NOAA Great Lakes Environmental Research Laboratory Blog

The latest news and information about NOAA research in and around the Great Lakes

September 3, 2026
by GLERL Communications Team
Comments Off on Understanding Great Lakes Harmful Algal Blooms: From Monitoring to Forecasting Health Risks

Understanding Great Lakes Harmful Algal Blooms: From Monitoring to Forecasting Health Risks

2022 Lake Erie harmful algal bloom (HAB) observed during weekly sampling efforts used to monitor bloom conditions, water quality, and toxin levels throughout the season. (Photo Credit: Holly Kelchner).

In the Great Lakes, harmful algal blooms (HABs) are dominated by cyanobacteria, commonly called blue-green algae, that grow rapidly when conditions warrant (warm water temperatures and excess nutrients). Cyanobacteria are ancient organisms that have been producing oxygen through photosynthesis for billions of years, helping shape Earth’s atmosphere. Today, these blooms can form dense surface scums and sometimes produce toxins that pose risks to people, pets, wildlife, and drinking water supplies.

HABs primarily occur in several areas across the Great Lakes, including western Lake Erie, Saginaw Bay in Lake Huron, and Green Bay in Lake Michigan. They reduce water clarity, disrupt recreational activities, and affect local ecosystems. While HABs are a concern throughout the region, western Lake Erie experiences some of the largest and most intense cyanobacterial blooms, making it a focal point for extensive monitoring for research and forecasting. These blooms are often dominated by the Microcystis algae, a type of cyanobacteria capable of producing toxins known as microcystins.

Each year, researchers at NOAA’s Great Lakes Environmental Research Laboratory (GLERL) and the University of Michigan’s Cooperative Institute for Great Lakes Research (CIGLR) monitor and track Great Lakes HABs using field observations and advanced technologies. Together, these efforts help scientists better understand bloom development, toxin levels, and potential impacts on communities, improving our ability to warn people about bloom conditions.

What the 2026 Lake Erie Seasonal HAB Forecast Tells Us

According to NOAA’s National Centers for Coastal Ocean Science (NCCOS) early season HAB outlook released on June 25, western Lake Erie was forecast to experience a moderate cyanobacterial harmful algal bloom (HAB) during the 2026 season (roughly July to October).

A satellite view of the August 9, 2026, Lake Erie harmful algal bloom (HAB) shows the bloom’s extent, captured by the European Space Agency’s Sentinel-3 Ocean and Land Colour Instrument (OLCI).

In western Lake Erie, bloom severity is largely driven by the amount of phosphorus entering the lake from the Maumee River watershed during the spring and early summer. NOAA measures bloom severity using an index that reflects the amount of cyanobacterial biomass, or blue-green algae, present during the bloom’s peak 30-day period, which generally occurs in August but can vary from year to year. A severity index between 3 and 4.5 indicates a moderate bloom, while values above 5 indicate a severe bloom. This season’s bloom was forecast to fall between 3 and 4.5, comparable to the blooms observed in 2020 and 2023 but in contrast to 2011 when extreme bloom severity reached a record-setting index of 10. Although an early April rainfall event caused phosphorus loading in western Lake Erie, bloom severity ultimately depends on weather conditions and rainfall through July.

Bloom size tells only part of the story. Because toxin levels can vary independently of bloom conditions, researchers are developing forecasts for both bloom severity and toxicity.

Tracking Harmful Algal Blooms Across the Great Lakes

Predicting the season’s bloom severity is only part of the challenge in managing impacts from HABs. Throughout the season, scientists from GLERL and CIGLR monitor bloom development, movement, and toxicity across the Great Lakes to better understand bloom dynamics, detect emerging HAB activity, and provide timely information to resource managers, water treatment operators, and the public.

From late April through October, researchers conduct regular monitoring cruises in western Lake Erie and Saginaw Bay, collecting water samples that are analyzed for indicators such as chlorophyll, phosphorus, and microcystin concentrations. Researchers also rely on a network of observations including buoys, satellite and aircraft-based remote sensing datasets, autonomous vehicles, and Environmental Sample Processors (ESPs) to track bloom conditions across the basin, including areas such as Green Bay.

Together, these observations provide near real-time information on bloom location, intensity, and toxicity. The data help scientists evaluate forecast performance, improve predictive models, and identify changes in bloom behavior as environmental conditions shift. By combining field observations with advanced monitoring technologies, researchers can provide more accurate and actionable information to support decision-making throughout the Great Lakes region. These observations are being used to develop new forecasting tools designed to predict toxin concentrations.

Recent research also demonstrated the importance of monitoring HAB conditions across areas of the lake. A study led by CIGLR and NOAA GLERL researchers examined how water from the Detroit and Maumee rivers interacts in western Lake Erie, creating distinct environmental conditions that influence bloom development. “We expected to find a gradient between the Detroit and Maumee river inflows, but I was surprised by how much the transition zones shifted from month to month and how distinct they were,” said CIGLR’s Jasmine Mancuso, lead author of the study. CIGLR researchers explain the study and its findings in a recent blog post, highlighting how observations across this gradient provide a more complete picture of the factors that shape HABs and can improve future bloom forecasts.

