Groundwater Flow at Barton Springs
Surface Water Hydrology
Spring 2005
Prepared by Gil Strassberg, and David R. Maidment
Center for Research in Water Resources
Computer and
Data Requirements
Data location and description:
Barton Springs
segment of the Edwards aquifer:
Creating a GIS
representation of the model
Creating MODFLOW cells and nodes
Estimation of
Groundwater recharge:
Creating a
potentiometric surface
Computer and Data Requirements
Data location and description:
All the files needed for this exercise are contained in the zip file BartonSprings.zip. The file can be obtained from http://www.ce.utexas.edu/prof/maidment/gradhydro2005/groundwater/bartonsprings.zip
Once you unzip the file you should see the following folders and files:
If you have Windows XP you can use the installation wizard to install the tools. In the MODFLOWTools folder double click on the setup.exe file go through the installation wizard. The files will be installed under C:\Program Files\ModflowTools. It can occur that if you have an older version of Windows XP that the Setup file asks you to update your version of XP and then reboot the computer. If this happens, you need to register the tools manually.
Once you have completed the installation you can open ArcMap and select to add a new toolbox by right clicking in the toolbox window.
Browse to the Support folder in the MODFLOWTools folder and select the MODFLOWTools toolbox.
You are now ready to run the tools from ArcMap! Right click in the Arc Toolbox window and specify to save settings to default so that the toolbox always shows up when you open ArcMap.
Barton Springs segment of the Edwards aquifer:
The Barton Springs
segment of the Edwards Aquifer can be defined as the section of the aquifer
that discharges to Barton Springs and Cold Springs. The hydrogeologic
boundaries of this segment are a groundwater divide along Onion Creek in the
south, and the
Boundary of the MODFLOW model
The model grid consists of one layer constructed of 120 rows by 120 columns; each cell in the grid is 1000 ft long and 500 feet wide. Two models were developed; a steady state model for 1979 through 1998 based on average recharge during this time period and pumpage during 1989, and a transient model for a 10 year period (1979 through 1989) that includes periods of low and high water levels. Hydraulic conductivity was estimated by calibrating the model to the flow at Barton springs and to water elevations in monitoring wells. Throughout the exercise we will use a modified version of the steady state model to which transient stress periods were added.
Creating a GIS representation of the model
In this section of the exercise you will create a GIS representation of the MODFLOW model. We will focus on creating the model cells and nodes.
Creating MODFLOW cells and nodes
· Browse to the Boundary feature class as the input boundary layer, specify the grid origin as upper left, the number of rows and columns as 120, the width as 1000 and the length as 500. For the output feature class browse to the Cell2D feature class in the BartonSprings feature dataset.
Once the tool is done you should see a set of polygons which represent the MODFLOW mesh cells. You can zoom in and use the identify tool to view the properties of the cells.
You can see that the area of the cell is about 500,000 square ft and that each cell has attributes describing the row and column of the model (in the above example Row = 1 Column = 2). All the MODFLOW inputs and outputs are based on the Layer, Row, and Column numbering system.
Within a model not all the cells need to be activated and only a portion of the cells are actually participating in the model calculations. Next you will define the active cells of the model.
You can now view the active cells of the model by changing the symbology. (The active cells are in purple in the below figure). Active = 1 are the active cells. Set the Outline Color to No Color to avoid having the picture overwhelmed with black lines.
Model cells actually have three dimension properties. Each cell in a modflow grid has a top and bottom elevation associated with it. The elevations are stored in the discretization file (.dis). Next you will read the top and bottom elevations for each cell from the model files and store the values in a table.
You can open the elevation table and see that the top and bottom elevations for each cell were populated
Next you will create three dimensional cells from the 2D mesh and the elevations in the elevation table.
When the tool is done a set of 3DCells should be created. Each cell has a top and bottom elevation field and you can create a map showing the top or bottom elevations of the model. Below is a map showing the top elevations of the model.
Another way to view the cells is to use ArcScene to get a 3D view of the model mesh (To view the cells open ArcScene and load the 3DCells into the scene. You can change the vertical exaggeration under View > Scene Properties to get a better 3D view of the model).
You can also load the DEM (demfeet) into the scene to show the model cells in comparison with the land surface.
To
be turned in: What is the average
thickness of the aquifer cells (ft)? What
is the volume of solid materials encompassed by this aquifer (ft3)?
Next you will create the model nodes. MODFLOW is a finite difference model that uses a finite difference mesh to solve the groundwater flow equations. The model actually solves the head fields at the model nodes, which are located at the center of each cell.
