Water resources and hydrochemistry of the Alluvial and Sparta aquifers of the Grand Prairie region Chad D. Cooper, Ralph K. Davis, Kenneth F. Steele University of Arkansas, Department of Geosciences Arkansas Water Resources Center
The Problem Multiple ground-water uses Ground-water level declines Critical Ground-Water Area as of 1998 Salinization  may be  related to ground-water level decline Water-quality variations resulting from lower water levels can impact all uses
Objectives Delineate spatial distribution and magnitude of varying water quality conditions as related to areas of ground-water level decline Determine areas of ground-water salinization (high in chloride, SpC, TDS)  Examine varying water-quality conditions spatially over the study area Provide baseline water-quality data to water users of the region
Physiography of Study Area Approximately  8,900 square kilometers Little to no relief Dominated by agricultural production
1999 Land Use/Land Cover (summer)
Water level, Alluvial aquifer, spring 1998 Declines in Alluvial: 1915-1933 – up to  60  feet, Arkansas Co. 1938-1953 – from  10-20  feet 1955-1961 – from  3-10  feet 1969-1996 -  32  feet, Lonoke Co.
Wells completed in the Alluvial aquifer About 7,000 wells!
Water level, Sparta aquifer, spring 1998 Declines in Sparta: 1949 –  50  feet near Pine Bluff 1958-1965 –  160  feet at Pine Bluff 1969-1999 –  70  feet+ in Arkansas Co. 1988-1999 – almost  20  feet in Lonoke Co.
Wells completed in the Sparta aquifer About 325 wells  (and rising)!
Sample Sites July/Aug 2000 78 Alluvial 39 Sparta 8 QA/QC Analyses at WQL of AWRC
Ground-water quality, Alluvial aquifer Good to acceptable Calcium-magnesium-bicarbonate type No MCL’s exceeded SMCL’s exceeded: Mn (0.05 mg/L) Fe  (0.3 mg/L) Chloride: 3-172 mg/L
Ground-water quality, Sparta aquifer Better Range from Ca-Na-HCO 3  type to Na-HCO 3  type No MCL’s exceeded SMCL’s exceeded: Mn (0.05 mg/L) Fe  (0.3 mg/L) Chloride: 2-56 mg/L
Salinization related to declines? Cl, Alluvial Aquifer Cl, Sparta Aquifer
Salinization related to declines? TDS, Alluvial Aquifer TDS, Sparta Aquifer
Spatial trends, Sparta aquifer GW FLOW Lonoke Jefferson Arkansas Prairie
Spatial trends, Sparta aquifer Ionic Strength Calcium Saturation
Spatial trends, Sparta aquifer Transect Location Results GW FLOW
Spatial trends, Alluvial aquifer Conductivity vs. Well Depth
Spatial trends, Alluvial aquifer Ionic Strength Calcium Saturation 37 of 78 samples saturated
Spatial trends, Alluvial aquifer pH vs. Ca Saturation pH~6.85
Spatial trends, Alluvial aquifer pH vs. Iron pH~6.85
Results and Conclusions Salinization not widespread Water quality for both aquifers: Alluvial:  Acceptable, with high Cl and Fe  Sparta:  Better, lower Cl and Fe Varying hydrochemistry not result of  ground-water level declines Varying hydrochemistry is instead result of geochemical evolution along flowpath
Results and Conclusions Dominant processes: Alluvial: Ca saturation, precipitation of calcium- and iron-rich cements Sparta: Ca saturation, precipitation of calcium-rich cement; cation exchange Future work: Combine and compare with other datasets from the region Statistical analysis of spatial data Examine relationships with rivers Iron in the Alluvial aquifer?
Acknowledgements Arkansas Water Resources Center (AWRC) Water Quality Lab, AWRC Arkansas Soil and Water Conservation Commission United States Geological Survey, Little Rock Arkansas Department of Environmental Quality Center for Advanced Spatial Technologies, University of Arkansas
Questions?