Heading out into the western basin of Lake Erie for weekly harmful algal bloom (HAB) sampling in June 2023. CIGLR scientists Paris Schofield (left) and Andrew Camilleri (right), along with NOAA GLERL Western Lake Erie Operations Research Vessel Captain Kent Baker (middle), are pictured aboard the vessel. (Photo Credit: Aubrey Lashaway).
CIGLR scientist Andrew Camilleri collects water samples using a Niskin rosette during a 2024 weekly Lake Erie harmful algal bloom (HAB) monitoring cruise, with the Toledo Harbor Lighthouse in the background. (Photo Credit: Paige Williams).
CIGLR scientists Paris Schofield (front) and Jasmine Mancuso (back) process Lake Erie water samples during weekly harmful algal bloom (HAB) sampling efforts in the 2025 field season.
A rosette water sampler sits just below the surface of Lake Erie’s western basin, preparing to collect water from multiple depths during the 2026 sampling season. (Photo credit: Paris Schofield).

Forecasting Bloom Toxin Levels

As monitoring improves, researchers are working to better predict not only where blooms will occur, but also how toxin levels change. Because bloom size and toxin levels are not always closely linked, forecasting toxins has become an important area of harmful algal bloom research.

NOAA researchers have developed an experimental five-day toxin forecast system that predicts the probability of exceeding the recreational public health advisory level for microcystins in western Lake Erie. The system combines weekly measurements of microcystins with data on bloom conditions, weather, and lake circulation to estimate where and when elevated microcystin levels may occur. NOAA GLERL is currently working with partners at NCCOS to move the system into operational use, timely information about toxin risks in Lake Erie.

Testing with ten years of historical Lake Erie data shows that it performs well in identifying areas of increased toxin risk, including near drinking water intakes, within bloom-affected regions, and across the western basin. This long-term record was essential for testing the forecast across a range of toxin levels. “It is a relatively rare event for microcystin levels to exceed the public health advisory level,” said Mark Rowe, Ph.D., a research physical scientist at NOAA GLERL. “Only 3% of observations in the ten-year database exceeded that level. It was necessary to have a large database of observations, including the rare exceedances, to calibrate the statistical models that underpin the forecast, showing the value of long-term monitoring programs.”

By focusing on the likelihood of elevated toxins rather than bloom presence alone, these forecasts can help water treatment managers, public health officials, and coastal communities make informed decisions during the bloom season. A public version of the forecast is planned, providing earlier and more accurate information about potential toxin exposure.

Understanding the Health Risks of Harmful Algal Blooms

Some cyanobacteria that form harmful algal blooms produce toxins that can affect humans and animals. In Lake Erie, Microcystis blooms can produce microcystin, a toxin that affects the liver and contaminates drinking water sources when blooms occur near water intakes.

CIGLR scientists Erica Pillar (front left), Tait Algayer (front right), and Paris Schofield (back) prepare to collect water samples from Lake Erie as part of weekly harmful algal bloom (HAB) monitoring during the 2026 field season. (Photo credit: Paris Schofield).
CIGLR scientists Erica Pillar (left) and Paris Schofield (right) collect water samples during the 2026 harmful algal bloom (HAB) monitoring season in Saginaw Bay, Lake Huron. (Photo credit: Paris Schofield).

People can be exposed to HAB toxins through skin contact, accidental ingestion of contaminated water, or inhalation of water droplets and aerosols. Exposure can cause symptoms such as skin irritation, coughing, nausea, vomiting, and diarrhea, with more severe health effects possible in some cases.

Pets – particularly dogs – face an elevated risk when they swim in affected water and groom themselves after. Staying aware of local conditions and advisories can reduce exposure risks for both people and pets.

New research also shows that Lake Erie cyanobacteria blooms produce a mix of naturally occurring compounds that change over the course of the season. Instead of being dominated by a single toxin, blooms may shift through phases where different cyanobacteria compounds become more common. This variability adds another layer of complexity to understanding bloom impacts and highlights the importance of looking at all toxins when assessing potential risks. “These cyanobacteria are extraordinary chemical factories; they produce an astonishing diversity of chemical compounds, and we’re only just beginning to identify and understand them all. But there is some evidence that suggests that this mixture of compounds may affect human health in novel ways,” said Greg Dick, Ph.D., Director of CIGLR and senior author on the study. “CIGLR and GLERL scientists are partnering with colleagues around the region, including the Great Lakes Center for Freshwaters and Human Health, to better understand the impacts of blooms on human health and the risks they pose to people that live, work, and play in and near the lakes.”

Looking Ahead

Although 2026 is projected to be a moderate bloom year, conditions can change throughout the summer. GLERL and CIGLR scientists continue monitoring Lake Erie and other Great Lakes HAB blooms throughout the season, providing data for forecasts and water resource management. While western Lake Erie remains the primary focus of seasonal forecasting because of its large, recurring blooms, monitoring HABs in Saginaw Bay and Green Bay helps reduce HAB risks across the Great Lakes basin.

Together, these efforts support research, forecasting, and public health initiatives that help communities safely enjoy Great Lakes waters.

August 2017 Lake Erie harmful algal bloom (HAB). This aerial image shows the extent of a bloom in the western basin of Lake Erie. Pilots from Aerodata conducted flyovers to map HAB conditions, while hyperspectral imaging collected additional data to improve scientists’ ability to detect and monitor blooms. (Photo Credit: Aerial Associates Photography, Inc. by Zachary Haslick).

