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Article

Hydrodynamic Porosity: A New Perspective on Flow through Porous Media, Part I

by
August H. Young
1,2,* and
Zbigniew J. Kabala
3,*
1
Duke Center for WaSH-AID, Duke University, Durham, NC 27701, USA
2
Mechanical Engineering and Materials Science, Duke University, Durham, NC 27710, USA
3
Civil and Environmental Engineering, Duke University, Durham, NC 27710, USA
*
Authors to whom correspondence should be addressed.
Water 2024, 16(15), 2158; https://doi.org/10.3390/w16152158 (registering DOI)
Submission received: 7 May 2024 / Revised: 27 July 2024 / Accepted: 27 July 2024 / Published: 30 July 2024
(This article belongs to the Special Issue Groundwater Flow and Transport Modeling in Aquifer Systems)

Abstract

:
Pore-scale flow velocity is an essential parameter in determining transport through porous media, but it is often miscalculated. Researchers use a static porosity value to relate volumetric or superficial velocities to pore-scale flow velocities. We know this modeling assumption to be an oversimplification. The variable fraction of porosity conducive to flow, what we define as hydrodynamic porosity, θ m o b i l e , exhibits a quantifiable dependence on the Reynolds number (i.e., pore-scale flow velocity) in the Laminar flow regime. This fact remains largely unacknowledged in the literature. In this work, we quantify the dependence of θ m o b i l e on the Reynolds number via numerical flow simulation at the pore scale for rectangular pores of various aspect ratios, i.e., for highly idealized dead-end pore spaces. We demonstrate that, for the chosen cavity geometries, θ m o b i l e decreases by as much as 42% over the Laminar flow regime. Moreover, θ m o b i l e exhibits an exponential dependence on the Reynolds number, Re = R . The fit quality is effectively perfect, with a coefficient of determination (R2) of approximately 1 for each set of simulation data. Finally, we show that this exponential dependence can be easily fitted for pore-scale flow velocity through use of only a few Picard iterations, even with an initial guess that is 10 orders of magnitude off. Not only is this relationship a more accurate definition of pore-scale flow velocity, but it is also a necessary modeling improvement that can be easily implemented. In the companion paper (Part 2), we build upon the findings reported here and demonstrate their applicability to media with other pore geometries: rectangular and non-rectangular cavities (circular and triangular).

1. Introduction

Fluid flow and transport through porous media are ubiquitous to natural and engineered systems including groundwater remediation, surface water treatment, and various other industrial processes. Recent studies underscore the importance of considering pore-scale flow dynamics and structures, namely dead-end pores, in elucidating fluid transport mechanisms within porous media and describing macroscale trends.
In the study of porous media, the pore space is typically broken down into two regions: mobile and “immobile” zones, as described by van Genuchten and Wierenga [1] in application to groundwater flows. In the mobile zone, solute transport occurs via advection and dispersion. The immobile zone is defined by isolated volumes of cavities or dead-ended pore space adjacently located to well-connected, mobile regions. In these zones, fluid recirculates in eddies, and solute transport is limited to the mechanism of vortex-enhanced diffusion. By this definition, the “immobile” label is a misnomer—fluid in the cavity space is technically mobile; it does not, however, move through the pore space. Thus, the fluid in this zone remains immobile relative to the flow in the mobile zone. We illustrate these zones for an arbitrary matrix subject to an imposed flow in Figure 1, below. Magnification “A” provides an example of a mobile zone, and magnification “B” contains an example of an immobile zone in the form of a dead-end pore. The model we use to study this dead-end pore volume is pictured in Figure 2.
The relevance of the dead-end pores pictured in Figure 1, though media-specific, can be profound, especially in unwashed media such as glacial till or fractured rock. Indeed, the presence of dead-end pores has been shown to be abundant in the subsurface. For example, Lee et al. [2] found the fraction of immobile water content in an undisturbed soil core to range from 0.42 to 0.82, while Casey et al. [3] measured the average fraction to be 0.62 in the field. Testing in the 1960s revealed the significance of dead-end pores in reservoir rock: Fatt et al. [4] estimated a total volume of 20% in limestone and shellstone core samples, whereas Coats and Smith [5] estimated a volume of roughly 10% in sandstone core samples.
Typically, a substantial immobile zone volume results in solutes favoring preferential flow paths (i.e., well-connected pore volumes), bypassing immobile zones and dead-end pores. Models neglecting immobile zones and preferential flow paths may underestimate solute movement by half, as indicated by Jaynes et al. [6], highlighting the significance of considering dead-end pores in fluid transport dynamics. Dead-end pores have also been implicated in other macroscopic phenomena. Leismann et al. [7] discuss tailing in large-scale propagation processes, attributing it to pollutant persistence in immobile zones or dead ends of the pore space. Lake [8] identifies viscous fingering instabilities and stagnant areas, or dead-end pores, as critical limiting factors in miscible displacement processes in porous media, impacting remediation, CO2 sequestration, and energy extraction.
Recent studies have delved further into the impact of dead-end pores on fluid flow and macroscopic transport phenomena (e.g., see Bordoloi et al. [9]). Gao et al. [10] find that immobile water in dead-end pores not only affects solute transport processes but also crucially regulates breakthrough and tailing in soil columns. Yuan et al. [11] observe that dead-end pores impede the efficient removal of non-aqueous phase liquids from the pore space due to slow mass transfer rates between the mobile and immobile zones. Nguyen et al. [12] discuss the effect of dead-end pores on porous battery electrode performance, underscoring the importance of understanding their role in optimizing electrode design. Following an abundance of such evidence, Khuzhayorov et al. [13] conclude that zones of immobile liquid significantly influence transport in porous media.
Building upon the insights gained from studies on dead-end pores and pore-scale flow dynamics, the concept of effective porosity emerges as a central focus in understanding fluid transport in porous media. However, the interpretation of effective porosity has been mired in ambiguity across different disciplines, leading to varying definitions and applications. Take, for example, the definition of effective porosity assigned by the textile industry. In the context of hernia meshes, effective porosity is meant to define changes to the pore morphology after implantation of the mesh in situ (Jacombs et al. [14]). This is quite different from the definition used by Sevee [15] in a study on the effective porosity of marine clay. In this study, effective porosity describes the void space in the clay that participates in advective transport. Still, other definitions describe it as the difference between the total porosity minus the soil water content at 0.33 bar (Helalia [16]; Timlin et al. [17]). Readers are directed to Hapgood et al. [18], Flint and Selker [19], Cartwright et al. [20], and Ma et al. [21] for additional, alternative definitions. This ambiguity necessitates a more nuanced approach to characterize the portion of porosity influencing fluid transport.
In this work, we introduce the concept of hydrodynamic porosity, denoted as θ m o b i l e , to specifically capture flow-driven fluctuations in the pore volume conducive to through-flow. The objective of our analysis is to provide a more precise understanding of the dynamics underlying fluid and contaminant transport within porous media. The concept of hydrodynamic porosity not only differs from the many definitions of effective porosity, but also from that of dynamic porosity, which describes the shrinking or swelling of porous media (Sheng et al. [22]; McDonald et al. [23]), and dynamic effective porosity, which describes variably saturated porous media around the capillary fringe (Luo et al. [24]). By delving into the physics of pore-scale flow, we lay the theoretical groundwork for our study, aiming to provide a comprehensive analysis of hydrodynamic porosity and its implications for modeling fluid flow and transport in porous media, with particular emphasis on the role of dead-end pores.

