing in the area of modeling the transport and sorption of
nanoporous carbon adsorbents and membranes, we are not aware of any published
study of the same phenomena under SC conditions, through CMSM in the presence
of a strong chemical potential or pressure gradients. These are subjects of our study
in this chapter. In the context of the work reviewed above, the study of transport
properties of hydrocarbon/SC CO2 mixtures in nanoporous carbon membrane
materials represents a new class of research problems with great scientific interest
and technological importance. Although a number of studies have been reported,
there is still a lack of systematic studies of the non-equilibrium transport of SC
mixtures (even at a single pore level), and a lack of integrated experimental/
theoretical/computational studies of sorption and transport spanning the micro and
macro-scales.
33
This chapter represents the first part of our work aimed at developing a
fundamental understanding of the phenomena involved during the transport of
hydrocarbon/SC CO2 mixtures in a nanoporous membrane. The results of our studies
should be useful to applications that involve the regeneration of adsorbents by SC
CO2 and the use of membranes under SC conditions. The emphasis in this study is on
identifying the factors that control the ability of the membranes for separation of SC
mixtures.
In this work we use a dual control-volume-grand-canonical MD technique
(Heffelfinger and Van Swol, 1994; MacElroy, 1994) (DCV-GCMD), which has been
used over the past few years (Cracknell, Nicholson and Quirke, 1995; Ford, 1995;
Ford and Heffelfinger, 1998; Furukawa et al., 1996, 1997; Furukawa and Nitta,
1997; Heffelfinger and Van Swol, 1994; Heffelfinger and Ford, 1998; Kjelstrup and
Hafskjold, 1996; MacElroy, 1994; Nicholson et al., 1996; Nitta, 1995; Pohl et al.,
1996; Pohl and Heffelfinger, 1999; Smith, 1986; Sun and Ebner, 1992; Sunderrajan
et al., 1996; Thompson et al., 1998). Although molecular simulations have been used
for studying SC fluids in the bulk (Chialvo and Cummings, 1999; Chung and Shing,
1992; Cummings et al., 1991; Eckert et al., 1996; Martinez et al., 1996; Nouacer and
Shing, 1989; Shing and Chung, 1987; Shing, 1991; Yoshii and Okazaki, 1997), very
few such studies have been reported in which they have been used for investigating
the behavior of SC fluids in small pores (Nicholson, 1998).
34
2.2 The Pore Model As a prelude to understanding transport and separation of SC fluid mixtures in
CMSM, which consist of a pore space of interconnected nanosized pores, we first
consider the same phenomena in a single carbon nanopore. Recent molecular
simulations by Düren et al. (Düren et al., 2002, 2003) indicate that transport in a
nanopore is hardly influenced by its shape, so long as the correct average radius,
transport length and enclosing gradient are used. Thus, we consider here a simple a
slit-pore, a schematic representation of which is shown in Figure 2.1, in which the
origin of the coordinates is at the center. The two carbon walls are located at the top
and bottom xy planes. The external driving force is a chemical potential or,
equivalently, a pressure gradient applied in the x-direction. The system is divided
into three regions. The h- and l-regions represent, respectively, the control volumes
(CVs) exposed to the bulk fluid at high and low chemical potential or pressure, while
the middle region represents the pore. The pore's length is nL with n being an
integer. In most of our calculations we used n = 1; however, longer pores with n > 1
were also simulated, and were found to have no significant effect on the results.
Periodic boundary conditions were employed only in the y-direction.
The pore's walls are assumed to be smooth (structureless), since our group’s
previous studies of subcritical gas mixtures (Firouzi et al., 2003; Xu et al., 1998,
1999; Xu, Sedigh et al., 2000; Xu, Sahimi et al., 2000) indicated that the walls'
atomistic structure has little effect on the transport and separation properties. We
35
consider a mixture of CH4 (component 1) and CO2 (component 2), which are
represented as Lennard-Jones (LJ) spheres, characterized by effective LJ size and
energy parameters, σ and ε. We will present the results of our study for the mixtures
of SC CO2 and heavier alkane chains in Chapter 5. All the quantities of interest were
made dimensionless with the help of σ1 and ε1; the dimensionless groups are listed in
Table 2.1. As in our group’s work with subcritical gas mixtures (Xu, Sedigh et al.,
2000), we also considered a more realistic model for CO2, consisting of three LJ
interaction sites on the three atoms, plus point charges to account for the quadrupole
moment of CO2 molecules. However, we found no significant effect on the results.
Table 2.1: The conversion between the reduced and the actual units. Subscript 1
referes to the value of the parameters for CH4. Variable Reduced Form Length L 1/* σLL = Energy U 1/* εUU = Mass M 1/* MMM = Density ρ 3
1* ρσρ = Temperature T 1/* εTkT B= Pressure P 1
31 / εσP
Time t 2/12111 )/(* σε Mtt =
Flux J 2/111
31 )/(* εσ MJJ =
Permeability K 12/1
11 /)(* σεMKK =
36
The dimensions of the pore used were, W = 20 1σ and L = 40 1σ . Two pore
sizes (heights), H = HM = 5 1σ and H = Hm = 1.67 1σ , were used - narrow enough
sizes for which the carbon membranes may exhibit molecular sieving properties. Our
group’s simulations with subcritical gas mixtures (Xu et al., 1999; Xu, Sedigh et al.,
2000; Xu, Sahimi et al., 2000) indicated that the pore size Hm is optimal for
separation of binary gas mixtures into its components, yielding the highest separation
factor.
2.3 The DCV-GCMD Method In the simulations we combined MD moves in the entire system with GCMC
insertions and deletions in the two CVs that we described earlier. In the MD
simulations the Verlet velocity algorithm was used to solve the equations of motion.
Iso-kinetic conditions were maintained by rescaling the velocity independently in all
the three directions. It is essential to maintain the densities of each component in the
two CVs at some fixed values, which are in equilibrium with two bulk phases, each
at a fixed pressure and fluid concentration. The densities, or the corresponding
chemical potentials of each component in the CVs, were maintained by carrying out
a sufficient number of GCMC insertions and deletions of the particles. The
probability of inserting a particle of component i is given by
37
min exp( / ),11
i ci
i
Z VpN
+BU k T
⎧ ⎫= −Δ⎨ ⎬+⎩ ⎭
(2.1)
where is the absolute activity at temperature T, and 3exp( / ) /i i BZ k Tμ= iΛ iΛ iμ
are, respectively, the de Broglie wavelength and chemical potential of component i,
the Boltzmann's constant, U the potential energy change resulting from creating
or removing a particle, and and the volume of the CV and number of atoms of
component i in each CV, respectively. The probability of deleting a particle is given
by
Bk
cV iN
min exp( / ),1ii
i c
Np UZ V
−Bk T
⎧ ⎫= −Δ⎨ ⎬
⎩ ⎭ (2.2)
When a particle is inserted in a CV, it is assigned a thermal velocity selected from
the Maxwell-Boltzmann distribution at the given T. An important parameter of the
simulations is the ratio Ρ of the number of GCMC insertions and deletions in each
CV to the number of MD steps between successive GCMC steps. This ratio must be
chosen appropriately in order to maintain the correct density and chemical potentials
in the CVs, and also reasonable transport rates at the boundaries between the CVs
and the transport region. In our simulations Ρ was typically 10. During the MD
calculations particles crossing the outer boundaries of the CVs were removed. The
number of such molecules was, however, very small, typically about 1% of the total
number of molecules that were deleted during the GCMC simulations. In addition,
for each component we allowed for a nonzero streaming velocity (the ratio of the
flux to the concentration of each component) in the pore region, consistent with the
38
presence of bulk pressure/chemical potential gradients along the flow direction. The
unrealistic assumption of a zero streaming velocity in the transport region, used in
many of the previous works, leads to severely underestimated fluxes. Since the two
CVs are assumed to be well-mixed, and in equilibrium with the two bulk phases that
are in direct contact with them, there should be no overall nonzero streaming
velocity in these regions. However, the discontinuity of the streaming velocities at
the boundaries between the CVs and the transport region slows down the
computations. To address this, a very small streaming velocity was added to the
thermal velocity of all the newly inserted molecules within each CV that were
located within a very small distance from the boundaries between the CVs and the
transport region in the pore (Heffelfinger and Van Swol, 1994; Kjelstrup and
Hafskjold, 1996; Lupkowski and Swol, 1991; Maginn et al., 1993; Papadopoulou et
al., 1993). However, the actual streaming velocities of the molecules in the transport
pore region were still determined by the MD simulations. To study the transport of a
mixture due to a pressure gradient, the temperature of the system must be held
constant in order to eliminate any contribution of the temperature gradient to the
transport; hence special care was taken to achieve this. Figure 2.2 shows the
dimensionless time-averaged temperature profiles along a pore of size H = Hm =
1.67σ1 (the smallest pore used in the simulations; see above) containing an
equimolar mixture of CO2 and CH4. The upstream pressure in both cases is 120 atm,
while the downstream pressures are 90 atm and 20 atm. Both profiles, even in the
39
pore for which a pressure drop of 100 atm was applied, are reasonably smooth,
indicating the accuracy of the NEMD simulations.
2.4 Potential Models of the Molecules and the Walls As already mentioned, CH4 (component 1) and CO2 (component 2) were assumed to
be LJ spheres to which we assigned effective values of the LJ size and energy
parameters, σ and ε. We used σc = 3.4 Å , and εc/ = 28 K for the carbon atoms
constituting the pore's wall, and σ
Bk
1 = 3.81 Å, ε1/ = 148.1 K, σBk 2 = 3.79 Å, and
ε2/ = 225.3 K . For the cross-term LJ parameters, the Lorentz-Berthelot
combining rules were used:
Bk
2112 εεε = , and )(21
2112 σσσ += . We confirmed, by
carrying out equilibrium molecular simulations, that such a molecular representation
of CO2 produces a phase diagram which is in qualitative agreement with the
experimental data, under both subcritical and supercritical conditions.
The molecule-molecule interactions were modeled with the cut-and-shifted
LJ potential described earlier [Eq. (1.6)]. The cut-off distance was taken to be 2.5σ1
and long-range corrections were not applied. We utilized smooth pore walls for
which the 10-4-3 potential of Steele,
10 4 4
23
2( ) 25 3 (0.61 )
iw iw iwiw c iw iwU z
z z zσ σ σπρ ε σ
⎧ ⎫⎪ ⎪⎛ ⎞ ⎛ ⎞= Δ − −⎨ ⎬⎜ ⎟ ⎜ ⎟ Δ Δ +⎝ ⎠ ⎝ ⎠⎪ ⎪⎩ ⎭ (2.3)
40
was used to calculate the interaction between a molecule and the wall, where
= 0.335 nm is the space between the adjacent carbon layers, Δ cρ = 114 nm-3 is the
number density of carbon atoms in the layer, z is the distance from the wall, and iwσ
and iwε are the LJ parameters between the walls and molecule i.
2.5 Molecular Dynamics Simulations Unless otherwise specified, all of the simulations were carried out with the upstream
CV being in equilibrium with a bulk fluid at a total pressure of 120 atm. The
temperature of the system was either T = 40°C or higher. Such pressure and
temperatures are above the critical conditions for CO2 and its mixture with CH4. For
the downstream CV the pressure of the bulk phase with which it is in equilibrium
was varied between 1 and 110 atm in order to assess the effect of the applied
pressure gradient on the phenomena. The same mixture compositions were used in
both CVs.
We computed several quantities of interest, including the density profiles of the
component i along the x- and z-directions, (x) and ziρ x
iρ (z), respectively. To
calculate (x) the simulation box was divided in the x-direction into grids of size ziρ
1σ , and for each MD step the density profiles (x) were obtained by averaging the
number of particles of component i over the distance
ziρ
1σ . A similar procedure was
used for computing xiρ (z), with the averaging done over a small distance which was
41
about 0.16 1σ . As discussed below, these quantities are important to understanding
adsorption and transport properties of the fluids between the two pores walls.
For each component i we also calculated its flux by measuring the net
number of its particles crossing a given yz plane of area Ayz:
iJ
MD
LR RLi i
iyz
N NJN tA
−=
Δ (2.4)
where and are the number of the molecules of type i moving from the left
to the right and vice versa, respectively,
LRiN RL
iN
tΔ is the MD time step (we used * = 5 ×
10
tΔ
-3, i.e., 0.00685 ps, where t* is the dimensionless time), and N≈Δt MD is the
number of the MD steps over which the average was taken (we typically used NMD =
70,000). The system was considered to have reached steady state when the fluxes
calculated at various yz planes were within 5% from the averaged values, after which
the fluxes were calculated at the center of the transport region. The equations of
motion were integrated with up to 5 × 106 time steps. The steady state was typically
reached after 3 × 106 time steps.
The permeability of species i was calculated using iK
/i
ii i
iJ nLJKP nL P
= =Δ Δ
(2.5)
where is the partial pressure drop for species i along the pore, with xPxP ii Δ=Δ i
being the mole fraction of component i, and PΔ the total pressure drop imposed on
the pore. A most important property that we wish to study is the dynamic separation
factor S21 , defined as
42
221
1
KSK
= (2.6)
2.6 Results and Discussions Figure 2.3 presents the time-averaged density profiles of CO2 and CH4, in an
equimolar mixture of the two molecules at T = 40°C, as functions of X* = x / 1σ
along the pore, defined as the region, X≤− 20 * 20≤ . The downstream pressure
ranges from 20 atm, which is a subcritical condition, to 100 atm, which is
supercritical, and the pore size is HM = 5 1σ . In this and the subsequent figures, the
dashed lines indicate the boundaries of the pore region. The density profiles are
essentially flat in the two CVs, with numerical values that match those obtained by
the GCMC method at the same conditions, indicating that the chemical potentials in
the two CVs have been properly maintained during the NEMD simulations. The
small fluctuations in the profiles in the CV regions represent numerical noise. The
small downward curvature at X* = -50 (in the CO2 profile) or upward curvature at
X* = +50 (in the CH4 profile) is due to the “leakage” of the particles out of the two
CVs. These are the particles that, as discussed in Section 2.3, cross the outer
boundaries of the CVs and leave the system. However, such deviations from a flat
profile are insignificant. In the pore region, the densities for both components
decrease along the pore, which is expected. Due to the pressure drop applied to the
43
pore, the density profiles are not necessarily linear: the total flux is the sum of the
diffusive and convective parts, which result in density profiles that decay more or
less exponentially.
These features are quite pronounced when the pressure drop along the pore is
large enough. In particular, the CO2 density profiles clearly exhibit such features.
However, as the pressure drop along the pore decreases, the differences between the
various profiles become less pronounced, particularly for CH4. The reason is that,
with an upstream pressure of 120 atm, quite larger than the critical pressures for CO2
and CH4 (which are, respectively, about 73 atm and 45 atm), the molecules will be in
a liquid-like state everywhere in the pore, if the pressure drop in the pore is not large
(that is, if the downstream pressure is close to the upstream one). In contrast, when
the pressure drop along the pore is large, with the upstream pressure still being at
120 atm, the molecules will be in a gas-like state near the downstream CV, and
therefore the density profiles take on distinct shapes for the two CVs and the pore.
These features are clearly seen in Figure 2.4, where we show snapshots of the same
pore and the distribution of the molecules in it for the same mixture as in Figure 2.3,
for three different applied pressure drops, obtained after 3.5 × 106 time steps. In all
the cases the upstream pressure is 120 atm, but the downstream pressure is different
among the three. In the case of a pore with a downstream pressure of 20 atm (the top
panel), most molecules are distributed near the walls, which is what is expected for a
gaseous state in a pore. As the downstream pressure increases, the pore is
increasingly packed with molecules, creating a liquid-like state (middle panel). For a
44
downstream pressure of 100 atm the pore is packed with a very large number of
molecules (the bottom panel).
Figure 2.5 presents the same density profiles as in Figure 2.3, but for a mixture
with a CO2 mole fraction, x2 = 0.9. All the qualitative features of the profiles are
similar to those shown in Figure 2.3 except that, due to the low mole fraction of CH4
in the mixture, the differences between its density profiles in different regions of the
system (the two CVs and the pore) are not as large as those shown in Figure 2.3.
The density profiles shown in Figures 2.3 and 2.5 exhibit some fluctuations,
although their overall shapes are what one may expect. These fluctuations will
decrease and practically vanish if the simulation time is much larger than the time
that we used typically in the simulations, namely, 3.5 × 106 time steps. To
demonstrate this, we present in Figure 2.6 the density profiles of the two components
in an equimolar mixture, obtained after 5 million time steps in a pore of size HM =
5 1σ , and upstream and downstream pressures of 120 atm and 90 atm, and compare
them with the same profiles obtained after 3.5 million time steps. Two features of
this figure are noteworthy. (1) The density profiles obtained after the longer
simulations are much smoother than the one computed after the shorter simulations.
(2) The density profiles obtained after 3.5 × 106 time steps (the dashed curves)
fluctuate around the smoother profiles obtained after over 5 million time steps. The
fluctuations are, however, small.
Figure 2.7 shows the time-averaged density profiles for CO2 and CH4 in an
equimolar mixture at T = 40°C in the direction perpendicular to the pore's walls, in
45
three different regions of the pore. The downstream pressure is 70 atm, the pore size
is 5 1σ , and Z* = z / 1σ . These profiles were computed by averaging the results over
the last 300,000 time steps of the simulations. As these results indicate, the
supercritical fluid mixtures form several liquid-like layers, packing the pore almost
completely; see the distribution of the molecules in the pore, which is also shown in
Figure 2.7. This is in contrast with subcritical gases that form only two adsorbed
layers near the a pore's walls, leaving its middle region almost empty, an example of
which is shown in Figure 2.8 for exactly the same system as in Figure 2.7, except
that the upstream and downstream pressures are 3 atm and 1 atm, respectively.
Multilayer formation persists in the entire pore so long as the downstream pressure is
high enough for the mixture to exit the pore under supercritical conditions. If,
however, the downstream pressure is low, then multilayer formation occurs only near
the upstream region of the pore. As the molecules approach the downstream region,
only two layers, one near each wall, survive, hence signaling a phase transition from
a liquid-like state to a gaseous one. An example is shown in Figure 2.9, which is for
a system completely identical with that shown in Figure 2.7, except that the
downstream pressure is only 1 atm. Such feature will not change, if the composition
of the mixture changes. For example, Figure 2.10 presents the same density profiles
for a mixture with a CO2 mole fraction of x2 = 0.9. The rest of the parameters of the
system are the same as those of Figure 2.7. All but one of the qualitative features of
the two sets of density profiles are the same. The only difference is that the size of
the maxima in the CH4 density profiles of Figure 2.10 is much smaller than those of
46
Figure 2.7, but this is expected as the mole fraction of CH4 in this mixture is only x1
= 0.1 .
An important consequence of pore packing by supercritical fluids is the
formation of fluid clusters. We consider two molecules i and j to belong to the same
cluster if the distance rij between their centers is less than a critical distance Rc, where
we take Rc = 1.1 1σ . This definition can be used to define clusters of CO2, CH4, as
well as their mixtures. We find that such clusters are formed and travel the entire
length of the pore. Figure 2.11 presents the distribution of the molecules and the
various clusters that they have formed at three different times. All the parameters of
the system are the same as in Figure 2.7, except that the downstream and upstream
pressures are both 120 atm. We find that, even though the molecules' fluxes have
reached a steady state, over the time period in which these clusters were formed,
their sizes oscillate with the time. To establish this more quantitatively, we show in
Figure 2.12 the time-dependence of the largest clusters' sizes in the pores with sizes,
H = HM = 5 1σ and H = Hm = 1.67 1σ , where we set the downstream pressure at 70
atm, which is less favorable to cluster formation than when the downstream pressure
is also 120 atm (the rest of the parameters are the same as before). Despite this, large
mixed clusters, consisting of both CO2 and CH4, have formed, with sizes that
oscillate greatly with the time.
In general, we find that there is a distribution of the cluster sizes ns(t), where
ns(t) is the number of cluster of size s at time t, and a cluster's size is defined as the
number of molecules that it contains. Figure 2.13 presents the time-dependence of
47
the various cluster sizes ns(t) for the same two pore sizes shown in Figure 2.12. The
size of all the clusters, from the smallest to largest, oscillate with the time.
In dynamic critical phenomena, the cluster size distribution ns(t) follows
certain universal scaling in both the time t and cluster size s. In the present problem,
due to the oscillatory variations of ns(t) with the time t, one cannot expect the same
type of universal scaling as in dynamic critical phenomena. We do, however, find
that for small- to moderate-size clusters,
( ) ~sn t s τ− (2.7)
which is similar to what one finds in dynamic critical phenomenon (Vicsek and
Family, 1984). This is shown in Figure 2.14, where we show the results for a pore of
size 5 1σ . The rest of the system's parameters are the same as those of Figures 2.12
and 2.13. Note that the size of the pore imposes an upper cutoff on the size of the
molecular clusters that can form, and, therefore, the largest clusters may not follow
Equation 2.7, as they are very rare. It also implies that accurate determination of the
cluster size distribution for large cluster sizes in small pores may require very large-
scale simulations. Whether the cluster size distribution ns(t) follows any universal
dynamic scaling, i.e., whether the exponent τ is universal and independent of the
system's parameters (which would then be similar to what one finds in dynamic
critical phenomena), remains to be studied with much larger-scale simulations.
From a practical view point, two of the most important properties to be studied
are the permeance (permeability per unit length) of the two components, as well as
the dynamic separation factor defined by Equation 2.6. We find that the pore packing
48
and formation of the clusters have profound consequences for separation of a
supercritical fluid mixture into its components. More specifically, we find that,
(1) in the pore with a size near the optimal size Hm = 1.67 1σ , the permeances
(and the permeabilities Ki ) of the two components vary nonmonotonically with
increasing pressure drop PΔ along the pore. This is demonstrated in Figure 2.15,
where we show the fluxes of the two components in an equimolar mixture, along
with their permeances, and together with the corresponding separation factors. In this
figure, the upstream pressure is fixed at 120 atm, while the downstream pressure
varies. These results indicate that,
(2) there is an optimal pore size and optimal pressure drop PΔ for the
separation of the two components at which the separation factor is maximum:
whereas in larger pores decreases monotonically with increasing , in the
smaller pores with a size close to H
21S
21S PΔ
m = 1.67 1σ , the separation factor reaches a
maximum value at a certain value of PΔ , beyond which it decreases monotonically
with increasing . To demonstrate this, we present in Figure 2.16 the same
quantities as in Figure 2.15, under precisely the same conditions, except that the pore
size is now H = 5
PΔ
1σ . In this case, no maximum is seen in the separation factor. This
behavior persists for other mixture compositions. For example, Figure 2.17 presents
the same results as in Figure 2.16, except that the CO2 mole fraction in the mixture is
x2 = 0.9 . The physical reason for this novel, and unexpected, result may be as
follows.
49
We have fixed the upstream pressure at 120 atm, which is significantly
above the minimum pressure for supercriticality of the mixture, and have varied
the downstream pressure over a range of values that includes both supercritical
and subcritical conditions. If , the downstream pressure, is equal to , then the
only possible mechanism of transport in the pore is molecular diffusion. However,
since under supercritical conditions the fluid mixture is in a liquid-like state, and the
pore is very small, one may have a saturation effect, in which the pore is filled with
the molecules with a very small, if any, gradient in the concentrations, as a result of
which diffusion alone is an inefficient mechanism of transport in the pore, and,
therefore, the separation factor is relatively low. Suppose that is held fixed, and
the downstream pressure is decreased from its initial value = . As soon as
, there will be a net convective flux in the pore. Since CO
1P
cP
2P
2P 1P
1P
2P 2P 1P
21 PP ≠ 2 is in a liquid-like
state in much larger amounts than CH4, transport of its clusters helps carry CO2 in
amounts that are much larger than CH4, as a result of which the separation of the two
fluids improves, and hence the separation factor increases. Thus, as the downstream
pressure decreases, hence increasing the overall pressure drop , both
convection and diffusion of fluid clusters increase, and therefore the separation
factor also increases. Thus, the separation of the two fluids must be maximum at a
downstream pressure (with a corresponding value of the overall pressure drop
) which is just above the minimum pressure for supercriticality of the
2P PΔ
2P
PΔ cP
50
mixture, since a downstream pressure ensures that the mixture will be in a
liquid-like state in the entire pore. However, if the downstream pressure
decreases below , then as the fluid molecules approach the downstream region of
the pore, they make a transition from liquid-like states to gas-like state in which most
of the CO
cPP >2
2P
cP
2 is distributed in the slow region of the pore near its walls, as a result of
which convection and diffusion of the clusters will no longer be as effective in
transporting the molecules. Therefore, for cPP <2 the separation of the fluids must
be less efficient, and thus the separation factor must decrease beyond its maximum.
This phenomenon will not be as effective in larger pores, where there is less
condensation and the saturation effect is also less severe, which explains why the
maximum in the separation factor for larger pores is not as large and distinct as the
one for the smallest pore with a size near 1.67 1σ .
We may then conclude there must indeed be an optimal pore size and an
optimal pressure drop for which the separation of the two fluids is most efficient, a
discovery with potentially very important consequences for practical applications. It
would then be very interesting to compute the optimal PΔ for a realistic model of a
nanoporous membrane, such as the one developed by our group (Ghassemzadeh et
al., 2000; Xu, Sahimi et al., 2000; Xu et al., 2001) which consisted of a molecular
network of interconnected pores with distributed sizes. Work in this direction is in
progress.
51
We also studied the temperature- and composition-dependence of the
permeances and the corresponding separation factors. Shown in Figure 2.18 are these
quantities at two temperatures and several CO2 mole fractions in the two CVs. The
downstream pressure is 20 atm, while the pore size is 1.67 1σ . The permeance of
CH4 is affected only weakly by both the temperature and composition of the mixture,
while the permeance of CO2 appears to depend rather strongly the feed composition.
The separation factor, on the other hand, depends only mildly on the feed
composition.