Additional Resources

July 21, 2026
by GLERL Communications Team
Comments Off on Sentinels of the Inland Seas: Great Lakes Buoy Network Delivers Critical Real-Time Data for Public Safety and Science

Sentinels of the Inland Seas: Great Lakes Buoy Network Delivers Critical Real-Time Data for Public Safety and Science

As summer arrives and lake waters warm, researchers deploy buoys across the Great Lakes to gather vital environmental data. For over 20 years, the Great Lakes Environmental Research Laboratory (GLERL) and partners have developed and implemented these buoy systems to enhance NOAA’s observational capabilities and understanding of Great Lakes ecosystems. By gathering observations from across the Great Lakes, GLERL provides information that supports resource management decisions and promotes safe, sustainable ecosystems and communities.

Yellow buoy with solar panels in Lake Michigan.

A NOAA GLERL Real-Time Coastal Observation Network (ReCON) buoy in Lake Michigan.

From May through October, researchers are deploying a total of 10 buoys to collect data vital to safeguarding the millions of people who live, work, and play around the Great Lakes. Serving as a critical component of the Real-time Coastal Observation Network (ReCON), these systems stream environmental data through a wireless, internet-based system, allowing researchers to monitor lake conditions remotely without needing to be physically on the water. These platforms are strategically positioned in high-priority areas, including Western Lake Erie, Saginaw Bay and Thunder Bay National Marine Sanctuary in Lake Huron, and key coastal sites in Lake Michigan. By continuously tracking environmental conditions – such as waves, wind, water temperatures, dissolved oxygen, nutrients, and algal activity – they provide critical real-time data for safety, situational awareness, and water quality issues such as harmful algal bloom (HAB) detection, which directly informs beach closures and drinking water processing. Tracking waves and currents improves marine weather forecasts, rip current warnings, and safe navigation for commercial and recreational vessels. Beyond immediate safety risks, these observations contribute to a long-term environmental record to improve Great Lakes forecasting and ecosystem research.

“The Great Lakes buoy network monitors ecosystems to ensure environmental health, supporting vital commercial and recreational activities,” said Steve Ruberg, a research physical scientist with GLERL who specializes in observing systems research.

The M20 buoy on Lake Michigan near Muskegon, MI deployed the evening of May 14, 2026. This deployment is part of the annual spring roll-out by GLERL, and serves as a critical node in the Real-time Coastal Observation Network (ReCON). Positioned in 20 meters of water, the M20 buoy provides essential real-time meteorological and water quality data that supports safe navigation for commercial and recreational vessels in the region. By transmitting continuous updates via a wireless internet-based system, these systems allow researchers and the public to monitor rapidly changing lake conditions without the need for constant physical presence on the water.

The success of this observational network relies on strong partnerships between federal, regional, and academic organizations. The Great Lakes Observing System (GLOS) manages the collection and public presentation of data from the buoy network, ensuring that information is readily accessible through online platforms such as its Seagull site. Most ReCON buoy data is publicly available in near-real-time for researchers, water managers, boaters, anglers, and coastal communities. The Cooperative Institute for Great Lakes Research (CIGLR) also partners with GLERL on observing systems through research, technical development, and regional coordination that keep these complex systems running. Maintaining the network requires year-round engineering, calibration, data management, and field support to ensure the systems continue delivering reliable environmental observations.

CIGLR’s role is hands-on, encompassing the engineering and maintenance of several critical platforms. CIGLR deploys and maintains GLOS-funded buoys in Little Traverse Bay and Ludington on Lake Michigan, as well as specialized ecological Synthesis, Observations and Response System (SOAR) buoys in Western Lake Erie and Saginaw Bay. These platforms are custom-tailored to the specific ecological needs of their locations. While the Lake Michigan buoys feature temperature and meteorological sensors that provide a “near-shore” look at rapidly changing conditions, the Western Lake Erie and Saginaw Bay buoys carry nutrient sensors to track HABs.

“The Western Lake Erie buoys carry nutrient sensors that inform water managers and scientists about conditions conducive to growing toxic algae,” says Russ Miller, CIGLR’s lead engineer for the buoy program. He notes that the impact extends well beyond the lab to the local economies and public safety. “The Lake Michigan buoys have temperature strings that the fishermen love… and in Ludington, tournament fishermen use the wave sensors as an objective measurement. If it’s over three feet, they know to delay. It provides an objective measurement for the community.”

CIGLR Observing Systems Engineer Russ Miller stands with western Lake Erie SOAR buoys as they are prepared for seasonal deployment. These advanced, solar-powered monitoring stations utilize exterior weather sensors and telemetry systems to transmit real-time wind and wave data. Below the surface, specialized submerged sondes and data loggers track critical water quality parameters, such as dissolved oxygen and blue-green algae, to provide early warnings for hypoxia and HABs.
Russ Miller completes maintenance on one of the western Lake Erie real-time water quality monitoring buoys that is part of the SOAR project. Regular buoy tune-ups and deployments are conducted to ensure the instruments remain accurate, calibrated, and operating reliably throughout the field season in harsh lake conditions.
A SOAR buoy following deployment in Western Lake Erie.

Real-time and archived buoy observations help improve the reliability of Great Lakes forecasts for environmental conditions such as hypoxia (reduced oxygen levels) and HABs. Since the establishment of GLERL’s ReCON system in 2004, buoys deployed across the lakes have collected meteorological, biological, chemical, and physical observations that support monitoring and forecasting efforts. Archived at NOAA’s National Centers for Environmental Information (NCEI), these long-term datasets are used by researchers, educators, and resource managers to improve scientific models, evaluate past events, and understand changes in lake conditions over time. Data collected by buoys deployed in Lake Erie allows forecasters to predict when HAB or hypoxic water moves toward municipal water intakes, providing critical information for water management decisions.

“The observing systems established on western Lake Erie greatly enhance our environmental awareness and decision-making regarding this vital drinking water resource,” said Douglas R. Stephens, president of the Northwestern Water & Sewer District and former director of the City of Toledo Department of Public Utilities. “Access to real-time water quality data is critical for treatment decisions impacting the 500,000 citizens served by Toledo’s Collins Park Water Treatment Plant. These physical and chemical buoy observations provide background information for the continued improvement of the western Lake Erie HAB forecast, which our staff highly values for early warning of potentially toxic HAB conditions.”

This work is fundamental to the mission of GLERL to study, understand, and protect Great Lakes ecosystems and coastal communities. The GLERL Observing Systems and Ecosystem Monitoring team develops and operates technology that supports coastal environmental observation networks and advances NOAA’s ecosystem forecasting research goals, with much of this work supported by funding from the Great Lakes Restoration Initiative (GLRI), a multi-agency effort focused on protecting and restoring the Great Lakes ecosystem. Together, these observing systems provide a regional environmental intelligence network for the Great Lakes. The network of buoys is more than a collection of sensors, it is a backbone of coastal resiliency. By providing real-time insights into physical and chemical changes in the lakes, these systems help protect coastal communities, track the health of the Great Lakes, support drinking water safety, improve understanding of ecosystem conditions, and strengthen the region’s maritime economy.

Looking ahead, GLERL and partners continue to build on these observing systems by using aerial drones, autonomous surface vehicles, and real-time toxin models for harmful algal blooms. This network of buoys is far more than than a collection of sensors; it is the backbone of Great Lakes coastal resiliency.


Get to Know Your Buoys

The buoys highlighted below help form a coordinated Great Lakes observing network across the basin. By capturing real-time data from nearshore zones, offshore waters, and ecologically sensitive regions, these systems provide a continuous view of how the lakes are changing throughout the spring and summer seasons. Check these links throughout the season for real-time data, updates, and additional information.

Lake Michigan: Tracking Nearshore to Offshore Conditions

In Lake Michigan, multiple buoys are positioned to capture gradients from nearshore waters to deeper offshore environments.

M20 Buoy — Muskegon, Michigan

Deployed near the 20-meter depth zone, this GLERL-built and maintained system provides nearshore meteorological and water quality data that support marine forecasting and recreational safety as summer lake activity increases

Little Traverse Bay Buoy — Northern Lake Michigan

Deployed near the 20-meter depth zone, this GLERL-built and maintained system provides nearshore meteorological and water quality data that support marine forecasting and recreational safety as summer lake activity increases.

Ludington Buoy — Central Lake Michigan

This CIGLR-maintained buoy, funded by GLOS, provides wave, weather, and water condition data used by researchers and the local maritime community alike.

Lake Huron: Understanding Coastal Ecosystems and Change

In Lake Huron, deployments focus on both ecosystem monitoring and sensitive coastal environments.

Alpena Buoy — Thunder Bay National Marine Sanctuary

At the Thunder Bay National Marine Sanctuary near Alpena, this long-term monitoring buoy operated by GLERL supports ecological research and sanctuary resource management in a sensitive coastal environment.

Point Au Gres, MI Buoy — Saginaw Bay

At Point Au Gres in outer Saginaw Bay, this long-term monitoring buoy is built and maintained by GLERL and collects weather, wave, current, and water quality data in approximately 40 feet of water. These observations support ecosystem research, environmental monitoring, and forecasting efforts throughout Saginaw Bay.

SB14 & SB26 Buoys — Inner & Outer Saginaw Bay

In Saginaw Bay, two buoys co-built by GLERL and CIGLR and funded through the Ocean Acidification Program track changing water chemistry and ecosystem conditions in one of the Great Lakes’ most biologically productive regions.

Lake Erie: Monitoring Harmful Algal Blooms and Water Quality

In Lake Erie, deployments focus on high-resolution monitoring of water quality conditions that directly support harmful algal bloom forecasting and drinking water safety for surrounding communities.

WE02, WE04, WE08 Western Lake Erie SOAR Network

In western Lake Erie, the SOAR buoy network, funded through the GLRI and maintained by CIGLR, provides high-resolution observations of water quality, meteorology, and biological activity. These data are essential for monitoring and forecasting HABs and supporting drinking water safety for surrounding communities.


Resources

Access data from across the Great Lakes using this observational network by clicking on the resources below.

June 11, 2026
by GLERL Communications Team
Comments Off on Freshwater SHARC: new HAB monitoring technology to be deployed in Saginaw Bay

Freshwater SHARC: new HAB monitoring technology to be deployed in Saginaw Bay

This summer, Saginaw Bay is getting a high-tech visitor! The Great Lakes Environmental Research Laboratory (GLERL) is deploying a SeaTrac uncrewed surface vessel from July 29th to September 4th as part of the SHARC (Surface Harmful Algal Research Craft) project. SHARC is a cutting-edge effort to monitor and understand Harmful Algal Blooms (HABs) in Saginaw Bay, Lake Huron. GLERL is partnering with the National Centers for Coastal Ocean Science and the Monterey Bay Aquarium Research Institute (MBARI) to take water quality monitoring in the Great Lakes to the next level to help keep our coastal communities safe.

