The age of groundwater is key in predicting which contaminants it might contain. There are many tracers and techniques that allow us to estimate the age—or mix of ages—of the groundwater we depend on as a drinking water supply.
Featured: Predicting Groundwater Age in the Glacial Aquifer System

A new 3-D model predicts the age groundwater at all depths across the 25-state span of the glacial aquifer system, reports a new USGS study. The glacial aquifer system provides more water for domestic and public supply than any other US aquifer.
Water that infiltrates the landscape moves downward to the water table as recharge to the aquifer system. As additional recharge continues to enter the aquifer, older recharge is pushed deeper by the newer recharge, resulting in a trend of increasing groundwater age with depth. Groundwater moves slowly—a flow rate of 1 foot per day is fast for groundwater, and flow rates can be as low as 1 foot per year or 1 foot per decade. It can take tens, hundreds, or even thousands of years for groundwater to travel through an aquifer.
Why does groundwater age matter? Young groundwater is more likely than old groundwater to have contaminants from recent manmade sources, such as pesticides, nitrate, and solvents, because those chemicals were applied to or released on the landscape when the young groundwater recharged the aquifer. For example, water that entered the aquifer after 1950 is more likely than older water to contain the herbicide atrazine, whose use has increased since that time. On the other hand, old groundwater is more likely than young groundwater to have contaminants from natural sources, such as metals and radionuclides, because old groundwater can spend thousands of years in contact with and reacting with aquifer rocks and minerals that might contain these elements. The geochemical processes that frequently occur in old water, such as redox reactions, can profoundly affect groundwater quality.
Groundwater usually is young—often only a few decades old—in shallow, unconfined aquifers with high rates of recharge. This recharge can be driven by precipitation, like in the eastern U.S., or by human applications of water for irrigation, like in parts of the western US. Groundwater can be thousands of years old in aquifers where recharge rates are low (arid regions), where the aquifer is very thick, or where aquifers are separated by confining units.
Try the Tools
Within the same aquifer, groundwater that is shallow and near the recharge area is younger than groundwater that is deep or that has moved far from the area where recharge occurs. Because wells are typically screened across long segments of aquifer, water from wells is often a mixture of many different ages. The tools below can aid in learning more about groundwater that is a mixture of ages.
- Groundwater Age Mixtures and Contaminant Trends Tool: Use the GAMCTT tool to explore how basic aquifer properties and well configurations affect groundwater age mixtures in groundwater discharge and on contaminant trends from nonpoint-source contaminant input scenarios.
- TracerLPM: Teasing out the distribution of groundwater ages in a single groundwater sample is a thorny task, but has been made easier by the development of the tool TracerLPM, an Excel workbook for interpreting groundwater age distributions from environmental tracer data.
Determining Groundwater Age
Groundwater age is determined from the measurement of age “tracers”, chemical or isotopic constituents dissolved in the groundwater. These tracers include naturally occurring isotopes, which decay at a known rate; isotopes that were introduced into the atmosphere at known times relating to nuclear tests; and manufactured gases whose concentration in the atmosphere over time is known.
Young groundwater is commonly defined as water that entered the aquifer since about 1950 because several chemical and isotopic substances related to human activities were released into the atmosphere since that time. The presence of these substances in groundwater tell us that the water is young. These substances include tritium (3H), which was released into the atmosphere by detonation of nuclear bombs in the 1950s and early 1960s, chlorofluorocarbons (CFCs), which were released into the atmosphere from refrigeration and other uses from the 1930s through the 1980s, and sulfur hexafluoride (SF6), which is used primarily in electrical equipment and manufacturing semiconductors and whose use has been increasing steadily since about 1965. These age-dating tracers can help water-resource managers to develop management strategies for shallow groundwater systems that contain mostly young groundwater.
Old groundwater is defined as water that entered the aquifer before 1950 and more commonly refers to water older than 1,000 years. Many common and rare isotopes are produced naturally in the Earth’s atmosphere from the bombardment of cosmic rays or solar radiation, and their presence in groundwater can help determine the groundwater age. These isotopes are adsorbed by rainfall and can enter the aquifer with recharge. Argon-39 can be used to identify water that recharged between 50 and 1,000 years ago. Carbon-14 or radiocarbon is the most common method used to determine groundwater ages between 1,000 and 30,000 years. Groundwater older than 30,000 years can be determined using isotopes like helium-4, which is produced from the decay of uranium and thorium in aquifer solids, or by chlorine-36 and krypton-81, which decay over extremely long timescales and thus are useful for determining the age of ancient groundwater—hundreds of thousands of years old or more.