1.1. Effective Porosity

Among the authors who define effective porosity as the portion of constant porosity used to transmit fluid through porous media are Li et al. [25], Kabala and Kim [26], Kim [27], Lindsay [28], and Werth [29]. Here, we note that while these authors qualitatively consider its hydrodynamic nature, they do not quantify it. For example, Li et al. [25] qualitatively note the dependence of effective porosity on flow velocity in a study of sedimentary rock flows. The authors attribute the observed decrease to the presence of selective pathways (i.e., fissures and cracks) in the studied rock formation. They do not discuss an explicit relationship between what they term effective porosity and flow velocity. Further, the morphology of the rock formation studied in this work is starkly different than that of granular media.
In his doctoral dissertation at Duke and a publication with his advisor, Kim [27] and Kabala and Kim [26] provide the most thorough discussion on the hydrodynamic quality of effective porosity; the authors state a dependence of effective porosity on both pore geometry and Reynolds number, Re = R . They demonstrate this dependence in the same idealized pore space we study in this work using the FIDAP software. The authors show that effective porosity varies by at least an order of magnitude for creeping flows and postulate that it may “vary by as much” for non-creeping flows but do not develop an explicit relationship between effective porosity and Reynolds number (Kabala and Kim [26]).
Other authors have qualitatively considered the impact of dead-end pores on effective porosity. Lindsay [28] notes that in water-saturated paper, flow can be restricted by mechanical obstructions in the form of isolated and dead-end pores. The author also discusses the development of stagnant zones in high Reynolds number flows, and the absence of these zones in creeping flows due to the ability of the flow to closely follow abrupt changes in medium geometry. In effect, the author contemplates the dependence of effective porosity on the Reynolds number, Re = R , but does not account for it in his analysis. The concept of flow-dependent porosity also appears in a study on baleen, though in a much different context. Werth [29] describes a linear relationship between fringe porosity and incident flow velocity until a certain limiting velocity is reached, at which point the effective porosity of the baleen decreases. Given that the application of this work is to learn more about the mechanical properties of baleen to better understand the feeding behaviors of various whale species, the spatial scale and flow path morphology are fundamentally different than those studied in this work.

1.2. Cavity Flows

As we discuss in the next section, flow past cavities (also known as dead-end or blind pores), which serve as the theoretical basis for this research, are a popular research topic and comparatively well explored. There are ample publications concerning contaminant transport and flow manipulation and instabilities in dead-end pores. The bulk of this work pertains to the geometric manipulation of pore geometry to determine the effect on the induced flow (Moffatt [30]; Coats and Smith [5]; Higdon [31]; Shen and Floryan [32]; Fang et al. [33]).
Three review articles cover the field well (Meier et al. [34]; Worthington [35]; Yan et al. [36]), but there are many other notable works, e.g., Li et al. [37], Yuan and Rezaee [38], Foroughi et al. [39], Verbovšek [40], Fenni et al. [41], Kango et al. [42], and Yao et al. [43].
Studies on flow modulation have also been published, though they are relatively less explored (Jana and Ottino [44]; Howes and Shardlow [45]; Horner et al. [46]; Kahler and Kabala [47]). Most of this work is geared at industry for the guise of expediting rate-limited manufacturing processes (e.g., etching, finishing, cleaning, etc.) that are applied to surfaces with cavities (Chilukuri and Middleman [48]; Alkire et al. [49]; Fang et al. [50]).
In this work, we leverage the same physical theory that describes flows past cavities to define a hydrodynamic porosity function θ m o b i l e ( v p o r e ) = θ m o b i l e ( R ) . Previously, Kahler and Kabala [47,51,52] used the same approach to describe contaminant transport in porous media—likening duct or surface flow to flow through a series of well-connected pores, and flow past grooves and cavities on surfaces to flow past dead-end pores in granular media. Such results are crucial to understanding how phenomena like contaminant rebound in groundwater reservoirs post-remediation can be mitigated. Although Kahler and Kabala implied the hydrodynamic nature of porosity, they did not quantify it. In this paper, we demonstrate and quantify, explicitly, this relationship for the first time. We also illustrate the ease with which this relationship can be incorporated into flow and contaminant transport models. To understand why contaminant rebound after traditional pump-and-treat groundwater remediation takes place, and how it could be mitigated, researchers need to account for hydrodynamic porosity, θ m o b i l e .

2. Pore Scale Flow Modeling

Here, we are solving the continuity equation (mass conservation) and the Navier–Stokes equation (the evolution of momentum) for incompressible Newtonian fluid (water) subject to no-slip and no-penetration boundary conditions on the walls of the channel and cavity. The pressure is specified at the outlet. The imposed inlet velocity distribution is parabolic, as in a fully developed channel flow (analogous to Hagen–Poiseuille flow).
u = 0
ρ u t + u u = p + μ 2 u
u x , y = w a l l = 0
p x = c h a n n e l   l e n g t h , y = 0
where u is a 2D velocity vector, ρ is density, t is time, p is pressure, and μ is dynamic viscosity. The Navier–Stokes equation is solved for steady state, i.e., the time derivative of the velocity is zero. Since we do not refer to these equations later, we list them unnumbered.
We assume a (quasi) steady-state, laminar flow in our model. It is typical for ambient groundwater conditions, which may vary on a time scale of weeks, as well as for pump-and-treat remediation conducted predominantly with a constant/fixed pumping rate. The ambient flow is usually characterized by Re = R < 1, whereas forced-gradient flows typically do not exceed Re = R < 100 even near a pumping well and thus are also laminar. For our numerical experiments, we chose Reynolds numbers that span this range: 1, 10, 50, and 100; they help us demonstrate the variability of hydrodynamic porosity. We further discuss our selection of Reynolds numbers in Section 3 Methods.

2.1. Total Porosity

The total porosity of a medium, θ , is defined by the cumulative volume of the mobile and immobile zones; and more specifically, as the ratio of the total pore space volume to the total volume of the media, V . In an isotropic or 2D medium, like the ones we study in this work, this definition can be written in terms of cross-sectional areas:
θ = V p o r e V = A p o r e A
We note that V = V b u l k = V t o t a l and A = A t o t a l . In the analysis that follows, we represent the pore volume (or area) by the dead-end pore model, which we illustrate in Figure 2. As a result, the pore volume can be defined in terms of mobile and immobile zones. Again, we provide the cross-sectional area expression for an isotropic medium or 2D media.
V p o r e = V m o b i l e + V i m m o b i l e A p o r e = A m o b i l e + A i m m o b i l e
Thus, we can define the total porosity of the medium, θ , as a function of mobile and immobile zone porosities, θ m o b i l e and θ i m m o b i l e , respectively, by dividing Equation (2) by the total volume of the medium, V (or cross-sectional area, A ):
θ = V m o b i l e + V i m m o b i l e V = θ m o b i l e + θ i m m o b i l e