Nautical chart of Saginaw Bay showing yellow hashed areas where SeaTrac will be working
You may see the SeaTrac out working in the yellow hashed areas this summer on Saginaw Bay.

Samples from the Water Surface

This summer, to carry our science payload into the shallowest parts of the bay we are using a SeaTrac Autonomous Surface Vessel (ASV). The SeaTrac ASV is a solar-powered, highly maneuverable surface craft designed specifically for coastal environments.

With a draft of only about 1.5 feet, it can access shallow nearshore areas that traditional research vessels simply can’t reach and areas where human-HAB interaction may be highest. Its bright yellow body, solar panels, and orange flag should make it instantly recognizable and easy to spot out on the water. This low-profile vessel measures just under 16 feet, slightly longer than a typical fishing dinghy, with a freeboard height of only 8.4 inches, and a mast height of 4 feet. Solar-powered batteries allow it to stay out on the lake for weeks at a time, providing continuous reporting back to our team in Ann Arbor.

A close-up, side-profile photograph shows the bright yellow SeaTrac Autonomous Surface Vessel floating in calm water.
The bright yellow SeaTrac Autonomous Surface Vessel (ASV), the core of the Freshwater SHARC project, is shown here underway in Lake Erie in 2024. This solar-powered craft is collecting water samples to monitor and understand harmful algal blooms in near-real-time to help keep the Great Lakes safe.

The Science of Harmful Algal Blooms

The primary goal of the SHARC project is to track and analyze HABs in Saginaw Bay in near-real-time. Saginaw Bay is a shallow, bloom-prone embayment where wind and currents can quickly shift the location of toxic algae. While GLERL has monitored these waters since 2010, the SHARC project will track harmful algal blooms as they occur this summer.

The “brain” of this mission is MBARI’s third-generation environmental sample processor (3G ESP). Integrated directly into the surface vessel, the 3G ESP automatically collects water samples and uses Surface Plasmon Resonance (SPR) to analyze them for toxins such as microcystins while still out on the water. It also preserves samples for later “omics” analysis, giving us a molecular-level look at the algal community and its genetic potential for toxicity that can affect drinking water quality. The SHARC system allows us to provide timely, actionable data to water managers and the public.

During the mission, SHARC will serve as a flexible, event-response platform. If a heat wave, passing weather front, strong winds, satellite imagery, or reports from people on the water suggest a bloom may be forming or moving to a new area, scientists can send SHARC to areas of concern to test the water directly. By pairing real-time toxin measurements with samples saved for later laboratory analysis, SHARC will help identify where blooms are occurring, how toxic they are, and what is causing them. and how they are changing over time. These observations will help scientists better understand HABs in Saginaw Bay and support informed decision-making for those who rely on its waters.

A map that displays the NOAA GLERL harmful algal bloom monitoring sites on Saginaw Bay, Lake Huron.
NOAA GLERL harmful algal bloom monitoring sites on Saginaw Bay, Lake Huron.

Images from the Sky

The SeaTrac ASV is not the only technology at use in the SHARC project. To find the best sampling spots, we’re using an Uncrewed Aerial System (UAS)—a hexacopter drone equipped with a specialized hyperspectral imager. The hyperspectral camera detects the unique light signature of cyanobacteria, identifying “hotspots” of high HAB biomass. Flying at altitudes below 400 feet, the imager provides high-resolution “eyes in the sky” that can see below the clouds that often block satellite views. The imagery also fills in the gaps nearshore, where shallow waters can disrupt satellite data due to low image resolution or light reflections from the lake floor. Scientists then use this data to help direct the ASV to the hot spots to determine if they contain the harmful algal bloom toxin.

While the hyperspectral data can identify the presence and extent of a bloom, it can not determine toxin levels. The water must then be sampled in order to determine the toxin level, and that is when the SeaTrac ASV moves in.

Two field researchers wearing white hard hats and reflective orange safety vests stand outdoors in front of a large black hexacopter drone resting in the center of a circular red and black landing pad.
The SHARC project’s hexacopter drone is preparing for a survey flight to locate toxic blooms in the shallow waters of Saginaw Bay.
An aerial photograph taken from a Cessna 210 airplane window looks down at light-colored turquoise and green swirls of a harmful algal bloom spreading across the blue water.
View from Cessna 210 window during crewed flight of a 2022 Saginaw Bay harmful algal bloom indicated by the areas of light-colored swirls spreading across the water.
A data visualization graphic displays NOAA GLERL hyperspectral imagery tracks mapping cyanobacteria levels over Saginaw Bay, Lake Huron.
In September 2021, a crewed Cessna 210 conducted a hyperspectral flight over Saginaw Bay’s drinking water intakes to map HAB blooms. The images from the flights are shown in the composite graphic here.

Setting Sail this July

Deployment of the SeaTrac ASV will operate out of Sebewaing, MI, with the craft conducting both underway sampling and holding location near a target station in locations as far northeast as Caseville, MI. 

As we set sail this July, we’re looking forward to the insights this mission will bring to help monitor local water quality, keep boaters and beachgoers safe from toxins, and protect our beloved Great Lakes. If you’re out on Saginaw Bay this summer and spot the SeaTrac vessel in action, be sure to snap a photo from a safe distance of 200 feet or more and share it with us! We love seeing our research through the eyes of the community. Tag your posts with #freshwaterSHARC to join the conversation as we work to keep our waters safe for everyone.