Resources on age dating groundwater can be found at the USGS Reston Groundwater Dating Laboratory web page.
Go to the Publications tab to read about USGS research that uses groundwater age dating.
The links below lead to web pages that provide additional information on groundwater quality and topics related to groundwater age.
Groundwater Quality Research
Chloride, Salinity, and Dissolved Solids
Arsenic and Drinking Water
Metals and Other Trace Elements
Public Supply Wells
Domestic (Private) Supply Wells
Radionuclides
Groundwater Quality in Principal Aquifers of the Nation, 1991–2010
Predicting Groundwater Quality in Unmonitored Areas
Factors Affecting Vulnerability of Public-Supply Wells to Contamination
Volatile Organic Compounds (VOCs)
Oxidation/Reduction (Redox)
Follow the links below to publications that discuss research that uses groundwater age dating.
Tritium as an indicator of modern, mixed, and premodern groundwater age
Three-dimensional distribution of residence time metrics in the glaciated United States using metamodels trained on general numerical models
Lithium in groundwater used for drinking-water supply in the United States
Radium mobility and the age of groundwater in public-drinking-water supplies from the Cambrian-Ordovician aquifer system, north-central USA
Using groundwater age distributions to understand changes in methyl tert-butyl ether (MtBE) concentrations in ambient groundwater, northeastern United States
A partial exponential lumped parameter model to evaluate groundwater age distributions and nitrate trends in long-screened wells
Educational webtool illustrating groundwater age effects on contaminant trends in wells
Use of classes based on redox and groundwater age to characterize the susceptibility of principal aquifers to changes in nitrate concentrations, 1991 to 2010
TracerLPM (Version 1): An Excel® workbook for interpreting groundwater age distributions from environmental tracer data
Estimates of tracer-based piston-flow ages of groundwater from selected sites: National Water-Quality Assessment Program, 1992–2005
A comparison of recharge rates in aquifers of the United States based on groundwater-age data
Effects of intraborehole flow on groundwater age distribution
Pesticide and transformation product detections and age-dating relations from till and sand deposits
Below are software products associated with groundwater age.
- Overview
The age of groundwater is key in predicting which contaminants it might contain. There are many tracers and techniques that allow us to estimate the age—or mix of ages—of the groundwater we depend on as a drinking water supply.
Featured: Predicting Groundwater Age in the Glacial Aquifer SystemA new 3-D model predicts the age groundwater at all depths across the 25-state span of the glacial aquifer system, reports a new USGS study. The glacial aquifer system provides more water for domestic and public supply than any other US aquifer.
Water that infiltrates the landscape moves downward to the water table as recharge to the aquifer system. As additional recharge continues to enter the aquifer, older recharge is pushed deeper by the newer recharge, resulting in a trend of increasing groundwater age with depth. Groundwater moves slowly—a flow rate of 1 foot per day is fast for groundwater, and flow rates can be as low as 1 foot per year or 1 foot per decade. It can take tens, hundreds, or even thousands of years for groundwater to travel through an aquifer.
Why does groundwater age matter? Young groundwater is more likely than old groundwater to have contaminants from recent manmade sources, such as pesticides, nitrate, and solvents, because those chemicals were applied to or released on the landscape when the young groundwater recharged the aquifer. For example, water that entered the aquifer after 1950 is more likely than older water to contain the herbicide atrazine, whose use has increased since that time. On the other hand, old groundwater is more likely than young groundwater to have contaminants from natural sources, such as metals and radionuclides, because old groundwater can spend thousands of years in contact with and reacting with aquifer rocks and minerals that might contain these elements. The geochemical processes that frequently occur in old water, such as redox reactions, can profoundly affect groundwater quality.
Groundwater usually is young—often only a few decades old—in shallow, unconfined aquifers with high rates of recharge. This recharge can be driven by precipitation, like in the eastern U.S., or by human applications of water for irrigation, like in parts of the western US. Groundwater can be thousands of years old in aquifers where recharge rates are low (arid regions), where the aquifer is very thick, or where aquifers are separated by confining units.
Try the Tools
Within the same aquifer, groundwater that is shallow and near the recharge area is younger than groundwater that is deep or that has moved far from the area where recharge occurs. Because wells are typically screened across long segments of aquifer, water from wells is often a mixture of many different ages. The tools below can aid in learning more about groundwater that is a mixture of ages.