2.2. Pore-Scale Flow Velocity

An expedient (and reductive) way to define the pore-scale flow velocity is to use the volumetric velocity, also known as the superficial or Darcy/Forchheimer velocity. This quantity is equivalent to the flow velocity of a fictitious fluid flowing through an entire cross section of the medium rather than just through the void space conducive to flow:
v v o l u m e t r i c = v = Q A = q
where Q is the volumetric flow rate, A , is the cross-sectional area of the medium, and q , is the “flux.” Neglecting inertial effects, Darcy’s law relates the volumetric velocity to the pressure gradient applied to the medium (Brutsaert [53]; Muljadi et al. [54]; Bear [55]):
p = μ k v               h = μ k γ v               h = 1 K v
where p is the pressure, h is the pressure head, k is the permeability of the medium, K is the hydraulic conductivity, γ is the specific weight of the fluid, and μ is its viscosity. The equivalences we show here are to illustrate the preferred forms in oil and gas reservoir modeling (left) and groundwater hydrology (right). When inertial effects cannot be neglected, as is the case for high Reynolds number flows, we must utilize the quadratic correction term, introduced by Èstudes [56] and Forchheimer [57]. Given this adjustment, Darcy’s law becomes the Forchheimer–Dupuit law:
p = μ k v + B ρ v 2 n               h = 1 K v + B 1 g v 2 n
where n is a unit vector in the direction of the volumetric velocity, ρ the flow density, and B , a coefficient that can be found experimentally (Chen et al. [58]). Depending on the flow conditions, the volumetric velocity can be estimated experimentally from Equation (5) or Equation (6) (i.e., from Darcy’s law or the Forchheimer–Dupuit law, respectively). To attain the true pore-scale flow velocity, which would be needed to determine quantities such as contaminant transport time, the volumetric velocity must be modified by the medium’s porosity (Bear [55]):
v p o r e = v θ
Back-of-the-envelope calculations may simply use the total porosity of the medium. If the mobile zone porosity is known, then θ m o b i l e would instead be used, but as a static quantity. This would also be suitable for washed media without any cavities or other effectively immobile zones. Equation (7) can be derived from a simple conservation of mass analysis:
v p o r e A p o r e = v A                 v p o r e = A A p o r e v                 v p o r e = 1 θ v
Given the fact that immobile zones do not contribute to through-flow, we know that use of the medium’s total porosity is an oversimplification. Pore-scale flow velocity should instead be defined by the total volume that is conducive to flow—a quantity that is itself dependent on pore-scale flow velocity. Equation (7) should instead read
v p o r e = v θ m o b i l e v p o r e = v θ m o b i l e R
where, rather than being modeled as static quantity, as is typically the case, θ m o b i l e is itself a function of pore-scale flow velocity, and thus, we proceed with the following notation: θ m o b i l e ( R ) . The implicit nature of Equation (8), while seemingly more difficult to solve than Equation (7), is quickly resolved by a few Picard iterations. Not only is Equation (8) a more accurate description of pore-scale flow velocity, but it is also a necessary improvement in the modeling of induced subsurface flows that can be easily implemented.

2.3. Defining the Pore-Space Partitioning Coefficient

Given that the pore space can be broken down into mobile and immobile zones, we can define a pore-space partitioning coefficient, ξ , to describe the ratio of pore space conducive to through-flow:
ξ = V m o b i l e V p o r e = A m o b i l e A p o r e
We note that the pore-space partitioning coefficient is related to the hydrodynamic porosity of the medium, θ m o b i l e ( R ) , by
ξ = V m o b i l e V p o r e = θ m o b i l e ( R ) V V p o r e = θ m o b i l e ( R ) θ
In the analysis that follows, it is the behavior of the pore-space partitioning coefficient that we numerically quantify as a function of the Reynolds number. We are able to use our results to describe the hydrodynamic porosity, θ m o b i l e ( R ) , of the medium because of the direct proportionality between these two quantities.

2.4. The Dead-End Pore Model

To geometrically simplify the pore space of a porous medium, we study a single cavity or dead-end pore, as pictured in Figure 1. The idea of a poorly connected, or dead-end pore was first explored by Turner [59], who studied channel flow with distributed pockets of stagnant fluid. Although Turner admitted such pore spaces would play a role in diffusion throughout the pore space, other researchers such as Fatt [60] and Goodknight et al. [61] initially regarded dead-end pore spaces as regions through which diffusion could not occur. Deans [62] noted that the division of pore space into flowing and stagnant regions, separated by a “resistance to mass transfer” is an “extreme limit” that can only be justified on the grounds of simplicity. Following this conclusion, Coats and Smith [5] relaxed the definition of the dead-end pore to account for diffusion, but still referred to the dead-end pore volume as stagnant. Physically, we know this enforcement to be an oversimplification of the recirculatory flow within the dead-end pore space. Chilukuri and Middleman [48] corrected for this oversimplification by describing mass transport from dead-end pores as a result of vortex-enhanced diffusion—a conclusion that coincides with a series of publications that detail the vortex structures within dead-ended pores (Moffatt [30]; Mehta and Lavan [63]; O’ Brien [64]; Shen and Floryan [32]; Kang and Chang [65]; Fang et al. [33]). The evolution of the dead-end pore model is illustrated in Figure 2, below.
Separation of the mobile and immobile zone volumes is described by the boundary- or shear-driven flow models; we refer to the boundary between these zones as the separatrix. In application to flow, the idea of a separatrix was first postured by Elderkin [66], who describes the boundary as a trajectory that is topologically abnormal in comparison to nearby trajectories. Weiss [67] later used this concept to describe the defining limit between free and trapped fluid regions. Other publications refer to this boundary as a dividing (Moffatt [30]; O’ Brien [64]; Higdon [31]) or separating streamline (Shen and Floryan [32]; Alkire et al. [49]). The modeling and experimental work on which we build, i.e., Kahler and Kabala [47,51,52], and even earlier publications such as Horner et al. [46], use this same terminology (the separatrix) to describe the fluidic boundary between the mobile and immobile zones in the idealized dead-end pore space.
In the case of the boundary-driven model (which is essentially the commonly studied driven-lid problem), the geometric boundary between the mobile and immobile zones also serves as the fixed location of the separatrix. With an increase in Reynolds number of the adjacent through-channel flow, the vortex structures within a cavity translate and smear in the direction of the imposed boundary condition movement. Such results have been illustrated by many and summarized by Shankar and Deshpande [68]. In shear-driven flows, the separatrix is free to move about the cavity space. As discussed by Fang et al. [50] and Kahler and Kabala [47], the exact location of the separatrix depends on the Reynolds number of the adjacent through-channel flow in the mobile zone. This means that, unlike in the case of the boundary-driven flow condition, the mobile and immobile zones cannot be defined based on the geometry of the pore space alone. Instead, the volumes of these zones must be defined as flow dependent. In application to square cavity flow, a comparison between the enforcement of the boundary-driven and shear-driven flow conditions is provided in Figure 3 below.
In the study of flow past cavities, it is standard practice to enforce the shear-driven boundary condition. Researchers who initially studied these flows, e.g., Moffatt [30], immediately identified through-flow penetration into the cavity space upon investigation. O’Neill [69] and Wakiya [70] found that attachment of the separatrix to the cavity wall occurs at some depth into the cavity and as Higdon [31] states, not at the sharp, leading edge of the cavity. In fact, for rectangular cavities exceeding a given depth ratio, researchers found that the downstream attachment of the separatrix, or dividing streamline, occurs at the bottom of the cavity wall, mimicking the behavior of a sudden-expansion flow (Shen and Floryan [32]; Alkire et al. [49]). Enforcement of the boundary-driven flow model would, in this application, yield significant error.
With these findings considered, we again refer to the discussion presented by Li et al. [25] wherein the effective porosity of the studied medium is found to be flow dependent. The authors of this study explain that this dependence is a result of physical macrostructures that act as preferential flow paths during high flow volumes. What the authors do not discuss, is the hydrodynamic behavior of the immobile zones within the medium—a behavior that is driven by separatrix movement in to and out of each effectively dead-end pore. As flow volumes increase, the separatrix moves toward its neighboring through channel, and the immobile zone it defines grows. The result of an increase in flow volume is a decrease in hydrodynamic porosity, θ m o b i l e ( R ) . It is only when the shear-driven flow condition is applied to the dead-end pore that this behavior is observed. If the mobile and immobile zones are improperly defined by the simplified boundary-driven flow condition, this behavior is missed.

3. Methods

To determine the hydrodynamic porosity, θ m o b i l e ( R ) , of a porous medium, we study the medium at the pore scale and assume an idealized dead-end pore geometry. The movement of the separatrix is tracked over a range of interstitial Reynolds numbers to determine the relative magnitudes of the mobile and immobile zones, which we then use to calculate the value of the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ .

3.1. Numerical Flow Solver

To observe movement of the separatrix in the idealized pore space, we use Mathematica’s numerical differential equation solver, NDSolve, to solve the continuity equation (mass conservation), Navier–Stokes equations (momentum evolution), and associated boundary conditions. The solver domain is a replica of the idealized pore space utilized by Kahler and Kabala [47] and is similar in geometry to the domain commonly used in the study of flow past cavities (Chilukuri and Middleman [48]; Higdon [31]; Fang et al. [33]). For the sake of simplicity, the flow is modeled as being two-dimensional. The height of the through channel is the same as the depth and width of the dead-end pore (i.e., the dead-end pore has a depth ratio of 1:1). In the study of flow past cavities, this geometry is by far the most prevalent, as noted by Shankar and Deshpande [68]. The through channel is extended past the dead-ended pore by twice the channel height to eliminate any end effects associated with the outflow boundary condition. Finally, the dead-ended pore is located one-fourth of the way into the through-channel given the need to input a fully developed flow profile at the through-channel inlet. To exaggerate the movement of the separatrix as a function of the Reynolds number, the solver domain is manipulated such that the through channel becomes much narrower than the depth and width of the cavity space.
The idealized flow geometry is discretized through use of the ElementMesh function, which, by default, generates a second-order, triangular element mesh. The interior and boundary mesh elements are further refined by specifying upper limits on the MaxCellMeasure and MaxBoundaryCellMeasure. A brief convergence analysis of the interior and boundary mesh cell sizes is provided in the Supplemental Materials. Further, a refinement region is specified at the geometric boundary of the channel–cavity interface to ensure proper resolution of the separatrix.
The solver itself is defined by the system of equations that describe steady-state flow through the idealized pore space (i.e., the incompressible form of the continuity and Navier–Stokes equations), as well as the boundary conditions that are assigned to the solver domain. These equations are normalized by the channel height, h, and the average inlet flow velocity, U. The flow is assumed to be a steady state and restricted to the laminar flow regime. A set of Dirichlet conditions are applied to the boundaries of the solver domain (i.e., the no-slip condition at the domain walls and a uniform pressure condition, wherein the pressure is arbitrarily set to zero, at the domain outlet). The inlet velocity profile is defined by the Hagen–Poiseuille model for fully developed channel flow. Finally, flow is assigned to the entire idealized pore space given that the application of this work is to fully saturated porous media. The properties of water at standard conditions are assigned to the fluid.
We note that the non-dimensional form of the Navier–Stokes equations is used in this analysis. The scaling on the pressure term is appropriate for flows that are dominated by convective action (i.e., flows in which viscous effects are relatively negligible). This choice was made to replicate the scaling utilized by Kahler and Kabala [47], who studied flows with channel-based Reynolds numbers of Re = R = 0.01–10. Fang et al. [33] used the same scaling, though for admittedly higher channel-based Reynolds numbers in the range of 50–1600. For our case, and the work on which we build, this scaling is justified because these studies aim to capture flow phenomena driven by convective action (i.e., changes in momentum to the bulk flow). When the Reynolds number approaches 0, and the flow can be approximated as creeping, the scaling on the pressure term can be achieved through use of the flow viscosity.
For this system of equations, NDSolve utilizes the Finite Element Method (Wolfram Finite Element Method [71]) to arrive at a solution. In general, the solver method is automatically determined by the results of symbolic analysis. The use of the Finite Element Method is triggered by specific user inputs. For example, specification of the Navier–Stokes equation using the “Inactive” operator or boundary conditions defined by the DirichletCondition function prompt the use of this solver method. Implementation of this solver method can be verified by validating that the solution contains an ElementMesh (Wolfram Symbolic and Numerical Computation [72]). The outputs of the solver are three interpolating functions that describe the pressure and velocity fields within the flow domain. Streamlines are visualized through the use of the built-in StreamPlot command. The error associated with each solver output is determined by the solver mesh (i.e., domain discretization), assigned working precision, and solver method.
The above-mentioned functions are very well documented in the Wolfram Language (Mathematica) Documentation [72,73] and in Wolfram Numerical Solutions of PDEs [74]. Furthermore, in Supplemental Materials, we provide the code used in this study. The main errors are numerical, but our convergence analysis, also included in Supplemental Materials, demonstrates that they are negligible. The adopted 2D flow simplifying assumption is consistent with flow through fractured-rock medium with wide fractures, and thus is not severely limiting—moreover, it is invoked by numerous studies in the literature (see further discussion at the end of Section 6).

3.2. Data Collection

In this work, we vary the Reynolds number of the through-channel flow (i.e., the flow in the mobile zone), and the depth ratio of the idealized dead-end channel–cavity geometry. As noted by Fang [75] and others, the location of the separatrix is a function of both Reynolds number and geometry (Mehta and Lavan [63]; O’Brien [64]; Higdon [31]; Kim [27]).

3.2.1. Reynolds Numbers

Below a Reynolds number of 1, the separatrix remains stationary (Kahler and Kabala [47]). Flows of this nature are classified by the creeping flow regime, where viscous effects dominate. It is not until we study Reynolds numbers within the inertial flow regime that we observe a mobile separatrix. This is because the location of the separatrix is dictated by the inertia of the adjacent through-flow. For this reason, we impose the following Reynolds number, Re, ranges to the through-flow:
  • Re = R = 0.01–1
    (to verify the stationary nature of the separatrix in the creeping flow regime)
  • Re = R = 1–100
    (to illustrate the mobility of the separatrix in the laminar flow regime)
To remain within the laminar flow regime, we limit our Reynolds number to a maximum of 100. This choice is admittedly arbitrary, given that transition to turbulence in pipe flow typically occurs over a diameter-based Reynolds number of 2000 and at least one order of magnitude above the particle-based Reynolds number at which the deviation from Darcy’s Law occurs in porous media (Bear [55]); deviation from Darcy’s Law generally occurs between a particle-based Reynolds number of 1 and 10.
In terms of particle-based Reynolds numbers, there is ample evidence that the onset of transitionary behavior occurs around 100. For columns of packed spheres, Jolls and Hanratty [76] report the onset of transitionary behavior within the range of 110–150. Wegner et al. [77] found a slightly lower range of 90–120 for beds of packed spheres. Latifi et al. [78] encountered transitionary behavior at 110, also for a bed of packed spheres; however, the authors did note unsteady laminar flow behavior until 370. A similar study conducted by Rode et al. [79] reports transitionary behavior in the range of 110–150. Finally, Bu et al. [80] define a critical particle-based Reynolds number of 100 as the cutoff for laminar flow, with the onset of turbulence occurring between 230–400.
If we instead consider the interstitial Reynolds number, which is based on average pore size and average pore-scale flow velocity, we encounter the commonly cited Reynolds number ranges provided by Dybbs and Edwards [81], summarized in Table 1 below.
We can easily imagine representing our system in terms of the interstitial Reynolds number. Given our assumption that the medium is homogeneous, we know the average pore size. Pore-scale flow velocity is typically calculated by dividing the flux through the medium by the porosity of the medium, but in our case, we will impose it directly by assigning a mean velocity to the through-channel flow. Capping our Reynolds number at a value of 100 keeps our analysis within the steady laminar flow regime.

3.2.2. Flow Geometries

The effect of pore geometry manipulation has been extensively studied in the literature. In these studies, the authors vary the type of cavity (i.e., rectangular, circular, etc.), the depth ratio of the cavity, and the size of the cavity relative to the size of the adjacent through channel. To replicate the results obtained by Kahler and Kabala [47], we use an idealized geometry wherein the height of the through channel is equivalent to the depth and width of the cavity geometry, as provided in the top-left quadrant of Figure 4. To exaggerate the mobility of the separatrix in the laminar flow regime, the depth and width of the cavity, relative to the through channel, are equally increased in magnitude. These geometries are provided in Figure 4, below, and referred to by channel–cavity depth ratios (i.e., 1:1, 3:4, 1:2, and 1:4). For example, the depth ratio 1:2 corresponds to the geometry in which the cavity depth and width are twice that of the through-channel height.
We note that in this paper (Part 1), we consider rectangular pores of various aspect ratios, i.e., a highly idealized case of the dead-ended pore spaces. In the companion paper (Part 2), we build upon our findings from this paper and demonstrate their applicability to media with other geometries: rectangular and non-rectangular cavities (i.e., circular, and triangular).

