Simulation of contaminant transport in fractured permeable formations by multiporosity modeling
This paper concerns contaminant transport in aquifers comprising fractured porous formations. It is considered that the aquifer subject to contamination is composed of macro-blocks, which embed two sets of macro-fractures. Each macro-block incorporates numerous micro-blocks of low permeability, whic...
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Published in | Journal of hydrology (Amsterdam) Vol. 223; no. 3; pp. 107 - 130 |
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Main Authors | , , , |
Format | Journal Article |
Language | English |
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Amsterdam
Elsevier B.V
01.10.1999
Elsevier Science |
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Abstract | This paper concerns contaminant transport in aquifers comprising fractured porous formations. It is considered that the aquifer subject to contamination is composed of macro-blocks, which embed two sets of macro-fractures. Each macro-block incorporates numerous micro-blocks of low permeability, which embed micro-fractures. Therefore, the basic conceptual model, used in this study, is a triple-porosity two-dimensional model.
It is shown that five dimensionless parameters govern contaminant transport in the triple-porosity domain. However, a group of eight so-called practical parameters is convenient to be used for consideration of possible scenarios. From this group, major effects of contaminant diffusion into the micro-blocks are attributed to the density of micro-fractures and porosity of the micro-blocks. Coefficient of diffusivity of contaminant into the micro-block is also a significant parameter. Its effective value increases due to the presence of vertical fractures, which do not transfer contaminant by advection, and it is dependent on the tortuosity of the micro-block material.
Simulations of various possible scenarios were carried out by solving the basic dimensionless equations developed in the present study. The solutions were obtained by a combination of analytical and numerical solutions. The simulations indicate that at a comparatively high porosity of the micro-blocks, of the order 10
−1, the effect of contaminant diffusion into the micro-blocks can be approximated as a retardation phenomenon, similar to contaminant adsorption. An increase of the fracture density reduces that retardation effect. If the micro-block porosity is comparatively low, of the order 10
−3, then contaminant diffusion into the micro-blocks changes the shape of the breakthrough curves, which are ended with very long tails. This phenomenon is reduced by the increase of the fracture density. |
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AbstractList | This paper concerns contaminant transport in aquifers comprising fractured porous formations. It is considered that the aquifer subject to contamination is composed of macro-blocks, which embed two sets of macro-fractures. Each macro-block incorporates numerous micro-blocks of low permeability, which embed micro-fractures. Therefore, the basic conceptual model, used in this study, is a triple-porosity two-dimensional model. It is shown that five dimensionless parameters govern contaminant transport in the triple-porosity domain. However, a group of eight so-called practical parameters is convenient to be used for consideration of possible scenarios. From this group, major effects of contaminant diffusion into the micro-blocks are attributed to the density of micro-fractures and porosity of the micro-blocks. Coefficient of diffusivity of contaminant into the micro-block is also a significant parameter. Its effective value increases due to the presence of vertical fractures, which do not transfer contaminant by advection, and it is dependent on the tortuosity of the micro-block material. Simulations of various possible scenarios were carried out by solving the basic dimensionless equations developed in the present study. The solutions were obtained by a combination of analytical and numerical solutions. The simulations indicate that at a comparatively high porosity of the micro-blocks, of the order 10 super(-1), the effect of contaminant diffusion into the micro-blocks can be approximated as a retardation phenomenon, similar to contaminant adsorption. An increase of the fracture density reduces that retardation effect. If the micro-block porosity is comparatively low, of the order 10 super(-3), then contaminant diffusion into the micro-blocks changes the shape of the breakthrough curves, which are ended with very long tails. This phenomenon is reduced by the increase of the fracture density. This paper concerns contaminant transport in aquifers comprising fractured porous formations. It is considered that the aquifer subject to contamination is composed of macro-blocks, which embed two sets of macro-fractures. Each macro-block incorporates numerous micro-blocks of low permeability, which embed micro-fractures. Therefore, the basic conceptual model, used in this study, is a triple-porosity two-dimensional model. It is shown that five dimensionless parameters govern contaminant transport in the triple-porosity domain. However, a group of eight so-called practical parameters is convenient to be used for consideration