14. Multi-Aquifer Well Package Problem 1

This is the multi-aquifer well simulation described in (Neville & Tonkin, 2004). The example simulates an upper and lower aquifer separated by an impermeable confining unit but connected by a well that is open across both aquifers.

../_images/ex-gwf-maw-p01-grid.png

Figure 14.1 Location of inactive cells and the multi-aquifer well.

14.1. Example Description

Model parameters for the example are summarized in Table 14.1. The model consists of a grid of 101 columns, 101 rows, and 2 layers. The model domain is 14,342 \(m\) in the x- and y-directions (Figure 14.1). The discretization is in the row and column directions is 142 \(m\). The top of the model is specified to be -50 \(m\) and the bottom of each layer is specified to be 142.9 and -514.5 \(m\). Groundwater flow was inactivated beyond a distance of 7,163 \(m\) from the center cell (row 51, column 51) in model layers 1 and 2 by specifying an IDOMAIN value of zero in these cells (Figure 14.1).

One transient stress period 2.1314815 days in length is simulated. The stress period has 50 time steps and uses a time step multiplier equal to 1.2, which results in time step lengths that range \(0.51 \times 10^{-4}\) to \(0.39\) days. A short simulation time is specified to prevent the effect of the well propagating to the model boundary.

Table 14.1 Model parameters for example ex-gwf-maw-p01.

Parameter

Value

Number of periods

1

Number of layers

2

Number of rows

101

Number of columns

101

Column width (\(m\))

142.0

Row width (\(m\))

142.0

Top of the model (\(m\))

–50.0

Bottom elevations (\(m\))

–142.9, –514.5

Starting head (\(m\))

3.05, 9.14

Horizontal hydraulic conductivity (\(m/d\))

1.0

Vertical hydraulic conductivity (\(m/d\))

1.0e-16

Specific storage (\(1/d\))

1e-4

Well radius (\(m\))

0.15

The horizontal and vertical hydraulic conductivity is 1 and \(1 \times 10^{-16}\) \(m/d\). The transmissivity of of the upper and lower aquifer is 92.9 and 371.6 \(m^2/d\). A constant specific storage value of \(1 \times 10^{-4}\) (\(1/d\)) is specified. All model layers are specified to be confined. An initial head of 3.05 and 9.14 \(m\) are specified in the upper and lower aquifer, respectively.

The multi-aquifer well was the only boundary condition specified in the model. The well is located in the center of the model domain (Figure 14.1), fully penetrates both aquifers, and has a well radius of 0.15 \(m\). The Thiem conductance equation was used to calculate the well conductance in each aquifer. The initial head in the well was set equal to the initial head in the lower aquifer (9.14 \(m\)) and well storage was not simulated.

14.2. Example Results

The model was run for the case where the well was not pumping and a case where the well is pumping 1,767 \(m^{3}/d\). Transient results for non-pumping and pumping case are shown in Figure 14.2. For the non-pumping case, the flow from the lower aquifer is balanced by flow to the upper aquifer (Figure 14.2A). The water level in the multi-aquifer well under non-pumping can be calculated using the Sokol solution (Sokol, 1963). The Sokol solution is

(14.1)\[ h_w = \frac{\sum\limits_{m=1}^{N} T_m h_m}{\sum\limits_{m=1}^{N} T_m}\]

where \(h_w\) is the water-level in the well (L), \(T_m\) is the aquifer transmissivity (L\(^{2}\)/T), and \(h_m\) is the aquifer head at the outer-constant head boundary (L). For the non-pumping case, the water-level in the well calculated using equation 14.1 is 7.922 \(m\), which is identical the water-level in the multi-aquifer well.

../_images/ex-gwf-maw-p01-01.png

Figure 14.2 Simulated aquifer discharges to the multi-aquifer well. Discharge rates are relative to the multi-aquifer well; positive and negative discharge rates represent inflow to and outflow from the multi-aquifer, respectively. A. Non-pumping case. B. Pumping case.

For the pumping case, the flow from the upper aquifer is actually initially negative, indicating that at early time water flows up the wellbore and into the upper aquifer, rather than discharging from it (Figure 14.2B).

14.3. References Cited

Neville, C. J., & Tonkin, M. J. (2004). Modeling multiaquifer wells with MODFLOW. Ground Water, 42(6), 910–919. https://doi.org/10.1111/j.1745-6584.2004.t01-9-.x

Sokol, D. (1963). Position and fluctuations of water level in wells perforated in more than one aquifer. Journal of Geophysical Research, 68(4), 1079–1080. https://doi.org/10.1029/JZ068i004p01079

14.4. Jupyter Notebook

The Jupyter notebook used to create the MODFLOW 6 input files for this example and post-process the results is: