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About Groundwater Monitoring

Seventy-five percent of all Iowans rely on groundwater as their drinking water source.  Groundwater is one of the better understood water resources in Iowa, yet much remains unknown.  The objective of the groundwater monitoring network is to describe and measure groundwater quality throughout Iowa, characterize aquifers in different hydrogeological environments, and measure water quality changes and identify trends in Iowa's aquifers.  The information gathered through this program can be used to assess the groundwater resource, project future conditions of supply, address contamination concerns, and provide the information necessary to effectively manage the resource.  

Information about Iowa's groundwater is being gathered through a groundwater level network, a ground water quality network, development of a monitoring well network, and private well-water monitoring.  

 

 

Groundwater Level Network

Since 1982, the Iowa Department of Natural Resources and the U.S. Geological Survey have cooperatively conducted the Iowa Groundwater Level Network.  The objectives of the groundwater level network are:  to collect data documenting any change in groundwater storage over time in the principal aquifers; to provide both long-term and short-term data necessary to assess and predict the response of hydrologic systems to natural climatic variations and human-induced stresses; to quantify the hydrologic characteristics of aquifers including transmissivity, hydraulic conductivity, and specific capacity; and to provide historical baseline data for studies of Iowa's aquifers.

The current groundwater level network in Iowa consists of 175 wells completed in the principal bedrock and surficial aquifers that supply groundwater to numerous users throughout the state.  The advantage of the groundwater level network is that static water levels for principal aquifers can be monitored through time, generally under non-pumping conditions. Water levels are measured on a quarterly to monthly basis and entered into the USGS Groundwater Site Inventory database.  The majority of wells are monitoring wells, while some are municipal wells.  Each year, a selected aquifer and its respective wells are reevaluated to determine which wells to continue to monitor and whether additional wells in that aquifer should be included in the groundwater level network.  The Devonian Aquifer water-level network was evaluated during the 1999-2000 water year, and the Mississippian Aquifer will be evaluated in 2000-2001.  Other aquifers that have been evaluated in recent years include the Cambrian-Ordovician (statewide), the Silurian (northeast Iowa), and the Dakota (northwest Iowa).  

Network data collected from all aquifers are compiled and published in the annual U.S. Geological Survey Water-Resources Data, Iowa report.  The U.S. Geological Survey Open-File Report 92-27 titled "The Ground-Water-Level Monitoring Network in Iowa" was published in 1992 and describes in detail the groundwater level network in Iowa.  To request a copy of the publication, contact the U.S. Geological Survey at (319)337-4191.

 

Groundwater Quality Network

Since 1982, the Iowa Department of Natural Resources, U.S. Geological Survey, and University of Iowa Hygienic Laboratory have conducted the Iowa groundwater quality monitoring program.  The purpose of the program is to provide consistent and representative data describing the chemical water quality of the principal aquifers in Iowa and to determine possible spatial or temporal trends in water quality.

The groundwater monitoring program was initiated to continue a program begun in 1950 by the State Health Department that consisted of periodic, nonspecific sampling of untreated water from municipal water supply wells.  Each year, approximately 250 wells, primarily municipal supply wells, were randomly selected for sampling between April and November.  Between 1985 and 1989, the program focused on the concentration of nitrate and herbicides in wells less than 200 feet deep.  Because of the random pattern of sampling, both spatially (different wells each year) and seasonally (different times during the year), trends in groundwater quality were difficult to determine from the data.  In 1990, the focus of the program was changed to provide year-to-year continuity of data and a more statistically sound basis for the study of long-term, water-quality trends.  The sampling strategy was changed to a random selection of wells weighted by aquifer vulnerability.  Aquifer vulnerability was determined by the frequency of atrazine detections in water samples collected from wells in the respective aquifers.  In 1990 and 1991, a fixed network of 50 wells was selected to be sampled annually, and approximately 200 wells continued to be selected on a rotational basis.

