Groundwater flow equation

Used in hydrogeology, the groundwater flow equation is the mathematical relationship which is used to describe the flow of groundwater through an aquifer. The transient flow of groundwater is described by a form of the diffusion equation, similar to that used in heat transfer to describe the flow of heat in a solid (heat conduction). The steady-state flow of groundwater is described by a form of the Laplace equation, which is a form of potential flow and has analogs in numerous fields.

The groundwater flow equation is often derived for a small representative elemental volume (REV), where the properties of the medium are assumed to be effectively constant. A mass balance is done on the water flowing in and out of this small volume, the flux terms in the relationship being expressed in terms of head by using the constituitive equation called Darcy's law, which requires that the flow is laminar. Other approaches are based on Agent Based Models to incorporate the effect of complex aquifers such as karstic or fractured rocks (i.e. volcanic) [1]

Mass balance

A mass balance must be performed, and used along with Darcy's law, to arrive at the transient groundwater flow equation. This balance is analogous to the energy balance used in heat transfer to arrive at the heat equation. It is simply a statement of accounting, that for a given control volume, aside from sources or sinks, mass cannot be created or destroyed. The conservation of mass states that, for a given increment of time (Δt), the difference between the mass flowing in across the boundaries, the mass flowing out across the boundaries, and the sources within the volume, is the change in storage.

${\displaystyle {\frac {\Delta M_{stor}}{\Delta t}}={\frac {M_{in}}{\Delta t}}-{\frac {M_{out}}{\Delta t}}-{\frac {M_{gen}}{\Delta t}}}$

Diffusion equation (transient flow)

Mass can be represented as density times volume, and under most conditions, water can be considered incompressible (density does not depend on pressure). The mass fluxes across the boundaries then become volume fluxes (as are found in Darcy's law). Using Taylor series to represent the in and out flux terms across the boundaries of the control volume, and using the divergence theorem to turn the flux across the boundary into a flux over the entire volume, the final form of the groundwater flow equation (in differential form) is:

${\displaystyle S_{s}{\frac {\partial h}{\partial t}}=-\nabla \cdot q-G.}$

This is known in other fields as the diffusion equation or heat equation, it is a parabolic partial differential equation (PDE). This mathematical statement indicates that the change in hydraulic head with time (left hand side) equals the negative divergence of the flux (q) and the source terms (G). This equation has both head and flux as unknowns, but Darcy's law relates flux to hydraulic heads, so substituting it in for the flux (q) leads to

${\displaystyle S_{s}{\frac {\partial h}{\partial t}}=-\nabla \cdot (-K\nabla h)-G.}$

Now if hydraulic conductivity (K) is spatially uniform and isotropic (rather than a tensor), it can be taken out of the spatial derivative, simplifying them to the Laplacian, this makes the equation

${\displaystyle S_{s}{\frac {\partial h}{\partial t}}=K\nabla ^{2}h-G.}$

Dividing through by the specific storage (S_s), puts hydraulic diffusivity (α = K/S_s or equivalently, α = T/S) on the right hand side. The hydraulic diffusivity is proportional to the speed at which a finite pressure pulse will propagate through the system (large values of α lead to fast propagation of signals). The groundwater flow equation then becomes

${\displaystyle {\frac {\partial h}{\partial t}}=\alpha \nabla ^{2}h-G.}$

Where the sink/source term, G, now has the same units but is divided by the appropriate storage term (as defined by the hydraulic diffusivity substitution).

Rectangular cartesian coordinates

Three-dimensional finite difference grid used in MODFLOW

Especially when using rectangular grid finite-difference models (e.g. MODFLOW, made by the USGS), we deal with Cartesian coordinates. In these coordinates the general Laplacian operator becomes (for three-dimensional flow) specifically

${\displaystyle {\frac {\partial h}{\partial t}}=\alpha \left[{\frac {\partial ^{2}h}{\partial x^{2}}}+{\frac {\partial ^{2}h}{\partial y^{2}}}+{\frac {\partial ^{2}h}{\partial z^{2}}}\right]-G.}$

MODFLOW code discretizes and simulates an orthogonal 3-D form of the governing groundwater flow equation. However, it has an option to run in a "quasi-3D" mode if the user wishes to do so; in this case the model deals with the vertically averaged T and S, rather than k and S_s. In the quasi-3D mode, flow is calculated between 2D horizontal layers using the concept of leakage.

Circular cylindrical coordinates

Another useful coordinate system is 3D cylindrical coordinates (typically where a pumping well is a line source located at the origin — parallel to the z axis — causing converging radial flow). Under these conditions the above equation becomes (r being radial distance and θ being angle),

${\displaystyle {\frac {\partial h}{\partial t}}=\alpha \left[{\frac {\partial ^{2}h}{\partial r^{2}}}+{\frac {1}{r}}{\frac {\partial h}{\partial r}}+{\frac {1}{r^{2}}}{\frac {\partial ^{2}h}{\partial \theta ^{2}}}+{\frac {\partial ^{2}h}{\partial z^{2}}}\right]-G.}$

Assumptions

This equation represents flow to a pumping well (a sink of strength G), located at the origin. Both this equation and the Cartesian version above are the fundamental equation in groundwater flow, but to arrive at this point requires considerable simplification. Some of the main assumptions which went into both these equations are:

• the aquifer material is incompressible (no change in matrix due to changes in pressure — aka subsidence),
• the water is of constant density (incompressible),
• any external loads on the aquifer (e.g., overburden, atmospheric pressure) are constant,
• for the 1D radial problem the pumping well is fully penetrating a non-leaky aquifer,
• the groundwater is flowing slowly (Reynolds number less than unity), and
• the hydraulic conductivity (K) is an isotropic scalar.