- Groundwater Age Mixtures and Contaminant Trends Tool: Use the GAMCTT tool to explore how basic aquifer properties and well configurations affect groundwater age mixtures in groundwater discharge and on contaminant trends from nonpoint-source contaminant input scenarios.
- TracerLPM: Teasing out the distribution of groundwater ages in a single groundwater sample is a thorny task, but has been made easier by the development of the tool TracerLPM, an Excel workbook for interpreting groundwater age distributions from environmental tracer data.
Determining Groundwater Age
Groundwater age is determined from the measurement of age “tracers”, chemical or isotopic constituents dissolved in the groundwater. These tracers include naturally occurring isotopes, which decay at a known rate; isotopes that were introduced into the atmosphere at known times relating to nuclear tests; and manufactured gases whose concentration in the atmosphere over time is known.
Young groundwater is commonly defined as water that entered the aquifer since about 1950 because several chemical and isotopic substances related to human activities were released into the atmosphere since that time. The presence of these substances in groundwater tell us that the water is young. These substances include tritium (3H), which was released into the atmosphere by detonation of nuclear bombs in the 1950s and early 1960s, chlorofluorocarbons (CFCs), which were released into the atmosphere from refrigeration and other uses from the 1930s through the 1980s, and sulfur hexafluoride (SF6), which is used primarily in electrical equipment and manufacturing semiconductors and whose use has been increasing steadily since about 1965. These age-dating tracers can help water-resource managers to develop management strategies for shallow groundwater systems that contain mostly young groundwater.
Old groundwater is defined as water that entered the aquifer before 1950 and more commonly refers to water older than 1,000 years. Many common and rare isotopes are produced naturally in the Earth’s atmosphere from the bombardment of cosmic rays or solar radiation, and their presence in groundwater can help determine the groundwater age. These isotopes are adsorbed by rainfall and can enter the aquifer with recharge. Argon-39 can be used to identify water that recharged between 50 and 1,000 years ago. Carbon-14 or radiocarbon is the most common method used to determine groundwater ages between 1,000 and 30,000 years. Groundwater older than 30,000 years can be determined using isotopes like helium-4, which is produced from the decay of uranium and thorium in aquifer solids, or by chlorine-36 and krypton-81, which decay over extremely long timescales and thus are useful for determining the age of ancient groundwater—hundreds of thousands of years old or more.
Resources on age dating groundwater can be found at the USGS Reston Groundwater Dating Laboratory web page.
Go to the Publications tab to read about USGS research that uses groundwater age dating.
- Groundwater Age Mixtures and Contaminant Trends Tool: Use the GAMCTT tool to explore how basic aquifer properties and well configurations affect groundwater age mixtures in groundwater discharge and on contaminant trends from nonpoint-source contaminant input scenarios.
- Science
The links below lead to web pages that provide additional information on groundwater quality and topics related to groundwater age.
Groundwater Quality Research
Every day, millions of gallons of groundwater are pumped to supply drinking water for about 140 million people, almost one-half of the Nation’s population. Learn about the quality and availability of groundwater for drinking, where and why groundwater quality is degraded, and where groundwater quality is changing.Chloride, Salinity, and Dissolved Solids
All natural waters contain some dissolved solids (salinity) from contact with soils, rocks, and other natural materials. Too much, though, and dissolved solids can impair water use. Unpleasant taste, high water-treatment costs, mineral accumulation in plumbing, staining, corrosion, and restricted use for irrigation are among the problems associated with elevated concentrations of dissolved solids.Arsenic and Drinking Water
Arsenic is a naturally occurring element, but long-term exposure can cause cancer in people. There has been a substantial amount of research done to address arsenic in groundwater and drinking-water supplies around the country. The USGS studies local and national sources of arsenic to help health officials better manage our water resources.Metals and Other Trace Elements
Metals, metalloids, and radionuclides all are trace elements that occur naturally in the Earth's crust. In small quantities many trace elements are essential for health in all living organisms, but some trace elements can be toxic or cause cancer, and some can bioaccumulate. The USGS investigates where and how trace elements make their way into our Nation's surface water and groundwater.Public Supply Wells