You can also view the nodes within ArcScene to see the three dimensional structure of the mesh.
If you zoom in, and change the transparency of the Cell3D layer to 70%, you can see the nodes lie at the center of the cells.
If you zoom in you can see that there is a node at the center of each cell
Later we will read model results (heads) based on the node feature class. We will use the ArcHydro time series structure, thus we need to assign HydroIDs to the nodes.
· In Arc Map Use the Assign HydroIDs tool in the Arc Hydro toolbar to assign HydroID values to all the nodes.
To be turned in: (1) A map showing the
model boundary and model cells. Color the mesh by the active cell field to show
the active part of the model. (2) A map showing the top elevations of the
3DCells.
Estimation of Groundwater recharge:
The primary source of recharge (about 85%) to the aquifer is
from seepage from streams crossing the aquifer outcrop area. Flow losses from
five major creeks (Barton, Williamson, Slaughter, Bear, and Onion) provide most
of the recharge to this area. A linear relationship between streamflow at USGS
gaging stations and recharge is used to estimate the recharge in all the creeks
except for Barton Creek. Recharge increases linearly with flow in the upstream
gaging station until a threshold of maximum recharge is exceeded and then the
recharge is constant at that threshold. For Barton Creek, a cubic equation
(Barrett and Charbeneau, 1996) is used to relate the flow in Barton Creek with
recharge. In addition to recharge from the creeks diffuse interstream recharge
is estimated at about 15% of the total recharge.
Recharge zones in the model
The main discharge sources are Barton and Cold springs, where Barton springs is the major discharge source accounting for 75 to 95 percent of the discharge.
In the previous exercise you looked at stream discharge at two
USGS gaging stations in Barton Creek (Lost Creek and station at loop 360). The
hydrographs of measured upstream and downstream discharge indicated that the
stream between the gages is a loosing stream. Groundwater recharge to the
Edwards can be estimated based on measured streamflow at USGS gaging stations. The
following set of equations describes the groundwater recharge from Barton Creek
as a function of the flow at USGS gaging station 08155240 (Barton Creek at
In the BartonSprings.xls spreadsheet you are provided with monthly mean streamflow measurements at Lost Creek Boulevard gaging station and at the downstream gage, Barton Creek at loop 360 (Gage number 08155300), for 2002. In addition you are provided with the discharge measurements at Barton Springs (Gage 08155500).
By plotting the streamflow discharge over time at the two gages you will see that the downstream gage has less flow than the upstream gage. This means that the stream connecting the two gages is a loosing stream (assuming there are no diversions between the two gages).
To translate the calculated recharge values into model inputs it is necessary to transform the recharge estimations from flows to fluxes. MODFLOW inputs require recharge values in the form of areal fluxes on cells in the modflow grid. In the Barton Springs GAM model Barton Creek is represented by a set of 50 cells (the green cells shown in the figure below)
Creating a potentiometric surface
In this section you will read model results to create a potentiometric surface within the aquifer. First we need to relate the model time domain to a date/time format. The modflow time discretization is based on stress periods. Each stress period has a length that defines the time interval in model units (in this model the units are days).
· Select the Build Stress table tool in the Stress Packages toolset.
·
Select the StressPeriods table as the input
table, BARTONMF2K.dis as the
discretization file, specify the StressPeriod, StressDateTime, Multiplier,
Length, TimeSteps, and SSorTR fields. The starting date
of the model is
After the model executes the stress periods table should be populated as shown below.
You can see that the model has 14 stress periods. The first two are steady state time steps (0 in the SSorTR field). The first two stress periods are from 1979 to 2000 and from 2000 to 2001. Then there are 12 transient stress periods, one for each month of 2002.
Next you will read in the heads simulated by the model.
· Select the Read Heads into Time Series tool from the Budget and Results toolset
·
Select the Node
feature class and the TimeSeries
table as the input files, specify BARTONMF2K.hed
as the modflow head file, the starting date as 1/1/1979, TSTypeID as 1 , Time step as days, 1 layer, 120 rows and columns, and -9999
for HNOFLO (the value assigned to inactive cells). Select OK to run the
tool.
The tool reads the modeled heads from the modflow output head file and puts it into the ArcHydro time series format. Each node now has a set of time series in the TimeSeries table.
To create a potentiometric surface we need to extract information for one time step. As mentioned before two surfaces will be created one for January and one for July.
· In the general ArcToolbox, under Data Management tools select the Make Query Table tool
· Select the Nodes and the Time Series as the input tables, and select the select all fields option.