April 21, 2026
by GLERL Communications Team
Comments Off on Eyes in the Sky: How Hyperspectral Flights Improve Knowledge of Great Lakes Winter Ice

Eyes in the Sky: How Hyperspectral Flights Improve Knowledge of Great Lakes Winter Ice

Figure 1. Aerial view of Western Lake Erie ice conditions, out the window of a Cessna 210 aircraft during a January 23, 2025 survey.

It was a cold and icy winter in 2025-2026. Lake ice affects everything from snowfall and fishery populations to recreational activities and the multibillion-dollar commercial shipping industry, making Great Lakes ice cover data highly valuable. However, once winter arrives boats and buoys are removed from the water to protect them from ice, so the NOAA Great Lakes Environmental Research Laboratory (GLERL) monitors the Great Lakes by taking to the sky. GLERL has been using a technique called hyperspectral imagery for over a decade to monitor Great Lakes harmful algal blooms in the summer. This method, which uses cameras to collect wide band data from across the electromagnetic spectrum, can also be utilized to monitor lake ice.

One possible method is monitoring ice conditions from the sky, using a camera that collects a wide band of data from across the electromagnetic spectrum. By using a technique called hyperspectral imagery, GLERL has been collecting data over the Great Lakes for over a decade, frequently to monitor harmful algal blooms during the summer. Starting in 2024, our researchers began to explore flying a hyperspectral camera to monitor lake ice during the winter.

What is hyperspectral data?

Hyperspectral data or imagery contains much more information than a visible image. Traditional images capture what a human eye sees (visible light spectra), which consists of three bands: red, green and blue. The ‘hyper’ in hyperspectral means that the data collected captures parts of light beyond what our eyes can see, such as the near-infrared (thermal/heat range). Instead of three bands like our eyes or a traditional camera captures, hyperspectral cameras capture over 150 bands. How does all that extra information fit into an image? Hyperspectral data isn’t analyzed as a flat 2D image, but forms a 3D data cube. Different materials reflect and absorb light in a unique way, creating a spectral fingerprint similar to the uniqueness of a human fingerprint. By collecting hyperspectral data we are able to shift from looking at an object to identifying it by its spectral fingerprint. A spectral signature plot (or spectra plot) provides a graphical representation of a selected pixel in a hyperspectral image. The x-axis represents the wavelength in nanometers while the y-axis represents the intensity, also referred to as brightness, which is a measure of the amount of light being reflected at a particular wavelength. The blue, green and red vertical lines indicate the specific bands used to render the current hyperspectral image; in Figure 2, which shows different hyperspectral images, they were selected to mimic the standard red-green-blue spectrum seen with a human eye.

Figure 2. Comparison of spectral signatures from Lake Erie hyperspectral flights: open water (top left), lake ice (top right), a harmful algal bloom (bottom left), and a calibration tarp used as a baseline (bottom right). The images above show distinct variances that can help to identify water conditions. The open water spectra (top left) shows a steep drop after 600 nm due to the way water absorbs light – the red wavelength is the first to be absorbed. The lake ice image (top right) displays the highest y-axis values of intensity due to the reflective nature of ice, which bounces back nearly all visible light. The harmful algal bloom spectral plot (bottom left) shows a distinct green peak, a characteristic of chlorophyll reflectance. While the final spectral plot for the calibration tarp (bottom right) is a much flatter spectra overall because the gray tarp is designed to be spectrally neutral by not reflecting light.

The first step in hyperspectral data collection begins with outfitting a small aircraft – a Cessna 210 in our case – with the hyperspectral camera (Figure 3). Once the camera is installed, the pilot flies a pre-defined flight path surveying an area of interest. Throughout our most recent ice flight mission, the aircraft maintained a survey altitude of 10,500 ft, capturing high resolution ice data.

Figure 3. Cessna 210 with hyperspectral camera system and power source installed in a modified luggage compartment.

Quick Shifts, Complex Conditions

The Great Lakes are known for their propensity to change rapidly. Many know the phrase “if you don’t like the weather, wait five minutes”, and the lakes are no different. Figure 5 below shows three visible webcam images from the same viewpoint highlighting the shift of Lake Erie ice sheets across a three hour timeframe. Winds and currents have a dramatic impact on how quickly the ice moves. This shows how monitoring, prediction, and reporting ice conditions can be challenging.

Figure 4. Webcam imagery from Lake Erie Channel Marker 2 during Jan 23, 2026 ice survey. (Realtime imagery accessed through GLERL’s ReCON webpage: https://www.glerl.noaa.gov/res/recon/station-cmt.html)

How is Great Lakes ice tracked and forecast now? A combination of numerical models and satellites that use radar, visible and infrared imagery determine ice conditions. Ice condition information is crucial for shipping in the Great Lakes, as commercial shipping traffic still transects the lakes throughout the winter months when conditions allow – even when ice is present. However, existing methods to monitor and track ice in the Great Lakes have limitations: satellites only provide periodic static images, and numerical models require high-fidelity data for validation. To address these gaps, GLERL is exploring hyperspectral imaging as a way to improve current monitoring systems and improve model predictions.

After hyperspectral data is collected it can be processed multiple ways. One of the products from these ice flights is true color imagery. Figure 4 below consists of four north-to-south passes over Lake Erie when covered with ice. At first glance one can observe a few different features by eye in the visible imagery: wind-blown snow, rough ice, possibly open water and a wispy cloud that created a slight shadow.