3.3. Measurement Method

To determine the value of the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , and therefore the hydrodynamic porosity, θ m o b i l e ( R ) , for each inlet flow condition, we use the following procedure:
  • Generate a monochromatic stream plot of the flow.
  • Draw the separatrix in the area between the bulk flow in the through channel and the recirculatory flow in the dead-end pore space in a contrasting color, using the streamlines in the stream plot for guidance.
  • Use an interpolating function to mathematically describe the location of the separatrix.
  • Define the area below the separatrix as the immobile zone, and the area above as the mobile zone and use numerical integration to quantify the magnitude of these regions.
To draw the separatrix, we use a DynamicModule in Mathematica to generate an interpolating function that includes five points (or more) of our choosing between the mobile and immobile zones. This process is pictured below in Figure 5. To determine the sizes of the mobile and immobile zones, we apply numerical integration to the resulting interpolating function.
Given that the shape and location of this interpolating function are a direct result of user input, there is an inherent error built into the measurement process that we are unable to precisely quantify. Additional errors in the measurement process result from the chosen resolution of the stream plots which is in turn limited by the quality of the solver mesh and working precision assigned to the numerical solver method.

4. Results

4.1. Separatrix Movement

Because the cavity flow is driven by the adjacent through-channel flow, we start by providing a stream plot of the entire dead-end pore geometry adjacent to the corresponding cavity flow in Figure 6. We then provide stream plots for each cavity geometry at Reynolds numbers of 1, 10, 50, and 100 in Figure 7.
With the flow in the flow-through channel (shown in Figure 6) from the left to the right, note in Figure 7 clear inertial effects: with the increasing Reynolds number the center of the cavity vortex moves to the right and rises up.
The corresponding movement of the separatrix as a function of Reynolds number was first explored by Kahler and Kabala [47]. In their work, the authors track the bottom-most point of the separatrix to determine its maximum penetration depth into the dead-end pore. To confirm the numerical accuracy of the results produced in this work, we replicate this plot, which is provided in the Supplemental Material. We expand upon this plot by tracking the movement of the separatrix for three additional flow geometries, as pictured below.
The results obtained by Kahler and Kabala [47] reveal an immobile separatrix in the creeping flow regime (i.e., Re < 1), and a mobile separatrix in the inertial flow regime. In the former, the bottom-most point of the separatrix does not exceed 25% of the depth of the idealized pore space. Our results replicate the separatrix behavior observed by Kahler and Kabala [47] and are within, at most, a 2% difference. Over the range of Reynolds numbers plotted in Figure 8, the maximum penetration depth of the separatrix diminishes by 20%.
Building upon the test conditions utilized by Kahler and Kabala [47], we observe movement of the separatrix toward the geometric boundary of the cavity space for Reynolds numbers approaching 100. Movement of the separatrix within the cavity space is further exaggerated by manipulation of the flow geometry, as illustrated in Figure 9 below.
Movement of the separatrix toward the adjacent through channel (and out of the cavity space) results in a decrease in the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , and therefore, the hydrodynamic porosity, θ m o b i l e R , of the medium. For example, media with cavities described by the dead-end pore model pictured in the top-left quadrant of Figure 4 experience roughly a 4% reduction in θ m o b i l e over the tested Reynolds number range. By comparison, when the channel–cavity depth ratio is 1:4 (i.e., the cavity depth is four times that of the through-channel height), θ m o b i l e ( R ) decreases by approximately 42%. See Table 2 for a summary of the changes associated with each channel–cavity depth ratio; note that given Equation (10), the provided percent-decrease values are the same for the pore-space partitioning coefficient, ξ , and the hydrodynamic porosity, θ m o b i l e ( R ) , of the medium.

4.2. Exponential Dependence of Hydrodynamic Porosity on Pore-Scale Flow Velocity

When plotted, the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , and therefore the hydrodynamic porosity, θ m o b i l e ( R ) , of the medium, approaches the value suggested by the boundary-driven model we previously discussed for Reynolds numbers approaching the upper limit of the laminar regime (Re = R = 100). See Figure 10 below for evidence of this behavior. In this figure, we also demonstrate that these quantities exhibit a linear dependence on Reynolds number, in the inertial flow regime (Re = R = 1–10). Extrapolation of this relationship past Re = R = 10 is provided to illustrate the error that would result from not utilizing the exponential relationship provided in Equation (12). Again, we remind readers of the direct proportionality between the partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , and the hydrodynamic porosity of the medium, θ m o b i l e .
The fit parameters for each channel–cavity depth ratio are provided in Table 3. The quality of each fit is measured by the coefficient of determination (R2), which is approximately 1 for each tested depth ratio. In the inertial flow regime, the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , exhibits a linear dependence on Reynolds number. However, as the Reynolds number increases, the partitioning coefficient deviates from this linear model. Instead, a nonlinear dependence on Reynolds number explains the calculated partitioning coefficient values at higher Reynolds numbers, and more significantly, over the entire range of Reynolds numbers, Re, in the laminar regime (Re = 1–100). This dependence is well fitted by an exponential function:
ξ = a + b e c v p o r e             ξ = a + b e d R , w h e r e   d = c   h e i g h t ν
This expression can be easily re-written using the help of Equation (10) to define the hydrodynamic porosity of the medium, θ m o b i l e :
θ m o b i l e v p o r e = a + b e c v p o r e θ             θ m o b i l e ( R ) = ( a + b e d R ) θ
where a is the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , value approximated by the boundary-driven model (i.e., Re → ∞), and the quantity ‘a + b’ is the value in the creeping flow regime (i.e., Re 0 ). We note that these values, as written, are the same for Equations (11) and (12).
Mathematically, the fit parameter, b, drives the exponential behavior of our fit. When on the order of magnitude of 10 1 the exponential behavior of our fit becomes most exaggerated. This is exemplified in Figure 11, below, for depth ratios 1:4 and 1:2.
In Figure 11, we normalize the hydrodynamic porosity, θ m o b i l e ( R ) , by the static mobile-zone porosity value, θ M I M , that results from enforcement of the mobile–immobile zone model (i.e., the boundary-driven flow condition at the cavity–channel interface) in the dead-end pore space, defined as
θ M I M = ξ M I M θ
The geometric pore-space partitioning coefficient, ξ M I M , is determined by the relative magnitudes of the through-channel and cavity volumes of each dead-end pore geometry. For the 1:1 depth ratio pictured in Figure 4, ξ M I M = 4/5. For the 1:2 depth ratio pictured in Figure 4, however, ξ M I M = 8/12. We define these quantities to compare the relative change in hydrodynamic porosity across the four geometries provided in Figure 4.

5. Calculating Pore-Scale Flow Velocity and Hydrodynamic Porosity Parameters

5.1. Pore-Scale Flow Velocity

We can use this newfound exponential relationship outlined in Equation (12) to fill in the details of Equation (8):
v p o r e = v ( a + b e c v p o r e ) θ
Here, we remind readers that v is the volumetric velocity used in Darcy’s or Forchheimer–Dupuit’s law (Equations (5) and (6), respectively). To illustrate the ease at which the exponential relationship in Equation (12) can be incorporated into current models, we provide a brief example utilizing the idealized pore geometry provided in the top left quadrant of Figure 4, the associated exponential fit coefficients (i.e., a = 0.80 , b = 3.80 × 10 2 , and c = 25.91 s / m ), and the properties of water assumed by Kahler and Kabala [47]. In this example, we assume the volumetric velocity has a magnitude 10 3 (m/s) and a total porosity ( θ ) of 0.4—an arbitrary total porosity value in the range typically measured for unconsolidated, unwashed media (i.e., 20–45%) (Woessner and Poeter [82]).
Using only 3 Picard iterations with an initial guess of 2 × 10 3 (m/s), we converge to 3 decimal places and a pore-scale flow velocity of 2.99 × 10 3 (m/s). Below, we illustrate the power of Mathematica’s built-in Nest function, which will, for the same parameter set, converge for an initial guess spanning twenty orders of magnitude. In the code provided below, we use the sister, NestList function to quickly determine the number of iterations needed for convergence.
Incidentally, why only 3 iterations? This is not surprising once one realizes that our exponential function f(x) fulfills the Lifschitz condition: |xn+1 − xn| < |f’(xn)| |xn − xn−1| or |f’(xn)| < 1 that is necessary for the mapping, f(x), to be a contraction and thus have a fixed point—see the Banach Fixed-Point Theorem [83].
Water 16 02158 i001
In Table 4 below, we repeat this process for an initial guess 10 orders of magnitude larger and smaller than our original guess to illustrate the robust nature of this method.
From this demonstration, we conclude that implementation of Equation (12) is no more mathematically burdensome to implement than the constant porosity model, which results in unnecessary error.