Figure 2.19 presents the temperature-dependence of the permeances and the
corresponding separation factors for two downstream pressures (the upstream
pressure is 120 atm). For a downstream pressure of 90 atm, the CO2 permeance
reaches a maxium at T = 100°C, beyond which it decreases with increasing
temperature, which is in agreement with the experimental observations (Afrane and
Chimowitz, 1993, 1996; Chimowitz and Afrane, 1996; Fujii et al., 1996; Kelley and
Chimowitz, 1990; Muller et al., 1989; Nakamura et al., 1994; Ohya et al., 1993;
Sarrade et al., 1996; Semenova et al., 1992b,1992a; Tokunaga et al., 1997). The
same trend is not seen for a downstream pressure of 110 atm, but this is probably
because the upstream and downstream pressures are close to each other, hence
rendering convection ineffective in transporting the molecules. The separation factor
, on the other hand, appears to be a relatively weak function of the temperature.
This is also illustrated in Figure 2.19. It appears that the maximum separation factor
is reached at T = 40°C, when the downstream pressure is 90 atm, while it decreases
21S
52
monotonically with the temperature, when the downstream pressure is 110 atm, very
close to the upstream pressure (of 120 atm), hence making convection an inefficient
mechanism of molecular transport.
2.7 Summary Extensive molecular simulations, using the dual control-volume-nonequilibrium
molecular dynamics method, were carried out to study transport and separation of
binary mixtures of supercritical CO2 and CH4 in a carbon nanopore. The driving
force was a pressure (chemical potential) gradient. The effect of the pore size, the
composition of the feed, the temperature of the system, as well as the applied
pressure gradient on the transport and separation of the mixtures were all studied.
Among these factors, the pore size and the applied pressure gradient strongly affect
the separation process. In particular, if the upstream and downstream pressures are
both above the critical pressure for the supercriticality of the mixture, then there is an
optimal pressure gradient for maximum separation of the mixture into its
components. The pore size plays a similar role, namely, there is an optimal pore size
for the separation of the fluid mixtures. These results, if confirmed by a realistic
model of a nanoporous membrane with interconnected pores, will have important
implications for the design of such membranes for use under supercritical conditions.
53
A closely related phenomenon is the formation of dynamic clusters of the
fluids' molecules that pack the pore and travel its entire length under an applied
pressure gradient. The sizes of the clusters oscillate with the time. This phenomenon
is closely tied to formation of multilayers of the fluids' molecules that pack the pore,
and is, in fact, primarily responsible for the existence of an optimal pressure gradient
for maximum separation of a supercritical fluid mixture into its components.
54
Figure 2.1: Schematics of the slit pore used in the simulations. The h and l regions represent the high- and low-pressure control volumes respectively.
55
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-60 -40 -20 0 20 40 60X*
Tem
pera
ture
Figure 2.2: Dimensionless temperature distribution in the pore containing an equimolar mixture of CO2 and CH4. The upstream pressure in both cases is 120 atm, while the downstream pressures are 90 atm (top) and 20 atm (bottom). The pore size is 1.67 1σ . Dashed lines indicate the boundaries of the pore region.
56
0.1
0.2
0.3
0.4
-50 -30 -10 10 30 50X*
Den
sity
of C
O2
0.04
0.08
0.12
0.16
-50 -30 -10 10 30 50X*
Den
sity
of C
H4
Figure 2.3: Time-averaged density profiles in the transport direction x in a pore of size 5 1σ , containing an equimolar mixture of the two components at T = 40°C. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (open triangles), 50 atm (open circles), 70 atm (solid triangles), and 100 atm (solid circles). Dashed lines indicate the boundaries of the pore region.
57
-2
0
2
Z*
-2
0
2Z*
-2
0
2
10 12 14 16 18 20X*
Z*
Figure 2.4: The distribution of CO2 (circles) and CH4 (triangles) in a pore of size 5 1σ , containing an equimolar mixture at T = 40°C. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 70 atm (middle) and 100 atm (bottom).
58
0.1
0.2
0.3
0.4
0.5
-50 -30 -10 10 30 50
X*
Den
sity
of C
O2
0.00
0.02
0.04
0.06
-50 -30 -10 10 30 50
X*
Den
sity
of C
H4
Figure 2.5: Time-averaged density profiles in the transport direction x in a pore of size 5 1σ , containing a mixture of CO2 and CH4 with a CO2 mole fraction of x2 = 0.9 at T = 40°C. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (open triangles), 50 atm (circles), and 70 atm (solid triangles. Dashed lines indicate the boundaries of the pore region.
59
0.20
0.25
0.30
0.35
0.40
-50 -30 -10 10 30 50
X*
Den
sity
0.05
0.10
0.15
0.20
-50 -30 -10 10 30 50
X*
Den
sity
Figure 2.6: Comparison of the density profiles of CO2 (top) and CH4 (bottom), computed after 3.5 million times steps (dashed curves) and 5 million time steps (solid curves). All other parameters of the system are the same as those in Figure 2.3. The upstream and downstream pressure are, respectively, 120 atm and 90 atm. Dashed lines indicate the boundaries of the pore region.
60
0 < X* < 1
-2
-1
0
1
2
0.0 0.4 0.8 1.2 1.6 2.0 2.4
Density
-20 < X* < -19
-2
-1
0
1
2
0.0 0.4 0.8 1.2 1.6 2.0 2.4
Density
Z* Z*
19 < X* < 20
-2
-1
0
1
2
0.0 0.4 0.8 1.2 1.6 2.0 2.4
Density
Z*
-2
-1
0
1
2
-25 -20 -15 -10 -5 0 5 10 15 20 25X*
Z*
Figure 2.7: Time-averaged density profiles between the upper and lower walls, in three different regions of a pore of size 5 1σ , containing an equimolar mixture of CO2 (dashed curve) and CH4 (solid curve) at T = 40°C. The upstream and downstream pressures are, respectively, 120 atm and 70 atm. Also shown is the distribution of the molecules in the pore. The arrows indicate the boundaries of the pore region.
61
-20 < X* < -19
-2
-1
0
1
2
0 0.1 0.2 0.3 0.4
Density
Z*
Figure 2.8: Same as in Figure 2.7, except that the upstream and downstream pressures are, respectively, 3 atm and 1 atm.
62
-10 < X* < -9
-2
-1
0
1
2
0.0 0.4 0.8 1.2 1.6
Density
- 20 < X* < -19
-2
-1
0
1
2
0.0 0.4 0.8 1.2 1.6
Density
Z* Z*
0 < X*< 1
-2
-1
0
1
2
0.0 0.4 0.8 1.2 1.6
Density
Z*
-2
-1
0
1
2
25 -20 -15 -10 -5 0 5 10 15 20 25X*
Z*
-
Figure 2.9: Same as in Figure 2.7, except that the upstream and downstream pressures are, respectively, 120 atm and 1 atm.
63
-20 < X* < -19
-2
-1
0
1
2
0 0.4 0.8 1.2 1.6 2 2.4 2.8
Density
Z*
0 < X* < 1
-2
-1
0
1
2
0 0.4 0.8 1.2 1.6 2 2.4 2.8
Density
Z*
19 < X* < 20
-2
-1
0
1
2
0 0.4 0.8 1.2 1.6 2 2.4 2.8
Density
Z*
Figure 2.10: Same as in Figure 2.7, except that the mole fraction of CO2 in the mixture is x2 =0.9.
64
-2
-1
0
1
2
Z*
-2
-1
0
1
2Z*
Figure 2.11: The distribution of the molecular clusters after 5 × 105 (top), 106 (middle) and 1.5 × 106 (bottom) time steps, in a pore of size 5 1σ , containing an equimolar mixture of CO2 and CH4 at T = 40 °C. The upstream and downstream pressures are both 120 atm. Numbers indicate the size of the clusters.
147 87 85 73 72 66 61 55 53 52 47 40 39 37 36 35 31
-2
-1
0
1
2
-20 -15 -10 -5 0 5 10 15 20X*
Z*
65
0
40
80
120
160
200
5.1 5.2 5.3 5.4 5.5
Time x 10-6
Clu
ster
Siz
e
CO2
CH4
Mixture
0
20
40
60
80
5.1 5.2 5.3 5.4 5.5
Time x 10-6
Clu
ster
Siz
e
CO2
CH4
Mixture
Figure 2.12: Time dependence of the size of the largest clusters in a pore of size 5 1σ (left) and 1.67 1σ (right), containing an equimolar mixture of CO2 and CH4 at T = 40°C. The upstream and downstream pressures are, respectively, 120 atm and 70 atm.
66
0
10
20
30
40
50
5.1 5.2 5.3 5.4 5.5Time × 10-6
Num
ber o
f Clu
ster
s
6-9
26-45
4-5
10-12
13-1516-25
0
10
20
30
5.1 5.2 5.3 5.4 5.5
Time × 10-6
Num
ber
of C
lust
ers 4-5
26-45
6-9
10-12
13-1516-25
Figure 2.13: Time-dependence of the size distribution of the molecular clusters. All the parameters are the same as those in Figure 2.12. Numbers next to the curves indicate the size of the clusters.
67
0
5
10
15
20
25
30
35
40
45
50
4-5 6-9 10-12 13-15 16-25 26-45
Cluster Size
Num
ber o
f Clu
ster
s
Figure 2.14: Cluster size distribution ns(t) in a pore of size 5 1σ , containing an equimolar mixture of CO2 and CH4 at T = 40 °C. The results are for times 5.1 × 106 (◊), 5.2 × 106 ( ), 5.4 × 106 (ο), and 5.5 × 106 (Δ).
68
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
10 20 30 40 50 60 70 80 90 100
ΔP
Flux
CH4
CO2
1.5
2.0
2.5
3.0
3.5
4.0
10 20 30 40 50 60 70 80 90 100
ΔP
Sepa
ratio
n Fa
ctor
0.0000
0.0005
0.0010
0.0015
0.0020
0.0025
0.0030
10 20 30 40 50 60 70 80 90 100
ΔP
Perm
eanc
e
CO2
CH4
Figure 2.15: The dependence of the flux and permeance of CO2 and CH4, and the corresponding separation factor, on the pressure drop PΔ applied to a pore of size 1.67 1σ at T = 40°C. The mixture is equimolar, with the upstream pressure being 120 atm.
69
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
10 20 30 40 50 60 70 80 90 100
ΔP
Flux
CO2
CH4
1.5
2.0
2.5
3.0
3.5
4.0
10 20 30 40 50 60 70 80 90 100
ΔP
Sepa
ratio
n Fa
ctor
0.0000
0.0005
0.0010
0.0015
0.0020
0.0025
0.0030
10 20 30 40 50 60 70 80 90 100
ΔP
Perm
eanc
e
CO2
CH4
Figure 2.16: Same as in Figure 2.15, but for a pore of size 5 1σ .
70
0.0000
0.0005
0.0010
0.0015
0.0020
0.0025
0.0030
50 60 70 80 90 100
ΔP
Perm
eanc
e
CO2
CH4
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
50 60 70 80 90 100
ΔP
Flux
CO2
CH4
0.9
1.2
1.5
1.8
2.1
2.4
2.7
50 60 70 80 90 100
ΔP
Sepa
ratio
n Fa
ctor
Figure 2.17: Same as in Figure 2.15, but for a pore of size 5 1σ and CO2 mole fraction of 2x =0.9.
71
0.000
0.001
0.001
0.002
0.002
0.003
0.003
0.3 0.4 0.5 0.6 0.7 0.8 0.9
Mole Fraction of CO2
Perm
eanc
e
1
2
3
4
5
6
0.3 0.4 0.5 0.6 0.7 0.8 0.9
Mole Fraction of CO2
Sepa
ratio
n Fa
ctor
Figure 2.18: Dependence of the permeance of CO2 (solid curves) and CH4 (dashed curves), and the corresponding separation factors, on the mole fraction of CO2 in the feed, in a pore of size 1.67 1σ at T = 40°C (circles) and 100°C (triangles). The upstream and downstream pressures are, respectively, 120 atm and 20 atm.
72
1.0
1.5
2.0
2.5
3.0
3.5
4.0
0 20 40 60 80 100 120 140 160
Temperature (°C)
Sepa
ratio
n Fa
ctor
0.0000
0.0005
0.0010
0.0015
0.0020
0 20 40 60 80 100 120 140 160
Temperature (°C)
Perm
eanc
e
Figure 2.19: Temperature-dependence of the permeance of CO2 (solid symbols) and CH4 (open symbols), and the corresponding separation factors, for a pore of size 1.67 1σ and downstream pressures of 90 atm (squares) and 110 atm (triangles). The upstream pressure is 120 atm, and the mixture is equimolar.
73
Chapter 3 Transport and Separation of Carbon Dioxide-Alkane Mixtures in Carbon Nanopores 3.1 Introduction
here is a considerable practical and theoretical interest in developing
predictive models and understanding the effect of chemical structure for the
separation and transport properties of alkanes. A better understanding of the
separation of alkane mixtures, as well as their mixtures with other gases, is important
for the optimization of chemical and petrochemical industries. Membrane separation
appears to be a promising candidate for alkene/alkane separation, with the process
recognized by the petrochemical industry to be a key technology.
T
Molecular dynamics simulations have been used to study the dynamic
behavior of alkane chains in bulk conditions. In this chapter, we focus on separation
of mixtures of normal alkanes (n-alkanes), and also mixtures of CO2 and an n-alkane,
by carbon molecular-sieve membranes (CMSMs). Although separation of n-alkanes
by zeolites has been studied by many groups (Funke et al., 1996; Kapteijn et al.,
1995; Kusakabe et al., 1996; Van de Graaf et al., 1999; Vroon et al., 1996), our
study, to our knowledge, is the first that investigates their separation by CMSMs. In
this chapter, we report our preliminary results of experimental studies and molecular
74
simulation of transport and separation of several binary mixtures involving n-alkanes
in CMSM. Our molecular modeling is based on nonequilibrium molecular dynamics
(NEMD) simulations. We utilize a dual control-volume grand-canonical MD (DCV-
GCMD) technique. The alkane chains are generated by the configurational-bias
Monte Carlo method. To our knowledge, this is the first time that the DCV-GCMD
method is combined with the configurational-bias Monte Carlo technique.
The plan of this chapter is as follows. In the next section, we describe the
pore model that we employ in our simulations. Next, the molecular models of the
gases are described, after which we describe the growth of the alkane chains by the
configurational-bias Monte Carlo method. We then describe the DCV-GCMD
technique. The results are then presented and analyzed.
3.2 Model of Carbon Nanopore The pore model we used here is exactly the same as in Section 2.2. The dimensions
of the pore used are, W = 20σ1 and L = 40σ1, while its height H was varied, in the
range of typical pore sizes for which CMSM exhibit molecular sieving properties, in
order to study the effect of the pore size on the results. Here, σ1 is the effective
molecular size of CH4 (see below).
75
3.3 Molecular Models of the Gases and the Interaction Potentials We consider binary mixtures of CH4/C3H8, CH4/C4H10, and CO2/C3H8. The CH4 and
CO2 molecules are represented as Lennard-Jones (LJ) spheres, characterized by
effective LJ size and energy parameters, σ and ε. All the quantities of interest are
made dimensionless with the help of the CH4 parameters, σ1 and ε1. Table 2.1 lists
the conversions between the dimensionless and dimensional quantities.
The C3H8 and C4H10 molecules are grown by a configurational-bias Monte
Carlo method, which is described in the next section. These molecules are
represented by a united-atom (UA) model (Ryckaert and Bellemans, 1978) in which
the CH2 and CH3 groups are considered as single interaction centers with their own
effective potentials. The nonbonded interactions between interaction centers of
different molecules are described with a cut-and-shifted LJ potential with rc =
11.43Å. No tail corrections were applied to this potential. The Lorentz-Berthelot
mixing rules were used in the simulations to compute the size and energy parameters
of the unlike molecules (see Section 2.4). We utilized smooth pore walls and the
Steele potential was used to calculate the interaction between a molecule and the
wall (see Section 2.4).
For simplicity the total molecular mass of alkane was equally divided
between the C atoms, and therefore CH2 and CH3 groups had equal molecular mass.
Table 3.1 lists the size and energy parameters of CH4, CO2, and those of the CH2 and
CH3 groups.
76
Table 3.1: Values of the molecular parameters used in the simulations. kB is the Boltzmann’s constant.
B
Parameter Numerical Value
2CHσ (Å) 3.905
3CHσ (Å) 3.905
4CHσ (Å) 3.810
2COσ (Å) 3.794
2
/CH Bkε (K) 59.38
3
/CH Bkε (K) 88.06
4
/CH Bkε (K) 148.1
2
/CO Bkε (K) 225.3
Bond length (Å) 1.53 kθ (K rad -2) 62,500
0θ (degrees) 112
(K) 1116 0C
(K) 1462 1C
(K) -1578 2C
(K) -368 3C
(K) 3156 4C
(K) -3788 5C
The atoms and the UA centers are connected by harmonic potentials. The
distance between the atoms is fixed at 1.53Å. The intramolecular interactions consist
77
of the contributions by bond-bending (BB) and torsional forces. For the BB term, the
van der Ploeg-Berendsen potential (Van der Ploeg and Berendsen, 1982) is used:
20
1( ) ( )2BBU kθθ θ θ= − (3.1)
where θ is the angle between the atomic bonds. For the torsional potential, the
Ryckaert-Bellemans (Ryckaert and Bellemans, 1975) potential is used:
5
0( ) cos ( )k
tor kk
U cφ φ=
= ∑ (3.2)
where φ is the dihedral angle. Numerical values of all the parameters are listed in
Table 3.1. The 10-4-3 potential of Steele was used to compute the interaction
between a molecule and the wall with the same parameter as mentioned in Section
2.4.
3.4 Configurational-Bias Monte Carlo Method Because direct generation of the n-alkanes and their insertion into the CVs that are
connected to the nanopore greatly slows down the simulations, we used the
configurational-bias Monte Carlo (CBMC) technique (De Pablo et al., 1992; Frenkel
et al., 1991; Harris and Rice, 1988; Laso et al., 1992; Macedonia and Maginn, 1999;
Mooij et al., 1992; Siepmann and Frenkel, 1992; Smit et al., 1995) to grow the
alkane molecules. We then combined the CBMC method with the grand-canonical
MC technique to insert the grown alkane chains in the two CVs and, therefore, in the
nanopore. The atom-by-atom growth of the molecules is done in such a way that
78
regions of favorable energy are identified, and overlap with other molecules is
avoided, hence speeding-up the computations greatly.
More specifically, we consider the potential energy of an atom as the sum of
two contributions: (1) the internal energy uint, which includes parts of the
intramolecular interactions, and (2) the external energy uext, which contains the
intermolecular interactions and those intramolecular interactions that are not part of
the internal energy. The division is, of course, to some extent arbitrary and depends
on the details of the model. The following procedure is then used to grow an n-
alkane atom by atom (Smit et al., 1995).
(i) We insert the first atom at a random position, and compute the energy
u1(n) along with a quantity w1, which is similar to a Boltzmann factor,
[ ]1 1( ) exp ( )w n u nβ= − (3.3)
where , with being the Boltmann’s constant, T is the temperature of the 1( )Bk Tβ −= Bk
system, and n indicates the new state in which the system is in.
(ii) We then generate k trial orientations, denoted by { } 1 2, ,... kk=b b b b , in
order to insert the next atom l. These orientations are generated with a probability
which is a function of the internal energy: int ( )l ip b
int int1( ) exp ( )l i l ip b uC
β⎡ ⎤= −⎣ ⎦b (3.4)
where C is a normalization factor. For each of these trial orientations, the external
energy is also computed, along with the quantity ex ( )tl iu b
79
(3.5) 1
( ) exp[ ( )]k
extl
jw n uβ
=
= −∑ bl j
We then select one orientation, out of the k trial positions, with the probability
1( ) exp[ ( )]( )
ext extl i l i
l
p b uw n
β= − b (3.6)
We typically generated five trial orientations for propane and butane chain
molecules, since our preliminary simulations with as many as k = 20 trial
orientations did not result in large differences.
(iii) We repeat step (ii) M - 1 times until the entire alkane molecule is grown,
and the Rosenbluth factor (Rosenbluth and Rosenbluth, 1955) W(n) of the molecule
is calculated:
(3.7) 1
( ) ( )M
ll
W n w n=
= ∏
As mentioned above, this algorithm biases the insertion of a molecule in such a way
that regions with favorable energy are found, and overlap with other atoms is
avoided. Any given molecular conformation is generated with a probability given by
{ }int int
2 2
1
1( ) ( ) ( ) exp [ ( ) ( )]( )
1 exp[ ( )]( )
M Mext ext
l l l ll l l
M
P n p n p n u n u nCw n
U nC W n
β
β
= =
−
= = − +
= −
∏ ∏ (3.8)
where the total energy of the inserted molecule is, . int
1 1( )
M Mext
l l ll l
U u u u= =
= = +∑ ∑
The above algorithm constitutes the CBMC technique. It must be
supplemented with acceptance rules that remove the bias from the insertion step.
80
These rules depend on the type of the move and of the ensemble used in the
simulations.
3.5 Configurational-Bias Grand-Canonical Monte Carlo Method After generating the n-alkanes and accepting them, the next step is to insert them into
the CVs. To do this, we combine the CBMC method described above with a grand-
canonical MC method and refer to it as the CBGCMC technique. This is a method of
computing the sorption thermodynamics of linear-chain molecules when the sorbates
are represented with a UA force field and have flexible dihedral and bond angles.
This method consists of two steps. First, it generates the chain configurations one
atom at a time by the CBMC method described above. Second, as the chain molecule
is generated, the Rosenbluth weight (Rosenbluth and Rosenbluth, 1955) W is
accumulated and utilized in the acceptance rule of the GCMC method for insertion of
the molecules into the system.
The probability of adding a single chain to a system of Ni chains is given by
(Macedonia and Maginn, 1999),
3
exp( )min ( ),1( 1)
i ci
i i
VpNβμ+ W n
⎧ ⎫= ⎨ ⎬Λ +⎩ ⎭
(3.9)
where µi is the chemical potential of chain i, V is the volume of the CV, and iΛ is
the thermal de Broglie wavelength of component i. Equation (3.9) is completely
similar to the probability of inserting a molecule into a system in a standard GCMC
81
computations, with the main difference being the inclusion of the Rosenbluth weight
W. For a deletion from the system, the Rosenbluth weight is evaluated by pretending
to grow the alkane chain into its current position. To accomplish this, the
quantities, [ ]1 1( ) exp ( )w o u oβ= − , '
1( ) exp ( )
kext
l l jj
w o uβ=
⎡ ⎤= −⎣ ⎦∑ b 1( ) ( )Ml lw o== Π, and W o
are computed, using k - 1 trial orientations, together with the actual current position
of the atom l, which form the set , where o indicates the old state of the
molecules. The probability of deletion of a chain from the system is then given by
'{ }kb
3 1min ,1
exp( ) ( )i i
ii c
NpV W oβμ
− ⎧ ⎫Λ= ⎨ ⎬
⎩ ⎭ (3.10)
which, aside from the Rosenbluth weight, is again similar to that of a standard
GCMC computation. To insert the CO2 and CH4 molecules in the two CVs, the
probabilities and are computed according to the standard GCMC method,
namely, the Rosenbluth factor W is replaced by
ip+ip−
exp( )Uβ− Δ , where is the
potential energy change of the system as a result of adding or removing a particle to
the CVs.
UΔ
3.6 Non-equilibrium Molecular Dynamics Simulations The NEMD simulations consist of integration of Newton’s equation of motion in the
entire system, combined with the CBGCMC insertions and deletions in the two CVs.
In the MD simulations the Verlet velocity algorithm was used to solve the equations
82
of motion. During the motion of the n-alkanes in the system, the RATTLE algorithm
(Andersen, 1983) was used to satisfy the constraints imposed on the n-alkane chains.
Iso-kinetic conditions were maintained by rescaling the velocity independently in all
the three directions. It is essential to maintain the densities of each component in the
two CVs at some fixed values, which are in equilibrium with two bulk phases, each
at a fixed pressure and fluid concentration. The densities, or the corresponding
chemical potentials of each component in the CVs, were maintained by carrying out
a sufficient number of CBGCMC insertions and deletions of the particles, as
described above. The chemical potentials were converted to equivalent pressures
using a LJ equation of state (Johnson et al., 1993).
When a molecule is inserted in a CV, it is assigned a thermal velocity
selected from the Maxwell-Boltzmann distribution at the given temperature T. An
important parameter of the NEMD simulations is the ratio Ρ of the number of
CBGCMC insertions and deletions in each CV to the number of MD steps between
successive CBGCMC steps. This ratio must be chosen appropriately in order to
maintain the correct density and chemical potentials in the CVs, and also reasonable
transport rates at the boundaries between the CVs and the pore region. In our
simulations, Ρ was typically 10. During the MD computations molecules crossing
the outer boundaries of the CVs were removed. The number of such molecules was,
however, very small, typically about 1% of the total number of molecules that were
deleted during the CBGCMC simulations with a probability that is given by
Equation 3.10. In addition, for each component we allowed for a nonzero streaming
83
velocity (the ratio of the flux to the concentration of each component) in the pore
region, consistent with the presence of bulk pressure/chemical potential gradients
along the flow direction. Since the two CVs are assumed to be well-mixed and in
equilibrium with the two bulk phases that are in direct contact with them, there
should be no overall nonzero streaming velocity in these regions. However, the
discontinuity of the streaming velocities at the boundaries between the CVs and the
pore region slows down the computations. To address this problem, a very small
streaming velocity was added to the thermal velocity of all the inserted molecules
within each CV that were located within a very small distance from the boundaries
between the CVs and the pore (Arya et al., 2001; Firouzi et al., 2003; Martin et al.,
2001; Xu et al., 1998, 1999; Xu, Sedigh et al., 2000; Xu, Sahimi et al., 2000). In the
case of the n-alkanes, this was done when the lead atom or UA center was within that
small distance, in which case the small velocity was assigned to all of the atoms and
UA center of the alkanes. However, the actual streaming velocities of the molecules
in the transport pore region were still determined by the MD simulations. To study
the transport of a mixture due to a pressure gradient, the temperature of the system
must be held constant in order to eliminate any contribution of the temperature
gradient to the transport; hence special care was taken to achieve this (see also
below).
We computed several quantities of interest, including the density profiles of
the component i along the x- and z-directions, ( )zi xρ and , respectively. To
calculate
( )xi zρ
( )zi xρ and we used the same method as discussed in Chapter 2 (Sec. ( )x
i zρ
84
2.5). For each component i we also calculated its flux Ji by measuring the net
number of its particles crossing a given yz plane of area Ayz as discussed in Chapter 2
(Sec. 2.5).
