- Groundwater flow equation
Used in

hydrogeology , the**groundwater flow equation**is the mathematical relationship which is used to describe the flow ofgroundwater through anaquifer . Thetransient flow of groundwater is described by a form of thediffusion equation , similar to that used inheat transfer to describe the flow of heat in a solid (heat conduction ). The steady-state flow of groundwater is described by a form of theLaplace equation , which is a form ofpotential 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 constituative equation called

Darcy's law .**Mass balance**A mass balance must be performed, along with

Darcy's law , to arrive at the transient groundwater flow equation. This balance is analogous to the energy balance used inheat transfer to arrive at theheat 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.: $frac\{Delta\; M\_\{stor\{Delta\; t\}\; =\; frac\{M\_\{in\{Delta\; t\}\; -\; frac\{M\_\{out\{Delta\; t\}\; -\; frac\{M\_\{gen\{Delta\; t\}$

**Diffusion equation (transient flow)**Mass can be represented as

density timesvolume , and under most conditions, water can be consideredincompressible (density does not depend on pressure). The mass fluxes across the boundaries then become volume fluxes (as are found inDarcy's law ). UsingTaylor series to represent the in and out flux terms across the boundaries of the control volume, and using thedivergence 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:: $S\_s\; frac\{partial\; h\}\{partial\; t\}\; =\; -\; abla\; cdot\; q\; -\; G.$

This is known in other fields as the

diffusion equation or heat equation, it is a parabolicpartial differential equation (PDE). This mathematical statement indicates that the change inhydraulic head with time (left hand side) equals the negativedivergence 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: $S\_s\; frac\{partial\; h\}\{partial\; t\}\; =\; -\; abla\; cdot\; (-k\; abla\; h)\; -\; G.$

Now if

hydraulic conductivity ("k") is spatially uniform and isotropic (rather than atensor ), it can be taken out of the spatial derivative, simplifying them to theLaplacian , this makes the equation: $S\_s\; frac\{partial\; h\}\{partial\; t\}\; =\; k\; abla^2\; h\; -\; G.$

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: $frac\{partial\; h\}\{partial\; t\}\; =\; alpha\; abla^2\; h\; -\; G.$

Where the sink/source term, "G", now has the same units, but a different definition.

**Rectangular cartesian coordinates**Especially when using rectangular grid finite-difference models (e.g.

MODFLOW , made by theUSGS ), we deal withCartesian coordinates . In these coordinates the generalLaplacian operator becomes (for three-dimensional flow) specifically: $frac\{partial\; h\}\{partial\; t\}\; =\; alpha\; left\; [\; frac\{partial^2\; h\}\{partial\; x^2\}\; +frac\{partial^2\; h\}\{partial\; y^2\}\; +frac\{partial^2\; h\}\{partial\; z^2\}\; ight]\; -\; G.$

As an aside, MODFLOW is actually a "quasi 3D" simulation; it only deals with the vertically averaged "T" and "S", rather than "k" and "S

_{s}". In the PDE solved by MODFLOW there is no vertical ("z"-direction) derivative, 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),: $frac\{partial\; h\}\{partial\; t\}\; =\; alpha\; left\; [\; frac\{partial^2\; h\}\{partial\; r^2\}\; +\; frac\{1\}\{r\}\; frac\{partial\; h\}\{partial\; r\}\; +\; frac\{1\}\{r^2\}\; frac\{partial^2\; h\}\{partial\; heta^2\}\; +frac\{partial^2\; h\}\{partial\; z^2\}\; ight]\; -\; G.$

**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 anisotropic 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 .: $abla^2\; h=0$

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 andsoil mechanics is to use the graphical technique of drawingflownet s; wherecontour line s of hydraulic head and the stream function make acurvilinear 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 surfacewater 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 assumption (or Dupuit-Forcheimer assumption), where it is assumed that heads do not vary in the vertical direction (i.e., $partial\; h/partial\; z=0$). A horizontal water balance is applied to a long vertical column with area $delta\; x\; delta\; y$ extending from the aquifer base to the unsaturated surface. This distance is referred to as thesaturated thickness , "b". In aconfined aquifer , the saturated thickness is determined by the height of the aquifer, "H", and the pressure head is non-zero everywhere. In an unconfinedaquifer , thesaturated thickness is defined as the vertical distance between the water table surface and the aquifer base. If $partial\; h/partial\; z=0$, 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., $partial\; q\_x\; /partial\; z=0$ and $partial\; k\; /partial\; z=0$), we can expressDarcy's law in terms of integrated discharges, "Q_{x}" and "Q_{y}":: $Q\_x=int\_0^b\; q\_x\; dz\; =\; -k\; bfrac\{partial\; h\}\{partial\; x\}$: $Q\_y=int\_0^b\; q\_y\; dz\; =\; -k\; bfrac\{partial\; h\}\{partial\; y\}$

Inserting these into our

mass balance expression, we obtain the general 2D governing equation for incompressible saturated groundwater flow:: $frac\{partial\; nb\}\{partial\; t\}\; =\; abla\; cdot\; (k\; b\; abla\; h)\; +\; N.$

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 forsaturated thickness ,specific storage , andspecific yield , we can transform this into two unique governing equations for confined and unconfined conditions:: $S\; frac\{partial\; h\}\{partial\; t\}\; =\; abla\; cdot\; (k\; H\; abla\; h)\; +\; N.$

(confined), where "S=S

_{s}b" is the aquiferstorativity and: $S\_yfrac\{partial\; h\}\{partial\; t\}\; =\; abla\; cdot\; (k\; h\; abla\; h)\; +\; N.$

(unconfined), where "S

_{y}" is thespecific 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:: $abla\; cdot\; (k\; abla\; h^2)\; =\; -\; 2N.$

Or, for homogeneous aquifers,

: $abla^2\; h^2\; =\; -\; frac\{2N\}\{k\}.$

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.**ee also***

Analytic element method , a numerical method used for the solution of partial differential equations

*Dupuit assumption , a simplification of the groundwater flow equation regarding vertical flow

*Groundwater energy balance , groundwater flow equations based on the energy balance**Further reading***cite book |author=Wang, H.F. and Anderson, M.P. |year=1982 |title=Introduction to Groundwater Modeling: Finite Difference and Finite Element Methods |publisher W.H. Freeman and Company |address=San Francisco |pages=237 |isbn=0-7167-1303-9 :An excellent beginner's read for groundwater modeling. Covers all the basic concepts, with "simple" examples in

FORTRAN 77 .**External links*** [

*http://water.usgs.gov/software/ground_water.html USGS groundwater software*] — free groundwater modeling software like MODFLOW

*Wikimedia Foundation.
2010.*

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