5.2. Hydrodynamic Porosity Fit Parameters

In this work, we illustrate how to solve for the exponential fit parameters in Equations (11) and (12) through numerical simulation. But this is an idealized case—porous media have an array of randomly distributed and sized pore spaces, not to mention drastic changes in pore geometry. If we wanted to use the relationship provided in Equation (12), we would need to quantify the volumetric and pore-scale flow velocities to then be able to determine the corresponding exponential fit parameters. This could be achieved through column experiments with a known pressure gradient (to solve for the volumetric flow velocity), and a measurable tracer pulse (to solve for the pore-scale flow velocity). Given that Equation (12) contains three unknown parameters, we would need to conduct this experiment at least three times, each at a different, judiciously selected flow condition. We note in passing that measuring the pore-scale flow velocity is not trivial and will require care as demonstrated or implied by Wood et al. [84], Berkowitz and Scher [85], Haggerty and Gorelick [86], Medina and Carrera [87], Carrera et al. [88], Bolster et al. [89], and others. Since this issue is not central to the focus of this work, we will address it in the follow-up paper.
Here we offer only a numerical example and work with an artificial dataset, generated from use of Equation (14) and the exponential fit parameters we used in our last example (i.e., a = 0.80 , b = 3.80 × 10 2 , and c = 25.91 s / m ). We assume we have measured volumetric velocities that correspond to the laminar flow regime (Re = 1–100); for the characteristic height, we assign to the dead-end pore geometry (i.e., 0.001 m), the corresponding pore-scale velocity range is approximately 0.001–0.1 (m/s). We assume we measure the volumetric flow velocities 0.01, 0.05, and 0.09 (m/s). Given this assumption, we can calculate the corresponding pore-scale flow velocities:
Moving forward, we assume that we have measured these values experimentally and that we actually do not know the values of our exponential fit parameters, a, b, and c. We can use the synthetic dataset provided in Table 5 to calculate them. This is easily achieved through the use of Mathematica’s FindFit function. Specifying a Newton solution method, we arrive at the anticipated parameter values, exactly in 100 iterations (the default value used by the FindFit function).
Water 16 02158 i002
Here we note that we have utilized the arbitrary precision assigned by Mathematica to generate a set of pore-scale velocity values. Realistically, the precision of our measurements would be restricted by our measurement device. Thus, we re-run the above calculation, but this time with only three significant digits rather than the six that we previously used. This time, we arrive at a, b, and c values of 0.801, 0.0366, and 26.4, respectively. The error in our estimated values is 0.09%, 3.65%, and 1.73%. If we increase the precision of our measurements to four significant digits, the error in our estimated values reduces to 0.14%, 0.10%, and 0.25%, respectively. Clearly, accurate estimation of a, b, and c will require numerical fine-tuning and surplus velocity data. This process will need to be conducted via numerical and experimental column tests, which we are currently pursuing.

6. Discussion

At scale, the implications of these results are easily observed. For example, consider a periodic medium well approximated by the dead-end pore model with a measurable total porosity of 0.4. If we assume the non-dimensional idealized pore space pictured in the top left quadrant of Figure 4, we know that the entire area of the through channel contributes to the mobile porosity of the medium. The immobile zone is occupied by the vortex, which resides within the dead-end pore. For a Reynolds number of 1, the pore-space partitioning coefficient ( ξ ) of the dead-end pore geometry is approximately 0.84. Given this value, we can calculate the hydrodynamic porosity of the medium using Equation (10):
θ m o b i l e = ξ θ
As a result, the medium has a hydrodynamic porosity of approximately 0.34. If we had used the boundary-driven flow condition to determine θ m o b i l e ( R ) (provided in Figure 2 and Figure 3), we would have under-approximated the value at 0.32 by roughly 5%; similarly, we would have over-approximated the immobile porosity by roughly 20%. For the most exaggerated channel–cavity depth ratio we test (1:4), use of the boundary-driven model would have resulted in a 42% error in θ m o b i l e . This is due to the deep impingement of the through-flow into the dead-end pore for this configuration. We summarize these calculations in Table 6 below:
Comparing the shear-driven and boundary-driven models, we see that the error in the latter (in terms of the pore-space partitioning coefficient) is largest for flows approaching the creeping flow regime and does not become less than 1 until a Reynolds number of roughly 49 for the channel–cavity depth ratio of 1:1. For the exaggerated flow geometries (i.e., 3:4, 1:2, and 1:4 depth ratios), the Reynolds number must exceed 51, 48, and 45, respectively. Referring to Figure 3, we see a 17% error associated with the use of the boundary-driven model.
We note that the exponential relation in (12) along with its excellent fit quality is not surprising, as its analogs show up in several areas of mathematical physics. Exponential forms play an important role in the solution of differential equations and are common in groundwater flow modeling—see the low-velocity non-Darcy flow model in shale and tight reservoirs (e.g., Wang and Sheng [90]) and the various renditions of the well function (e.g., Theis [91], Hantush [92]); also, see their applications in the percolation theory (e.g., Hunt et al. [93]); Gardner’s equation (Gardner [94]) relating hydraulic conductivity and matric potential in flows through unsaturated porous media (vadose zone); and even the relationship between soil water content and electrical resistivity (Pozdnyakov et al. [95]). Furthermore, in nature, an exponential decline in hydraulic conductivity with depth is considered a hallmark of catchment hydrology (Ameli et al. [96]).
As already mentioned in Section 3.2.2 Flow Geometries, in this paper (Part 1) we consider rectangular pores of various aspect ratios, i.e., highly idealized dead-end pore spaces. Our main finding is that hydrodynamic porosity can be described by an exponential function of pore-scale flow velocity (or interstitial Reynolds number). In the companion paper (Part 2), we build upon this finding and demonstrate its applicability to media with other geometries: rectangular and non-rectangular cavities (i.e., circular, and triangular). Furthermore, we show that not only does the exponential relationship hold for media with a variety of cavity geometries, but it does so almost perfectly with a coefficient of determination (R2) of approximately 1 for each new set of simulation data. In this way, the research results have, hopefully, practical value in applications where unwashed porous media play an important role.
The fit parameters to our exponential relationship are likely to be affected slightly by numerical errors in the least-square fitting algorithm, which can be minimized by appropriately choosing tolerance parameters. However, the main source of errors in their estimation is likely to be anomalous (non-Fickian) tracer transport in column experiments. How often such transport will be encountered remains to be seen—we will investigate it in column lab experiments in a follow-up paper.
Naturally, the next steps for this work are an application to groundwater flow models at the macro-scale and laboratory column experiments. The ability to quantify the exponential fit parameters for sites needing remediation, as previously discussed, is also necessary to demonstrate the ease with which this relationship can be tailored to any given media. We are currently pursuing these research avenues.
As mentioned earlier, we have verified our numerical results by conducting convergence analysis, i.e., refining the numerical grids used by the Mathematica superfunction NDSolve—see the Supplemental Materials. Our numerical errors related to finite-element discretization do not exceed 2% and are likely significantly smaller. Given that our analysis exactly aligns with the analytical solution for channel flow (i.e., the Hagen–Poiseuille flow profile), we are confident that our numerical results are excellent approximations of the true (but unknown) solutions of the Navier–Stokes and continuity equations involved in our boundary-value problems.
We note that several articles and a dissertation on flow over cavities present results analogous to ours. Although none of them introduce the concept of hydrodynamic porosity, their results confirm ours qualitatively or even quantitatively (for specific Reynolds numbers and specific cavity geometries). These papers are mostly limited to a short range of Reynolds numbers. They include studies of flow in tubes with circumferential cavities and in 2D channels with cavities. The numerical studies confirming our results include Takematsu [97]; Friedman [98]; Stevenson [99]; O’Brien, [64]; Higdon [31]; Driesen et al. [100]; and Young et al. [101]. The experimental studies confirming our results include Taneda [102]; Shankar and Deshpande [68]; and particularly the dissertation Laskowska [103]. There are also mixed studies (numerical and experimental) confirming our results: Shen and Floryan [32]; and Pan and Acrivos [104].