We used a dimensionless time step, tΔ * = 5 × 10-3, which is equivalent to,
= 0.00685 ps, and NtΔ MD = 30,000. The system was considered to have reached a
steady state, when the fluxes calculated at various yz planes were within 5% from the
averaged values, after which the fluxes were calculated at the center of the pore
region. The equations of motion were integrated with up to 3 × 106 time steps. The
permeability Ki of species i and dynamic separation factor S21 were calculated using
the same equations as defined in Chapter2 (Sec. 2.5)
3.7 Experimental Study Transport and separation properties of three mixtures, namely, CH4/C3H8, CO2/CH4,
and CO2/C3H8 mixtures, have also been measured in a CMSM by our colleague Kh.
Molaai Nezhad. The average pore size of the membrane is about 4.5Å, which is in
the range of the pore sizes used in our simulations. The techniques for preparation of
the membrane, as well as measuring its transport and separation properties, have all
been described previously (Sedigh et al., 1998, 1999, 2000), and need not be
repeated here. All the experiments were carried out at T = 50°C. The pressure drop
85
that was applied to the membrane was the same as the one used in the molecular
simulations.
3.8 Results and Discussions We have carried out extensive NEMD simulations of three binary mixtures involving
an n-alkane. In what follows, we present and discuss the results for each mixture
separately, and compare the results with our experimental data, when possible.
Unless otherwise specified, in all the cases discussed below, the pressures in the
upstream and downstream CVs, that are in equilibrium with the two bulk states, are 3
atm and 1 atm, respectively.
3.8.1 Methane-Propane Mixtures Figure 3.1 presents the time-averaged distribution of the dimensionless temperature
in the carbon nanopore, for two different binary mixtures of CH4 and C3H8. In this
and the subsequent figures, the dashed lines indicate the boundaries of the pore
region. The pore size is 4
* / CHH H 5σ= = , the mole fractions of CH4 in the two
mixtures are 0.5 and 0.7 and, in both cases, the temperature of the system is set at T
= 50°C. As can be seen, the temperature in both cases is constant throughout the pore
and its two CVs and, moreover, the two systems’ temperatures are equal, as they
should be.
86
Figure 3.2 shows a snapshot of the mixture in a pore of size at T =
50°C, in which the mole fraction of CH
* 5H =
4 in the feed is 0.9. Both components are
mostly distributed near the pores’ walls by forming two condensed layers there.
These results are also consistent with equilibrium molecular simulations. The
densities of both components decrease from left to right. To understand better the
distribution shown in Figure 3.2, we present in Figure 3.3 the density profiles of the
two components, in two different mixtures, over the cross-section of a pore of size
, computed near its center. In the mixture in which the mole fraction of CH* 5H = 4
in the feed is 0.9 (the bottom panel), the two density profiles are almost identical,
except that the CH4 density is somewhat larger near the center, which is consistent
with the snapshot of the system shown in Figure 3.2. However, in the equimolar
mixture (top panel), the density of propane is larger than that of CH4 everywhere in
the pore. This is due to the much larger density of C3H8 under the bulk conditions (in
the two CVs), which results in much larger amounts of propane entering the pore. At
the same time, the C3H8 chains have a “shielding” effect in that; they prevent CH4
from entering the pore region. Reducing the size of the pore shifts the profiles to the
pore’s center, since the location of the fluid-wall potential minima changes: Shown
in Figure 3.4 is the comparison between such density profiles for a mixture in which
the CH4 mole fraction in the feed is 0.7, in pores of sizes *H = 5, 3 and 1.75 at T =
50°C. In all the cases, the density of C3H8 is much larger than that of CH4, since the
shielding effect mentioned above is even stronger for tighter pores. The fact that, in
all cases, there is great overlap between the two density profiles is indicative of the
87
mixture’s tendency not to segregate into two distinct regions, each essentially filled
with one of the components.
Another way of understanding the density profiles shown in Figures 3.3 and
3.4 is as follows. If we were to represent C3H8 as a simple LJ sphere, then its
effective energy parameter 3 8C Hε would be larger than
4CHε by a factor of about 1.6.
Since the energy parameters control the interaction of the molecules with the pore’s
walls, it becomes clear why the density of C3H8 near the walls is much larger than
that of CH4, since it is energetically more favorable for C3H8 to adsorb on the pore’s
walls than CH4. On the other hand, the effective LJ size parameter of C3H8 is not
much larger than that of CH4, hence explaining why the locations of the peaks in the
density profiles of the two components are not far apart.
To shed further light on the properties of this system, we also study the
density profiles in the two CVs and the pore along the transport (x-) direction. These
are shown in Figure 3.5, where we present the time-averaged density profiles for
both components in two different mixtures in a pore of size . The density
profiles are essentially flat in the two CVs (in the region -60 < X* < -20 and 20 < X*
< 60), with numerical values that match those obtained by the standard GCMC
method under the same conditions, indicating that the chemical potentials in the two
CVs have been properly maintained during the NEMD simulations. The small
fluctuations in the profiles in the CV regions represent numerical noise. The small
downward curvature at X* = -60 (in the C
* 5H =
3H8 profile) is due to the “leakage” of the
molecules out of the two CVs. These are the molecules that, as described above,
88
cross the outer boundaries of the CVs and leave the system. However, such
deviations from a flat profile are insignificant. Note that even when the mole fraction
of C3H8 in the feed is only 0.3 (top panel), its density in the two CVs is much larger
than that of CH4. In the pore region (-20 < X* < 20), the two profiles decrease from
left to right, which is expected. Due to the existence of the overall bulk pressure
gradient (or an overall nonzero streaming velocity in the pore), however, the density
profiles are not linear, and as the total flux is the sum of the diffusive and convective
parts, resulting in nonlinear profiles for C3H8 in both mixtures. For CH4, on the other
hand, the convective effect is much weaker, and, therefore, the decrease in its density
and the associated nonlinearity are also much weaker. The qualitative aspects of the
profiles shown in Figure 3.5 will not change if we impose a larger pressure gradient
on the pore system. Shown in Figure 3.6 are the density profiles of the two
components along the transport direction for two different systems. In one (the top
panel) the upstream and downstream pressures are, respectively, 3 atm and 1 atm,
while the corresponding pressures in the second pore system (the bottom panel) are
ten times larger, 30 atm and 10 atm. The pore size for both cases is . The CH* 5H = 4
mole fraction in the feed for both cases is 0.9, and the simulations were carried out at
T = 50°C. All the qualitative aspects of Figures 3.5 and 3.6 are similar, except that
the densities and their fluctuations in the pore under the larger pressure gradient are
somewhat larger, as one might expect. These fluctuations will eventually vanish if
the simulations are continued for much longer times. Our simulations also indicate
that the separation factor of this system is insensitive to the applied pressure
89
gradient. At the same time, the qualitative features of these profiles are not very
sensitive to the pore size (unless, of course, the pore is too small). We show in Figure
3.7 the density profiles in a pore of size * 3H = . The CH4 mole fraction in the feed is
0.7, with the rest of the parameters being the same as in Figures 3.5 and 3.6. The
similarities between these profiles and those shown in Figures 3.5 and 3.6 are clear.
Figures 3.8 present the dependence of the permeance (permeability per unit
length of the pore) of the two components on the temperature and feed composition,
and compare them with the experimental data. Several features of these figures are
noteworthy:
(1) The experimental permeances are about two orders of magnitude smaller
than those obtained by the molecular simulations. This is expected, as the CMSM
possesses a tortuous three-dimensional pore space, and therefore the gas permeances
of such a pore space must be smaller than those of a single straight pore with no
spatial tortuosity.
(2) Both the simulations and experiments indicate that the permeances are not
very sensitive to the composition of the mixture in the feed. For example, as the mole
fraction of C3H8 in the feed increases from 0.5 to 0.9, its permeance (both computed
and measured) changes by a factor which is less than 2, and an even smaller change
is seen in the permeance of CH4.
(3) The permeance of CH4 is practically independent of the temperature,
while that of C3H8 decreaeses essentially linearly with increasing temperature.
90
Figures 3.9 present the separation factor 3 8 421S /C H CHK K= for the mixture and
its dependence on the temperature and feed composition. Although both the
simulations and experiments suggest that the separation factor is not very sensitive to
the feed composition, the experimental data do not agree with the simulation results.
The reason is that, the most effective mechanism of separating a CH4/C3H8 mixture
into its components is by molecular sieving and kinetic effects (the rates of transport
of the two components), as it is much more difficult for the C3H8 chains to pass
through the membrane with the same rate as the CH4 molecules.
To study the effect of the pore size on the separation factors, we carried out
extensive simulations using a range of pore sizes. Figures 3.10 show the results for
the permeances and separation factors and their dependence on the pore size. The
mole fraction of CH4 in the feed is 0.7, and T = 50°C. Only when the pore size is
H* = 1.7, does the separation factor fall below one (its value for a pore of size
H* = 1.7 is about 0.8) and in the range of the experimental values (which, for this
mixture, is about 0.5). This critical pore size is, in fact, the same as what we
previously determined (Xu, Sedigh et al., 2000; Xu, Sahimi et al., 2000) to be the
optimal size for the separation of certain binary mixtures, such as CO2 and CH4.
Note also that, had we represented the C3H8 chains as LJ spheres, the critical pore
size would have been about H* = 2.15, indicating the significance of the proper
model of these molecules.
Therefore, to obtain quantitative results for the transport and separation
properties of binary mixtures of CH4 and C3H8, one must resort to 3D molecular pore
91
network models of CMSM (Ghassemzadeh et al., 2000; Xu, Sahimi et al., 2000; Xu
et al., 2001), in which interconnected pores of various shapes and sizes are
distributed in the space. In such a system, one may have a type of phase separation
such that the smaller pores carry CH4, while larger pores contain the C3H8 chains.
However, if the pores are not interconnected, then, no flux of the two components
can pass through the pore network. Therefore, the interconnectivity of the pores
plays a fundamental role in the separation of the two components.
3.8.2 Methane-Butane Mixtures Figure 3.11 presents a snapshot of the system at steady state in a pore of size H* = 5,
in which the mole fraction of methane in the feed is 0.9. Clearly, despite the mixture
being rich in CH4, there is a lot more C4H10 in the pore than CH4, which is again
attributed to the shielding effect described above. The corresponding time-averaged
density profiles of CH4 and n-C4H10 at T = 50°C and in the same system are shown
in Figure 3.12. Similar to the CH4/C3H8 mixtures, and consistent with Figure 3.11,
the density of n-butane is much larger than that of CH4. This feature of the system
can again be explained by defining an effective LJ energy parameter for n-butane,
which would be larger than that of CH4 by a factor of about 1.5, hence making it
energetically more favorable for n-C4H10 to form a thick layer near the pore’s walls.
At the same time, the effective LJ size parameter of n-butane is about twice as large
as that of CH4. This, together with the fact that the actual molecular structure of
92
n-butane is a chain with four atoms or UA centers, imply that as the components of
the mixture attempt to enter the pore from a CV, there is a shielding effect that
prevents many of the CH4 molecules from entering the pore, as a result of which the
density of n-butane inside the pore is much larger than that of CH4.
Figure 3.13 depicts the time-averaged density profiles of the two components
in the transport direction, both inside the two CVs and a pore of size H* = 5. The
densities of the two molecules are essentially constant in the two CVs, with the
density of n-C4H10 being much larger than that of CH4. In between the two CVs, the
two densities decrease from the upstream area to the downstream area in a nonlinear
fashion, with the nonlinearity being due to the convective effect imposed on the
system by the applied pressure gradient.
We show in Figure 3.14 the dependence of the two components’ permeances
on the temperature and feed composition, in a pore of size H* = 5. The qualitative
features of these results are similar to those for the CH4/C3H8 mixture, shown in
Figure 3.8. Once again, the CH4 permeance is essentially independent of its mole
fraction in the feed, as well as the temperature of the system, while the permeance of
n-C4H10 appears to vary linearly with both variables. As a result, the separation
factor of the pore system, defined as4 10 421S /C H CHK K= , also varies essentially
linearly with the feed composition and the temperature. In addition, the simulations,
for a range of pore sizes, yield large separation factors in favor of C4H10. Although
we do not yet have experimental data for this mixture, we suspect, based on the
CH4/C3H8 mixtures discussed above and the physics of the problem, that in real
93
membranes the separation factor would be in favor of CH4, the opposite of what the
simulations indicate. To show this, we carried out extensive simulations to
investigate the effect of the pore size on the permeances and the separation factors.
Figure 3.15 presents the results, obtained at T = 50°C, for a mixture in which the
CH4 mole fraction is 0.7. Even for a pore as small as H* = 1.7, the separation factor
is still about 2.4, indicating that a single pore is a gross representation of a
membrane, at least so far as this mixture is concerned.
Let us mention in passing that insertion of n-alkanes in a tight pore by the
configurational bias Monte Carlo method is difficult, since the atom or UA center of
the chain that is closest to the pore’s walls interacts with the walls much more
strongly than the rest of the chain. As a result, the standard CBMC method fails
when the pores are too tight and the alkane chains are initially inserted into the
system near the walls. To address this problem, we initially inserted the alkane
chains into the system only near its center.
3.8.3 Carbon Dioxide-Propane Mixtures In previous works (Firouzi et al., 2003; Sedigh et al., 1998, 1999, 2000; Xu et al.,
1998, 1999; Xu, Sedigh et al., 2000; Xu, Sahimi et al., 2000) we studied the
CO2/CH4 mixtures in carbon nanopores. Figure 3.16 presents the (time-averaged)
dimensionless temperature distribution in a pore of size H* = 5 and the two CVs,
obtained with two different mixtures of CO2 and C3H8. Once again, the temperature
94
is essentially constant throughout the entire system, indicating that the isothermal
condition has been maintained. A snapshot of the same system that contains a binary
mixture in which the CO2 mole fraction in the feed is 0.9 is shown in Figure 3.17,
indicating that most of the CO2 molecules are near the pore’s walls, forming a layer
near each wall. This is confirmed by the (time-averaged) density profiles shown in
Figure 3.18 for two different mixtures of CO2 and C3H8 in a pore of size H* = 5. The
temperature of the system is T = 50°C, and the data are collected at the center of the
pore. In the equimolar mixture (the top panel), the density of C3H8 near the walls is
much larger than that of CO2, since there is much more C3H8 in the pore than is CO2.
However, when the C3H8 mole fraction decreases to only 0.1 (the bottom panel), its
density inside the pore is much smaller than that of CO2, which, together with the
strong affinity of carbon dioxide for adsorption on carbon surfaces, mean that C3H8
can be present in the two layers near the walls only in relatively small amounts.
Figure 3.19 depicts the (time-averaged) density profiles of the two
components, for two different binary mixtures, in the transport direction of the same
pore as in Figure 3.18. In both cases, the densities of the two components are
constant in the two CVs, while they decrease nonlinearly from the upstream region
to the downstream region. Although, the mole fraction of CO2 in the feed is larger
(the top panel) than that of propane, the density of C3H8 is larger in both cases. This
can be explained again based on the higher density of C3H8 under the bulk condition
(in the two CVs) and the shielding effect described earlier.
95
The experimental data for the dependence of the two components’
permerances on the temperature and feed composition are compared in Figure 3.20
with the simulation results. The size of the pore is H* = 5. There are two noteworthy
features in these results:
(1) The CO2 permeance is essentially independent of the temperature and
feed composition. This is due to the affinity of this molecule to adsorb on carbon
surfaces, which means that CO2 does not really “see” the pore structure. At the same
time, the permeance of C3H8 varies essentially linearly with the temperature and
composition.
(2) Although there is quantitative agreement between the simulation results
and the experimental data, so far as the order of magnitude of their numerical values
is concerned, the trends in the two sets of results do not agree with each other: While
the simulations indicate that3 8 2C H COK K> , the experimental data indicate the opposite
trend.
This discrepancy is reflected in the separation factor, defined as,
. Shown in Figure 3.21 are the separation factors, obtained for a
pore of size H*= 5, where they are compared with the experimental data. Whereas
the simulations indicate that, S
3 8 221 /C H COS K K=
21 > 1, the data indicate the opposite. To further study
the effect of the pore size, we carried out extensive simulations at T = 50°C, using a
mixture in which the CO2 mole fraction in the feed was 0.7, and varied the pore size.
The results are presented in Figure 3.22. Only when the pore size H* is below 1.97,
does the separation factor fall below 1. For H* = 1.95, one has a separation factor of
96
about 0.94, still about one order of magnitude larger than the experimental value.
Had we represented C3H8 as a LJ sphere, the corresponding critical pore size would
have been H* = 2.28, indicating again the significance of a proper model of n-
alkanes.
Hence, similar to the mixtures of CH4/C3H8 and CH4/C4H10, the results for
CO2/C3H8 mixtures indicate that a single pore is inadequate for modeling a
membrane which has a 3D pore space consisting of interconnected pores of various
shapes and sizes. That is, for the mixtures considered in this study, the
morphological characteristics of a membrane - its topology, or pore connectedness,
and its geometry representing the pores’ shapes and sizes - control its separation
properties.
Let us mention that our previous studies (Sedigh et al., 1998, 1999; Xu,
Sedigh et al., 2000; Xu, Sahimi et al., 2000) of CO2/CH4 mixtures in a single carbon
nanopore, as well as in a molecular pore network, indicated qualitative agreement
between the simulations results and the experimental data. This is due to the fact that
for this mixture energetic effects dominate the separation process, as a result of
which even a single pore model is adequate for obtained qualitative insight into these
phenomena. However, as our study described in this chapter indicates, while
transport and separation of mixtures involving CO2 and n-alkanes (n > 1), and also
mixtures of various n-alkanes (and presumably many other mixtures) in a single
pore, with almost any realistic size, are dominated by energetic effects, the same
phenomena in a real membrane are controlled by its morphology, implying that a
97
single pore is not a reasonable model of a real membrane, although such a model has
been used extensively in the past.
3.9 Modeling of Long n-Alkane Chain Mixtures and their
Transport and Separation in CMSM We carried out non-equilibrium molecular dynamics simulation of transport and
separation properties of mixtures of carbon dioxide and long n-alkane chains, such as
n-hexane in a slit carbon nanopore. The n-hexane molecules have been represented
by a united-atom (UA) model. We used configurational-bias Monte Carlo method for
efficient generation of the n-hexane molecules. Since the length of hexane chain
molecules are longer than propane or butane chains, we generated eight trial
orientations for n-hexane in this method. The Rattle algorithm for constrained
dynamics of chain molecules has been applied. We used the Lennard-Jones potential
for intramolecular contribution of those sites which are connected by more than four
bonds inside the alkane chain molecules.
Figure 3.23 shows the time-average density profiles for CO2 and C6H14 in a
mixture of 90% CO2 and 10% C6H14 at T=50°C in the direction perpendicular to the
pore’s walls, in three different regions of a pore of size 2* =H . The upstream and
downstream pressures are, respectively, 3 atm and 1 atm. The distribution of the
molecules in the pore is also shown in Figure 3.23. The density of C6H14 is much
smaller than that of CO2 inside the pore. This is due to the higher mole fraction of
98
CO2 in the feed which is 0.9 and also the size of the pore, 2* =H which is very
small to accommodate long hexane chain molecules inside the pore. Figure 3.24
shows this distribution of the molecules at the larger scale around the pore center. If
we increase the size of the pore to be large enough to accommodate inserted hexane
chain molecules inside CVs, then since the adsorption of hexane is much higher than
CO2, the density of hexane becomes larger than CO2. In order to study the effect of
pore size on density, we increased the size of the pore to 5* =H . Figure 3.25 shows
the density profiles of the two components of a mixture of CO2 and C6H14 at
T=200°C, along the transport direction of a pore of size 5* =H . The CO2 mole
fraction in the feed is 0.9, and the upstream and downstream pressures are,
respectively, 20 atm and 5 atm. As we can see in this figure, the density of hexane is
larger than CO2 even though the mole fraction of CO2 in feed is much higher than
hexane. The temperature profile of the mixture is also shown in figure 3.25. As can
be seen, the temperature is constant throughout the pore and its two CVs.
3.10 Summary Extensive molecular simulations, combining the configurational-bias Monte Carlo
method and the dual control-volume-nonequilibrium molecular dynamics technique,
were carried out to study transport and separation of binary mixtures of n-alkanes,
and also those involving CO2 and an n-alkane, in a carbon nanopore. The driving
force was a pressure (chemical potential) gradient. The effect of the composition of
99
the feed and the size of the pore, as well as that of the temperature of the system, on
the transport and separation of the mixtures were studied, and were compared with
the experimental data. Our study indicates that, in a real membrane, transport and
separation of the mixtures considered in this chapter are dominated by the
geometrical and topological characteristics of the membrane. As a result, a single
carbon nanopore, in which only energetics of the system mostly control the transport
and separation phenomena, is a grossly inadequate model and, therefore, one must
resort to full three-dimensional molecular pore network models for modeling these
phenomena in a real membrane. We will present our simulation results using three-
dimensional molecular pore network model for the membrane in Chapter 5.
100
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-60 -40 -20 0 20 40 60
X*
Tem
pera
ture
Figure 3.1: Dimensionless temperature distribution in a pore of size H* = 5 and the two control volumes, containing mixtures of CH4 and C3H8 with methane mole fraction in the feed being 0.7 (top) and 0.5 (bottom). Dashed lines indicate the boundaries of the pore region.
101
-2
-1
0
1
2
-20 -15 -10 -5 0 5 10 15 20
X*
Z*
Figure 3.2: Snapshot of the pore containing CH4 (triangles) and C3H8 (chains), at steady state. The mole fraction of CH4 in the feed is 0.9, and the pore size is H*= 5.
102
-2
-1
0
1
2
0 0.1 0.2 0.3 0.4 0.5 0.6
Density
Z*
-2
-1
0
1
2
0 0.04 .08 0.12 0.16
Density
Z*
0
Figure 3.3: Time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transverse direction (perpendicular to the walls), measured near the pore’s center at T = 50°C. The pore size is H* = 5, while the mole fraction of CH4 in the feed is 0.5 (top) and 0.9 (bottom).
103
H*=5
-2.5
-1.5
-0.5
0.5
1.5
2.5
0 0.1 0.2 0.3 0.4 0.5 0.6
Density
Z*H*=3
-1.5
-0.5
0.5
1.5
0.0 0.5 1.0 1.5
Density
Z*
H*=1.75
-1.0
-0.5
0.0
0.5
1.0
0.0 0.5 1.0 1.5 2.0
Density
Z*
Figure 3.4: Comparison of the time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transverse direction (perpendicular to the walls), measured near the pore’s center at T = 50°C, in three pores. The mole fraction of CH4 is 0.7.
104
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
-60 -40 -20 0 20 40 60
X*
Den
sity
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
Den
sity
Figure 3.5: Time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transport direction x in a pore of size H* = 5, in which the methane mole fraction in the feed is 0.7 (top) and 0.5 (bottom), and T = 50°C. Dashed lines indicate the boundaries of the pore region.
105
0.00
0.01
0.02
0.03
0.04
0.05
0.06
Den
sity
0.00
0.04
0.08
0.12
0.16
-60 -40 -20 0 20 40 60
X*
Den
sity
Figure 3.6: Time-averaged density profiles of CH4 (solid curves) and C3H8 (dashed curves) in the transport direction x in a pore of size H* = 5 in which the CH4 mole fraction is 0.9. The upstream and downstream pressures are, respectively, 3 atm and 1 atm (top), and 30 atm and 10 atm (bottom). Dashed lines indicate the boundaries of the pore region.
106
0.00
0.05
0.10
0.15
0.20
0.25
-60 -40 -20 0 20 40 60
X*
Den
sity
Figure 3.7: Time-averaged density profiles of CH4 (solid curve) and C3H8 (dashed curve) in the transport direction x in a pore of size H* = 3. The CH4 mole fraction in the feed is 0.7, and T=50°C.
107
0.00
0.02
0.04
0.06
0.08
0.4 0.5 0.6 0.7 0.8 0.9 1
CH4 Mole Fraction in the Feed
Perm
eanc
e ( s
imul
atio
n )
0.0000
0.0004
0.0008
0.0012
0.0016
0.0020
Perm
eanc
e ( e
xper
imen
t )
0.00
0.02
0.04
0.06
0.08
20 40 60 80 100 120
Temperature(°C)
Perm
eanc
e ( s
imul
atio
n )
0.0000
0.0004
0.0008
0.0012
0.0016
0.0020
Perm
eanc
e ( e
xper
imen
t )
Figure 3.8: Comparison of the simulation results for the permeance of CH4 (open triangles) and C3H8 (open circles) with the corresponding experimental data (solid symbols). The mole fraction of CH4 in the feed in the upper Figure is 0.7, while T = 50°C in the lower Figure. The pore size is H* = 5.
108
0
3
6
9
12
15
0.4 0.5 0.6 0.7 0.8 0.9 1
CH4 Mole Fraction in the Feed
Sepa
ratio
n Fa
ctor
( si
mul
atio
n )
0.0
0.5
1.0
1.5
2.0
Sepa
ratio
n Fa
ctor
( ex
perim
ent )
0
3
6
9
12
15
20 40 60 80 100 120
Temperature(°C)
Sepa
ratio
n Fa
ctor
( si
mul
atio
n )
0.0
0.5
1.0
1.5
2.0
Sepa
ratio
n Fa
ctor
( ex
perim
ent )
Figure 3.9: Comparison of the computed separation factors (open circles) with the experimental data (solid circles) for a CH4/C3H8 mixture. The mole fraction of CH4 in the feed in the upper Figure is 0.7, while T = 50°C in the lower Figure.
109
0.00
0.02
0.04
0.06
0.08
0.10
1 2 3 4 5 6
Pore Size
Perm
eanc
e
0
5
10
15
20
25
30
1 2 3 4 5 6
Pore Size
Sepa
ratio
n Fa
ctor
Figure 3.10: The effect of pore size on the permeances of CH4 and C3H8 and the corresponding separation factors in a binary mixture in which the CH4 mole fraction in the feed is 0.7, and T = 50°C.