of possible scenarios. From this group, major effects of contaminant diffusion into the micro-blocks are attributed to the density of micro-fractures and porosity of the micro-blocks. Coefficient of diffusivity of contaminant into the micro-block is also a significant parameter. Its effective value increases due to the presence of vertical fractures, which do not transfer contaminant by advection, and it is dependent on the tortuosity of the micro-block material. Simulations of various possible scenarios were carried out by solving the basic dimensionless equations developed in the present study. The solutions were obtained by a combination of analytical and numerical solutions. The simulations indicate that at a comparatively high porosity of the micro-blocks, of the order 10(-1), the effect of contaminant diffusion into the micro-blocks can be approximated as a retardation phenomenon, similar to contaminant adsorption. An increase of the fracture density reduces that retardation effect. If the micro-block porosity is comparatively low, of the order 10(-3), then contaminant diffusion into the micro-blocks changes the shape of the breakthrough curves, which are ended with very long tails. This phenomenon is reduced by the increase of the fracture density. This paper concerns contaminant transport in aquifers comprising fractured porous formations. It is considered that the aquifer subject to contamination is composed of macro-blocks, which embed two sets of macro-fractures. Each macro-block incorporates numerous micro-blocks of low permeability, which embed micro-fractures. Therefore, the basic conceptual model, used in this study, is a triple-porosity two-dimensional model. It is shown that five dimensionless parameters govern contaminant transport in the triple-porosity domain. However, a group of eight so-called practical parameters is convenient to be used for consideration of possible scenarios. From this group, major effects of contaminant diffusion into the micro-blocks are attributed to the density of micro-fractures and porosity of the micro-blocks. Coefficient of diffusivity of contaminant into the micro-block is also a significant parameter. Its effective value increases due to the presence of vertical fractures, which do not transfer contaminant by advection, and it is dependent on the tortuosity of the micro-block material. Simulations of various possible scenarios were carried out by solving the basic dimensionless equations developed in the present study. The solutions were obtained by a combination of analytical and numerical solutions. The simulations indicate that at a comparatively high porosity of the micro-blocks, of the order 10 −1, the effect of contaminant diffusion into the micro-blocks can be approximated as a retardation phenomenon, similar to contaminant adsorption. An increase of the fracture density reduces that retardation effect. If the micro-block porosity is comparatively low, of the order 10 −3, then contaminant diffusion into the micro-blocks changes the shape of the breakthrough curves, which are ended with very long tails. This phenomenon is reduced by the increase of the fracture density. |
Author | Jansen, D. Rubin, H. Forkel, C. Köngeter, J. |
Author_xml | – sequence: 1 givenname: H. surname: Rubin fullname: Rubin, H. email: hrub@turbo.technion.ac.il – sequence: 2 givenname: D. surname: Jansen fullname: Jansen, D. email: d.jansen@iww.rwth-aachen.de – sequence: 3 givenname: C. surname: Forkel fullname: Forkel, C. email: forkel@iww.rwth-aachen.de – sequence: 4 givenname: J. surname: Köngeter fullname: Köngeter, J. email: koengeter@iww.rwth-aachen.de |
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Cites_doi | 10.2136/sssaj1993.03615995005700040012x 10.1029/WR023i003p00467 10.1029/WR017i003p00555 10.1007/BF00233176 10.1016/0022-1694(95)02783-1 10.1016/S0022-1694(96)03258-1 10.1016/0016-7061(90)90010-7 10.1029/WR020i007p01021 10.2172/5671386 10.1029/WR024i012p02019 10.1029/WR020i010p01390 10.3133/pp411A 10.1029/WR024i008p01360 10.1016/0022-1694(95)02775-0 10.1016/0022-1694(93)90163-4 10.1029/95WR03397 10.1016/0022-1694(93)90164-5 10.2172/6937127 10.1029/WR018i006p01634 |
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Keywords | Transport simulation Multi-porosity modeling Fractured formations Multiple aquifers models diffusion density porosity permeability ground water digital simulation transport pollution contamination aquifers diffusivity fractures |
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Snippet | This paper concerns contaminant transport in aquifers comprising fractured porous formations. It is considered that the aquifer subject to contamination is... |
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SubjectTerms | adsorption aquifers diffusivity Earth sciences Earth, ocean, space Engineering and environment geology. Geothermics equations Exact sciences and technology Fractured formations groundwater contamination Hydrogeology Hydrology. Hydrogeology mathematical models Multi-porosity modeling Multiple aquifers permeability pollutants Pollution, environment geology porosity simulation models transport processes Transport simulation |
Title | Simulation of contaminant transport in fractured permeable formations by multiporosity modeling |
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