7. Study Limitations

The location of the separatrix, the streamline separating the flow in the flow-through channel from the vortex in the dead-end cavity, is determined by an approximate, yet relatively accurate, hybrid graphical-computational method illustrated in Figure 5. From the stream plot, the separatrix location, and ultimately the hydrodynamic porosity, θ m o b i l e ( R ) , is determined by means of an interpolation function between 5 (or more) points placed (graphically) on the smooth separatrix. The area below the separatrix (and above) is then calculated by analytic integration. The repeatability of this measurement process is reasonably good—for the idealized pore space pictured in Figure 2 (i.e., a channel–cavity depth ratio of 1:1), and a Reynolds number of 0.01, the maximum penetration depth of the separatrix was found to vary by 0.005 across five measurements. Relative to an average penetration depth of 0.25, this variation accounts for less than 2% of the magnitude of the mean.
Our algorithm for determining the separatrix location is robust and is presented in our highly legible code available in the Supplemental Materials. Its errors are smaller than the numerical errors of solving the PDEs. An alternative method could be based on image processing, but with our robust algorithm, there is no need for it.
Additionally, we consider only the immobile zones generated by dead-end pores and cavity-like structures that generate flow separation. We do not consider the immobile zones that result from molecular forces between the media and the flowing solution, nor do we consider surface tension effects. However, we assume that these immobile zones, just as the ones studied in this work, would behave similarly so long as the Reynolds number of the interstitial flow is appropriate, i.e., up to about 100.
Finally, this work focuses on groundwater flow, i.e., flow through fully saturated porous media with dead-end pores (unwashed sand and gravel, fractured rock, etc.). Consequently, our results do not apply to multiphase flow such as water and air in unsaturated (vadose) zone. Also, our results are derived for Newtonian, incompressible fluids and thus do not apply to non-Newtonian, rheological flows.

8. Conclusions

In this work, we explore a physical phenomenon that has been largely neglected in the literature. Generally, the porosity of a medium that is conducive to through-flow, what we define as hydrodynamic porosity, θ m o b i l e , is still thought to be a static parameter. Researchers define this quantity using the cumulative volume of the flow through channels (i.e., mobile zones); cavities and other effectively immobile zones are not considered to significantly contribute to the through-flow volume. We find this approximation to be a notable oversimplification in the creeping and inertial flow regimes, resulting in the misrepresentation of porous media flows and associated transport processes.
Although a few researchers have previously acknowledged the dependence of what they analogously define as effective porosity on the flow velocity in rock formations, these researchers did not quantify this relationship. In this work, we demonstrate and quantify, explicitly, the dependence of hydrodynamic porosity, θ m o b i l e , on pore-scale flow velocity, for the first time. We begin with a direct replication of the results provided by Kahler and Kabala [47], wherein the boundaries between the mobile and immobile zones of porous media are shown to be hydrodynamic in nature. We then study the movement of this boundary over a range of interstitial, or channel-based, Reynolds numbers in the laminar flow regime in porous media. The movement of this boundary defines the pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ (i.e., the fraction of the pore space conducive to through-flow), and therefore, the hydrodynamic porosity, θ m o b i l e ( R ) , of the medium. Given the direct proportionality between these quantities, we find both to have an exponential dependence on Reynolds number or pore-scale flow velocity, which we provide in Equations (11) and (12). Finally, we show that this dependence can be easily incorporated into porous media flow modeling using only a few Picard iterations, even with an initial guess that is over 10 orders of magnitude off.
The flow-dependent nature of hydrodynamic porosity, θ m o b i l e ( R ) , plays an unmistakable role in the transport of contaminants in porous media. Moving forward, our research opens avenues for further exploration into the impact of dead-end pores on fluid flow dynamics and macroscopic transport phenomena. By integrating insights from recent studies and leveraging advances in modeling techniques, we can advance our understanding of porous media behavior and contribute to the development of more accurate predictive models for practical applications in groundwater remediation, surface water treatment, and various industrial processes.
The exponential relationship and our results reported here can find broad applications: from groundwater flow to flow-through filters (for example, our work: Young et al. [101]) and flows for cleaning grooved surfaces, such as in the production of computer motherboards (e.g., Fang et al. [33,50]; Fang [75]).
Finally, our segmenting of the material into two papers has a guiding logic: Part 1 (this paper) presents the hydrodynamic porosity as an exponential function of pore-scale flow velocity (or interstitial Reynolds number) for a pore with a square cavity—a highly idealized case of the dead-ended pore spaces in a porous medium. In contrast, Part 2 (companion paper: Young and Kabala [105]) demonstrates the applicability of the exponential relationship to media with other cavity geometries: rectangular and non-rectangular (e.g., circular and triangular). It appears this relationship is widely applicable to porous/fractured media.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/w16152158/s1, The supporting materials include Codes: MDPI_Water_Paper1_DataFile.nb and MDPI_Water_Paper1_SolverModules.wl and convergence analysis: MDPI_Water_MeshConvergenceAnalysis.nb and MDPI_Water_MeshConvergenceAnalysis.pdf.

Author Contributions

Conceptualization (Z.J.K.), data curation (A.H.Y.), formal analysis (A.H.Y.), investigation (A.H.Y. and. Z.J.K.), methodology (A.H.Y. and. Z.J.K.), project administration (Z.J.K.), supervision (Z.J.K.), validation (A.H.Y.), visualization (A.H.Y.), writing—original draft (A.H.Y. and. Z.J.K.), writing—review and editing (A.H.Y. and. Z.J.K.). All authors have read and agreed to the published version of the manuscript.

Funding

This work was, in part, supported by the Bill & Melinda Gates Foundation through Duke University’s Center for WaSH-AID by a grant, OPP1173370 (Sanitation Technology Cluster). And the APC was funded by the same source. All opinions, findings, and conclusions or recommendations expressed in these works are those of the author(s) and do not necessarily reflect the views of the Foundation, Duke, or the Center.

Data Availability Statement

The simulation data that support the findings of this study, the corresponding Mathematica/Wolfram language code files (notebooks), and convergence analysis notebook are available in Supplemental Materials.

Acknowledgments

We acknowledge the academic editor, assistant editor, and three anonymous reviewers for their careful reading of our initial manuscript and for offering constructive and insightful critique. Their comments and suggestions allowed us to significantly improve the manuscript.

Conflicts of Interest

The authors declare no competing conflicts of interest.