In 1992, investigation of water-quality trends became the primary focus of the program, and a 10-year work plan was designed to eliminate spatial and seasonal variance, yet allow flexibility within the schedule to address additional data needs.  In 1992, the well inventory was divided into categories based on aquifer type and again on well depth for surficial aquifers, and into categories designated "vulnerable to contamination" and "not vulnerable to contamination" based on the map Groundwater Vulnerability Regions of Iowa (Hoyer, B.E., and Hallberg, G.R., 1991, Special Map Series 11:  Iowa Department of Natural Resources, scale 1:500,000) for bedrock aquifers.  Geologic and soil data, thickness of Quaternary cover (unconsolidated sediments), proximity to agricultural drainage wells and sinkholes through which contaminants can be introduced to the aquifer, and evaluation of historical groundwater quality and well contamination were all used to determine the vulnerability of each well.  A total of 90 wells were selected for sampling from a well inventory comprised of approximately 1,640 public water supply wells.  From the 90 sites in the fixed network, 45 wells from two surficial aquifer types were selected to be sampled annually.  These surficial aquifer types were alluvial and Pleistocene.  The other 45 wells (from the bedrock aquifer types) were selected to be sampled on a rotational schedule based on aquifer vulnerability to contamination.   The wells determined to be vulnerable to contamination would be sampled every 2 years, and those wells categorized as not vulnerable to contamination would be sampled every 4 years.  All 90 wells were sampled in the first 2 years (1992 and 1993) and the sampling rotation began in 1994.  

Currently, in addition to the sampling of the core 90 municipal wells, 60 other municipal wells from particular aquifers are rotated into the sampling routine each year. The rotating wells will allow an in-depth investigation into the water quality of each primary aquifer in the state. In 2002, the 60 rotating wells were from the Mississippian and Cretaceous aquifers (32 Mississippian wells and 28 Cretaceous wells). The rotating wells for 2003 are from the Silurian/Devonian Aquifer. All of the aquifers in the state will be covered over a period of five years

 

Ambient (Dedicated) Groundwater Monitoring Network

A monitoring well network will be developed throughout the state to evaluate the ambient or background quality of aquifers in Iowa.  The target is to develop 60 well-nest sites, or about 180 monitoring wells.  (A well nest is two or more wells located in close proximity to each other where each well is completed to a different depth.)  These will be developed at different depths to tap specific aquifers used in the region.  In most instances, this will include one or more bedrock sources, but will also include glacial drift, alluvial, or buried alluvial sources.  Annually, two to five well-nest sites will be developed through contracts with drilling companies.  Water will be age dated from each well to indicate vulnerability.  Annually, each well will have the mineral content analyzed and common parameters assessed.  For the first year after the wells are constructed, water levels will be measured continuously to characterize each aquifer and the hydraulic connection of that particular aquifer to aquifers located above and below it.  After year one, water levels will be measured less frequently.

Development of monitoring wells will provide important information for the overall management of groundwater in Iowa.  Pump tests and geophysical tests will assess aquifer characteristics.  A continuous rock core will be obtained from each site as part of a lithologic and stratigraphic reference collection.  This information will enhance our understanding about the distribution and variability of rock units throughout the state, and their potential as future or expanded sources of groundwater for Iowans.  

The advantage of a monitoring well network is that the well construction is well known, the rock core provides detailed information about the sequence of bedrock in the subsurface, allows determination of aquifer properties and water quality from a specific aquifer under non-pumping conditions.

 

Rural Well Water Survey

The State-Wide Rural Well-Water Survey (SWRL) was a one-time, statistically based sampling of 686 private wells across Iowa to evaluate the quality of private drinking-water supplies used by rural Iowans.  The survey, completed in 1988 and 1989, addressed two questions:  (1) What proportion of private wells in rural Iowa are affected by various environmental contaminants?  (2) What proportion of rural Iowa residents are utilizing well water containing these environmental contaminants?  The survey was conducted as part of the implementation of the Iowa Groundwater Protection Act of 1987.  Water sampling was conducted by the Iowa Department of Natural Resources and the University of Iowa Center for Health Effects of Environmental Contamination.  Results provide a 'snapshot' of the condition of the private well-water supplies in Iowa and some insight into the condition of Iowa's groundwater resource.  It also serves as a baseline for measuring future trends and changes in groundwater and rural private drinking-water quality.  The well-water was analyzed for an extensive list of parameters, including pesticides, bacteria, inorganic chemicals, and radionuclides.  An inventory questionnaire was completed for each household and a health assessment questionnaire was completed for each individual in the household.