110
-2
-1
0
1
2
-5 -4 -3 -2 -1 0 1 2 3 4 5
X*
Z*
Figure 3.11: A snapshot of the pore containing CH4 (triangles) and C4H10, at steady state in a pore of size H* = 5 at T = 50°C. The CH4 mole fraction in the feed is 0.9.
111
-2
-1
0
1
2
0 0.1 0.2 0.3 0.4 0.5 0.6
Density
Z*
Figure 3.12: Time-averaged density profile of CH4 (solid curve) and C4H10 (dashed curve), between the upper and lower walls of a pore of size H* = 5 at T = 50°C. The profiles were calculated in the middle of the pore, and CH4 mole fraction in the feed is 0.9.
112
0.00
0.02
0.04
0.06
0.08
0.10
0.12
-60 -40 -20 0 20 40 60
X*
Den
sity
Figure 3.13: Same as in Figure 3.12, but in the transport direction x. Dashed vertical lines indicate the boundaries of the pore region.
113
0.00
0.05
0.10
0.15
0.20
20 40 60 80 100 120
Temperature(°C)
Perm
eanc
e
0.00
0.05
0.10
0.15
0.20
0.4 0.5 0.6 0.7 0.8 0.9 1
CH4 Mole Fraction in the Feed
Perm
eanc
e
Figure 3.14: The computed permeances of CH4 (triangles) and C4H10 (circles). The mole fraction of CH4 in the feed in the upper Figure is 0.9, while T = 50°C in the lower Figure.
114
0.00
0.02
0.04
0.06
0.08
0.10
1 2 3 4 5 6
Pore Size
Perm
eanc
e
0
5
10
15
20
25
30
35
40
45
1 2 3 4 5 6
Pore Size
Sepa
ratio
n Fa
ctor
Figure 3.15: The effect of pore size on the permeances of CH4 (triangles) and C4H10 (circles), and the corresponding separation factors at T = 50°C. The CH4 mole fraction in the feed is 0.7.
115
0
1
2
3
4
-60 -40 -20 0 20 40 60
X*
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
Figure 3.16: Time-averaged temperature distribution in a pore of size H* = 5 and the two CVs that contain a binary mixture of CO2 and C3H8. The mole fraction of CO2 is 0.7 (top) and 0.5 (bottom). Dashed vertical lines indicate the boundaries of the pore.
116
-2
-1
0
1
2
-20 -15 -10 -5 0 5 10 15 20
X*
Z*
Figure 3.17: Distribution of CO2 (triangles) and C3H8 chains in a pore of size H* = 5 at T = 50°C, obtained at steady state. The CO2 mole fraction in the feed is 0.9.
117
-2
-1
0
1
2
0 0.1 0.2 0.3 0.4 0.5 0.6
Density
Z*
-2
-1
0
1
2
0 0.08 .16 0.24 0.32
Density
Z*
0
Figure 3.18: Density profiles of CO2 (solid curves) and C3H8 (dashed curves) between the upper and lower walls of a pore of size H* = 5, computed at the pore’s center and obtained at steady state. The CO2 mole fraction in the feed is 0.5 (top) and 0.9 (bottom), and T = 50°C.
118
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
Den
sity
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0.14
-60 -40 -20 0 20 40 60
X*
Den
sity
Figure 3.19: Same as in Figure 3.18, but in the transport direction x. The CO2 mole fraction in the feed is 0.7 (top) and 0.5 (bottom), and T = 50°C. Dashed vertical lines indicate the boundaries of the pore.
119
0.00
0.02
0.04
0.06
0.08
0.4 0.5 0.6 0.7 0.8 0.9 1
CO2 Mole Fraction in the Feed
Perm
eanc
e ( s
imul
atio
n )
0.00
0.01
0.02
0.03
0.04
Perm
eanc
e ( e
xper
imen
t )
0.00
0.02
0.04
0.06
0.08
20 40 60 80 100 120
Temperature(°C)
Perm
eanc
e ( s
imul
atio
n )
0.00
0.01
0.02
0.03
0.04
Perm
eanc
e ( e
xper
imen
t )
Figure 3.20: Comparison of the computed permeances of CO2 (open triangles) and C3H8 (open circles), for a pore of size H* = 5, with the corresponding experimental data (solid symbols). The CO2 mole fraction in the feed in the upper Figure is 0.7, while T = 50°C in the lower Figure.
120
0
3
6
9
12
15
20 40 60 80 100 120
Temperature(°C)
Sepa
ratio
n Fa
ctor
( si
mul
atio
n )
0.00
0.02
0.04
0.06
0.08
0.10
0.12
Sepa
ratio
n Fa
ctor
( ex
perim
ent )
0
3
6
9
12
15
0.4 0.5 0.6 0.7 0.8 0.9 1
CO2 Mole Fraction in the Feed
Sepa
ratio
n Fa
ctor
( si
mul
atio
n )
0.00
0.02
0.04
0.06
0.08
0.10
0.12
Sepa
ratio
n Fa
ctor
( ex
perim
ent )
Figure 3.21: Comparison of the computed separation factors of CO2/C3H8 binary mixtures (open circles), for a pore of size H* = 5, with the experimental data (solid circles). The CO2 mole fraction in the feed in the upper Figure is 0.7, while T = 50°C in the lower Figure.
121
0.00
0.02
0.04
0.06
0.08
0.10
1 2 3 4 5 6
Pore Size
Perm
eanc
e
0
3
6
9
12
15
1 2 3 4 5 6
Pore Size
Sepa
ratio
n Fa
ctor
Figure 3.22: The effect of the pore size on the permeances of CO2 (triangles) and C3H8 (circles), and the corresponding separation factors at T = 50°C. The CO2 mole fraction in the feed is 0.7.
122
-20<X*<-19
-1.0
-0.6
-0.2
0.2
0.6
1.0
0 1 2 3X*
Z*
0<X*<1
-1.0
-0.6
-0.2
0.2
0.6
1.0
0 1 2 3X*
Z*
-0.3
-0.1
0.1
0.3
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Z*
19<X*<20
-1.0
-0.6
-0.2
0.2
0.6
1.0
0 1 2 3X*
Z*
Figure 3.23: Time-averaged density profiles of CO2 (solid curves) and C6H14 (dashed curves) between the upper and lower walls, in three different regions of a pore of size H* = 2. The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The CO2 mole fraction in the feed is 0.9 and T = 50°C. Also shown is the distribution of the CO2 (triangles) and C6H14 (chains) in the pore. The arrows indicate the boundaries of the pore region.
123
-0.3
-0.1
0.1
0.3
-5 -4 -3 -2 -1 0 1 2 3 4 5
X*
Z*
Figure 3.24: Snapshot of the pore containing CO2 (triangles) and C6H14 (chains) with the same parameters as figure 3.23.
124
0.00
0.02
0.04
0.06
0.08
0.10
0.12
-60 -40 -20 0 20 40 60
X*
Den
sity
0
2
4
6
-60 -40 -20 0 20 40 60
X*
Tem
pera
ture
Figure 3.25: Time-averaged density profile (top) of CO2 (solid curves) and C6H14 (dashed curves) and temperature profile (bottom), in the transport direction x in a pore of size in which the CO5* =H 2 fraction is 0.9 and T=200°C. The upstream and downstream pressures are, respectively, 20 atm and 5 atm. Dashed lines indicate the boundaries of the pore region.
125
Chapter 4 Sub- and Supercritical Fluids in Nanoporous Materials: Direction-Dependent Flow Properties 4.1 Introduction
anoporous membranes have been used for separating gas mixtures. These
membranes offer high selectivities and sufficient mechanical under a variety
of conditions. In particular, nanoporous membranes have been considered for
separation of CO2 /alkane mixtures under sub- and supercritical conditions. We have
been investigating use of carbon molecular-sieve membranes (CMSMs) for this
purpose(Linkov, Sanderson and Rychkov, 1994; Sedigh et al., 1998, 1999, 2000;
Shiflett and Foley, 1999; Steriotis et al., 1997). In practice, however, such
membranes consist of a porous support made of at least two layers of macro- and
mesopores, and a nanoporous film deposited on the support. Flow and transport of
fluids in such composite porous materials have rarely been studied.
N
In this Chapter, we present the results of the first atomistic simulation of flow
and transport of fluid mixtures in a composite porous material that consists of three
distinct pores, referred to as the macro-, meso-, and nanopores. The effect of
assymetry in the permeation properties of fluid in nanoporous membrane have been
studied. In order to understand how the permeation properties of the membranes
126
depends on its structure, we investigate the impact of the multilayer structure of a
CMSM on transport of fluids under sub- and supercritical conditions. The results of
extensive nonequilibrium molecular dynamics simulations of flow and transport of a
pure fluid, as well as a binary fluid mixture, through a porous material composed of a
macro-, a meso-, and a nanopore, in the presence of an external pressure gradient, are
presented. In practice, a fluid mixture passes through a porous membrane by
applying a pressure gradient to two opposing external surfaces of the membrane. To
simulate this process we use the dual control-volume grand-canonical MD (DCV-
GCMD) simulation technique which is most suitable for simulating transport
processes in systems that operate under an extermal potential gradient (see Section
2.3). One goal of this Chapter is to understand the effects of the membrane structure,
and the pressure gradient applied to the membrane, on the flow properties of the fluid
mixture passing through the membrane.
We find that under supercritical conditions, unusual phenomena occur that
give rise to direction- and pressure-dependent permeabilities for the mixture's
components. Hence, the classical models of fluid flow and transport through porous
materials that are based on single-valued permeabilities that are independent of the
direction of the applied pressure gradient are completely in error.
127
4.2 Asymmetric Pore Models Real porous membranes consist of support and several layers, therefore the cross-
section of pores in real membranes may change as fluid transfer from the support to
the different layers of the membrane. A simple model for this change in the cross-
section is a pore with a step that consisits of two or more slits pores with different
sizes. Recent MD simulations (Düren et al., 2003) indicate that atomistic-scale
transport in a pore is hardly influenced by the pore’s shape. Thus, as a prelude to
understanding flow and transport of fluid mixtures in a real membrane, we consider
the same phenomena in the composite pore system shown in Figure 4.1, which
consists of three slit pores in series. (A somewhat similar pore model was utilized by
Düren et al. (2003) in their study of gas transport through a membrane.) Each pore
represents one layer of a three-layer supported membrane. The membrane is
connected to two control volumes (CVs) that are exposed to the bulk fluid at high
and low chemical potentials μ or pressures . The external driving force is a
chemical potential or pressure gradient applied in the
P
x − direction.
We studied this phenomena by considering two models of the composite
membrane as illustrated in Figure 4.1 and 4.2. In the first model, as shown in Figure
4.1, the control volumes are placed inside the pore at the two end parts of the pore,
therefore the size of the the control volumes is different in this model. Periodic
boundary conditions are used only in the y − direction in the pore and two CVs. In the
second model, as shown in Figure 4.2, two bulks have been considered as the control
128
volumes at the two end parts of the pore. Periodic boundary conditions are used only
in the direction in the pore and in both yy − − and z − directions in the two CVs.
Additionally, in the first model we considered three layers of graphite as the pore
wall, while in the second model, all the layers of graphite in the simulation cell have
been considered as the pore wall, which needs much more computation but
represents more realistic model of the composite membarne structure. In the wall of
the pore, carbon atoms were packed with the structure corresponding to graphite, so
that the number density of the carbon atoms was 114 nm-3, and the spacing between
the adjacent graphite layer in the z − direction was 3.35 Å. The total number of
carbon atoms in the simulation cell was 42,328 in the first model, and 56,472 in the
second model. The pores’ heights, H1, H2 and H3 as shown in Figure 4.1 and Figure
4.2, are 77, 23 and 10 Å respectively, while they all have the same length, about 43Å
in both models. The length of the two CVs are the same and equal to 63.90 Å. The
width of the pores and the two CVs are equal to 63.95 Å.
129
Figure 4.1: Asymmetric pore model with CVs inside the pore.
Figure 4.2: Asymmetric pore model with CVs outside the pore.
130
4.3 Adsorption and Transport in Asymmetric Pore Real membranes consist of pores with different sizes and shapes, which are a
significant source of heterogeneity in a membrane. As the pore size decreases, the
potential energy well becomes progressively deeper and its effect becomes stronger
and goes on until a limiting radius is reached where the repulsive interaction being to
dominate. Therefore, pores which are slightly larger than limiting radius present
very strong adsorption site, while for the larger pores, the influence of the pore walls
on particles in the center of the pore decreases and finally vanishes and only fluid
molecules located to the pore walls feel its influence. In asymmetric pore model, the
favorable adsorption sites at the step show that the most attractive potential, which is
the smallest value, is found in the corner of the steps.
In asymmetric pore model, different transport mechanisms contribute in
different regions. The diffusion mechanisms are classified according to the
interactions of the fluid molecules with the pore wall. In real adsorbents consisting
of networks of interconnected pores with varying diameters and shape, the
mechanisms cannot be distinguished so clearly. In the largest (macro-) pore, gas
permeation takes place by convective flow. In the mesopore, gas permeation is by
Knudsen diffusion (and some surface diffusion if the pressure is very large). Surface
diffusion is the main mechanism in the smallest (nano-) pore. Adsorption on the
walls becomes important when the pore diameter < 100 Å.
131
If the pore diameter is large in comparison to the mean free path of the fluid
molecules, collisions between diffusing molecules occur far more frequently than
collisions between the molecules and the pore walls. The influence of the pore wall
is small. The diffusion mechanism is the same as in the bulk and is called molecular
diffusion. In small pores and at low pressure when the mean free path is larger than
the pore diameter, the fluid molecules collide more often with the pore wall than
with each other. Knudsen diffusion takes place. Knudsen diffusion and molecular
diffusion often occur together. In the so-called transition region, the mean free path
is comparable to the pore diameter. Molecule-molecule as well as molecule-wall
collisions take place.
4.4 Molecular Dynamics Simulations in Asymmetric Pore We have carried out extensive NEMD simulations to study flow and transport
properties of pure CO2, as well as a mixture of CH4 and CO2, in the membrane. The
two components, as well as the carbon atoms that the pores’ walls consist of, are
represented by Lennard-Jones (LJ) spheres and characterized by effective LJ size and
energy parameters, σ and ε, respectively. All the quantities of interest are made
dimensionless with the help of the CH4 parameters, σ1 and ε1. Table 2.1 lists the
conversions between the dimensionless and dimensional quantities. We used the
same value for the size and energy parameters of CH4, CO2 molecules, and carbon
atoms that the pores’ walls consist of, as we used in Section 2.4. The Lorentz-
132
Berthelot mixing rules were used in the simulations to compute the size and energy
parameters of the unlike molecules (see Section 2.4)(Allen and Tildesley, 1987).
As mentioned earlier, we use the DCV-GCMD method (Cracknell,
Nicholson and Quirke, 1995; Ford and Heffelfinger, 1998; Heffelfinger and Van
Swol, 1994; Xu et al., 1998, 1999; Xu, Sedigh et al., 2000; Xu, Sahimi et al., 2000)
which combines the MD method in the entire pore system with the grand-canonical
Monte Carlo (GCMC) insertions and deletions of the molecules in the CVs.
Therefore, to mimic the experimental conditions, the densities, or the corresponding
chemical potentials, of the components in the CVs were maintained using a sufficient
number of the GCMC insertion and deletions (see Section 2.3). The two CVs are
well mixed and in equilibrium with the two bulk phases that are in direct contact
with them. Typically, 10 GCMC insertions and deletions in each CV were followed
by one MD integration step. The molecule-molecule interactions were modeled with
the cut-and-shifted LJ 6-12 potential with a cut-off distance 14cr δ= . To calculate the
interactions between the fluids’ molecules and the walls, we used the LJ potential for
the interactions between the molecules and the individual carbon atoms on the walls,
arranged as in graphite. The cut-off distance between the molecules and the carbon
atoms on the wall was 13.5cr δ= . The interaction between the gas molecules with the
entire carbon pore wall was taken to be the sum of the LJ potentials between the gas
molecules and each individual carbon atoms in the wall. In computer simulation of
confined fluids, this is the most realistic solid wall model which is an assembly of
atoms constrained to remain at the lattice sites of a crystal. However, this type of
133
wall is computationally expensive to simulate, since interactions between each fluid
and wall atom must be calculated.
In order to make the computation faster, at the beginning of each simulation
run, the simulation cell was devided into a large number of small subcells and a test
particle was assigned to each subcell. The simulation cell was discretized into
grid points along the three directions. In the first model as we shown in
Figure 4.1, we considered
zyx nnn ××
444=xn , 112=yn , and 158=zn , thus resulting in over
7,850,000 small subcells. In the second model as we shown in Figure 4.2, we
considered the same values for and , but since we do not have graphite atoms
in the CVs the value of is smaller and we considered
yn zn
xn 283=xn , thus resulting in
over 5,000,000 small subcells for this model. The test particle-solid wall interaction
energies and their three derivaties, associated with all the subcells, were then
calculated and recorded. To reduce the simulation time for calculation the interaction
between a gas molecule and all the carbon atoms in the wall, we used a 3D piecewise
cubic Hermite interpolation (Kahaner et al., 1989; Schultz, 1973) (which interpolates
a function and its first three derivatives) to compute the potential energy and forces
for the gas particle at any position using the previously recorded information at the
grid points. zyx nnn ××
The Verlet velocity algorithm was used to integrate the (dimensionless)
equations of motion with a dimensionless time step, 3* 5 10t −Δ = × (i.e., 0.00685
ps). The equations of motion were integrated with up to 1.2
tΔ ≈
× 107 time steps to
134
ensure that the steady state has been reached. Molecules that crossed the outer
boundaries of the CVs were removed. The number of such molecules was, however,
small, typically about 1% of the total number of molecules that were deleted during
the GCMC simulations. In addition, for each component we allowed for a nonzero
streaming velocity (the ratio of the component's flux and concentration) in the pore
system, consistent with the presence of a bulk pressure/chemical potential gradient
along the x − direction. In the CVs, however, the overall streaming velocity was
zero. Iso-kinetic conditions were maintained by rescaling the velocity independently
in the three directions.
Two important quantities of interest are the density profiles along the
x − direction, the direction along which the chemical potential gradient μ∇ is
imposed on the membrane, and in the yz planes that are perpendicular to the
direction of μ∇ . The density profile (x) of component i along the ziρ x − direction
was computed by dividing the simulation box in that direction into grids of size,
11.12l σ= . For each MD step, (x) was computed by averaging the number of
particles of type i over the distance l . A similar procedure was used for computing
the density profile
ziρ
xiρ (z) in the planes that are perpendicular to the direction of yz
μ∇ , with the averaging done over a small distance which was about 0.67 1σ ,
0.21 1σ , and 0.09 1σ for macro-, meso- and nanopore, respectively. As discussed
below, these quantities are important to understanding adsorption and transport
properties of the fluids in a composite membrane.
135
In addition, a most important characteristic property of a membrane is the
permeability of a fluid passing through the membrane. Thus, for each component i
we calculated its flux and permeability in the direction of the applied chemical
potential or pressure gradient. We calculated the flux and permeability in the
composite membrane with the same method as we descried earlier in Section 2.5. We
computed the permeabilities for two cases. In one, the upstream condition (higher
pressure) was maintained in the CV connected to the macropore, while in the second
case the upstream condition was maintained in the nanopore.
iJ iK
In what follows, we present and discuss the results of our simulation. The
temperature was held constant in order to eliminate any contribution of the
temperature gradient to the transport. Unless otherwise specified, in all the cases
discussed below, the temperature is fixed at T=35°C, and for the mixture of CH4 and
CO2, the mixture is equimolar.
4.5 Results and Discussions Figures 4.3 to 4.11 represent our simulation results when CVs are considered inside
the pore. The schematic of the system that we simulate has been shown earlier in
Figure 4.1. We apply a pressure drop PΔ to the system in one direction and
measure the fluid’s fluxes at steady state, and then reverse the direction of and
repeat the simulations. Figure 4.3 represents the molecules’ distribution and the
PΔ
136
density profiles (x) for COziρ 2 in the two CVs and the pore along the transport ( )x −
direction under supercritical - subcritical conditions for both directions of applied
pressure gradient. The upstream and downstream pressures are, 82.63 atm (1200
psig) and 5 atm (59 psig), respectively. These results have been obtained after
1,500,000 time steps when the upstream pressure is on the macro side, and after
4,000,000 time steps when the upstream pressure in on the nano side. The densities
in the two CVs regions are constant, as they should be and the density decreases
along the pore from upstream pressure to downstream pressure. Figure 4.4 shows
the snapshots of CO2 molecules in 3D for both direction of applied pressure gradient
along the pore. The upstream and downstream pressures are the same as Figure 4.3.
The snapshots show that most of the CO2 molecules are near the pore’s wall and the
corner of the steps. Figure 4.5 shows the time-averaged density profiles xiρ (z) for
CO2 in the direction perpendicular to the pore’s walls, at different regions of the
pore. The upstream and downstream pressures are, respectively, 82.63 atm and 5
atm and the upstream pressure is applied on the macropore. As these results
indicate, fluid packed the pore almost completely. The density is high everywhere
inside the macropore. In mesopore fluid forms several liquid-like layers and by
decreasing the pore size in nanopore, fluid forms only two adsorbed layers near the
pore’s walls. Note that the density profile has lots of fluctuations in the area which
are close to the corner of each steps. Fig. 4.6 represents the same results as Figure
4.5, except that the pressure gradient has been applied in the opposite direction along
the pore. There is a phase transition from liquid-like to gaseous one, as fluid
137
transport from upstream pressure in the nanopore to downstream pressure in the
macropore.
We have also studied these phenomena under subcritical conditions. Fig. 4.7
shows the time-averaged density and temperature profiles in the two CVs and the
pore along the transport ( )x − direction under subcritical - subcritical conditions
obtained after 5,100,000 time steps for both directions of applying pressure gradient.
The upstream and downstream pressures are, respectively, 21.4 atm (300 psig) and
11.2 atm (150 psig). Since the pressure gradient which is applied along the pore is
not very large the density is higher in nanopore for both cases due to the adsorption.
As can be seen, the temperature is constant along the pore and in the two CVs as it
should be. When the upstream pressure is on the macro side, the molar flow is about
1.4 times larger than when the upstream pressure is on the nano side. We also
increased the pressure gradient along the pore to see how it affects on the molar flow
when we apply the pressure gradient from both directions along the pore under
subcritical conditions. Fig. 4.8 represents the time-averaged density and number of
the molecules profiles in the two CVs and the pore in the transport ( )x − direction
for both directions of applied pressure gradient, in which the upstream and
downstream pressures are, respectively, 41.8 atm (600 psig) and 4.4 atm (50 psig).
Note that the time-averaged number of the molecules is the same as density except
that it has not been divided by the volume. When the upstream pressure is on the
macro side, although the average number of the molecules in nanpore is less than
138
macropore, but the density in the nanopore is higher than the macropore. This is due
to contribution of cross-sectional area of the pore in density calculation. When the
upstream pressure is on the macro side, the molar flow is about 2.3 times larger than
when the upstream pressure is on the nano side.
The binary mixture of CH4 and CO2 was also simulated. We considered the
equimolar mixture of CH4 and CO2 at T=35°C. Figure 4.9 represents the distribution
of CH4 and CO2 molecules in the pore and the two bulk regions under supercritical -
subcritical conditions, obtained after 4,000,000 time steps when the pressure drop
applied in the two opposite directions. The upstream and downstream pressures are,
respectively, 82.6 atm (1200 psig) and 35 atm (500 psig). Due to affinity of CO2 for
carbon surfaces, there are more CO2 molecules inside the pore than CH4 molecules.
Figure 4.10 depicts the time-averaged density profiles of two components in the two
CVs and the pore in the transport ( )x − direction with the same upstream and
downstream pressures as Figure 4.9. The time-averaged distribution of the
dimensionless temperature has been shown in figure 4.11. The permeabilities of
both components in the mixture are larger when the upstream pressure is applied on
the macropore than when the upstream pressure is applied on the nanopore. When
the upstream pressure is on the macro side the permeabilities of both CH4 and CO2
components in the mixture are, respectively, 1.14E-06 and 2.09E-06
(grmole.cm/min.psi.cm2), while when the upstream pressure is on the nano side, the
permeabilities of both CH4 and CO2 components are, respectively, 3.89E-08 and
9.22E-08 (grmole.cm/min.psi.cm2).
139
In the previously discussed model for the composite membrane in which the
CVs has been considered inside the pore, the size of the two CVs is not the same.
Since the size of the CV which is connected to the nanpore is much smaller, it will
saturate after reaching to some pressures. Therefore, the smaller CV can not
accommodates enough molecules to reach to high pressures which can affect on the
flux and permeability of the fluids when we apply the pressure gradient from both
opposite directions in the asymmetric pore model.
In order to study a more realistic model, the CVs were placed outside of the
asymmetric pore. Figures 4.12 to 4.29 represent our simulation results, considering
two bulks outside of the pore, as the CVs. The schematic of the system that we
simulate has been shown earlier in Figure 4.2. As in the previous model, we apply a
pressure drop to the system in one direction and measure the fluid’s fluxes at
steady state, and then reverse the direction of
PΔ
PΔ and repeat the simulations. Figure
4.12 shows the molecules’ distribution in the pore containing CO2 under subcritical -
subcritical conditions obtained after about 3,500,000 time steps for both direction of
applied pressure gradient. The upstream and downstream pressures are, respectively,
62.2 atm (900 psig) and 28.2 atm (400 psig). To understand better the molecules’
distribution in Figure 4.12, the density profile for CO2 in the two CVs and the pore
along the transport ( )x − direction have been shown in Figures 4.13 for both
directions of applied pressure gradient. The densities in the two bulk regions are
constant, as they should be. As one moves from the macro- to meso- to nanopore,
the densities, regardless of the direction of PΔ , increase since the pores’ sizes
140
decrease. Figure 4.12 and 4.13 and close inspection of the densities in the pores
indicate that, for the applied PΔ , one has a gas-like (very low density) fluid in the
macropore in both cases, followed by a transition to a liquid-like fluid (due to
condensation) in the mesopore, while the liquid-like fluid packs the nanopore
completely. The position of the transition depends on the pores’ sizes and the
direction of . The time-averaged temperature profiles of COPΔ 2 in the two CVs and
the pore along the transport ( )x − direction have been shown in Figure 4.14 for both
directions of applied pressure gradient with the same condition as Figure 4.12 and
4.13. As can be seen, the temperature in both cases is constant throughout the pore
and its two bulk regions.