Figure 5. Overview of true color results from hyperspectral ice survey Jan 23, 2026 (left), with a snapshot view of ice conditions and possible features (right).

Looking Forward

In addition to using airplanes, we can also use aerial drones to capture hyperspectral data. To leverage this emerging technology, GLERL established an aerial drone program in 2024. This provides a significantly different perspective since aerial drones fly much lower to the ground,  allowing them to capture much higher resolution images. Additionally, some drones are able to hover in one place while collecting data.

Collecting hyperspectral data from planes and drones is critical to understanding ice cover and ecology in the Great Lakes. By monitoring harmful algal blooms with hyperspectral imagery, we can safeguard drinking water intakes for millions of people, while also gaining insight into the dynamics of ecosystems in the lakes. Capturing hyperspectral ice cover data is fairly new but the potential payoff is big. Providing timely ice cover data at a resolution and accuracy never before available benefits all those that depend on the Great Lakes. Ice impacts everything from wildlife populations and health to the freighters that navigate the ice moving almost 200 million tons of materials each year, keeping our regional economy strong.

The ice features identified in Figure 4 are just the beginning of ice analysis based on hyperspectral data. More detailed analysis can confirm the ice classification (for example, determining different types or ice formation or thickness of ice) with more confidence and accuracy, thanks to the wealth of data that is embedded in a hyperspectral image. Advanced techniques are able to turn big datasets – including hyperspectral data – into valuable information. One technique is called deep learning, which allows an algorithm to study a big data set and then make predictions about that data. In our case, a deep learning algorithm  studied 150 bands of an image and then described more about the ice types than we would be able to tell by looking at it with our red-green-blue detecting eyes. This takes trial and error and requires us to have the “ground truth” in order to train and check the algorithm. Finally, GLERL also conducts an analysis of how Great Lakes ice conditions progressed throughout the previous winter. Comparing the past winter’s conditions to historical trends, helps us understand the key factors that influence ice formation, how ice conditions have changed over time, and how we might predict future ice cover. With an increase in both the quality and quantity of ice condition data, GLERL predictions will continue to improve services for a broad range of Great Lakes stakeholders.

July 18, 2025
by GLERL Communications Team
Comments Off on June 21, 2025 Storm Causes Significant Meteotsunami and Seiche on Lake Superior

June 21, 2025 Storm Causes Significant Meteotsunami and Seiche on Lake Superior

On June 21, 2025 there were numerous social media reports showing dramatic water level changes across Lake Superior, with photos and videos of water at beaches receding to expose dry land over the course of a couple of hours and then rapidly rising again. These rapid water level changes were experienced by coastal communities all around Lake Superior, with reports and images from areas including Munising, Michigan; Thunder Bay, Ontario; Duluth, Minnesota; and Algoma, Ontario. These significant water level fluctuations had notable impacts on boating and shipping, with ships remaining offshore to avoid groundings resulting in delays, vessel docks being damaged and overturned, and small boats being stranded or pushed into docks and slips. However, no injuries have been reported.

NOAA water level data from Lake Superior shows that the storm caused large fluctuation in water levels, triggering a multi-stage event, with an atmospheric pressure-induced meteotsunami, wind-driven storm surge, and strong seiche activity all interacting to generate the extreme water level fluctuations observed on the lake. The strongest impacts were observed in the lake’s southeastern region, around Whitefish Bay and Sault Ste Marie.

Ketzel Levens, meteorologist with the National Weather Service at the Duluth, MN Weather Forecast Office (WFO), stated that a significant weather system transited through the region causing this event.

At NWS Duluth, our primary concern with this event was warning on the initial line of thunderstorms that moved across Lake Superior in the early morning hours of June 21, which were producing strong winds and hazardous to mariners. Once the line of storms had passed, we were monitoring for reports of large hail or wind damage when we were alerted to large water level fluctuations occurring in Ashland, WI along with subsequent minor flooding in the Maslowski Beach area. Seiche and meteotsunami events can be difficult to message, due to their displacement in timing from the convective system that initiates them, as well as a sparse data network to actually track water level fluctuations so some events may go un-observed, especially if they are nocturnal. We also don’t have a specific headline to issue for these events, though depending on the severity level they might fit under Lakeshore Flood Advisory or Special Marine Warning. Additionally, we don’t get events of this magnitude as frequently as some of the southern Great Lakes, though low magnitude seiches kicked off by synoptic weather systems are common. Thus, we put out a call for reports in order to better understand the impacts being felt around Lake Superior, and try to tie those to the few water level sensors that do exist as well as the timing of the storm system. Reports poured in, with significant water level fluctuations observed around Lake Superior that caused water to pull out of harbors and then come back in and flood over docks. It also produced a strong current in and out of the Duluth Harbor Canal, with observed flows up to 8 feet/second from the USGS gauge! That current led to chaotic wave action at the mouth of the canal leading to some hazardous conditions for mariners. These reports along with archived weather and water station data will allow an internal team to perform operational research on the event, hopefully making for more efficient pattern recognition in the future! Additionally, due to the quick nature of these events, even high resolution models that have 1-hour granularity may not be able to capture them. More warn-on forecast systems with higher temporal granularity could be helpful in identifying events as well as performing post event analysis.

NOAA Water Level Station 9099004 in Point Iroquois, MI (https://tidesandcurrents.noaa.gov/stationhome.html?id=9099004).