Despite these large assumptions, the groundwater flow equation does a good job of representing the distribution of heads in aquifers due to a transient distribution of sources and sinks.

Laplace equation (steady-state flow)

If the aquifer has recharging boundary conditions a steady-state may be reached (or it may be used as an approximation in many cases), and the diffusion equation (above) simplifies to the Laplace equation.

${\displaystyle 0=\alpha \nabla ^{2}h}$

This equation states that hydraulic head is a harmonic function, and has many analogs in other fields. The Laplace equation can be solved using techniques, using similar assumptions stated above, but with the additional requirements of a steady-state flow field.

A common method for solution of this equations in civil engineering and soil mechanics is to use the graphical technique of drawing flownets; where contour lines of hydraulic head and the stream function make a curvilinear grid, allowing complex geometries to be solved approximately.

Steady-state flow to a pumping well (which never truly occurs, but is sometimes a useful approximation) is commonly called the Thiem solution.

Two-dimensional groundwater flow

The above groundwater flow equations are valid for three dimensional flow. In unconfined aquifers, the solution to the 3D form of the equation is complicated by the presence of a free surface water table boundary condition: in addition to solving for the spatial distribution of heads, the location of this surface is also an unknown. This is a non-linear problem, even though the governing equation is linear.

An alternative formulation of the groundwater flow equation may be obtained by invoking the Dupuit–Forchheimer assumption, where it is assumed that heads do not vary in the vertical direction (i.e., ${\displaystyle \partial h/\partial z=0}$). A horizontal water balance is applied to a long vertical column with area ${\displaystyle \delta x\delta y}$ extending from the aquifer base to the unsaturated surface. This distance is referred to as the saturated thickness, b. In a confined aquifer, the saturated thickness is determined by the height of the aquifer, H, and the pressure head is non-zero everywhere. In an unconfined aquifer, the saturated thickness is defined as the vertical distance between the water table surface and the aquifer base. If ${\displaystyle \partial h/\partial z=0}$, and the aquifer base is at the zero datum, then the unconfined saturated thickness is equal to the head, i.e., b=h.

Assuming both the hydraulic conductivity and the horizontal components of flow are uniform along the entire saturated thickness of the aquifer (i.e., ${\displaystyle \partial q_{x}/\partial z=0}$ and ${\displaystyle \partial K/\partial z=0}$), we can express Darcy's law in terms of integrated groundwater discharges, Q_x and Q_y:

${\displaystyle Q_{x}=\int _{0}^{b}q_{x}dz=-Kb{\frac {\partial h}{\partial x}}}$

${\displaystyle Q_{y}=\int _{0}^{b}q_{y}dz=-Kb{\frac {\partial h}{\partial y}}}$

Inserting these into our mass balance expression, we obtain the general 2D governing equation for incompressible saturated groundwater flow:

${\displaystyle {\frac {\partial nb}{\partial t}}=\nabla \cdot (Kb\nabla h)+N.}$

Where n is the aquifer porosity. The source term, N (length per time), represents the addition of water in the vertical direction (e.g., recharge). By incorporating the correct definitions for saturated thickness, specific storage, and specific yield, we can transform this into two unique governing equations for confined and unconfined conditions:

${\displaystyle S{\frac {\partial h}{\partial t}}=\nabla \cdot (KH\nabla h)+N.}$

(confined), where S=S_sb is the aquifer storativity and

${\displaystyle S_{y}{\frac {\partial h}{\partial t}}=\nabla \cdot (Kh\nabla h)+N.}$

(unconfined), where S_y is the specific yield of the aquifer.

Note that the partial differential equation in the unconfined case is non-linear, whereas it is linear in the confined case. For unconfined steady-state flow, this non-linearity may be removed by expressing the PDE in terms of the head squared:

${\displaystyle \nabla \cdot (K\nabla h^{2})=-2N.}$

Or, for homogeneous aquifers,

${\displaystyle \nabla ^{2}h^{2}=-{\frac {2N}{K}}.}$

This formulation allows us to apply standard methods for solving linear PDEs in the case of unconfined flow. For heterogeneous aquifers with no recharge, Potential flow methods may be applied for mixed confined/unconfined cases.

See also

• Analytic element method
  • A numerical method used for the solution of partial differential equations
• Dupuit–Forchheimer assumption
  • A simplification of the groundwater flow equation regarding vertical flow
• Groundwater energy balance
  • Groundwater flow equations based on the energy balance
• Richards equation

References

1. Corona, Oliver López; Padilla, Pablo; Escolero, Oscar; González, Tomas; Morales-Casique, Eric; Osorio-Olvera, Luis (2014-10-16). "Complex groundwater flow systems as traveling agent models". PeerJ. 2: e557. doi:10.7717/peerj.557. ISSN 2167-8359.

Further reading

• H. F. Wang and M.P. Anderson Introduction to Groundwater Modeling: Finite Difference and Finite Element Methods
  • An excellent beginner's read for groundwater modeling. Covers all the basic concepts, with simple examples in FORTRAN 77.
• Freeze, R. Allan; Cherry, John A. (1979). Groundwater. Prentice Hall. ISBN 978-0133653120.

External links

• USGS groundwater software — free groundwater modeling software like MODFLOW
• Groundwater Hydrology (MIT OpenCourseware)