In order to study the effect of supercriticality, we increased the upstream
pressure to the value above the critical pressure of CO2 having the same pressure
gradient along the pore. Figure 4.15 shows the snapshot of the pore system and the
distribution of CO2 molecules in it under supercritical - subcritical conditions. The
upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 48.6
atm (700 psig). In both cases, the state of CO2 in the nano- and mesopores is liquid-
like, caused by condensation. The state of CO2 in the macropore, on the other hand,
depends on where the upstream condition is maintained. If the upstream condition is
maintained in the CV connected to macropore, then the CO2 density in the pore is
high almost everywhere, resembling a liquid-like state. If, on the other hand, the
upstream condition is maintained in the CV connected to the nanopore, the CO2
density in the macropore near its entrance to the mesopore is high, but decreases
141
somewhat as one gets away from this region towards the CV on the left side of the
figure. These are consistent with the time-averaged density profile ρ (x) of CO2
shown in Figure 4.16. The time-averaged temperature profiles of CO2 in the two CVs
and the pore along the transport ( )x − direction have been shown in Figures 4.17 for
both directions of applied pressure gradient.
Figure 4.18 presents the CO2 permeabilities and molar flows as a function of
the upstream pressure, when a pressure drop PΔ = 500 psi was applied to the pore
system. The direction-dependence of K is striking, with the permeabilities in the
two opposite directions differing by a factor which can be as large as nearly four.
Moreover, the trends for the two cases are opposite of each other. Whereas K
decreases when the upstream is on the macropore side, it increases when the
direction of is reversed. The reason can be understood by considering Figures
4.15 and 4.16 at a constant overall
PΔ
PΔ , with increasing the upstream pressure on the
macropore side, practically the entire pore system is packed with CO2 molecules.
This makes the passage of the molecules from the macropore to the mesopore very
difficult, resulting in reduced values of K . On the other hand, at the same overall
, increasing the upstream pressure when applied on the nanopore side moves the
transition point between a gas-like and liquid-like state to inside the macropore,
hence making the passage of the molecules from the mesopore to the macropore
easier, which increases
PΔ
K in that direction.
The effect of pressure gradient along the pore has been also investigated.
Figure 4.19 represents the snapshot of the pore containing CO2 molecules under
142
supercritical - subcritical conditions for both directions of applied pressure gradient,
in which the upstream and downstream pressures are, respectively, 82.6 atm (1200
psig) and 11.2 atm (150 psig). As we can see in this figure, the high pressure
gradient forces the molecules to move in the transport direction in macro- meso and
nanopores, even the adsorbed molecules to the horizontal carbon walls seems to be
carried away. There are not many molecules which stay inside the pore because the
stream velocity in the pore is very high. The time-averaged density profile of CO2 in
the two CVs and the pore along the transport ( )x − direction has been shown in
Figure 4.20 for both directions of applied pressure gradient along the pore. As it has
been shown in this figure the density is very low inside the pore, expect close to the
corner of the steps where the molecules can not move forward and accumulate due to
presence of pore walls.
We also increased the length of macro-, meso- and nanopore to investigate
the effect of the pore length on the transport and permeation properties in
asymmetric pore. We found no significant effect on the results.
The binary mixture of CH4 and CO2 was also simulated. We considered the
equimolar mixture at T=35°C. Figure 4.21 presents a snapshot of the pore system
and the distribution of CO2 and CH4 molecules in it, after the steady state has been
reached, with the upstream and downstream pressures being 82.6 atm (1200 psig)
and 35 atm (500 psig), respectively. Figure 4.22 presents the time-averaged density
profiles iρ (x) of the two components for the two upstream conditions. The densities
in the two bulk regions are constant, as they should be. As one moves from the
143
macro- to meso- to nanopore, the densities, regardless of the direction of (or the
upstream condition), increase since the pores' sizes decrease. A closer inspection of
the densities in the pores indicates that, for the applied
PΔ
PΔ , one has a gas-like (low
density) mixture in much of the macropore in both cases, followed by a transition to
a liquid-like mixture (due to condensation) which packs the meso- and nanopores
completely at high densities. The position of the transition line from the gas-like to
liquid-like mixture depends on the pores' sizes and the direction of . The density
profiles shown in Figure 4.22 are consistent with the snapshot of the system shown
in Figure 4.21, as they should be. Figure 4.23 shows the (dimensionless) temperature
throughout the pore system, which indicates that it remains constant. Hence, all the
possible effects due to a temperature gradient have been eliminated. To understand
the distributions of the two molecules in the pores better, we present in Figures 4.24
and 4.25 the time-averaged densities
PΔ
xiρ (z) for the two molecules at six different
planes that are perpendicular to the direction of PΔ (the coordinates' center is on the
centerline that passes through the three pores). Figure 4.24 shows the density profiles
when the upstream condition is maintained in the CV which is connected to the
macropore. In plane 1 near the pore mouth connected to the CV, two layers of each
type of molecule have been formed. One, with high densities, is near the walls, while
the second one with lower densities is closer to the center. Near the macropore
mouth that connects it to the mesopore (denoted by 2 in the Figure 4.24), the density
profiles look chaotic, with several layers of the two molecules forming. This is
caused by the entrance effect whereby, due to the size of the mesopore which is
144
much smaller than that of the macropore, a large number of molecules accumulate at
the macropore's entrance to the mesopore. But, if we inspect the density profiles just
inside the mesopore (denoted by 3 in the figure), we find again that two layers of
each type of molecules have been formed inside the mesopore. The molecules'
distributions in the region where the mesopore is connected to the nanopore (denoted
by 4 in the figure) are qualitatively similar to those in plane 2, and are again
dominated by the entrance effects. The very small size of the nanopore allows only
monolayer formation. As a result, one obtains the density profiles shown in Figure
4.24 for planes 5 and 6 shown in the figure. The same qualitative patterns are
obtained when the upstream condition is held in the CV connected to the nanpore
(see Figure 4.25), but with one difference: Only one layer of each type of molecules
has been formed in plane 1, where the macropore is connected to the CV. This is
clearly caused by the low downstream pressure which gives rise to a gas-like state in
that region, and is also consistent with the snapshot of the pore system shown in
Figure 4.21.
Figure 4.26 shows the time-averaged densities ρ (z) of pure CO2 at nine
different planes that are perpendicular to the direction of PΔ . The upstream and
downstream pressures are, respectively, 96.2 atm (1400 psig) and 48.6 (700 psig)
and the upstream condition is held in the CV connected to the macropore. Figure
4.27 represents the same results as Figure 4.26, except that the upstream condition is
held in the CV connected to the nanopore.
145
Figure 4.28 presents the permeabilities and molar flows of the two
components in an equimolar mixture with PΔ = 700 psi, computed when the
pressure drop was applied in the two opposite directions along the pore, and the
upstream pressure was varied. The same qualitative patterns are obtained when other
values of pressure drops are applied, and the upstream and downstream conditions
are such that one crosses from a subcritical region to a supercritical one (the critical
pressure for CO2 is about 73 atm). In addition to the fact that the pressure-
dependence of and is in qualitative agreement with experimental data (Ohya
et al., 1993; Sarrade et al., 1996; Tokunaga et al., 1997; Molaai Nezhad et al.),
another noteworthy feature of Figure 4.28 is that the permeabilities differ
significantly, with - that of CO
1K 2K
2K 2 - being larger. The reason is that, due to affinity
of CO2 for carbon surfaces, there is significant flow of CO2 on or near the walls
which is not the case for CH4. This is particularly important, as the nano- and
mesopores are packed with molecules and, therefore, the molecules' motion in them
is exceedingly slow. Hence, surface flow becomes important.
Figure 4.29 presents the molar flow and permeabilities of the two
components in an equimolar mixture at T=35°C versus PΔ , which were measured
when the pressure drop was applied in the two opposite directions along the pore,
and the upstream pressure was 1400 psig. As can be seen, by increasing , the
permeabilities for both components increase which is more pronounced when the
upstream pressure is on the macro side.
PΔ
146
The results for the permeabilities, for both pure CO2 and those in the mixture,
are explained as follows. Transport in a macropore is dominated by convection,
which gives rise to a permeability independent of the direction of the applied
pressure gradient, even in a gaseous state (Sahimi, 1993, 1995; Torquato, 2002). In a
mesopore, transport is by a combination of convection and Knudsen diffusion
(Sahimi, 1993, 1995; Torquato, 2002), whereas in a nanopore, due to its small size,
transport occurs mostly through surface flow. In both meso- and nanopores, the
permeabilities depend in a complex manner on the upstream and downstream
pressures (Sahimi, 1993, 1995; Torquato, 2002). This fact, and packing of the meso-
and nanopores caused by condensation, imply that the overall permeability of a
porous membrane depends on both the upstream and downstream pressures and the
direction along which the pressure gradient is applied to the membrane.
4.6 Summary The effect of orientation of the external potential gradient on the permeation
properties of the composite CMSMs has been studied by nonequilibrium molecular
dynamics simulations under sub- and supercritical conditions. The results indicate
the significance of the pore structure and the fluids' state to their transport through a
porous material. In particular, aside from being in qualitative agreement with the
preliminary experimental data obtained by our group (Molaai Nezhad et al.), the
results have two important implications. (1) That the classical modeling of transport
147
of fluids through porous membranes based on a single effective permeability,
independent of the direction of the applied pressure gradient, is completely wrong.
Therefore, optimization of a separation process using nanoporous membranes
requires consideration of the direction-dependant permeation properties of the
membrane. (2) Unlike the popular practice, a single pore is a gross and inadequate
model of an actual membrane.
In practice, supercritical fluid extraction using CO2 is utilized when the
mixture contains heavier hydrocarbons, such as pentane and hexane. In such cases,
the molecular structure of the hydrocarbons and their motion through the nanopores
give rise to additional complexities, such as freezing phenomena whereby the
mixture does not move appreciably even over long periods of times (Firouzi et al.).
148
(a) (b) Figure 4.3: Snap-shots and density profiles of CO2 in supercritical – subcritical conditions. The upstream and downstream pressures are, respectively, 82.63 (1200 psig) and 5 atm (59 psig), and temperature is 35 °C, (a) the upstream pressure is on the macro side, obtained after 1,500,000 time steps, (b) the upstream pressure is on the nano side, obtained after 4,000,000 time steps. Vertical lines indicate the boundaries of the pore.
149
Transport Direction
Transport Direction
Figure 4.4: Snapshots of the pore containing pure CO2 in 3D. The upstream and downstream pressures are, respectively, 82.63 atm (1200 psig) and 5 atm (59 psig), and temperature is 35 °C. The upstream pressure is on the macro side (top) and nano side (bottom).
150
Figure 4.5: Density profiles of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.63 atm (1200 psig) and 5 atm (59 psig), and temperature is 35 °C. The upstream pressure is on the macro side.
151
Figure 4.6: Density profiles of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.63 atm (1200 psig) and 5 atm (59 psig), and temperature is 35 °C. The upstream pressure is on the nano side.
152
0.0
0.1
0.2
0.3
0.4
0.5
0.6
-35 -25 -15 -5 5 15 25 35
X*
Den
sity
0.0
0.1
0.2
0.3
0.4
0.5
0.6
-35 -25 -15 -5 5 15 25 35
X*
Den
sity
300 psig300 psig 150 psig 150 psig
0
1
2
3
(a) (b) Figure 4.7: Density and temperature profiles of pure CO2 along the pores for subcritical - subcritical conditions. The upstream and downstream pressures are, respectively, 21.4 atm (300 psig) and 11.2 atm (150 psig), and temperature is 35 °C, (a) the upstream pressure is on the macro side, (b) the upstream pressure is on the nano side. Dashed vertical lines indicate the boundaries of the pore.
4
-35 -25 -15 -5 5 15 25 35
X*
Tem
pera
ture
01234
-35 -25 -15 -5 5 15 25 35
X*Te
mpe
ratu
re 150 psig300 psig 150 psig 300 psig
153
0
0.1
0.2
0.3
0.4
0.5
0.6
-35 -25 -15 -5 5 15 25 35
X*
Den
sity
0
0.1
0.2
0.3
0.4
0.5
0.6
-35 -25 -15 -5 5 15 25 35
X*
Den
sity
(a) (b) Figure 4.8: Density profiles and number of the molecules of pure CO2 along the pores for subcritical - subcritical conditions. The upstream and downstream pressures are, respectively, 41.8 atm (600 psig) and 4.4 atm (50 psig), and temperature is 35 °C, (a) the upstream pressure is on the macro side, (b) the upstream pressure is on the nano side. Dashed vertical lines indicate the boundaries of the pore.
0
20
40
60
80
100
-35 -25 -15 -5 5 15 25 35
X*
Num
ber o
f mol
ecul
es
0
20
40
60
80
100
-35 -25 -15 -5 5 15 25 35
X*
Num
ber o
f mol
ecul
es
600 psig600 psig 50 psig50 psig
600 psig50 psig600 psig 50 psig
154
Figure 4.9: Snapshot of the pore containing equimolar mixture of CH4 (triangles) and CO2 (circles) under supercritical - subcritical conditions obtained after 4,000,000 time steps. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) and macro side (bottom).
155
1200 psig 500 psig
0
0.1
0.2
0.3
0.4
0.5
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Dens
ity500 psig 1200 psig
0
0.1
0.2
0.3
0.4
0.5
Den
sity
Figure 4.10: Time-averaged density profiles of both CH4 (solid curves) and CO2 (dashed curves) in the transport direction x in the pore with the same parameters as Figure 4.9. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
156
500 psig 1200 psig
0
2
4
6
8Te
mpe
ratu
re
1200 psig 500 psig
0
2
4
6
8
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Tem
pera
ture
Figure 4.11: Time-averaged temperature distribution along the pore with the same parameters as Figures 4.9 and 4.10. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
157
Figure 4.12: Snapshot of the pore containing CO2 under subcritical - subcritical conditions. The upstream and downstream pressures are, respectively, 62.2 atm (900 psig) and 28.2 atm (400 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) obtained after 3,125,000 time steps, and macro side (bottom) obtained after 3,410,000 time steps.
158
400 psig 900 psig
0.0
0.1
0.2
0.3
0.4
0.5
0.6
Den
sity
900 psig 400 psig
0.00
0.10
0.20
0.30
0.40
0.50
0.60
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Den
sity
Figure 4.13: Time-averaged density profiles of pure CO2 in the transport direction x in the pore with the same parameters as Figure 4.12. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
159
400 psig 900 psig
0
2
4
6
Tem
pera
ture
900 psig 400 psig
0
2
4
6
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Tem
pera
ture
Figure 4.14: Time-averaged temperature distribution of pure CO2 along the pore with the same parameters as Figures 4.12 and 4.13. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
160
Figure 4.15: Snapshot of the pore containing CO2 under supercritical - subcritical conditions. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 48.6 atm (700 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) and macro side (bottom).
161
1200 psig 700 psig
0
0.1
0.2
0.3
0.4
0.5
0.6
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Den
sity
700 psig 1200 psig
0
0.1
0.2
0.3
0.4
0.5
0.6
Den
sity
Figure 4.16: Time-averaged density profiles of pure CO2 in the transport direction x in the pore with the same parameters as Figure 4.15. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
162
700 psig 1200 psig
0
2
4
6
Tem
pera
ture
1200 psig 700 psig
0
2
4
6
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Tem
pera
ture
Figure 4.17: Time-averaged temperature distribution of pure CO2 along the pore with the same parameters as Figures 4.15 and 4.16. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
163
0
2
4
6
8
10
500 600 700 800 900 1000 1100 1200 1300
Upstream pressure (psig)
Perm
eabi
lity
(gm
ole.
cm/m
in. p
si. c
m2 )
x 1
07
Macro
Nano
0
2
4
6
8
10
500 600 700 800 900 1000 1100 1200 1300
Upstream pressure (psig)
Mol
ar fl
ow (g
mol
e/m
in) x
10
11
Nano
Macro
Figure 4.18: The dependence of the permeability and molar flow of pure CO2 on the upstream pressure at T=35°C, when PΔ =500 psi is applied in the two opposite directions. Continuous and dashed curves show, respectively, the results when the upstream pressure is applied on the macropore and nanopore.
164
Figure 4.19: Snapshot of the pore containing CO2 under supercritical - subcritical conditions. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 11.2 atm (150 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) obtained after 770,000 time steps, macro side (bottom) obtained after 810,000 time steps.
165
150 psig 1200 psig
0.0
0.1
0.2
0.3
0.4
0.5
Den
sity
1200 psig 150 psig
0.0
0.2
0.4
0.6
0.8
1.0
1.2
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Den
sity
Figure 4.20: Time-averaged density profiles of pure CO2 in the transport direction x in the pore with the parameters as Figure 4.19. The upstream pressure is on the nano side (top), macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
166
Figure 4.21: Snapshot of the pore containing equimolar mixture of CH4 (triangles) and CO2 (circles) under supercritical - subcritical conditions. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on the nano side (top) and macro side (bottom).
167
500 psig 1200 psig
0.0
0.1
0.2
0.3
0.4
0.5
Den
sity
1200 psig 500 psig
0.0
0.1
0.2
0.3
0.4
0.5
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Den
sity
Figure 4.22: Time-averaged density profiles of both CH4 (solid curves) and CO2 (dashed curves) in the transport direction x in the pore with the same parameters as Figure 4.21. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
168
500 psig 1200 psig
0
2
4
6
8
Tem
pera
ture
1200 psig 500 psig
0
2
4
6
8
-35 -28 -21 -14 -7 0 7 14 21 28 35
X*
Tem
pera
ture
Figure 4.23: Time-averaged temperature distribution along the pore with the same parameters as Figures 4.21 and 4.22. The upstream pressure is on the nano side (top) and macro side (bottom). Dashed vertical lines indicate the boundaries of the pore.
169
Figure 4.24: Density profiles of an equimolar mixture of CH4 (solid curves) and CO2 (dashed curves) in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on the macro side.
170
Figure 4.25: Density profiles of an equimolar mixture of CH4 (solid curves) and CO2 (dashed curves) in pore’s cross sections. The upstream and downstream pressures are, respectively, 82.6 atm (1200 psig) and 35 atm (500 psig), and temperature is 35 °C. The upstream pressure is on the nano side.
171
Figure 4.26: Density profiles of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 96.2 atm (1400 psig) and 48.6 atm (700 psig), and temperature is 35 °C. The upstream pressure is on the macro side.
172
Figure 4.27: Density profile of pure CO2 in pore’s cross sections. The upstream and downstream pressures are, respectively, 96.2 atm (1400 psig) and 48.6 atm (700 psig), and temperature is 35 °C. The upstream pressure is on the nano side.
173
0
2
4
6
8
800 900 1000 1100 1200 1300 1400 1500
Upstream pressure (psig)
Perm
eabi
lity
(gm
ole.
cm/m
in. p
si. c
m2 )
x 1
0 7
0
1
2
3
4
5
6
7
800 900 1000 1100 1200 1300 1400 1500
Upstream pressure (psig)
Mol
ar fl
ow (g
mol
e/m
in) x
10
11
Figure 4.28: The dependence of the permeabilities and molar flows of CO2 (circles) and CH4 (triangles) on the upstream pressure in an equimolar mixture at T=35°C, when =700 psi is applied in the two opposite directions. Continuous and dashed curves show, respectively, the results when the upstream pressure is applied on the macropore and nanopore.
PΔ
174
0
2
4
6
8
10
12
600 700 800 900 1000
Δ P (psi)
Perm
eabi
lity
(gm
ole.
cm/m
in. p
si. c
m2 )
x 1
0 7
0
2
4
6
8
10
600 700 800 900 1000
Δ P (psi)
Mol
ar fl
ow (g
mol
e/m
in) x
10
11
Figure 4.29: The dependence of the permeabilities and molar flows of CO2 (circles) and CH4 (triangles) on the pressure drop in an equimolar mixture at T=35°C, when the upstream pressure is 1400 psig. Continuous and dashed curves show, respectively, the results when the upstream pressure is applied on the macropore and nanopore.
175
Chapter 5 Transport and Separation of Carbon Dioxide-Alkane Mixtures in a Carbon Pore Network under Sub- and Supercritical Conditions 5.1 Introduction
he results presented in Chapters 2 and 3, using a single carbon nanopore,
provided qualitative insight into the transport and separation of mixtures in
nanoporous materials. However, such simple pore models cannot quantitatively
represent real nanoporous membranes, a two-dimensional example of which is
shown in Figure 5.1.
T
Figure 5.1 Two-dimensional representation of a porous membrane.
176
Transport and separation properties of fluid mixtures in a real membrane are strongly
influenced, and sometimes even dominated, by the morphology of a membrane,
which consists of the connectivity of its pores, and their shapes, sizes, and surface
characteristics. Therefore, a single nanopore is an inadequate model of a membrane.
Many real nanoporous membranes have a polycrystalline or amorphous structure.
Fine crystals of various sizes create grains of different forms and sizes. Cracks,
fissures, cavities, and other defects occur on the pore surface. Yet, the main source of
heterogeneity for nanoporous membranes is their complex porous structure which
contains nanopores of different sizes and shapes, including pores with straight and
snapped parts, and contracting and diverging channels. When such single pores are
connected, they forms pore networks. The structure of real disordered porous solids,
such as activated carbon, is very complicated and, therefore, cannot be represented
by a single pore.
Chapter 4 attempted to improve the single pore model by considering a three-
pore model that were in series. The results indicated unexpected phenomena, such as
the asymmetry of the permeabilities. Therefore, the results presented in Chapter 4
indicated the significance of a representative pore network model for representing a
nanoporous membrane, in addition to the effect of the various controlling
parameters, such as the temperature, the applied pressure gradient, and the
composition of the mixture in the feed.
177
To address the problem of representing the morphology of a nanoporous
membrane by a more realistic model, we use in this chapter a three-dimensional (3D)
molecular pore network model for carbon molecular-sieve membranes (CMSMs)
based on the Voronoi tessellation. As described below, in this model the pores have
completely irregular shapes and sizes. The model allows us to investigate the effect
of the morphology of the pore space, i.e., its pore size distribution and pore
connectivity, on the transport and separation properties of fluid mixtures in a
nanoporous membrane. After describing the Voronoi model, we describe the
transport and separation properties of sub- and supercritical mixtures in the model.
5.2 Pore Network Model of CMSMs In order to generate the molecular pore network model, first we create a 3D
simulation box of carbon atoms with a structure corresponding to graphite, so that
the number density of the carbon atoms is 114 nm-3 and the spacing between the
adjacent graphite layers in the z- direction is 0.335 nm. If the pyrolysis of the
polymeric precursor is done at high enough temperatures, the resulting matrix of the
pore space has a structure similar to that of graphite and, therefore, graphite structure
can be used for the membrane atomistic structure. We then tessellate the graphitic
box by inserting in it a given number of Poisson (randomly and uniformly-selected)
points, each of which is the basis for a Voronoi polyhedron. Each polyhedron is that
178
part of the box which is nearer to its Poisson point than to any other Poisson point.
The pore space is created by specifying the desired porosity and then selecting a
number of the polyhedra in such a way that their total volume fraction equals
specified porosity. The chosen polyhedra are then designated as the membrane pores
by removing the carbon atoms inside them, as well as those that are connected to
only one neighboring carbon atom (the dangling atoms), since it is impossible to
actually have such atoms connected to the surface of the pores. The remaining
carbon atoms constitute the membrane's solid matrix, while the pore space consists
of interconnected pores of various shapes and sizes. Figure 5.2 shows a 2D Voronoi
network with 50% porosity, in which the gray polygons represent the pores of the
system.
The designation of the polyhedra as the pores can be done by at least two
different methods. If the pore polyhedra are selected at random, then, if the size of
the simulation box is large enough, the size distribution of the polyhedra will always
be Gaussian, regardless of the porosity of the pore space. This, however, is not
realistic from a practical view point, because often the membranes that are used in
practice do not possess a Gaussian pore size distribution (PSD). In the second
method, one designates the pore polyhedra in such a way that the resulting PSD can
mimic that of a real membrane, which is typically skewed. To obtain such PSDs, we
first sort and list the polyhedra in the box according to their sizes, from the largest to
smallest. The size of each polyhedron is taken to be the radius of a sphere that has
179
the same volume as the polyhedron. We then designate the polyhedra as the pores
according to their sizes, starting from the largest ones in the list.
Figure 5.3 compares the PSDs of the pore networks generated by the two
methods with 2500 Poisson points, and 50% porosity. Figure 5.4 shows the PSDs of
the pore networks generated by the biased method with 2500 Poisson points for
several porosities. The PSDs and the average pore sizes that are generated with the
bias towards the largest pores are, of course, dependent upon the porosity, and
resemble to some extent the experimental PSD (Sedigh et al., 1998, 1999, 2000; Xu
et al., 1999; Xu, Sedigh et al., 2000). Figure 5.5 shows the PSD of a typical CMSM
that has been measured experimentally by our group. Note that, unlike the traditional
pore networks that are used in the simulation of flow and transport in porous media
(Sahimi, 1993, 1995), the pore networks generated here are molecular networks in
which the interaction of the gas molecules with all the atoms in the network are
taken into account. While the PSD of the system in which the pore polyhedra are
selected at random is independent of the porosity, the PSD obtained with the bias
toward the largest pores is dependent upon the porosity. By controlling the box size
and the number of the initial Poisson points, one can independently fix the average
pore size of the pore network.
180
Figure 5.2: A two-dimensional Voronoi network.
181
Random
0.00
0.05
0.10
0.15
0.20
0.25
2 4 6 8 10 12
Pore Diameter (°A)
Pore
Siz
e D
istr
ibut
ion
Biased
0.00
0.05
0.10
0.15
0.20
0.25
2 4 6 8 10 12
Pore Diameter (°A)
Pore
Siz
e D
istr
ibut
ion
Figure 5.3: Computed pore size distribution (PSD) for the model CMSMs. On the top is the PSD for a system in which the pores are selected randomly. On the bottom is the PSD for a system in which the pores are generated according to their sizes, starting from the largest size.