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Figure 1. Mobile zone composed of well-connected pore space (A), and an immobile zone in the form of a poorly connected/dead-end pore (B).
Figure 1. Mobile zone composed of well-connected pore space (A), and an immobile zone in the form of a poorly connected/dead-end pore (B).
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Figure 2. Mobile–immobile zone model of the dead-end pore space (left), boundary-driven condition, and vortex-enhanced diffusion (middle), shear-driven boundary condition yielding a deformable, mobile separatrix (right).
Figure 2. Mobile–immobile zone model of the dead-end pore space (left), boundary-driven condition, and vortex-enhanced diffusion (middle), shear-driven boundary condition yielding a deformable, mobile separatrix (right).
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Figure 3. Vortex location for the mobile and immobile separatrix (left and right, respectively). The location of the mobile separatrix is determined from a shear-driven flow condition. The location of the immobile separatrix is determined from a boundary-driven flow condition. These results are generated for the idealized pore space provided in Figure 4 for Re = R = 10, see Section 3.2.2.
Figure 3. Vortex location for the mobile and immobile separatrix (left and right, respectively). The location of the mobile separatrix is determined from a shear-driven flow condition. The location of the immobile separatrix is determined from a boundary-driven flow condition. These results are generated for the idealized pore space provided in Figure 4 for Re = R = 10, see Section 3.2.2.
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Figure 4. Study geometries 1:1 3:4, 1:2, and 1:4; specified by their depth ratio (i.e., channel height to cavity depth/width) in non-dimensional space.
Figure 4. Study geometries 1:1 3:4, 1:2, and 1:4; specified by their depth ratio (i.e., channel height to cavity depth/width) in non-dimensional space.
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Figure 5. A DynamicModule automatically places five points on a monochromatic stream plot in the vicinity of the separatrix (left). Given user input (i.e., movement of these five points to the approximate location of the separatrix), the DynamicModule produces an interpolating function that can be used to describe the location of the separatrix (right).
Figure 5. A DynamicModule automatically places five points on a monochromatic stream plot in the vicinity of the separatrix (left). Given user input (i.e., movement of these five points to the approximate location of the separatrix), the DynamicModule produces an interpolating function that can be used to describe the location of the separatrix (right).
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Figure 6. Stream plot magnification example.
Figure 6. Stream plot magnification example.
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Figure 7. Dead-end pore stream plots for each depth ratio (1:1, 3:4, 1:2, and 1:4 from top to bottom) for Reynolds numbers (1, 10, 50, and 100 from left to right).
Figure 7. Dead-end pore stream plots for each depth ratio (1:1, 3:4, 1:2, and 1:4 from top to bottom) for Reynolds numbers (1, 10, 50, and 100 from left to right).
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Figure 8. Maximum relative penetration depth of the separatrix into the dead-end pore space as a function of Reynolds number, Re.
Figure 8. Maximum relative penetration depth of the separatrix into the dead-end pore space as a function of Reynolds number, Re.
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Figure 9. Immobile zone vortex streamlines, corresponding to Re = 1, bounded by the separatrix (highlighted in yellow) for each channel–cavity depth ratio, 1:1, 3:4, 1:2, and 1:4 (from left to right). Additional separatrix locations for Reynolds numbers corresponding to 10, 50, and 100 are plotted in orange, purple, and blue, respectively.
Figure 9. Immobile zone vortex streamlines, corresponding to Re = 1, bounded by the separatrix (highlighted in yellow) for each channel–cavity depth ratio, 1:1, 3:4, 1:2, and 1:4 (from left to right). Additional separatrix locations for Reynolds numbers corresponding to 10, 50, and 100 are plotted in orange, purple, and blue, respectively.
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Figure 10. The pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , exhibits a linear dependence on Reynolds number, Re = R , for Re = 1–10 and an exponential dependence for Re = R = 1–100. At Reynolds numbers approaching 100, the partitioning coefficient of the flow geometry approaches the value predicted by the boundary-driven flow model. The results pictured here are for the 1:1 channel–cavity depth ratio.
Figure 10. The pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , exhibits a linear dependence on Reynolds number, Re = R , for Re = 1–10 and an exponential dependence for Re = R = 1–100. At Reynolds numbers approaching 100, the partitioning coefficient of the flow geometry approaches the value predicted by the boundary-driven flow model. The results pictured here are for the 1:1 channel–cavity depth ratio.
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Figure 11. The exponential decay of hydrodynamic porosity, θ m o b i l e ( R ) , as a function of Reynolds number, Re, for media with cavities of varying channel–cavity depth ratios. For ease of comparison, θ m o b i l e ( R ) is normalized by the value that corresponds to the mobile–immobile zone model, θ M I M .
Figure 11. The exponential decay of hydrodynamic porosity, θ m o b i l e ( R ) , as a function of Reynolds number, Re, for media with cavities of varying channel–cavity depth ratios. For ease of comparison, θ m o b i l e ( R ) is normalized by the value that corresponds to the mobile–immobile zone model, θ M I M .
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Table 1. Reynolds number ranges corresponding to pre-turbulent flow regimes, as provided by Dybbs and Edwards [81].
Table 1. Reynolds number ranges corresponding to pre-turbulent flow regimes, as provided by Dybbs and Edwards [81].
Flow RegimeReynolds Number Range
Creeping/Darcy0–1
Inertial1–10
Laminar, non-linear10–150
Laminar, unsteady150–300
Table 2. Maximum and minimum pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , values corresponding to an increase in Reynolds number in each tested flow geometry.
Table 2. Maximum and minimum pore-space partitioning coefficient, ξ = θ m o b i l e ( R ) / θ , values corresponding to an increase in Reynolds number in each tested flow geometry.
Pore-Space Partitioning Coefficient, ξ = θmobile/θ
Depth RatioMax.Min.% Decrease
1:10.840.84.34
3:40.810.757.47
1:20.790.6715.81
1:40.870.5141.50
Table 3. Hydrodynamic porosity, θ m o b i l e ( R ) , parameters for Reynolds number dependence (d) and pore-flow velocity (c) defined in Equations (11) and (12).
Table 3. Hydrodynamic porosity, θ m o b i l e ( R ) , parameters for Reynolds number dependence (d) and pore-flow velocity (c) defined in Equations (11) and (12).
Equation (12) Exponential Fit Parameters
Depth RatioR2abc (s/m)d
1:11.00000.803.80 × 10−225.913.19 × 10−2
3:41.00000.756.20 × 10−233.624.14 × 10−2
1:21.00000.671.26 × 10−149.796.13 × 10−2
1:40.99930.503.66 × 10−177.329.52 × 10−2
Table 4. The pore-scale flow velocity (m/s) can be determined in only a few Picard iterations.
Table 4. The pore-scale flow velocity (m/s) can be determined in only a few Picard iterations.
Pore-Scale Velocity (m/s)
Iteration Number
Initial Guess1234
2 × 10 3 0.00299016 0.00299344 0.00299345 0.00299345
2 × 10 13 0.00298329 0.00299342 0.00299345 0.00299345
2 × 10 7 0.003125 0.00299388 0.00299346 0.00299345
Table 5. Artificial volumetric and pore-scale flow velocity (m/s) data set, generated from Equation (13).
Table 5. Artificial volumetric and pore-scale flow velocity (m/s) data set, generated from Equation (13).
Volumetric Velocity (m/s) × 10−2 Pore-Scale Flow Velocity (m/s) × 10−2
1 3.05939
5 15.6122
9 28.1241
Table 6. Error in the mobile–immobile zone model for a periodic medium with a total porosity of 0.4 and cavity geometry pictured in the top left quadrant of Figure 4.
Table 6. Error in the mobile–immobile zone model for a periodic medium with a total porosity of 0.4 and cavity geometry pictured in the top left quadrant of Figure 4.
Pore-Space Partitioning Coefficient,
ξ = θmobile/θ
Mobile Zone Porosity,
θmobile
Immobile Zone Porosity,
θimmobile
Hydrodynamic porosity model0.840.3360.064
Mobile–immobile zone model0.80.320.08
Mobile–immobile zone model error (%)5%20%
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Young, A.H.; Kabala, Z.J. Hydrodynamic Porosity: A New Perspective on Flow through Porous Media, Part I. Water 2024, 16, 2158. https://doi.org/10.3390/w16152158

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Young, August H., and Zbigniew J. Kabala. 2024. "Hydrodynamic Porosity: A New Perspective on Flow through Porous Media, Part I" Water 16, no. 15: 2158. https://doi.org/10.3390/w16152158

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