Aquifer test


An aquifer test is conducted to evaluate an aquifer by "stimulating" the aquifer through constant pumping, and observing the aquifer's "response" in observation wells. Aquifer testing is a common tool that hydrogeologists use to characterize a system of aquifers, aquitards and flow system boundaries.
A slug test is a variation on the typical aquifer test where an instantaneous change is made, and the effects are observed in the same well. This is often used in geotechnical or engineering settings to get a quick estimate of the aquifer properties immediately around the well.
Aquifer tests are typically interpreted by using an analytical model of aquifer flow to match the data observed in the real world, then assuming that the parameters from the idealized model apply to the real-world aquifer. In more complex cases, a numerical model may be used to analyze the results of an aquifer test, but adding complexity does not ensure better results.
Aquifer testing differs from well testing in that the behaviour of the well is primarily of concern in the latter, while the characteristics of the aquifer are quantified in the former. Aquifer testing also often utilizes one or more monitoring wells, or piezometers. A monitoring well is simply a well which is not being pumped. Typically monitoring and pumping wells are screened across the same aquifers.

General characteristics

Most commonly an aquifer test is conducted by pumping water from one well at a steady rate and for at least one day, while carefully measuring the water levels in the monitoring wells. When water is pumped from the pumping well the pressure in the aquifer that feeds that well declines. This decline in pressure will show up as drawdown in an observation well. Drawdown decreases with radial distance from the pumping well and drawdown increases with the length of time that the pumping continues.
The aquifer characteristics which are evaluated by most aquifer tests are:
Additional aquifer characteristics which are sometimes evaluated, depending on the type of aquifer, include:
An appropriate model or solution to the groundwater flow equation must be chosen to fit to the observed data. There are many different choices of models, depending on what factors are deemed important including:
Nearly all aquifer test solution methods are based on the Theis solution; it is built upon the most simplifying assumptions. Other methods relax one or more of the assumptions the Theis solution is built on, and therefore they get a more flexible result.

Transient Theis solution

The Theis equation was created by Charles Vernon Theis in 1935, from heat transfer literature, for two-dimensional radial flow to a point source in an infinite, homogeneous aquifer. It is simply
where s is the drawdown, u is a dimensionless time parameter, Q is the discharge rate of the well, T and S are the transmissivity and storativity of the aquifer around the well, r is the distance from the pumping well to the point where the drawdown was observed, t is the time since pumping began, and W is the "Well function". The well function is approximated by the infinite series
Typically this equation is used to find the average T and S values near a pumping well, from drawdown data collected during an aquifer test. This is a simple form of inverse modeling, since the result is measured in the well, r, t, and Q are observed, and values of T and S which best reproduce the measured data are put into the equation until a best fit between the observed data and the analytic solution is found.
The Theis solution is based on the following assumptions:
Even though these assumptions are rarely all met, depending on the degree to which they are violated the
solution may still be useful.

Steady-state Thiem solution

Steady-state radial flow to a pumping well is commonly called the Thiem solution, it comes about from application of Darcy's law to cylindrical shell control volumes about the pumping well; it is commonly written as:
In this expression h0 is the background hydraulic head, h0-h is the drawdown at the radial distance r from the pumping well, Q is the discharge rate of the pumping well, T is the transmissivity, and R is the radius of influence, or the distance at which the head is still h0. These conditions never truly occur in nature, but it can often be used as an approximation to actual conditions; the solution is derived by assuming there is a circular constant head boundary surrounding the pumping well at a distance R.

Analysis software