Georgia Water Science Center
This report is available online in pdf format (15 MB): USGS SIR 2006-5058 ()
Alden M. Provost, Dorothy F. Payne, and Clifford I. Voss
U.S. Geological Survey Scientific Investigations Report 2006-5058, 124 pages (Published 2006)
A digital model was developed to simulate ground-water flow and solute transport for the Upper Floridan aquifer in the Savannah, Georgia–Hilton Head Island, South Carolina, area. The model was used to (1) simulate trends of saltwater intrusion from predevelopment to the present day (1885–2004), (2) project these trends from the present day into the future, and (3) evaluate the relative influence of different assumptions regarding initial and boundary conditions and physical properties. The model is based on a regional, single-density ground-water flow model of coastal Georgia and adjacent parts of South Carolina and Florida.
Variable-density ground-water flow and solute transport were simulated using the U.S. Geological Survey finite-element, variable-density solute-transport simulator SUTRA, 1885–2004. The model comprises seven layers: the surficial aquifer system, the Brunswick aquifer system, the Upper Floridan aquifer, the Lower Floridan aquifer, and the intervening confining units.
The model was calibrated to September 1998 water levels, for single-density freshwater conditions, then refined using variable density and chloride concentration to give a reasonable match to the trend in the chloride distribution in the Upper Floridan aquifer inferred from field measurements of specific conductance made during 2000, 2002, 2003, and 2004. The model was modified to simulate solute transport by allowing saltwater to enter the system through localized areas near the northern end of Hilton Head Island, at Pinckney Island, and near the Colleton River, and was calibrated to match chloride concentrations inferred from field measurements of specific conductance. This simulation is called the "Base Case." Water-level residuals ranged from –5.3 to 23.4 feet for September 1998 conditions and single-density freshwater conditions. When chloride transport was simulated, water-level residuals ranged from –12.5 to 23.3 feet. The simulated chloride distribution captures the general trends in the field data. Chloride transport is sensitive to the permeabilities assigned to the confining units in the source areas and the porosity assigned to the Upper Floridan aquifer.
Results of the study indicate thatModel limitations include uncertainty in (1) field data, (2) the conceptual model, (3) the physical properties and representation of the hydrogeologic framework, and (4) uncertainty in the boundary and initial conditions. Results of simulations projected far into the future must be interpreted with caution because they are based on an assumed future pumping distribution and fixed boundary conditions, and because these conditions may differ substantially from those for which the model is calibrated.
Abstract
Introduction
Purpose and scope
Approach
Description of Study Area
Previous Investigations
Acknowledgments
Hydrogeology
Geologic Setting
Hydrogeologic Units
Surficial and Brunswick Aquifer Systems
Floridan Aquifer System
Ground-Water Flow System
Predevelopment
Present Day: 1980 – 2000
Recharge and Discharge
Ground-Water Pumpage
Ground-Water Level Trends
Salinity Distribution
Possible Mechanisms of Saltwater Intrusion
Simulation of Variable-Density Ground-Water Flow and Solute Transport
Model Construction
Model Layering
Spatial Discretization
Hydraulic and Transport Properties
Boundary Conditions
Top and Bottom Boundaries
Lateral Boundaries
Pumpage
Model Calibration to Observed Head ("Head Calibration") and Flow-Model Sensitivity
Head Calibration Method
Head Observations
Head Calibration Results
Simulated Heads and Residuals
Calibrated Permeability Values, Confidence Intervals, and Correlations
Composite Scaled Sensitivities
Predevelopment Steady State
Evaluation of Steady-State Assumption
Flow Budget
Model Calibration to Observed Chloride ("Chloride Calibration") and Solute-Transport Model Sensitivity
Chloride Calibration Method
Base Case
Solute-Transport Model Sensitivity
Permeability of the Upper Confining Units in the Source Areas
Permeability of the Upper Florida Aquifer
Porosity
Dispersion
Surface-Water Chloride Concentration
Spatial Discretization
Temporal Discretization and Nonlinearity Iterations
Matrix Solver Convergence Tolerances
Summary of Solute-Transport ModelSensitivity
Variations on the Base Case
Variation 1: No Salt during 1965
Variation 2: Predevelopment Plumes
Variation 3: Model Truncated Below Upper Floridan Aquifer
Simulation of Future Saltwater Intrusion
Base Case
Variation 1: No Salt during 1965
Variation 2: Predevelopment Plumes
Variation 3: Model Truncated Below Upper Floridan Aquifer
Effect of Uncertainty in Porosity
Model Limitations
Field Data
Conceptual Model
Geometry and Physical Properties
Boundary and Initial Conditions
Numerical Approximation and Solution
Future Predictions of Chloride Distribution
Discussion
Summary and Conclusions
Selected References
Appendix A. Modifications to SUTRA Code
Irregular Three-Dimensional Meshes
Generalized Observation Points
Time-Dependent Pumping
Time-Step Cycling
Other Changes
Appendix B. Observed Specific Conductance Measurements and Estimated Chloride Concentration
Appendix C. Altitude of Top and Bottom Surface of Hydrogeologic Units
Appendix D. Solid Matrix Compressibility
Appendix E. Effect of Porosity on Rate of Transport
Appendix F. Distribution of Specified Pressure Applied at Model Boundaries
Appendix G. Observed and Simulated Water Levels
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