182
Biased
0.00
0.05
0.10
0.15
0.20
0.25
2 4 6 8 10 12
Pore Diameter (°A)
Pore
Siz
e D
istr
ibut
ion
50%25%70%
Figure 5.4: Computed PSD for the model CMSMs for different porosities. The pores are generated according to their sizes, starting from the largest size.
Figure 5.5: PSD of the membrane used in the experiments.
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5.3 NEMD Simulation in CMSM Pore Network Non-equilibrium molecular dynamics simulations have been implemented to study
the transport and separation properties of binary mixtures consisting of CO2 and n-
alkanes, under both sub- and supercritical conditions using a 3D molecular pore
network model for the CMSM that we described above. The dimensions zyx LLL ××
of the simulation cell that we used are 65.6395.6390.63 ×× Å. The total initial
number of carbon atoms in the simulation cell was 29,640. We used the biased
method of generating the pore space with 50% porosity to construct the pore
network. We inserted 5200 Poisson points in the cell and constructed a 3D Voronoi
tessellation of the cell containing the same number of polyhedra. We generated three
different pore network structures with 50% porosity with the biased method. The
simulation results of three different structures were averaged to make the results
more uniform. Since the Poisson points in each structure were generated randomly,
the pore network structures are different. The average pore size for the pore networks
is about 5.1Å, if the pore polyhedra are selected with a bias toward the largest sizes.
As can be seen in Figure 5.5, the experimental PSD for CMSM also shows a peak
around 5 Å. Periodic boundary conditions were used to construct the pore network
model in all the three directions.
We considered two models in our work in order to study by NEMD
simulations the transport of the fluids in the pore network model. First, we
considered two bulk regions as the control volumes (CVs) at the two opposite
184
surfaces of the pore network. In the second approach, we extended the graphite
atoms positions of the pore network structure at the interfaces of the pore and CVs,
and inserted the molecules inside the empty spaces in the CVs. The latter model
creates isolated channels of carbon atoms in the CVs which originate from pore
polyhedra at the enterance and the exit of the pore network structure.
5.4 Molecular Models of the Fluid and the Interaction Potentials The transport and separation properties of the following binary mixtures were
studied using the pore network model: CH4/CO2, CH4/C3H8, CO2/C3H8, and
CH4/C4H10. The CH4 and CO2 molecules are represented as Lennard-Jones (LJ)
spheres, characterized by effective LJ size and energy parameters, σ and ε . All the
quantities of interest are made dimensionless with the help of the CH4 parameters,
1σ and 1ε . Table 2.1 lists the conversions between the dimensionless and
dimensional quantities. The C3H8, and C4H10 molecules are represented by united-
atom (UA) model (Ryckaert and Bellemans, 1978) as we described earlier in Section
3.3, and grown by a configurational-bias Monte Carlo method (De Pablo et al., 1992;
Frenkel et al., 1991; Harris and Rice, 1988; Laso et al., 1992; Macedonia and
Maginn, 1999; Mooij et al., 1992; Siepmann and Frenkel, 1992; Smit et al., 1995)
(see Section 3.4). The nonbonded interactions between interaction centers of
different molecules are described with cut-and-shifted LJ potential. No tail
corrections were applied to the potential. The Lorentz-Berthelot mixing rules were
185
used in the simulations to compute the size and energy parameters of the unlike
molecules (see Section 2.4).
For simplicity, the total molecular mass of alkane was equally divided
between the C atoms and, therefore, CH2 and CH3 groups had equal molecular mass.
Table 3.1 lists the size and energy parameters of CH4, CO2, and those of the CH2 and
CH3 groups. The atoms and the UA centers are connected by harmonic potentials.
The distance between the atoms is fixed at 1.53 Å. The intramolecular interactions
consist of the contributions by bond-bending (BB) and torsional forces. For the BB
term, the van der Ploeg-Berendsen potential and for the torsional potential, the
Ryckaert-Bellemans potential is used (see Section 3.3). The cut off distance for the
interaction between the gas molecules was taken to be 4
5.3 CHσ for CH4/C3H8,
CO2/C3H8, and CH4/C4H10 mixtures, and 4
0.4 CHσ for CH4/CO2 mixture. The cut off
distance for the interaction between the gas molecules and carbon wall atoms was
taken to be 4
5.3 CHσ for all of the above mentioned mixtures. The interaction
between the gas molecules with the entire carbon pore wall was taken to be the sum
of the LJ potentials between the gas molecules and each individual carbon atoms in
the wall. In order to calculate the potential between the gas molecules and carbon
atoms in the wall, the simulation cell was discretized into zyx nnn ×× grid points
along the three directions, using the same method as we described in Section 4.4.
186
5.5 Results and Discussions We have carried out extensive NEMD simulations of several binary mixtures
mentioned above in the 3D molecular pore network model of CMSM, under sub- and
supercritical conditions. In what follows we present and discuss the results for each
mixture separately.
5.5.1 Methane-Carbon Dioxide Mixtures Figure 5.6 presents the density profiles ( )z
i xρ for an equimolar mixture of CH4 and
CO2, for the case in which two bulk regions are connected to two opposite surfaces
of the pore network. In order to compute the density profiles, the system was, as
described above, divided into zyx nnn ×× small subcells with ,216=xn 140=yn ,
and , thus resulting in over 4,233,600 subcells. This allowed us to
accurately compute the profiles. To study the effect of the external pressure gradient
and supercriticality, we fixed the upstream pressure at 120 atm, which is
significantly above the minimum pressure for supercriticality of the mixture, and
varied the downstream pressure over a range of values that includes both
supercritical and subcritical conditions. Figure 5.6 shows the time-averaged density
profiles for both components at T = 40°C, in the two CVs and the pore along the
transport direction. The downstream pressures are 20 atm, 50 atm, and 90 atm.
The density profiles are essentially flat in the two CVs (in the region
140=zn
( −x )
187
38.8*15.25 −<<− X and 15.25*38.8 << X ). The downward curvatures at
and are attributed to two facts: (i) the leakage of the
molecules out of the two CVs, and (ii) no molecules have been inserted in a 0.5
15.25* −=X 15.25* =X
4CHσ
distance from the end of CVs. However, such deviations from a flat profile are
insignificant. In the pore region ( )38.8*38.8 <<− X , the two profiles decrease from
left to right, which is expected. The fluctuations in the density profile in the pore
network are caused by adsorption on the pores' walls, and the inhomogeneous
structure of the pore network. Due to the shapes of the pores in a Voronoi structure,
which are in the form of polyhedra made of insecting planes, one may have
significant accumulation of the molecules that attempt to pass from one such
polyhedron to another with a smaller pore mouth. The density profiles show that by
increasing the downstream pressure to 90 atm the pore network is almost packed,
with the fluids being in a liquid-like state, indicating by their high densties.
To show that the fluctuations in the density profiles of Figure 5.6 are not due
to non-isothermal effects, we show in Figure 5.7 the time-averaged distribution of
the dimensionless temperature for the same equimolar mixture as that in Figure 5.6,
indicating that the temperature is constant throughout the pore network and two CVs.
Hence, there is no contribution by a temperature gradient to the distribution of the
molecules in the pore network. Moreover, all the three systems' temperatures are
equal, as they should be.
The fluxes of CO2 and CH4 in their equimolar mixture, along with their
permeabilities and the corresponding separation factors are exhibited in Figure 5.8.
188
In this case, the upstream pressure is fixed at 120 atm, while the downstream
pressure varies. Figure 5.8 shows that by increasing PΔ , the fluxes' and
permeabilities' of both components will increase, while separation factor stays
essentially constant. The separation factors are comparable with those that we
obtained in Chapter 2 with a single pore. This results is somewhat surprising, since
one expects to obtain higher separation factors with a pore space of interconnected
pores as molecular sieving, which is absent in a single-pore model, is present in a
Voronoi network. However, the porosity of the Voronoi network is relatively high,
which implies that the pore space is relatively open and, therefore, the actual mean
pore size is larger than the nominal mean pore size of 5Å.
Figure 5.9 shows the time-averaged density profiles ( )zi xρ for both
components in a mixture in which the mole fraction of CO2 is 0.9, and T = 40°C.
Once again, the upstream pressure is 120 atm, while the downstream pressures are 20
atm, 50 atm, and 90 atm. As expected, the density of CO2 is much larger than CH4.
The corresponding time-averaged temperature profiles for the same system and
mixtures are shown in Figure 5.10. Figure 5.11 presents the corresponding fluxes and
permeabilites of the two components of the same mixture, along with the
corresponding separation factors. The surprising aspect of these results is that, the
separation factor attains a maximum when the downstream pressure is equal to 50
atm. Recall that the same type of maximum was also obtained when transport of such
mixtures was simulated in a single pore (see Chapter 2), except that in the present
case the maximum is very pronounced. The reason for the existence of this
189
maximum was already explained in Chapter 2, where we reasoned that it is due to
the optimal condition for convection/diffusion of the two components of the mixture.
Figure 5.12 shows a snapshot of the system for an equimolar mixture at T =
40°C, obtained after 2,220,000 time steps, where the upstream and downstream
pressures are, respectively, 120 atm and 90 atm, while Figure 5.13 presents a
snapshot of a mixture in which the mole fraction of CO2 is 0.9, obtained after
1,740,000 time steps.
Since the pore sizes in the pore network are very small, with their average
size being about 5Å, it is very difficult for the molecules to be transported inside the
pore network. This is particularly true for the alkane chains. In fact, the fluid
molcules adsorb on the carbon structure and block the pore entrances. In addition,
due to the pore entrance and exit effects, controlling the temperature and holding it
constant are difficult, especially when alkane chains are present in the system. This
effect leads to hot spots and noticeable peaks in the temperature profile at the
interfaces between the pore network and bulk regions. In order to resolve this
problem, we extended the pores that are connected to two opposing surfaces of the
network. The extended part of such pores than act as the CVs for them that are in
equilibrium with the bulk regions. In effect, for each pore that is connected to the
external surface of the system, we create its own CV, similar to the single-pore
model studied in Chapter 2. The molecules are then inserted in such CVs using the
GCMC method. Since each CV acts independent of all other CVs, the GCMC part of
the computations becomes amenable to parallel processing and computations. In
190
such a model, the fluid molecules go directly inside the actual pores in the pore
network that are connected to the external surface, hence helping to eliminate the
accumulation of the fluid molecules at the pores' mouth. In the what follows we
present our simulation results using this model. For the results that we describe
below, we used ,456=xn 140=yn , and 140=zn to create the small subcells and
compute the density profiles.
Figures 5.14 represents the resulting density profiles ( )zi xρ for a binary
mixture of CH4 and CO2 at T = 40°C. The upstream pressure is 120 atm, while the
downstream pressures are 20 atm, 50 atm, and 90 atm. Qualitatively, the density
profiles shown in Figure 5.14 are similar to those in Figure 5.6, except that they are
much smoother. Moreover, (i) the density of CO2 in two CVs is much higher due to
the adsorption of CO2 molecules in the created graphite channel, and (ii) the two
peaks at the entrance and exit of the pore network that are seen in Figure 5.6 no
longer exist in Figure 5.14. The corresponding temperature profile is shown in
Figure 5.15, while a snapshot of the molecules' distribution in the pore network,
obtained after 2,650,000 time steps, is shown in Figure 5.16.
The dependence of the components' fluxes and permeabilities, in an
equimolar mixture, on the pressure drop PΔ applied along the pore is shown in
Figure 5.17. The upstream pressure is fixed at 120 atm, and T = 40°C. Numerically,
the results shown in Figure 5.17 are similar to those in Figure 5.8, which might be
expected, but the shapes of the curves are somewhat different, which might be due to
191
less fluctuations in the density profiles of the two components, and the absence of
hot spots in the system.
Using the same simulation technique, we also studied the effect of mixture's
composition on its transport and separation properties, in order to see whether any
discernable differences exist between these systems and those described above when
we connect the pore network to two large CVs in equilibrium with two bulk regions.
Figure 5.18 shows the snapshot of the pore network and the distribution of the
molecules in it, in which the CO2 mole fraction in the feed is 0.7. The snapshot was
obtained after 2,315,000 time steps. The upstream and downstream pressures are,
respectively, 120 atm and 20 atm and T = 40°C, which should be compared to Figure
5.16.
Figure 5.19 shows the time-averaged density profiles of the two components
of three mixtures with different compositions at T = 40°C. The upstream and
downstream pressures are, respectively, 120 atm and 20 atm, and the mole fraction
of CO2 in the feed is 0.5, 0.7, and 0.9. The corresponding time-averaged distributions
of the dimensionless temperature are shown in Figure 5.20, indicating the
temperature is constant throughout the pore network and CVs.
The dependence of the fluxes and permeabilities of CO2 and CH4, and the
corresponding separation factor, on the mole fraction of CO2 in the feed are shown in
Figure 5.21. The rest of the parameters of the system are the same as before. It is
somewhat surprising that as the CO2 mole fraction increases, the separation factor
decreases, since one might expect that, due to high affinity of CO2 for adsorption on
192
carbon surfaces, a mixture with more CO2 can be better separated than one which is
leaner in CO2.
Figure 5.22 present the time-averaged density profiles ( )zi xρ of both
components in an equimolar mixture at three different temperatures. The upstream
and downstream pressures are, respectively, 120 atm and 90 atm. Increasing the
temperature reduces adsorption and, therefore, the densities decrease, since there
would be a larger flux of molecules leaving the pore network. The corresponding
time-averaged temperature profiles are shown in Figure 5.23.
5.5.2 Carbon Dioxide-Propane, Methane-Propane, and Methane-Butane Mixtures We now present and discuss the simulation results for the CO2/C3H8, CH4/C3H8, and
CH4/C4H10 mixtures. In these simulations we used the second method of creating
CVs for those pores that are directly connected to the external surface of the pore
network, namely, extending the graphite walls of the pores and creating independent
CVs for each pore.
Figure 5.24 demonstrates the time-averaged density profiles ( )zi xρ of CO2
and C3H8 at three different temperatures. The upstream and downstream pressures
are, respectively, 3 atm and 1 atm, and the mole fraction of CO2 in the feed is 0.7. As
can be seen, by increasing the temperature not only the density of both components
decreases due to reduction in the amount of adsorption, but they also become
193
increasingly similar. However, note that despite the fact that the mixture is rich in
CO2, the propane density is higher, due to adsorption and shielding effects described
in Chapter 3 for alkane chain molecules. The corresponding average temperature
distributions are shown in Figure 5.25, which show that the dimensionless
temperature of the mixture is almost constant throughout the system.
Temperature-dependence of the flux and permeability of the components in a
mixture of CO2 and C3H8 in which the CO2 mole fraction is 0.7, and the
corresponding separation factors are shown in Figure 5.26. The upstream and
downstream pressures are, respectively, 3 atm and 1 atm. Increasing the temperature
reduces adsorption. This results in the fluxes and permeabilities of both components
becoming increasingly similar. As a result, the separation factor decreases.
The effect of the composition on the transport and separation of CO2/C3H8
mixtures was also studied. Figure 5.27 shows the time-averaged density profiles
( )zi xρ of both components at T = 50°C for three composition of the mixture. The
upstream and downstream pressures are, respectively, 3 atm and 1 atm. In the
equimolar feed mixture the density of propane is higher in the pore network,
signifying the effect of stronger tendency of the graphite atoms to attract propane due
to its energy parameter which is larger than that of CO2. Even if we increase the
mole fraction of CO2 in the feed to higher values, the trends remain the same. The
corresponding time-averaged distribution of the dimensionless temperature with the
same parameters as in Figure 5.27 are shown in Figure 5.28.
194
Figure 5.29 shows the dependence of the fluxes and permeabilities of CO2
and C3H8, and the corresponding separation factors, on the mole fraction of CO2 in
the feed at T = 50°C. The upstream and downstream pressures are, respectively, 3
atm and 1 atm. While the flux of CO2 increases with increasing its mole fraction in
the feed, the opposite is true about the flux of C3H8. But, the permeabilities and,
therefore, the separation factors are almost independent of the mixture's composition.
Figure 5.30 shows a 3D snapshot of the mixture in the pore network at T =
50°C, obtained after 4,000,000 time steps. The CO2 mole fraction in the feed is 0.85,
and the upstream and downstream pressures are, respectively, 3 atm and 1 atm. The
snapshot has been also shown at a larger scale to show better the positions of C3H8
and CO2 molecules.
Figure 5.31 presents the time-averaged density ( )zi xρ and temperature
profiles for a mixture of CH4 and C3H8 at T = 50°C. The upstream and downstream
pressures are, respectively, 3 atm and 1 atm, with CH4 mole fraction in the feed
being 0.7. Even though the mixture is rich in CH4, the density of C3H8 is higher, both
under the bulk conditions and in the pore network.
Figure 5.32 shows the time-averaged density profiles ( )zi xρ in equimolar
mixtures of CO2/C3H8 and CH4/C3H8 at T = 50°C. The upstream and downstream
pressures in both cases are 30 atm and 10 atm, respectively. Once again, the density
of C3H8 is higher than those of CH4 and CO2 in both mixtures, due to adsorption and
the shielding effect as described earlier in Chapter 3. We then increased the upstream
pressure to above the supercritical pressure for a mixture of CO2 and C3H8. Figure
195
5.33 presents the resulting time-averaged temperature and density profiles ( )zi xρ if
the upstream pressure is 120 atm, above the supercritical value, at T = 50°C, while
the downstream pressure is 20 atm. The mole fraction of CO2 in feed is 0.9. More
interesting from a practical view point are the fluxes and permeabilites of the two
components in the mixture and the corresponding separation factors. These are
shown in Figure 5.34. They indicate that the fluxes of both components increase by
increasing the pressure gradients imposed on the pore network. The separation factor
achieves a maximum where the permeabilities attain their minimum values. This
happens when the downstream pressure is equal to 50 atm.
Figure 5.35 represents the time-averaged density ( )zi xρ and temperature
profiles of CH4 and C4H10 at T = 50°C. The upstream and downstream pressures are,
respectively, 3 atm and 1 atm, with the mole fraction of CH4 in the feed being 0.7.
Once again, the density of C4H10 is higher than that of CH4, due to the effect of
adsorption and shielding effect.
Since the pore sizes in the pore network are very small, with an average of
about 5Å, it is diffult for long alkane chains, such as butane and hexane, to move in
the pore network, especially when the pressure is high. Experiments performed by
our group indicate that as the pressure gradient applied to a nanoporous CMS
membrane increases, the motion of n-alkanes in the membrane becomes increasingly
more difficult. At some point, there appears to be a freezing transition whereby the
n-alkane chains “freeze” inside the nanopores and do not move, hence completely
196
plugging the membrane. We have observed this phenomenon in our simulation as
well.
5.6 Asymmetric Pore Network Model In Chapter 4, we studied the effect of asymmetry on the permeation properties of a
model membrane when a pressure gradient is applied to the membrane, its
permeation properties are merasured, and then the direction of the pressure gradient
is reversed. Recall from Chapter 4 that the membrane was modeled as three single
carbon slit pores in series, with different sizes, representing the macro-, meso- and
nanopores, such that each of the slit pores represented one layer of the membrane.
In the present chapter a pore network is developed to model the morphology
of a membrane with different layers, each having different pore structures, which
represents more realistically a supported membrane. To do so, we modeled the
support and the membrane layer by using a pore network that has different average
pore sizes for each of the layers. To our knowledge, this is the first study that
considers both the support and membrane layers together as two continuous
connected pore network models. To this end, and as a first trial, we divided the
simulation cell into two equal sections. Then, we randomly inserted 40 Poisson
points in the first section and 2100 Poisson points in the second section in order to
construct each of the pore networks. Since the number of Poisson points in the first
section is less than the second part, its corresponding average size of the constructed
197
polyhedra is larger than that of the second part. By the same token, the average pore
size of the pore network in the support layer is larger than that of the membrane
layer. The dimensions zyx LLL ×× of the simulation cell are Å.
The carbon atoms were packed with a structure corresponding to graphite, with the
total initial number of carbon atoms in the simulation cell being 29640. In order to
make the pores uniformly in our entire cell, we used the Gaussian method of
generating the pore space in which the pore polyhedra are selected at random. Note
that since the average pore size in the support layer is larger than that of the
membrane part, we cannot use the biased method of generating the pore space. The
total porosity to construct the pore network was 0.5. The average pore sizes for the
first and second layers were about 14.4 Å and 5.2 Å, respectively. The resulting
three-dimensional pore network and the Poisson points are shown in Figure 5.36.
65.6395.6390.63 ××
After constructing the asymmetric 3D molecular pore network, the non-
equilibrium molecular dynamics method was used to expose the system to an
external pressure gradient in a fixed direction. The pore network was connected to
CVs in equilibrium to two bulk regions. We studied transport and separation of an
equimolar mixture of CH4 and CO2 at T = 40°C. The upstream and downstream
pressures are 120 atm and 20 atm, respectively. The simulation results were
computed after time steps. 6103×
Figure 5.37 presents the time-averaged density profiles of both components
when the pressure gradient is applied in two opposite directions. The corresponding
time-averaged dimensionless temperature of the system for both cases are shown in
198
Figure 5.38. Figure 5.39 shows the snapshots of the mixture in the asymmetric pore
network when the pressure gradient is applied in the two opposite directions, which
shows the fluid molecules are more packed in upstream. The fluxes and, hence, the
permeabilities of the two components are not the same when the pressure gradient is
applied in the two opposite directions, although the difference in the permeances for
the two components are small. However, if we model the support layer with larger
average pore size, e.g., 70-80 Å, which would be more appropriate than 14.4 Å that
we used in the present simulations, the difference between the average pore size of
the support and the membrane layer will increase. In that case, the difference
between the permeances should increase, if our results presented in Chapter 4 are
any indications. However, in order to construct such a model, one must use much
larger simulation cells which would require massive computations that are not
possible at the moment due to the computational facility limitations.
5.7 Summary
Extensive molecular dynamics simulations, using the dual control-volume
nonequilibrium molecular dynamics method, were carried out to study the transport
and separation of binary mixtures consisting of CO2 and n-alkane chains, under both
sub- and supercritical conditions in nanoporous CMS membranes. The membrane
was represented by a three-dimensional pore space, generated atomistically by the
199
Voronoi tessellation of the space, using tens of thousands of atoms. The Voronoi
model contains interconnected pores of various sizes and shapes, which is a realistic
model of the membrane and allows us to investigate the effect of morphology of the
pore space, i.e., its pore size distribution and pore connectivity, on the transport and
separation properties of fluid mixtures. The effect of the composition of the feed, the
temperature of the system, as well as the applied pressure gradient on the transport
and separation of the mixtures were all studied.
200
P2 =20 atm
0.00
0.05
0.10
0.15
0.20
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
P2 =50 atm
0.00
0.05
0.10
0.15
0.20
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
P2 =90 atm
0.00
0.05
0.10
0.15
0.20
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
Figure 5.6: Time-averaged density profiles of both components of an equimolar mixture of CO2 (dashed curves) and CH4 (solid curves) at T=40°C in the transport direction x . The upstream pressure is 120 atm, while the downstream pressures are 20 atm, 50 atm, and 90 atm. Dashed lines indicate the boundaries of the pore network region.
201
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.7: Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.6. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore network region.
202
0
20
40
60
80
10 20 30 40 50 60 70 80 90 100 110
ΔP (atm)
Flux
( gr
mol
e/m
in.c
m 2
)
CH4
CO2
1.0
1.5
2.0
2.5
3.0
10 20 30 40 50 60 70 80 90 100 110
ΔP (atm)
Sep
arat
ion
Fact
or
0
2
4
6
8
10
10 20 30 40 50 60 70 80 90 100 110
ΔP (atm)
Perm
eabi
lity
( gr
mol
.cm
/min
.atm
.cm
2 ) x
10
7
CO2
CH4
Figure 5.8: The dependence of the flux and permeability of CO2 (dashed curves) and CH4 (solid curves), and the corresponding separation factor, on the pressure drop ΔP applied to the pore network at T=40°C. The mixture is equimolar, with the upstream pressure being 120 atm.
203
P2 =20 atm
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
P2 =50 atm
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
P2 =90 atm
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
Figure 5.9: Time-averaged density profiles of both components of a mixture of CO2 (dashed curves) and CH4 (solid curves) with a mole fraction of 90% CO2 and 10% CH4 at T=40°C in the transport direction x . The upstream pressure is 120 atm, while the downstream pressures are 20 atm, 50 atm, and 90 atm. Dashed lines indicate the boundaries of the pore network region.
204
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.10: Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.9. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore network region.
205
0
2
4
6
8
10 20 30 40 50 60 70 80 90 100 110
ΔP (atm)
Per
mea
bilit
y (
grm
ole.
cm/m
in.a
tm.c
m 2
) x 1
0 7
CO2
CH4
1.0
2.0
3.0
4.0
5.0
6.0
10 20 30 40 50 60 70 80 90 100 110
ΔP (atm)
Sep
arat
ion
Fact
or0
20
40
60
80
10 20 30 40 50 60 70 80 90 100 110
ΔP (atm)
Flux
( gr
mol
e/m
in.c
m 2
) CO2
CH4
Figure 5.11: The dependence of the flux and permeability of CO2 (dashed curves) and CH4 (solid curves), and the corresponding separation factor, on the pressure drop ΔP applied to the pore network at T=40°C, in a mixture in which the mole fraction of CO2 is 0.9 and the upstream pressure is fixed at 120 atm.
206
Figure 5.12: Snapshot of the pore network containing an equimolar mixture of CH4 (circles) and CO2 (asterisks) at T=40°C, obtained after 2,220,000 time steps. The upstream and downstream pressures are, respectively, 120 atm and 90 atm.
207
Figure 5.13: Snapshot of the pore network containing CH4 (circles) and CO2 (asterisks) at T=40°C, obtained after 1,740,000 time steps. The CO2 mole fraction in the feed is 0.9. The upstream and downstream pressures are, respectively, 120 atm and 90 atm.
208
0.0
0.1
0.2
0.3
0.4
Dens
ity
0.0
0.1
0.2
0.3
0.4
Dens
ity
0.0
0.1
0.2
0.3
0.4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Dens
ity
Figure 5.14: Time-averaged density profiles of both components of an equimolar mixture of CO2 (dashed curves) and CH4 (solid curves) at T=40°C in the transport direction x . The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore network region.