Water resources and hydrochemistry of the Alluvial and Sparta aquifers of the Grand Prairie region

  • 1.
    Water resources andhydrochemistry of the Alluvial and Sparta aquifers of the Grand Prairie region Chad D. Cooper, Ralph K. Davis, Kenneth F. Steele University of Arkansas, Department of Geosciences Arkansas Water Resources Center
  • 2.
    The Problem Multipleground-water uses Ground-water level declines Critical Ground-Water Area as of 1998 Salinization may be related to ground-water level decline Water-quality variations resulting from lower water levels can impact all uses
  • 3.
    Objectives Delineate spatialdistribution and magnitude of varying water quality conditions as related to areas of ground-water level decline Determine areas of ground-water salinization (high in chloride, SpC, TDS) Examine varying water-quality conditions spatially over the study area Provide baseline water-quality data to water users of the region
  • 4.
    Physiography of StudyArea Approximately 8,900 square kilometers Little to no relief Dominated by agricultural production
  • 5.
    1999 Land Use/LandCover (summer)
  • 6.
    Water level, Alluvialaquifer, spring 1998 Declines in Alluvial: 1915-1933 – up to 60 feet, Arkansas Co. 1938-1953 – from 10-20 feet 1955-1961 – from 3-10 feet 1969-1996 - 32 feet, Lonoke Co.
  • 7.
    Wells completed inthe Alluvial aquifer About 7,000 wells!
  • 8.
    Water level, Spartaaquifer, spring 1998 Declines in Sparta: 1949 – 50 feet near Pine Bluff 1958-1965 – 160 feet at Pine Bluff 1969-1999 – 70 feet+ in Arkansas Co. 1988-1999 – almost 20 feet in Lonoke Co.
  • 9.
    Wells completed inthe Sparta aquifer About 325 wells (and rising)!
  • 10.
    Sample Sites July/Aug2000 78 Alluvial 39 Sparta 8 QA/QC Analyses at WQL of AWRC
  • 11.
    Ground-water quality, Alluvialaquifer Good to acceptable Calcium-magnesium-bicarbonate type No MCL’s exceeded SMCL’s exceeded: Mn (0.05 mg/L) Fe (0.3 mg/L) Chloride: 3-172 mg/L
  • 12.
    Ground-water quality, Spartaaquifer Better Range from Ca-Na-HCO 3 type to Na-HCO 3 type No MCL’s exceeded SMCL’s exceeded: Mn (0.05 mg/L) Fe (0.3 mg/L) Chloride: 2-56 mg/L
  • 13.
    Salinization related todeclines? Cl, Alluvial Aquifer Cl, Sparta Aquifer
  • 14.
    Salinization related todeclines? TDS, Alluvial Aquifer TDS, Sparta Aquifer
  • 15.
    Spatial trends, Spartaaquifer GW FLOW Lonoke Jefferson Arkansas Prairie
  • 16.
    Spatial trends, Spartaaquifer Ionic Strength Calcium Saturation
  • 17.
    Spatial trends, Spartaaquifer Transect Location Results GW FLOW
  • 18.
    Spatial trends, Alluvialaquifer Conductivity vs. Well Depth
  • 19.
    Spatial trends, Alluvialaquifer Ionic Strength Calcium Saturation 37 of 78 samples saturated
  • 20.
    Spatial trends, Alluvialaquifer pH vs. Ca Saturation pH~6.85
  • 21.
    Spatial trends, Alluvialaquifer pH vs. Iron pH~6.85
  • 22.
    Results and ConclusionsSalinization not widespread Water quality for both aquifers: Alluvial: Acceptable, with high Cl and Fe Sparta: Better, lower Cl and Fe Varying hydrochemistry not result of ground-water level declines Varying hydrochemistry is instead result of geochemical evolution along flowpath
  • 23.
    Results and ConclusionsDominant processes: Alluvial: Ca saturation, precipitation of calcium- and iron-rich cements Sparta: Ca saturation, precipitation of calcium-rich cement; cation exchange Future work: Combine and compare with other datasets from the region Statistical analysis of spatial data Examine relationships with rivers Iron in the Alluvial aquifer?
  • 24.
    Acknowledgements Arkansas WaterResources Center (AWRC) Water Quality Lab, AWRC Arkansas Soil and Water Conservation Commission United States Geological Survey, Little Rock Arkansas Department of Environmental Quality Center for Advanced Spatial Technologies, University of Arkansas
  • 25.

Editor's Notes

  • #2 Going to attempt to sum up 2.5 years of research This picture is typically of what you can see in the Grand Prairie region….this is a Sparta-aquifer irrigation well, with a jug of drip oil sitting there and the vent, which is where I was able to acquire the sample in most of my wells