Are you among the more than 100 million people in the U.S. who relies on a public-supply well for your drinking water? Although the quality of finished drinking water from public water systems is regulated by the EPA, long-term protection and management of the raw groundwater tapped by public-supply wells requires an understanding of the occurrence of contaminants in this invisible, vital resource...Domestic (Private) Supply Wells
More than 43 million people—about 15 percent of the U.S. population—rely on domestic (private) wells as their source of drinking water. The quality and safety of water from domestic wells are not regulated by the Federal Safe Drinking Water Act or, in most cases, by state laws. Instead, individual homeowners are responsible for maintaining their domestic well systems and for monitoring water...Radionuclides
Many people might be surprised to learn that drinking-water sources, especially groundwater, can contain radioactive elements (radionuclides). Radionuclides in water can be a concern for human health because several are toxic or carcinogenic. Other radionuclides are useful tools for determining the age of groundwater in an aquifer or of sediment deposited at the bottom of a water body.Groundwater Quality in Principal Aquifers of the Nation, 1991–2010
What’s in your groundwater? Learn about groundwater quality in the Principal Aquifers of nine regions across the United States in informative circulars filled with figures, photos, and water-quality information.Predicting Groundwater Quality in Unmonitored Areas
Groundwater provides nearly one-half of the Nation’s drinking water, and sustains the steady flow of streams and rivers and the ecological systems that depend on that flow. Unless we drill a well, how can we know the quality of the groundwater below? Learn about how the USGS is using sophisticated techniques to predict groundwater quality and view national maps of groundwater quality.Factors Affecting Vulnerability of Public-Supply Wells to Contamination
More than 100 million people in the United States—about 35 percent of the population—receive their drinking water from public-supply wells. These systems can be vulnerable to contamination from naturally occurring constituents, such as radon, uranium and arsenic, and from commonly used manmade chemicals, such as fertilizers, pesticides, solvents, and gasoline hydrocarbons. Learn about the...Volatile Organic Compounds (VOCs)
Volatile organic compounds (VOCs) are chemicals that both vaporize into air and dissolve in water. VOCs are pervasive in daily life, because they’re used in industry, agriculture, transportation, and day-to-day activities around the home. Once released into groundwater, many VOCs are persistent and can migrate to drinking-water supply wells.Oxidation/Reduction (Redox)
The redox state of groundwater—whether the groundwater is oxic (oxidized) or anoxic (reduced)—has profound implications for groundwater quality. Knowing the redox conditions of groundwater can help determine whether it contains elevated levels of many contaminants, including arsenic, nitrate, and even some manmade contaminants. - Publications
Follow the links below to publications that discuss research that uses groundwater age dating.
Tritium as an indicator of modern, mixed, and premodern groundwater age
Categorical classification of groundwater age is often used for the assessment and understanding of groundwater resources. This report presents a tritium-based age classification system for the conterminous United States based on tritium (3H) thresholds that vary in space and time: modern (recharged in 1953 or later), if the measured value is larger than an upper threshold; premodern (recharged prAuthorsBruce D. Lindsey, Bryant C. Jurgens, Kenneth BelitzFilter Total Items: 13Three-dimensional distribution of residence time metrics in the glaciated United States using metamodels trained on general numerical models
Residence time distribution (RTD) is a critically important characteristic of groundwater flow systems; however, it cannot be measured directly. RTD can be inferred from tracer data with analytical models (few parameters) or with numerical models (many parameters). The second approach permits more variation in system properties but is used less frequently than the first because large‐scale numericAuthorsJ. Jeffrey Starn, Leon J. Kauffman, Carl S. Carlson, James E. Reddy, Michael N. FienenLithium in groundwater used for drinking-water supply in the United States
Lithium concentrations in untreated groundwater from 1464 public-supply wells and 1676 domestic-supply wells distributed across 33 principal aquifers in the United States were evaluated for spatial variations and possible explanatory factors. Concentrations nationwide ranged from <1 to 396 μg/L (median of 8.1) for public supply wells and <1 to 1700 μg/L (median of 6 μg/L) for domestic supply wellsAuthorsBruce D. Lindsey, Kenneth Belitz, Charles A. Cravotta, Patricia Toccalino, Neil M. DubrovskyRadium mobility and the age of groundwater in public-drinking-water supplies from the Cambrian-Ordovician aquifer system, north-central USA