209
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.15: Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.14. The upstream pressure is 120 atm, while the downstream pressures are 20 atm (top), 50 atm (middle), and 90 atm (bottom). Dashed lines indicate the boundaries of the pore network region.
210
Figure 5.16: Snapshot of the pore network containing an equimolar mixture of CH4 (circles) and CO2 (asterisks) at T=40°C obtained after 2,650,000 time steps. The upstream and downstream pressures are, respectively, 120 atm and 20 atm.
211
0
20
40
60
80
10 30 50 70 90 110
ΔP (atm)
Flux
( gm
ole/
min
.cm
2 )
0
2
4
6
8
10
10 30 50 70 90 110
ΔP (atm)
Per
mea
bilit
y (
gmol
e.cm
/min
.atm
.cm
2 ) x
107
Figure 5.17: The dependence of the flux and permeability of CO2 (dashed curves) and CH4 (solid curves) in an equimolar mixture on the pressure drop ΔP applied to the pore network at T=40°C. The upstream pressure is fixed at 120 atm.
212
Figure 5.18: Snapshot of the pore network containing CH4 (circles) and CO2 (asterisks) at T=40°C obtained after 2,315,000 time steps. The CO2 mole fraction in the feed is 0.7. The upstream and downstream pressures are, respectively, 120 atm and 20 atm.
213
0.0
0.1
0.2
0.3
0.4
0.5
Den
sity
0.0
0.1
0.2
0.3
0.4
0.5
Dens
ity
0.0
0.1
0.2
0.3
0.4
0.5
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Dens
ity
Figure 5.19: Time-averaged density profiles of both components of CO2 (dashed curves) and CH4 (solid curves) at T=40°C in the transport direction x . The upstream and downstream pressures are, respectively, 120 atm and 20 atm. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.9 (bottom). Dashed lines indicate the boundaries of the pore network region.
214
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.20: Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.19. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.9 (bottom). Dashed lines indicate the boundaries of the pore network region.
215
0
20
40
60
80
0.4 0.5 0.6 0.7 0.8 0.9 1.0
CO2 Mole Fraction in the Feed
Flux
( gm
ole/
min
.cm
2 )
0
2
4
6
8
10
0.4 0.5 0.6 0.7 0.8 0.9 1.0
CO2 Mole Fraction in the Feed
Per
mea
bilit
y (
gmol
e.cm
/min
.atm
.cm
2 ) x
107
0.0
0.5
1.0
1.5
2.0
2.5
3.0
0.4 0.5 0.6 0.7 0.8 0.9 1.0
CO2 Mole Fraction in the Feed
Sep
arat
ion
Fact
or
Figure 5.21: The dependence of the flux and permeability of CO2 (dashed curves) and CH4 (solid curves), and the corresponding separation factor, on the mole fraction of CO2 in the feed at T=40°C. The upstream and downstream pressures are, respectively, 120 atm and 20 atm.
216
T = 20 °C
0.0
0.1
0.2
0.3
0.4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
T = 100 °C
0.0
0.1
0.2
0.3
0.4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
T = 140 °C
0.0
0.1
0.2
0.3
0.4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
Figure 5.22: Time-averaged density profiles of both components of CO2 (dashed curves) and CH4 (solid curves) in the transport direction x at different temperatures. The upstream and downstream pressures are, respectively, 120 atm and 90 atm, and the mixture is equimolar. Dashed lines indicate the boundaries of the pore network region.
217
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.23: Time-averaged temperature profiles of mixture of CO2 and CH4 with the same parameters as Figure 5.22. Temperature is fixed at 20°C (top), 100°C (middle), and 140°C (bottom). Dashed lines indicate the boundaries of the pore network region.
218
T=25°C
0.00
0.02
0.04
0.06
0.08
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
T=50°C
0.00
0.02
0.04
0.06
0.08
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Dens
ity
T=75°C
0.00
0.02
0.04
0.06
0.08
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
Figure 5.24: Time-averaged density profiles of both components of CO2 (solid curves) and C3H8 (dashed curves) in the transport direction x at different temperatures. The upstream and downstream pressures are, respectively, 3 atm and 1 atm and the mole fraction of CO2 in the feed is 0.7. Dashed lines indicate the boundaries of the pore network region.
219
0
1
2
3
4Te
mpe
ratu
re
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.25: Time-averaged temperature profiles of mixture of CO2 and C3H8 with the same parameters as Figure 5.24. Temperature is fixed at 25°C (top), 50°C (middle), and 75°C (bottom). Dashed lines indicate the boundaries of the pore network region.
220
0
5
10
15
20
10 30 50 70 90
Temperature (°C)
Flux
( gm
ole/
min
.cm
2
0
20
40
60
80
100
120
140
10 30 50 70 90
Temperature (°C)
Perm
eabi
lity
( gm
ole.
cm/m
in.a
tm.c
m 2
) x 1
07
)
0
2
4
6
8
10 30 50 70 90
Temperature (°C)
Sep
arat
ion
Fact
or
Figure 5.26: The dependence of the flux and permeability of CO2 (solid curves) and C3H8 (dashed curves), and the corresponding separation factor, on the temperature. The upstream and downstream pressures are, respectively, 3 atm and 1 atm, and the mole fraction of CO2 in the feed is 0.7.
221
0.00
0.02
0.04
0.06
0.08
Den
sity
0.00
0.02
0.04
0.06
0.08
Dens
ity
0.00
0.01
0.02
0.03
0.04
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Dens
ity
Figure 5.27: Time-averaged density profiles of both components of CO2 (solid curves) and C3H8 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.85 (bottom). Dashed lines indicate the boundaries of the pore network region.
222
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.28: Time-averaged temperature profiles of mixture of CO2 and C3H8 with the same parameters as Figure 5.27. The mole fraction of CO2 in feed is 0.5 (top), 0.7 (middle) and 0.85 (bottom). Dashed lines indicate the boundaries of the pore network region.
223
0
5
10
15
20
0.4 0.5 0.6 0.7 0.8 0.9 1.0
CO2 Mole Fraction in the Feed
Flux
( gm
ole/
min
.cm
2 )
0
20
40
60
80
100
120
0.4 0.5 0.6 0.7 0.8 0.9 1.0
CO2 Mole Fraction in the Feed
Perm
eabi
lity
( gm
ole.
cm/m
in.a
tm.c
m 2
) x 1
07
0
2
4
6
8
0.4 0.5 0.6 0.7 0.8 0.9 1.0
CO2 Mole Fraction in the Feed
Sepa
ratio
n Fa
ctor
Figure 5.29: The dependence of the flux and permeability of CO2 (solid curves) and C3H8 (dashed curves), and the corresponding separation factor, on the mole fraction of CO2 in the feed at T=50°C. The upstream and downstream pressures are, respectively, 3 atm and 1 atm.
224
Transport Direction
Figure 5.30: Distribution of CO2 (triangles) and C3H8 chains in a pore network at T=50°C, obtained after 4,000,000 time steps. The CO2 mole fraction in the feed is 0.85. The upstream and downstream pressures are, respectively, 3 atm and 1 atm.
225
0
0.01
0.02
0.03
0.04
0.05
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Dens
ity
0
2
4
6
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.31: Time-averaged temperature and density profiles of both components of CH4 (solid curves) and C3H8 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The mole fraction of CH4 in feed is 0.7. Dashed lines indicate the boundaries of the pore network region.
226
0.00
0.05
0.10
0.15
0.20
0.25
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
0.00
0.05
0.10
0.15
0.20
0.25
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
Figure 5.32: Time-averaged density profiles of both components in an equimolar mixture of CO2 (solid curves) and C3H8 (dashed curves) (top), and in an equimolar mixture of CH4 (solid curves) and C3H8 (dashed curves) (bottom), at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 30 atm and 10 atm. Dashed lines indicate the boundaries of the pore network region.
227
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
0.40
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
0
2
4
6
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.33: Time-averaged temperature and density profiles of both components of CO2 (solid curves) and C3H8 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 120 atm and 20 atm. The mole fraction of CO2 in feed is 0.9. Dashed lines indicate the boundaries of the pore network region.
228
0
1
2
3
4
5
6
7
8
10 30 50 70 90 110
ΔP (atm)
Sepa
ratio
n Fa
ctor
0
10
20
30
40
10 30 50 70 90 110
ΔP (atm)
Flux
( gm
ole/
min
.cm
2
0
2
4
6
8
10
10 30 50 70 90 110
ΔP (atm)
Per
mea
bilit
y (
gmol
e.cm
/min
.atm
.cm
2 ) x
107
)
Figure 5.34: The dependence of the flux and permeability of CO2 (solid curves) and C3H8 (dashed curves), and the corresponding separation factor, on the pressure drop ΔP applied to the pore network at T=50°C, in a mixture in which the mole fraction of CO2 is 0.9 and the upstream pressure is fixed at 120 atm.
229
0.00
0.03
0.06
0.09
0.12
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
0
2
4
6
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
Figure 5.35: Time-averaged temperature and density profiles of both components of CH4 (solid curves) and C4H10 (dashed curves) at T=50°C in the transport direction x . The upstream and downstream pressures are, respectively, 3 atm and 1 atm. The mole fraction of CH4 in feed is 0.7. Dashed lines indicate the boundaries of the pore network region.
230
Figure 5.36: A three-dimensional asymmetrical Voronoi network. Poisson points are shown in top figure and the pore polyhedra are shown in bottom figure.
231
0
0.04
0.08
0.12
0.16
0.2
Dens
ity
0
0.04
0.08
0.12
0.16
0.2
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Den
sity
Figure 5.37: Time-averaged density profiles of CH4 (solid curves) and CO2 (dashed curves) in an equimolar mixture at T=40°C in the transport direction x . The upstream pressure is fixed at 120 atm, in left CV (top) and right CV (bottom), and the downstream pressure is 20 atm. Dashed lines indicate the boundaries of the pore network region.
232
0
1
2
3
4
-25 -20 -15 -10 -5 0 5 10 15 20 25
X*
Tem
pera
ture
0
1
2
3
4
Tem
pera
ture
Figure 5.38: Dimensionless temperature distribution in a pore and the two control volumes, containing CH4 and CO2 in an equimolar mixture at T=40°C. The upstream pressure is fixed at 120 atm, in left CV (top) and right CV (bottom), and the downstream pressure is 20 atm. Dashed lines indicate the boundaries of the pore network region.
233
Figure 5.39: Snapshot of the pore network containing an equimolar mixture of CH4 (circles) and CO2 (asterisks) at T=40°C. The upstream pressure is fixed at 120 atm, in left CV (top) and right CV (bottom), and the downstream pressure is 20 atm.
234
Bibliography Acharya, M., B. A. Raich, H. C. Foley, M. P. Harold, and J. J. Lerou, 1997, Metal-
supported carbogenic molecular sieve membranes: synthesis and applications: Ind. Eng. Chem. Res., v. 36, p. 2924.
Adams, D. J., 1975, Grand canonical ensemble Monte Carlo for a Lennard-Jones
Fluid: Mol. Phys., v. 29, p. 307. Afrane, G., and E. H. Chimowitz, 1993, A molecular thermodynamic model for
adsorption equilibrium from supercritical fluids: J. Supercritical Fluids, v. 6, p. 143.
Afrane, G., and E. H. Chimowitz, 1996, Experimental investigation of a new
supercritical fluid-inorganic membrane separation process: J. Memb. Sci., v. 116, p. 293.
Akgerman, A. K., and S. D. Yao, 1993, ACS Symp. Ser., v. 514, p. 294. Alder, B. J., and T. E. Wainwright, 1957, Phase transition for a hard sphere system:
J. Chem. Phys., v. 27, p. 1208. Allen, M. P., and D. J. Tildesley, 1987, Computer Simulation of Liquids: Oxford,
Oxford University Press. Andersen, H. C., 1983, Rattle: A “velocity” version of the shake algorithm for
molecular dynamics calculations: J. Comp. Phys., v. 52, p. 24. Arya, G., H.-C. Chang, and E. J. Maginn, 2001, A critical comparison of
equilibrium, non-equilibrium and boundary-drive molecular dynamics techniques for studying transport in microporous materials: J. Chem. Phys., v. 115, p. 8112.
Bojan, M. J., R. Van Slooten, and W. Steele, 1992, Computer simulation studies of
the storage of methane in microporous carbons: Separation sci. tech, v. 27, p. 1837.
Brady, B. O., C.-P. C. Kao, K. M. Dooley, F. C. Knopf, and R. P. Gambrell, 1987,
Supercritical extraction of toxic organics from soils: Ind. Eng. Chem. Res., v. 26, p. 261.
235
Bratko, D., L. Blum, and M. S. Wertheim, 1989, Structure of hard sphere fluids in narrow cylindrical pores: J. Chem. Phys., v. 90, p. 2752.
Brignole, E. A., P. M. Andersen, and A. Fredenslund, 1987, Supercritical Fluid
extraction of Alcohols from water: Ind. Eng. Chem. Res., v. 26, p. 254. Cagin, T., and B. M. Pettitt, 1991, Grand molecular dynamics: a method for open
systems: Mol. Simul., v. 6, p. 5. Cascarini de Torre, L. E., E. J. Bottani, and W. A. Steele, 1996, Amorphous carbons:
Surface structure and adsorptive properties: Langmuir, v. 12, p. 5399. Chen, Y. D., and R. T. Yang, 1994, Preparation of carbon molecular sieve membrane
and diffusion of binary mixtures in the membrane: Ind. Eng. Chem. Res., v. 33, p. 3146.
Cheng, A., and W. Steel, 1990, Computer simulation study of the chemical potential
of argon adsorbed on graphite: Mol. Simu., v. 4, p. 349. Chialvo, A. A., and P. T. Cummings, 1999, Molecular-based modeling of water and
aqueous solutions at supercritical conditions: Adv. Chem. Phys., v. 109, p. 115.
Chimowitz, E. H., and G. Afrane, 1996, Classical, non-classical critical divergences
and partial molar properties from adsorption measurements in near-critical mixtures: Fluid Phase Equilibria, v. 120, p. 167.
Chung, S. T., and K. S. Shing, 1992, Multiphase behavior of binary and ternary
systems of heavy aromatic hydrocarbons with supercritical carbon dioxide: Part I. Experimental results: Fluid Phase Equilibria, v. 81, p. 321.
Cracknell, R. F., and K. E. Gubbins, 1993, Molecular simulation of adsorption and
diffusion in VIP-5 and other aluminophosphates: Langmuir, v. 9, p. 824. Cracknell, R. F., and D. Nicholson, 1993: J. Chem. Soc. Faraday Trans., v. 90, p.
885. Cracknell, R. F., D. Nicholson, and N. Quirke, 1993, A grand canonical monte carlo
study of Lennard-Jones mixtures in slit shaped pores: Mol. Phys., v. 80, p. 885.
236
Cracknell, R. F., and D. Nicholson, 1994, Grand canonical monte carlo study of Lennard-Jones mixtures in slit pores. part 3.-mixtures of two molecular fluids: ethane and propane: J. Chem. Soc. Faraday Trans., v. 90, p. 1487.
Cracknell, R. F., D. Nicholson, and K. E. Gubbins, 1995, Molecular dynamics study
of the self-diffusion of supercritical methane in slit-shaped graphit micropores: J. Chem. Soc. Faraday. Trans., v. 91, p. 1377.
Cracknell, R. F., D. Nicholson, and N. Quirke, 1995, Direct molecular dynamics
simulation of flow down a chemical potential gradient in a slit-shape micropore: Phys. Rev. Lett., v. 74, p. 2463.
Cummings, P. T., H. D. Cochran, J. M. Simonson, R. E. Mesmer, and S. Karaborni,
1991, Simulation of supercritical water and of supercritical aqueous solutions: J. Chem. Phys., v. 94, p. 5606.
Curtin, W. A., and N. W. Ashcroft, 1985, Weighted-density-functional theory of
inhomogeneous liquids and the freezing transition: Phys. Rev. A, v. 32, p. 2909.
De Filippi, R. P., V. J. Kyukonis, R. J. Robey, and M. Modell, 1980, Supercritical
fluid regeneration of activated carbon for adsorption of pesticides, EPA report 600/2-80, p. 054.
De Filippi, R. P., V. J. Kyukonis, R. J. Robey, and M. Modell, 1983, Protocol for
bioassessment of hazardous waste sites, EPA report 600/2 -83, p. 054. De Pablo, J. J., B. Marianne, and J. M. Prausnitz, 1992, Vapor-liquid equilibria for
polyatomic fluids from site-site computer simulations: pure hydrocarbons and binary mixtures containing methane: Fluid Phase Equilib., v. 73, p. 187.
Dooley, K. M., and F. C. Knopf, 1987, Oxidation catalysis in a supercritical fluid
medium: Ind. Eng. Chem. Res., v. 26, p. 1910. Dooley, K. M., C.-P. Kao, R. P. Gambrell, and F. C. Knopf, 1987, The use of
Entrainers in the supercritical extraction of soils contaminated with hazardous organics: Ind. Eng. Chem. Res., v. 26, p. 2058.
Düren, T., F. J. Keil, and N. A. Seaton, 2002, Composition dependent transport
diffusion coefficients of CH4/CF4 mixtures in carbon nanotubes by non-equilibrium molecular dynamics simulations: Chem. Eng. Sci., v. 57, p. 1343.
237
Düren, T., S. Jakobtorweihen, F. J. Keil, and N. A. Seaton, 2003, Grand canonical molecular dynamics simulations of transport diffusion in geometrically heterogeneous pores: Phys. Chem. Chem. Phys., v. 5, p. 369.
Eckert, C. A., B. L. Knutson, and P. G. Debenedetti, 1996, Supercritical fluids as
solvents for chemical and materials processing: Nature, v. 383, p. 313. Erkey, C., G. Madras, M. Orejuela, and A. Akgerman, 1993, Supercritical carbon
dioxide extraction of organics from soll: Environ. Sci. Technol., v. 27, p. 1225.
Firouzi, M., T. T. Tsotsis, and M. Sahimi, 2003, Nonequilibrium molecular
dynamics simulations of transport and separation of supercritical fluid mixtures in nanoporous membranes. I. Results for a single carbon nanopore: J. Chem. Phys., v. 119, p. 6810.
Firouzi, M., K. Molaai Nezhad, T. T. Tsotsis, and M. Sahimi, 2004, Molecular
dynamics simulations of transport and separation of carbon dioxide-alkane mixtures in carbon nanopores.: J. Chem. Phys., v. 120, p. 8172.
Firouzi, M., T. T. Tsotsis, and M. Sahimi: unpublished. Firus, A., W. Weber, and G. Brunner, 1997, Supercritical carbon dioxide for the
removal of hydrocarbons from contaminated soil: Sep. Sci. Technol., v. 32, p. 1403.
Fischer, J., and M. Methfessel, 1980, Born-Green-Yvon approach to the local
densities of a fluid at interfaces: Phys. Rev. A, v. 22, p. 2836. Ford, D. M., and E. D. Glandt, 1995, Molecular simulation study of the surface
barrier effect: dilute gas limit: J. Phys. Chem., v. 99, p. 11543. Ford, D. M., and G. S. Heffelfinger, 1998, Massively parallel dual control volume
grand canonical molecular dynamics with LADERA II. Gradient driven diffusion through polymers: Mol. Phys., v. 94, p. 673.
Frenkel, D., G. C. A. M. Mooij, and B. Smit, 1991, Novel scheme to study structural
and thermal properties of continuously deformable molecules: J. Phys.; Condense. Matter, v. 3, p. 3053.
Fujii, T., Y. Tokunaga, and K. Nakamura, 1996, Effect of solute adsorption
properties on its separation from supercritical carbon dioxide with a thin porous silica membrane: Biosci. Biotech. Biochem., v. 60, p. 1945.
238
Funke, H. H., M. G. Kovalchick, J. L. Falconer, and R. D. Noble, 1996, Separation of hydrocarbon Isomer vapors with silicalite zeolite membranes: Ind. Eng. Chem. Res., v. 35, p. 1575.
Furukawa, S., T. Shigeta, and T. Nitta, 1996, Non-equilibrium molecular dynamics
for simulating permeation of gas mixtures through nanoporous carbon membrane: J. Chem. Eng. Japan, v. 29, p. 725.
Furukawa, S., and T. Nitta, 1997, Computer simulation studies on gas permeation
through nanoporous carbon membranes by non-equilibrium molecular dynamics: J. Chem. Eng. Japan, v. 30, p. 116.
Furukawa, S., K. Hayashi, and Nitta, T., 1997, Effect of surface heterogeneity on gas
permeation through slit-like carbon membranes by non-equilibrium molecular dynamics simulations: J. Chem. Eng. Japan, v. 30, p. 1107.
Gale, J. D., A. K. Cheetham, R. A. Jackson, C. Richard, A. Callow, and J. M.
Thomas, 1990, Computing the structure of pillared clays: Adv. Mater., v. 2, p. 487.
Gamse, T., R. Marr, F. Froschl, and M. Siebenhofer, 1997, Extraction of furfural
with carbon dioxide: Sep. Sci. Technol., v. 32, p. 355. Ghassemzadeh, J., L. Xu, T. T. Tsotsis, and M. Sahimi, 2000, Statistical Mechanics
and Molecular Simulation of Adsorption in Microporous Materials: Pillared Clays and Carbon Molecular Sieve Membranes: J. Phys. Chem. B, v. 104, p. 3892.
Ghassemzadeh, J., and M. Sahimi, 2004, Molecular modelling of adsorption of gas
mixtures in montmorillonites intercalated with Al13-complex pillars: Mol. Phys., v. 102, p. 1447.
Gibson, J. B., A. N. Goland, M. Milgram, and G. H. Vineyard, 1960, Dynamics of
radiation damage: Phys. Rev., v. 120, p. 1229. Gusev, V. Y., J. A. O'Brien, and N. A. Seaton, 1997, A self-consistent method for
characterization of activated carbons using supercritical adsorption and grand canonical monte carlo simulations: Langmuir, v. 13, p. 2815.
Hall, D. W., J. A. Sandrin, and R. E. McBride, 1990, An overview of solvent
extraction treatment technologies: Env. Progr., v. 9, p. 98.
239
Hansen, J.-P., and L. Verlet, 1969, Phase transitions of the Lennard-Jones system: Phys. Rev., v. 184, p. 151.
Hansen, J.-P., and I. R. McDonald, 1991, Theory of Simple Liquids: San Diego,
Academic Press. Harris, J., and S. A. Rice, 1988, A lattice model of a supported monolayer of
amphiphile molecules: Monte Carlo simulations: J. Chem. Phys., v. 88, p. 1298.
Heffelfinger, G. S., and F. Van Swol, 1994, Diffusion in Lennard-Jones Fluids using
Dual Control Volume Grand Canonical Molecular Dynamics Simulation (DCV-GCMD): J. Chem. Phys., v. 100, p. 7548.
Heffelfinger, G. S., and D. M. Ford, 1998, Massively parallel dual control volume
grand canonical molecular dynamics with LADERA I. Gradient driven diffusion in Lennard-Jones fluids: Mol. Phys., v. 94, p. 659.
Helbaek, M., B. Hafskjold, D. K. Dysthe, and G. H. SФrland, 1996, Self-diffusion
coefficients of methane or ethane mixtures with hydrocarbons at high pressure by NMR: J. Chem. Eng. Data, v. 41, p. 598.
Hill, T. L., 1986, Statistical Thermodynamics: New York, Dover Publications. Horn R.G., and J. N. Israelachvili, 1981, Direct measurement of structural forces
between two surfaces in a nonpolar liquid: J. Chem. Phys., v. 75, p. 1400. Israelachvili, J. N., 1985, Intermolecular and surface forces: with applications to
colloidal and biological systems: London, Academic Press. Jaccucci, G., and I. R. Mcdonald, 1975, Structure and diffusion in mixtures of rare-
gas liquids: Physica, v. 80A, p. 607. Jiang, S., C. L. Rhykerd, and K. E. Gubbins, 1993, Layering, freezing transitions,
capillary condensation and diffusion of methane in slit carbon pores: Mol. Phys., v. 79, p. 373.
Johnson, J. K., J. A. Zollweg, and K. E. Gubbins, 1993, The Lennard-Jones equation
of state revised: Mol. Phys., v. 78, p. 591. Johnson, M., and S. Nordholm, 1981, Generalized van der Waals theory. VI.
Application to adsorption: J. Chem. Phys., v. 75, p. 1953.
240
Jolly, D. L., and R. J. Bearman, 1980, Molecular dynamics simulation of the mutual and self diffusion coefficients in Lennard-Jones liquid mixtures: Mol. Phys., v. 41, p. 137.
Jones, C. W., and W. J. Koros, 1994a, Carbon molecular sieve gas separation
membranes-I. Preparation and characterization based on polyimide precursors: Carbon, v. 32, p. 1419.
Jones, C. W., and W. J. Koros, 1994b, Carbon molecular sieve gas separation
membranes-II. Regeneration following organic exposure: Carbon, v. 32, p. 1427.
Jones, C. W., and W. J. Koros, 1995a, Characterization of ultramicroporous carbon
membranes with humidified feeds: Ind. Eng. Chem. Res., v. 34, p. 158. Jones, C. W., and W. J. Koros, 1995b, Carbon composite membranes: A solution to
adverse humidity effects: Ind. Eng. Chem. Res., v. 34, p. 164. June, R. L., A. T. Bell, and D. N. Theodorou, 1990, Molecular dynamics study of
methane and xenon in silicalite: J. Phys. Chem., v. 94, p. 8232. June, R. L., A. T. Bell, and D. N. Theodorou, 1992, Molecular dynamics studies of
butane and hexane in silicalite: J. Phys. Chem., v. 96, p. 1051. Kahaner, D., C. Moler, and S. Nash, 1989, Numerical Methods and Software: New
Jersey, Prentice-Hall: Englewood Cliffs. Kapteijn, F., W. J. W. Bakker, G. Zheng, J. Poppe, and J. A. Moulijn, 1995,
Permeation and separation of light hydrocarbons through a silicalite-1 membrane: Application of the generalized Maxwell-Stefan equations.: Chem. Eng. J., v. 57, p. 145.