·
Create a query in the Expression field to select only values for specific date (in the
below example the date is
· Select the Add Virtual key field option. Select OK to run the tool.
A new layer which joins the nodes with the time series should be created and added to the map. You can view the water elevations by symbolizing the layer based on the TimeSeries. TSValue attribute.
Next you will interpolate a surface from the nodes. Use the Spatial Analyst toolbar to interpolate a raster from the nodes with the time series.
· Before running the interpolation, set the analysis mask in the spatial analyst toolbar. Go to Options > Analysis mask and select the Nodes feature class as the analysis mask.
· From the toolbar select the Interpolate to Raster tool, and select the (Inverse Distance Weighted) IDW method.
· Select the TimeSeries_TSValue attribute as the Z value field, 1200 as the output cell size, and leave all the parameters as the default parameters. Select OK to run the tool.
A raster representing the interpolated potentiometric surface should appear in the map.
Create contour lines showing the potentiometric surface within the aquifer to better visualize the surface.
Make the piezometric head field a permanent grid
by saving as a grid HeadFeb2002.
In Arc Scene, add the HeatFeb2002 Grid and set the base height for display as follows:
Add the Demfeet raster from the Rasters folder, set the layer height as above and visualize this in Arc Scene by varying the transparency of the layers
If you make the Cell3D transparent, you can see that the piezometric head surface lies within the elevation range of the cells. What does this tell you?
By moving the display you can see how much the piezometric head surface is below the land surface. By doing information queries at particular points you can see the discrepancy between these two elevations.
· Select the Contour tool in the Spatial Analyst toolbar
· Select 50 feet as the contour interval, and the base contour as 400.
The contour of the potentiometric surface should be added to the map.
Load the EdwardsAquifer feature class, and symbolize the features based on the AQUIFER attribute. A value of 1 is for unconfined areas and values of 2 are for the confined zones.
To be turned in (a) a map showing the
contour lines of the potentiometric surface on top of the aquifer zones.
Discuss the groundwater flow directions within the zones of the aquifer. (b) A
3D plot from ArcScene showing the DEM and piezometric head surfaces.
Zone Budget is an application that runs on top of modflow results files and creates water budgets for defined sub regions within the model. You will use a tool that runs zone budget to calculate a water budget for the Barton Creek watershed.
· Load the watershed feature class into the map, if it is not already there, and make the watersheds features hollow.
·
Select the Barton
Creek lower watershed (between
The cells within the selected watershed should be selected.
Once the tool is done you should be able to show the defined zone by changing the Cell2D symbology based on the RechargeZone field.
The zone budget program creates an output file (bartonbudget.zbl) in the BartonSpringsMF2K folder that contains the water budget for the defined zone. You can view this data by opening the text file in NotePad.
The above figure shows the zone budget for zone 1 (which you just defined) for stress period 1. The budget is in terms of total flow rate over the zone. In stress period 1 the recharge from the watershed to the aquifer is about 710,000 cubic feet /day, the flux from adjacent cells into the zone is about 5.6E+6 cubic feet /day. The selected zone also includes a cell representing Barton Springs, and the flux from the drain cell is about 4.47E+6 cubic feet /day. This means that the majority of the recharge fluxes from the watershed discharge at the springs.
Another option for viewing the data is to use a charting tool developed by USGS for plotting modflow inputs and results. The name of the tool is GW_Chart and it is in the GW_Chart folder.
The budget terms for the selected zone should appear on the plot. You can specify which terms you want to plot. Select to plot the in recharge as shown below.
If you wish to extract data from the chart you can go into the Configure > Format Chart and select the Export and then the Data button. You should then be able to select the information you wish to copy from the chart.
To be turned in a plot of
the recharge (In) and Drains (out) over time for the Barton Creek watershed
between Town Lake and the gaging station at loop 360. The average discharge
from Barton Springs is 53 cfs. How does the discharge from the drains compare
to the average discharge?
Summary of items to be turned in:
1. What is the average thickness of the aquifer
cells (ft)? What is the volume of solid
materials encompassed by this aquifer (ft3)?
2. (a) A map showing the model boundary and model
cells. Color the mesh by the active cell field to show the active part of the
model. (b) A map showing the top elevations of the 3DCells.
3. (a) A map showing the contour lines of the potentiometric surface on top of the aquifer zones. Discuss
the groundwater flow directions within the zones of the aquifer. (b) A
3D plot from ArcScene showing the DEM and piezometric head surfaces.
4. A plot of the recharge
(In) and Drains (out) over time for the Barton Creek watershed between