High radium (Ra) concentrations in potable portions of the Cambrian-Ordovician (C-O) aquifer system were investigated using water-quality data and environmental tracers (3H, 3Hetrit, SF6, 14C and 4Herad) of groundwater age from 80 public-supply wells (PSWs). Groundwater ages were estimated by calibration of tracers to lumped parameter models and ranged from modern (<50 yr) in upgradient, regionallAuthorsPaul E. Stackelberg, Zoltan Szabo, Bryant C. JurgensUsing groundwater age distributions to understand changes in methyl tert-butyl ether (MtBE) concentrations in ambient groundwater, northeastern United States
Temporal changes in methyl tert-butyl ether (MtBE) concentrations in groundwater were evaluated in the northeastern United States, an area of the nation with widespread low-level detections of MtBE based on a national survey of wells selected to represent ambient conditions. MtBE use in the U.S. peaked in 1999 and was largely discontinued by 2007. Six well networks, each representing specific areaAuthorsBruce D. Lindsey, Joseph D. Ayotte, Bryant C. Jurgens, Leslie A. DeSimoneA partial exponential lumped parameter model to evaluate groundwater age distributions and nitrate trends in long-screened wells
A partial exponential lumped parameter model (PEM) was derived to determine age distributions and nitrate trends in long-screened production wells. The PEM can simulate age distributions for wells screened over any finite interval of an aquifer that has an exponential distribution of age with depth. The PEM has 3 parameters – the ratio of saturated thickness to the top and bottom of the screen andAuthorsBryant C. Jurgens, John Karl Böhlke, Leon J. Kauffman, Kenneth Belitz, Bradley K. EsserEducational webtool illustrating groundwater age effects on contaminant trends in wells
No abstract available.AuthorsJohn Karl Böhlke, Bryant C. Jurgens, David J. Uselmann, Sandra M. EbertsUse of classes based on redox and groundwater age to characterize the susceptibility of principal aquifers to changes in nitrate concentrations, 1991 to 2010
The National Water-Quality Assessment (NAWQA) Program of the U.S. Geological Survey is using multiple approaches to measure and explain trends in concentrations of nitrate in principal aquifers of the United States. Near decadal sampling of selected well networks is providing information on where long-term changes in nitrate concentrations have occurred. Because those studies do not include all thAuthorsP. B. McMahonTracerLPM (Version 1): An Excel® workbook for interpreting groundwater age distributions from environmental tracer data
TracerLPM is an interactive Excel® (2007 or later) workbook program for evaluating groundwater age distributions from environmental tracer data by using lumped parameter models (LPMs). Lumped parameter models are mathematical models of transport based on simplified aquifer geometry and flow configurations that account for effects of hydrodynamic dispersion or mixing within the aquifer, well bore,AuthorsBryant C. Jurgens, J.K. Böhlke, Sandra M. EbertsEstimates of tracer-based piston-flow ages of groundwater from selected sites: National Water-Quality Assessment Program, 1992–2005
This report documents selected age data interpreted from measured concentrations of environmental tracers in groundwater from 1,399 National Water-Quality Assessment (NAWQA) Program groundwater sites across the United States. The tracers of interest were chlorofluorocarbons (CFCs), sulfur hexafluoride (SF6), and tritium/helium-3 (3H/3He).Tracer data compiled for this analysis primarily were from wAuthorsStephen R. Hinkle, Stephanie D. Shapiro, Niel Plummer, Eurybiades Busenberg, Peggy K. Widman, Gerolamo C. Casile, Julian E. WaylandA comparison of recharge rates in aquifers of the United States based on groundwater-age data
An overview is presented of existing groundwater-age data and their implications for assessing rates and timescales of recharge in selected unconfined aquifer systems of the United States. Apparent age distributions in aquifers determined from chlorofluorocarbon, sulfur hexafluoride, tritium/helium-3, and radiocarbon measurements from 565 wells in 45 networks were used to calculate groundwater recAuthorsP. B. McMahon, Niel Plummer, J.K. Böhlke, S.D. Shapiro, S.R. HinkleEffects of intraborehole flow on groundwater age distribution
Environmental tracers are used to estimate groundwater ages and travel times, but the strongly heterogeneous nature of many subsurface environments can cause mixing between waters of highly disparate ages, adding additional complexity to the age-estimation process. Mixing may be exacerbated by the presence of wells because long open intervals or long screens with openings at multiple depths can trAuthorsB.A. Zinn, Leonard F. KonikowPesticide and transformation product detections and age-dating relations from till and sand deposits
Pesticide and transformation product concentrations and frequencies in ground water from areas of similar crop and pesticide applications may vary substantially with differing lithologies. Pesticide analysis data for atrazine, metolachlor, alachlor, acetochlor, and cyanazine and their pesticide transformation products were collected at 69 monitoring wells in Illinois and northern Indiana to documeAuthorsK.L. Warner, W.S. Morrow - Software
Below are software products associated with groundwater age.