No nationwide, systematic ground water level monitoring program exists. At present, there are approximately 42,000 long-term observation wells in the United States that have five or more years of water-level records. The density of existing monitoring wells, however, varies considerably from state to state. The extent of water level monitoring varies even more among major aquifers, with very limited monitoring in many aquifers. Thus, an inventory of existing water-level networks for major aquifer systems would be made early in the assessment to identify data gaps and opportunities for collaboration across the nation.

Ground Water Levels

To have national or even regional significance, indices of ground water levels have to be based on repeated observations at relatively large numbers of observation wells located in a wide range of representative hydrogeological environments. Ground water systems are dynamic and continually adjust to short-term and long-term changes in climate, ground water withdrawals and land uses. Water levels in wells change in response to a number of types of local and regional stresses, some of which are natural and some of which are human-induced. Because sub-surface hydraulic properties are highly variable, water level responses to stresses vary considerably with location and depth. Stresses take time to propagate through ground water systems, so water level changes are transient phenomena that are strongly affected by distances from the monitoring wells to imposed stresses.

The mechanisms that cause changes in ground water levels and storage can be split into two categories:

Natural mechanisms

• Recharge

• Evaporation from the water table

• Transpiration by vegetation

• Discharge to streams, springs and seeps

• Surface-water-level fluctuations in hydraulically connected streams, ponds or lakes

Human-induced mechanisms

• Ground water withdrawals

• Deep-well injection

• Agricultural irrigation

• Drainage of agricultural lands, swamps and wetlands

• Artificial recharge of water

• Wastewater recharge through lagoons, landfills and septic systems

• Dewatering of mines, tunnels or other structures

• Leakage from surface water reservoirs

• Urbanization impacts such as leaky water and sewer lines, lawn irrigation and impervious surfaces (paved roads, parking lots, etc.).

Ground water-level monitoring networks should include wells open to water table aquifers and deep artesian aquifers, wells tapping a variety of rock types, wells located both near and distant from pumping centers, wells located in typical land-use settings and wells that are widely distributed geographically. Because the magnitude of water level fluctuations in wells depends on many factors, water levels in some wells may fluctuate by tens of feet within a day, but in other wells, water levels may change by only tenths of a foot over a year. Therefore, some wells may need to be monitored continuously, whereas others only may need to be measured once per year. Among the several indices that would be derived for this assessment, some might be updated daily, others might be updated monthly and still others annually.

Ground Water Storage

Periodic national assessments of changes in aquifer storage due to ground water withdrawals, saltwater intrusion, mine dewatering, land drainage and other mechanisms that affect ground water availability should be undertaken. These assessments would be based on nationwide summaries of observed water level changes and ancillary data describing the aquifers and their changing storage conditions. These assessments would require a greater level of effort than that required for development of the ground water level indices because estimates of changes in ground water storage require knowledge of aquifer storage properties and spatial interpolation of ground water level measurements. The assessment also could provide measures of the nationwide status of ground water supply infrastructure, such as changes in the number and capacity of water supply wells and artificial recharge facilities; these measures would be analogous to those reported for surface water reservoirs.

Changes in ground water use and the effects of ground water development usually are not as variable year-to-year as are those for surface water. Therefore, the periodic assessments of ground water storage could be made at 5- to 10-year intervals. Ground water storage changes should be evaluated by major aquifer and then aggregated into regional and national assessments. A retrospective analysis of changes in ground water storage during the 20th century would be made at the beginning of the assessment. In some cases, historical changes in ground water storage may need to be estimated by use of ground water simulation models that account for all ground water storage processes, including storage changes in confining units. This modeling would build, in part, on work from the USGS Regional Aquifer System Analysis program, which studied and modeled the nation's regional aquifers from 1978 to 1995.

Changes in ground water storage through the past 100 years may be large enough to have global implications. If the volume of ground water stored on the continents has decreased significantly over the past century, then it might represent and account for a measurable fraction of the sea level rise observed during that time period. This would have implications for global climate modeling and predictions of future sea level rise. The impact of ground water declines could be offset by increases in water stored in reservoirs, so global impacts must be assessed in light of both components of water storage. An assessment of changes in ground water storage in the United States perhaps could be integrated into a global perspective in collaboration with other countries and international organizations.

Links

• water.usgs.gov/pubs/circ/circ1223/html