Keldsen, G. L., J. B. Nicholas, K. A. Carrado, and R. E. Winans, 1994, Molecular
modeling of the enthalpies of adsorption of hydrocarbons on Smectite clay: J. Phys. Chem., v. 98, p. 279.
Kelley, F. D., and E. H. Chimowitz, 1990, Near-critical phenomena and resolution in
supercritical fluid chromatography: AIChE J., v. 36, p. 1163. Kiran, E., and J. M. H. L. Sengers, 1994, Supercritical Fluids-Fundamentals for
Applications: Dordrecht, Kluwer.
241
Kjelstrup, S., and B. Hafskjold, 1996, Nonequilibrium molecular dynamics simulation of steady - state heat and mass transport in distillation: Ind. Eng. Chem. Res., v. 35, p. 4203.
Klochko, A. V., E. M. Piotrovskaya., and E. N. Brodskaya, 1996, Computer
simulations of the structural and kinetic characteristics of binary Argon-Krypton solutions in graphite pores: Langmuir, v. 12, p. 1578.
Koresh, J. E., and A. Sofer, 1983, Molecular sieve carbon permselective membrane.
Part I. Presentation of a new device for gas mixture separation: Sep. Sci. Techn., v. 18, p. 723.
Kusakabe, K., S. Yoneshige, A. Murata, and S. Morooka, 1996, Morphology and gas
permeance of ZSM-5-type zeolite membrane formed on a porous -alumina support tube: J. Memb. Sci., v. 116, p. 39.
Lane, J. E., and T. H. Spurling, 1979, Forces between adsorbing walls: Monte Carlo
calculations: Chem. Phys. Lett., v. 67, p. 107. Laso, M., J. J. de Pablo, and U. W. Suter, 1992, Simulation of phase equilibria for
chain molecules: J. Chem. Phys., v. 97, p. 2817. Lastoskie, C., K. E. Gubbins, and N. Quirke, 1993, Pore size distribution analysis of
microporous carbons: A density functional theory approach: J. Phys. Chem. A, v. 97, p. 4786.
Linkov, V. M., R. D. Sanderson, and B. A. Rychkov, 1994, Composite carbon-
polyimide membranes: Mat. Lett., v. 20, p. 43. Linkov, V. M., R. D. Sanderson, and E. P. Jacobs, 1994, Highly asymmetrical
carbon membranes: J. Memb. Sci., v. 95, p. 93. Liu, H., L. Zhang, and N. A. Seaton, 1992, Determination of the connectivity of
porous solids from nitrogen sorption measurements - II. Generalisation: Chem. Eng. Sci., v. 47, p. 4393.
Liu, H., L. Zhang, and N. A. Seaton, 1993, Analysis of sorption hysteresis in
mesoporous solids using a pore network model: J. Colloid Interface Sci., v. 156, p. 285.
Liu, K. S., M. H. Kalos, and G. V. Chester, 1974, Quantum hard spheres in a
channel: Phys. Rev. A, v. 10, p. 303.
242
Liu, M. H., S. Kapila, A. F. Yanders, T. E. Clevenger, and A. A. Elseewi, 1991, Role of entrainers in supercritical fluid extraction of chlorinated aromatics from soils: Chemosphere, v. 23, p. 1085.
Lopez-Ramon, M. V., J. Jagiello, T. J. Bandosz, and N. A. Seaton, 1997,
Determination of the pore size distribution and network connectivity in microporous solids by adsorption measurements and monte carlo simulation: Langmuir, v. 13, p. 4435.
Lupkowski, M., and F. V. Swol, 1991, Ultrathin films under shear: J. Chem. Phys.,
v. 95, p. 1995. Macedonia, M. D., and E. J. Maginn, 1999, A biased grand canonical Monte Carlo
method for simulating adsorption using all-atom and branched united atom models: Mol. Phys., v. 96, p. 1375.
MacElroy, J. M. D., 1994, Non-equilibrium molecular dynamics simulation of
diffusion and flow in thin microporous membranes: J. Chem. Phys., v. 101, p. 5274.
Macnaughton, S. J., and N. R. Foster, 1995, Supercritical adsorption and desorption
behavior of DDT on activated carbon using carbon dioxide: Ind. Eng. Chem. Res., v. 34, p. 275.
Maddox, M. W., and K. E. Gubbins, 1994, Molecular simulation of fluid adsorption
in buckytubes and MCM-41: International Journal of Thermophysics, v. 15, p. 1115.
Maddox, M. W., and K. E. Gubbins, 1995, Molecular simulation of fluid adsorption
in buckytubes: Langmuir, v. 11, p. 3988. Magda, J. J., M. Tirrell, and H. T. Davis, 1985, Molecular dynamics of narrow,
liquid-filled pores: J. Chem. Phys., v. 83, p. 1888. Maginn, E. J., A. T. Bell, and D. N. Theodorou, 1993, Transport diffusivity of
methane in silicalite from equilibrium and nonequilibrium simulations: J. Phys. Chem., v. 97, p. 4173.
Martin, M. G., A. P. Thompson, and T. M. Nenoff, 2001, Effect of pressure,
membrane thickness, and placement of control volumes on the flux of methane through thin silicalite membranes: A dual control volume grand canonical molecular dynamics study: J. Chem. Phys., v. 114, p. 7174.
243
Martinez, H. L., R. Ravi, and S. C. Tucker, 1996, Characterization of solvent clusters in a supercritical Lennard-Jones fluid: J. Chem. Phys., v. 104, p. 1067.
Matranga, K. R., A. L. Myers, and E. D. Glandt, 1992, Storage of natural gas by
adsorption on activated carbon: Chem. Eng. Sci., v. 47, p. 1569. McGovern, W. E., J. M. Moses, and R. Abrishamanian, 1987: Paper presented at the
Annual AIChE Meeting, New York. McQuarrie, D. A., 1976, Statistical Mechanics: New York, Harper and Row. Meguro, Y., S. Iso, H. Takeishi, and Z. Yoshida, 1996, Extraction of uranium (VI) in
nitric acid solution with supercritical carbon dioxide fluid containing tributylphosphate: Radiochimica Acta, v. 75, p. 185.
Metropolis, N., A. W. Rosenbluth, M. N. Rosenbluth, A. H. Teller, and E. Teller,
1953, Equation of state calculations by fast computing machines: J. Chem. Phys., v. 21, p. 1087.
Mezei, M., 1980, A cavity-biased (T, V, μ) monte carlo method for the computer
simulation of fluids: Mol. Phys., v. 40, p. 901. Miller, G. W., K. S. Knaebel, and K. G. Ikels, 1987, Equilibria of nitrogen, oxygen,
argon, and air in molecular sieve 5A: AIChE J., v. 33, p. 194. Molaai Nezhad, K., M. Sahimi, and T. T. Tsotsis: unpublished. Monnery, W. D., W. Y. Svrcek, and A. K. Mehotra, 1995, Viscosity: A critical
review of practical predictive and correlative methods: Can. J. Chem. Eng., v. 73, p. 3.
Mooij, G. C. A. M., D. Frenkel, and B. Smit, 1992, Direct simulation of phase
equilibria of chain molecules: J. Phys.; Condense. Matter, v. 4, p. L255. Muller, A., J. M. Martinet, and P. Vignet, 1989, Gas liquid and supercritical carbon
dioxide permeability through a 5nm port radius alumina membrane: Proc. 1st Int. Conf. Inorg. Memb., p. 337.
Naheiri, T., K. A. Ludwig, M. Anand, M. B. Rao, and S. Sircar, 1997, Scale-up of
selective surface flow membrane for gas separation: Sep. Sci. Technol., v. 32, p. 1589.
244
Nakamura, K., T. Hoshino, A. Morita, M. Hattori, and R. Okamoto, 1994, Developments in Food Engineering, in T. Yano, Matsuno, R., Nakamura, K., ed., p. 820.
Nicholson, D., 1994, Simulation study of nitrogen adsorption in parallel-sided
micropores with corrugated potential functions: J. Chem. Soc. Faraday Trans., v. 90, p. 181.
Nicholson, D., R. F. Cracknell, and N. Quirke, 1996, Transition in the diffusivity of
adsorbed fluid through micropores: Langmuir, v. 12, p. 4050. Nicholson, D., 1998, Simulation studies of methane transport in model graphite
micropores: Carbon, v. 36, p. 1511. Nitta, T., M. Nozawa, and Y. Hishikawa, 1993, Monte carlo simulation of adsorption
of gases in carbonaceous slitlike pores: J. Chem. Eng. Japan, v. 26, p. 266. Nitta, T., and J. Yoneya, 1995, Computer simulations for adsorption of benzene
diluted in supercritical carbon dioxide: J. Chem. Eng. Japan, v. 28, p. 31. Nitta, T., Nozawa, M., Hishikawa, Y., 1995: J. Chem. Eng. Japan, v. 28, p. 267. Nouacer, M., and K. S. Shing, 1989, Grand canonical Monte Carlo simulation for
solubility calculation in supercritical extraction: Mol. Simul., v. 2, p. 55. Novak, Z., and Z. Knez, 1997, Diffusion of methanol-liquid CO2 and methanol-
supercritical CO2 in silica aerogels: J. Non-Crystalline Solids, v. 221, p. 163. Ohya, H., T. Higashijima, Y. Tsuchiya, H. Tokunaga, and Y. Negishi, 1993,
Separation of supercritical carbon dioxide and isooctane mixtures with an asymmetric polyimide membrane: J. Memb. Sci., v. 84, p. 185.
Pang, T. H., M. Ye, F. C. Knopf, and K. M. Dooley, 1991, Catalytic oxidation of
model waste aromatic hydrocarbons in a dense fluid: Chem. Eng. Comm., v. 110, p. 85.
Papadopoulou, A., E. D. Becker, M. Lupkowski, and F. Van Swol, 1993, Molecular-
dynamics and monte-carlo simulations in the grand canonical ensemble: Local versus global control: J. Chem. Phys., v. 98, p. 4897.
Percus, J. K., 1986, The pressure tensor in a non-uniform fluid: Chem. Phys. Lett., v.
123, p. 311.
245
Petersen, J., M. Matsuda, and K. Haraya, 1997, Capillary carbon molecular sieve membranes derived from Kapton for high temperature gas separation: J. Memb. Sci., v. 131, p. 85.
Peterson, B. K., and K. E. Gubbins, 1987, Phase transitions in a cylindrical pore.
Grand canonical Monte Carlo, mean field theory, and the Kelvin equation: Mol. Phys., v. 62, p. 215.
Pinnavaia, T. J., and M. F. Thorpe, 1995, Access in Nanoporous Materials: New
York, Plenum. Plee, D., F. Borg, L. Gatineau, and J. J. Fripiat, 1985, High-Resolution solid-state
27Al and 29Si Nuclear magnetic resonance study of pillared clays.: J. Am. Chem. Soc., v. 107, p. 2362.
Pohl, P. I., G. S. Heffelfinger, and D. M. Smith, 1996, Molecular dynamics computer
simulation of gas permeation in thin silicalite membranes: Mol. Phys., v. 89, p. 1725.
Pohl, P. I., and G. S. Heffelfinger, 1999, Massively parallel molecular dynamics
simulation of gas permeation across porous silica membranes: J. Memb. Sci., v. 155, p. 1.
Rahman, A., 1964, Correlations in the motion of atoms in liquid Argon: Phys. Rev.,
v. 136, p. A405. Rao, M. B., and S. Sircar, 1993a, Nanoporous carbon membrane for gas separation:
Gas Sep. Purif., v. 7, p. 279. Rao, M. B., and S. Sircar, 1993b, Nanoporous carbon membranes for separation of
gas mixtures by selective surface flow: J. Memb. Sci., v. 85, p. 253. Rao, M. B., and S. Sircar, 1996, Performance and pore characterization of
nanoporous carbon membranes for gas separation: J. Memb. Sci., v. 110, p. 109.
Rhykerd, C., Z. Tan, L. A. Pozhar, and K. E. Gubbins, 1991, Properties of simple
fluids in carbon micropores.: J. Chem. Soc. Faraday Trans., v. 87, p. 2011. Roop, R. K., A. Akgerman, T. R. Irvin, and E. K. Stevens, 1988, Supercritical
extraction of creosote from water with toxicological validation: J. Supercrit. Fluids, v. 1, p. 31.
246
Rosenbluth, M. N., and A. W. Rosenbluth, 1955, Monte carlo calculation of the average extension of molecular chains: J. Chem. Phys., v. 23, p. 356.
Ryckaert, J.-P., and A. Bellemans, 1975, Molecular dynamics of liquid n-butane near
its boiling point: Chem. Phys. Lett., v. 30, p. 123. Ryckaert, J.-P., and A. Bellemans, 1978, Molecular dynamics of liquid alkanes:
Faraday Discuss. Chem. Soc., v. 66, p. 95. Sahimi, M., 1993, Flow phenomena in rocks: from continuum models to fractals,
percolation, cellular automata, and simulated annealing: Rev. Mod. Phys., v. 65, p. 1393.
Sahimi, M., 1994, Applications of Percolation Theory: London, Taylor and Francis. Sahimi, M., 1995, Flow and Transport in Porous Media and Fractured Rock: VCH,
Weinheim,Germany. Sahimi, M., 2003, Heterogeneous Materials, Volumes I & II: New York, Springer-
Verlag. Samios, S., A. K. Stubos, N. K. Kanellopoulos, R. F. Cracknell, G. K. Papadopoulos,
and D. Nicholson, 1997, Determinatin of micropore size distribution from grand canonical monte carlo simulations and experimental CO2 isotherm data: Langmuir, v. 13, p. 2795.
Sarrade, S., G. M. Rios, and M. Carles, 1996, Nanofiltration membrane behavior in a
supercritical medium: J. Memb. Sci., v. 114, p. 81. Schoen, M., and C. Hoheisel, 1984, The mutual diffusion coefficient D12 in binary
liquid model mixtures. Molecular dynamics calculations based on Lennard-Jones (12-6) potentials. I.The method of determination: Mol. Phys., v. 52, p. 33.
Schoen, M., J. H. Cushman, D. J. Diestler, and C. L. Rhykerd, 1988, Fluids in
micropores. II. Self-diffusion in a simple classical fluid in a slit pore: J. Chem. Phys., v. 88, p. 1394.
Schultz, M. H., 1973, Spline Analysis: New Jersey, Prentice-Hall: Englewood Cliffs. Seaton, N. A., J. P. R. B. Walton, and N. Quirke, 1989, A new analysis method for
the determination of the pore size distribution of porous carbons from nitrogen adsorption measurements: Carbon, v. 27, p. 853.
247
Seaton, N. A., 1991, Determination of the connectivity of porous solids from nitrogen sorption measurements: Chem. Eng. Sci., v. 46, p. 1895.
Seaton, N. A., S. P. Friedman, J. M. D. MacElroy, and B. J. Murphy, 1997, The
molecular sieving mechanism in carbon molecular sieves: A molecular dynamics and critical path analysis: Langmuir, v. 13, p. 1199.
Sedigh, M. G., W. J. Onstot, L. Xu, W. L. Peng, T. T. Tsotsis, and M. Sahimi, 1998,
Experiments and simulation of transport and separation of gas mixtures in carbon molecular sieve membranes: J. Phys. Chem. A, v. 102, p. 8580.
Sedigh, M. G., L. Xu, T. T. Tsotsis, and M. Sahimi, 1999, Transport and
Morphological Characteristics of Polyetherimide-Based Carbon Molecular Sieve Membranes: Ind. Eng. Chem. Res., v. 38, p. 3367.
Sedigh, M. G., M. Jahangiri, P. K. T. Liu, M. Sahimi, and T. T. Tsotsis, 2000,
Structural characterization of polyetherimide-based carbon molecular sieve membranes: AIChE J., v. 46, p. 2245.
Segarra, E. I., and E. D. Glandt, 1994, Model microporous carbons: Microstructure,
surface polarity and gas adsorption: Chem. Eng. Sci., v. 49, p. 2953. Semenova, S. I., H. Ohya, T. Higashijima, and Y. Negishi, 1992a, Dependence of
permeability through polyimide membranes on state of gas, vapor, liquid and supercritical fluid at high temperature: J. Memb. Sci., v. 67, p. 29.
Semenova, S. I., H. Ohya, T. Higashijima, and Y. Negishi, 1992b, Separation of
supercritical carbon dioxide and ethanol mixtures with an asymmetric polyimide membrane: J. Memb. Sci., v. 74, p. 131.
Sengers, J. V., and J. M. H. L. Sengers, 1986, Thermodynamic behavior of fluids
near the critical point: Annu. Rev. Phys. Chem., v. 37, p. 189. Shiflett, M. B., and H. C. Foley, 1999, Ultrasonic deposition of high-selectivity
nanoporous carbon membranes: Science, v. 285, p. 1902. Shigeta, T., J. Yoneya, and T. Nitta, 1996, Monte carlo simulation study of
adsorption characteristics in slit-like micropores under supercritical conditions: Mol. Simul., v. 16, p. 291.
Shing, K. S., and S. T. Chung, 1987, Computer simulation methods for the
calculation of solubility in supercritical extraction systems: J. Phys. Chem., v. 91, p. 1674.
248
Shing, K. S., M. Pirbazari, B. N. Badriyha, and S. T. Chung, 1988: Proceedings of the Joint CSCE-ASCE-NCEE Conference.
Shing, K. S., 1991, CRC Handbook on Supercritical Fluid Technology, p. 227. Shusen, W., Z. Meiyun, and W. Zhizhong, 1996, Asymmetric molecular sieve
carbon membranes: J. Memb. Sci., v. 109, p. 267. Siepmann, J. I., and D. Frenkel, 1992, Configurational bias Monte Carlo: a new
sampling scheme for flexible chains: Mol. Phys., v. 75, p. 59. Silva, L. J., L. A. Bray, and D. W. Matson, 1993, Catalyzed electrochemical
dissolution for spent catalyst recovery: Ind. Eng. Chem. Res., v. 32, p. 2485. Sircar, S., T. C. Golden, and M. B. Rao, 1996, Activated carbon for gas separation
and storage: Carbon, v. 34, p. 1. Skipper, N. T., K. Refson, and J. D. C. McConnell, 1989, Computer calculation of
water-clay interactions using atomic pair potentials: Clay Minerals, v. 24, p. 411.
Smit, B., S. Karaborni, and J. I. Siepmann, 1995, Computer simulations of vapor-
liquid phase equilibria of n-alkanes: J. Chem. Phys., v. 102, p. 2126. Smith, D. M., 1986, Knudsen diffusion in constricted pores: Monte carlo
simulations: AIChE J., v. 32, p. 329. Snook, I. K., and W. Van Megen, 1980, Solvation forces in simple dense fluids. I.:
J. Chem. Phys., v. 72, p. 2907. Sokhan, V. P., D. Nicholson, and N. Quirke, 2002, Fluid flow in nanopores:
Accurate boundary conditions for carbon nanotubes: J. Chem. Phys., v. 117, p. 8531.
Sokolowski, S., and J. Fischer, 1990, Lennard-Jones mixtures in slit-like pores: a
comparison of simulation and density-function theory: Mol. Phys., v. 71, p. 393.
Somers, S. A., and H. T. Davis, 1992, Microscopic dynamics of fluids confined
between smooth and atomically structured solid surfaces: J. Chem. Phys., v. 96, p. 5389.
249
Steriotis, T., A. K. Beltsios, A. C. Mitropoulos, N. Kanellopoulos, S. Tenisson, A. Wiedenman, and U. Keiderling, 1997: J. Appl. Poly. Sci., v. 64, p. 2323.
Stoddard, S. D., and J. Ford, 1973, Numerical experiments on the stochastic behavior
of a Lennard-Jones gas system: Phys. Rev. A, v. 8, p. 1504. Subramanian, G., and H. T. Davis, 1979, Molecular dynamics of a hard sphere fluid
in small pores: Mol. Phys., v. 38, p. 1061. Sun, M., and C. Ebner, 1992, Molecular-dynamics simulation of compressible fluid
flow in two-dimensional channels: Phys. Rev. A, v. 46, p. 4813. Sunderrajan, S., C. K. Hall, and B. D. Freeman, 1996, Estimation of mutual diffusion
coefficients in polymer/penetrant systems using nonequilibrium molecular dynamics simulations: J. Chem. Phys., v. 105, p. 1621.
Supple, S., and N. Quirke, 2003, Rapid imbibition of fluids in carbon nanotubes:
Phys. Rev. Lett., v. 90, p. 214501. Takaba, H., M. Katagiri, M. Kubo, R. Vetrivel, and A. Miyamoto, 1995, Molecular
design of carbon nanotubes for the separation of molecules: Microporous Materials, v. 3, p. 449.
Takaba, H., K. Mizukami, M. Kubo, A. Stirling, and A. Miyamoto, 1996, The effect
of gas molecule affinities on CO2 separation from the CO2/N2 gas mixture using inorganic membranes as investigated by molecular dynamics simulation: J. Memb. Sci., v. 121, p. 251.
Tan, C.-S., and D.-C. Liou, 1989, Supercritical regeneration of activated carbon
loaded with Benzene and Toluene: Ind. Eng. Chem. Res., v. 28, p. 1222. Tarazona, P., 1985, Free-energy density functional for hard spheres: Phys. Rev. A, v.
31, p. 2672. Thompson, A. P., D. M. Ford, and G. S. Heffelfinger, 1998, Direct molecular
simulation of gradient-driven diffusion: J. Chem. Phys., v. 109, p. 6406. Tokunaga, Y., T. Fujii, and K. Nakamura, 1997, Separation of caffeine from
supercritical carbon dioxide with a zeolite membrane: Biosci. Biotech. Biochem., v. 61, p. 1024.
250
Tomasko, D. L., K. J. Hay, G. W. Leman, and C. A. Eckert, 1993, Pilot scale study and design of a granular activated carbon regeneration process using supercritical fluids: Envir. Progr., v. 12, p. 208.
Tomasko, D. L., S. J. Macnaughton, N. R. Foster, and C. A. Eckert, 1995, Removal
of pollutants from solid matrices using supercritical fluids: Sep. Sci. Technol., v. 30, p. 1901.
Torquato, S., 2002, Random Heterogeneous Materials: Microstructure and
Macroscopic Properties: New York, Springer-Verlag. Unger, K. K., J. Rouquerol, K. S. W. Sing, and H. Kral, 1988, Characterization of
Porous Solids: Amsterdam, Elsevier. Van de Graaf, J. M., F. Kapteijn, and J. A. Moulijn, 1999, Modeling permeation of
binary mixtures through zeolite membranes: AIChE J., v. 45, p. 497. Van der Ploeg, P., and H. J. C. Berendsen, 1982, Molecular dynamics simulation of a
bilayer membrane: J. Chem. Phys., v. 76, p. 3271. Van Megen, W., and I. K. Snook, 1982, Physical adsorption of gases at high
pressure. I. The critical region: Mol. Phys., v. 45, p. 629. Van Megen, W., and I. K. Snook, 1985, Physical adsorption of gases at high
pressure. III. Adsorption in slit-like pores: Mol. Phys., v. 54, p. 741. Van Slooten, R., M. J. Bojan, and W. A. Steele, 1994, Computer simulation of the
high-temperature adsorption of methane in a sulfided graphit micropore: Lamgmuir, v. 10, p. 542.
Verlet, L., 1967, Computer “Experiments” on classical fluids. I. Thermodynamical
properties of Lennard-Jones molecules: Phys. Rev., v. 159, p. 98. Verlet, L., 1968, Computer ”Experiments” on classical fluids. II. Equilibrium
correlation functions: Phys. Rev., v. 165, p. 201. Vicsek, T., and F. Family, 1984, Dynamic scaling for aggregation of clusters: Phys.
Rev. Lett., v. 52, p. 1669. Vroon, Z. A. E. P., K. Keizer, M. J. Gilde, H. Verweij, and A. J. Burggraaf, 1996,
Transport properties of alkanes through ceramic thin zeolite MFI membranes: J. Memb. Sci., v. 113, p. 293.
251
Wawrzyniak, P., G. Rogacki, J. Pruba, and Z. Bartczak, 1998, Diffusion of ethanol-carbon dioxide in silica gel: J. Non-Crystalline Solids, v. 225, p. 86.
Xu, L., M. G. Sedigh, M. Sahimi, and T. T. Tsotsis, 1998, Non-equilibrium
molecular dynamics simulation of transport of gas mixtures in nanopores: Phys. Rev. Lett., v. 80, p. 3511.
Xu, L., T. T. Tsotsis, and M. Sahimi, 1999, Nonequilibrium molecular dynamics
simulation of transport and separation of gases in carbon nanopores. I. Basic results: J. Chem. Phys., v. 111, p. 3252.
Xu, L., M. G. Sedigh, T. T. Tsotsis, and M. Sahimi, 2000, Nonequilibrium molecular
dynamics simulation of transport and separation of gases in carbon nanopores. II. Binary and ternary mixtures and comparison with the experimental data: J. Chem. Phys., v. 112, p. 910.
Xu, L., M. Sahimi, and T. T. Tsotsis, 2000, Nonequilibrium molecular dynamics
simulations of transport and separation of gas mixtures in nanoporous materials: Phys. Rev. E, v. 62, p. 6942.
Xu, L., T. T. Tsotsis, and M. Sahimi, 2001, Statistical mechanics and molecular
simulation of adsorption of ternary gas mixtures in nanoporous materials: J. Chem. Phys., v. 114, p. 7196.
Yi, X., K. S. Shing, and M. Sahimi, 1995, Molecular dynamics simulation of
diffusion in pillared clays: AIChE J., v. 41, p. 456. Yi, X., K. S. Shing, and M. Sahimi, 1996, Molecular simulation of adsorption and
diffusion in pillared clays: Chem. Eng. Sci., v. 51, p. 3409. Yi, X., J. Ghassemzadeh, K. S. Shing, and M. Sahimi, 1998, Molecular dynamics
simulation of gas mixtures in porous media. I. Adsorption: J. Chem. Phys., v. 108, p. 2178.
Yoshii, N., and S. Okazaki, 1997, A large-scale and long-time molecular dynamics
study of supercritical Lennard-Jones fluid. An analysis of high temperature clusters: J. Chem. Phys., v. 107, p. 2020.
252