NOAA operates five water level stations on Lake Superior, which are used to monitor, track, and understand lake processes such as the extreme fluctuations experienced by coastal communities this weekend. The Point Iroquois water level station (9099004) is situated on Whitefish Bay in southeastern Lake Superior in Michigan’s Upper Peninsula, and has recorded water level measurements every 6 minutes since September 1995. On June 21, 2025, this station recorded a remarkable 45 inch increase in water level in Whitefish Bay over less than 2.5 hours, the largest water level surge ever recorded in the station’s 30-year history.

Animation of air pressure conditions over Lake Superior on June 21, as simulated by the NOAA High-Resolution Rapid Refresh (HRRR) weather forecast model.

The water level fluctuations began with a low pressure system that moved from west to east across Lake Superior between approximately 6:00 AM and 10:00 AM EDT on June 21. As a strong, low pressure storm moves across the lake, air pressure differences cause it to push down unevenly on the lake surface, which raises water levels with the storm’s passing. Under certain conditions, this displacement can result in the formation of large-scale waves known as meteotsunami. Meteotsunami happen regularly on the Great Lakes, forming when a storm is moving in the same speed and direction as the wave that’s building in front of it. This amplifies the wave, and as the wave reaches the shore, it produces a sudden rise in water level. As the June 21 storm moved west to east across Lake Superior, it produced a significant meteotsunami in eastern Lake Superior, and a water level rise of 19.3 inches between 8:00 AM and 9:48 AM was recorded at the Point Iroquois station as a result.

NOAA Buoy 45004 in eastern Lake Superior (https://www.ndbc.noaa.gov/station_page.php?station=45004).

At the tail end of the passing storm, eastern Lake Superior experienced strong sustained winds out of the south-southeast. NOAA’s Eastern Lake Superior Buoy (45004) recorded sustained winds of up to 20 to 35 mph with gusts up to 40 mph between approximately 9:00 AM and 1:00 PM.

Animation of wind conditions over Lake Superior on June 21, as simulated by the NOAA High-Resolution Rapid Refresh (HRRR) weather forecast model.

These strong winds produced a wind-driven storm surge, driving water to surge back out to the northern and western portions of the lake and away from the southern shore. The magnitude of wind-driven storm surges on the Great Lakes depends on both the speed of the wind and the distance it has to travel over the lake and build momentum, known as “fetch”. The strong south winds experienced in eastern Lake Superior produced a storm surge on the north-northwest shore, which was amplified both by lingering low pressure to the north, and because the lake was primed by the meteotsunami that had immediately preceded it. Additionally, there was a water level drop of -43.3 inches between 9:48 AM and 11:24 AM associated with the storm surge recorded at the Point Iroquois station. As the storm finished moving through and conditions on Lake Superior calmed, the displaced lake surface rebounded to produce strong seiche activity, with a water level rebound of +45.4 inches from 11:24 AM to 1:41 PM.

Water level measurements from the NOAA Point Iroquois Water Level Station, showing extreme fluctuations in response to the June 21 storm.

The 45.4 inch water level rise observed on June 21 was the highest-magnitude surge ever observed at the Point Iroquois station, which has continuous data dating back to September 1995. In fact, surges above 36 inches have only occurred on four other days in the station’s 30-year record, most recently a 42.3 inch magnitude surge that occurred on June 29, 2018. This makes the June 21 event quite uncommon and remarkable in its magnitude and complexity

Daily maximum surge magnitude at the NOAA Point Iroquois, MI Water Level Station (9099004), dating back to September 1995. Surge is calculated here as the range in water level over a rolling 6-hour period.

A seiche is the oscillation of water back and forth across a large body of water that can continue for several days. The Great Lakes can act like giant bathtubs, with water sloshing back and forth after being pushed around by a storm. Lake Superior’s size and shape result in it having a characteristic seiche period of appoximately 8 hours, meaning it takes about 8 hours for water to slosh back and forth across the lake (e.g., between Duluth and Sault Ste. Marie). Seiche activity is almost always present on Lake Superior. Under typical conditions, seiche fluctuations are only a few inches in magnitude, but when triggered by a strong storm, they can be much larger. On June 21, the initial rebound observed in Whitefish Bay likely occurred primarily within the lake’s eastern basin, thus explaining its shorter period, then relaxing to a more typical east-west lakewide seiche with a roughly 8-hour period in subsequent oscillations.

Water level measurements from the NOAA Point Iroquois, MI Water Level Station (9099004), showing elevated seiche fluctuations in the days following the June 21 storm.

With a strong trigger like the June 21 storm, elevated seiche activity can persist for several days following the initial event. Seiche fluctuations exceeding 18 inches continued throughout the following day, and elevated seiche activity persisted on the lake through June 25, several days after the initial event.

Model mesh for GLERL’s Lake Superior Forecast System in the Whitefish Bay region of Lake Superior.

Scientists at NOAA’s Great Lakes Environmental Research Laboratory (GLERL) are now working to understand exactly how water moved around the lake on that day. Existing Great Lakes forecast models, such as the Lake Superior FVCOM Forecast System are capable of simulating and forecasting many key processes in the lakes, such as currents and storm surges. However, fast moving squall lines, such as those that move across the lake to produce meteotsunami, often evolve too quickly to be fully represented in the hourly data generated by these models. Continued research and development of Great Lakes forecast models will be critical to understanding, simulating, and forecasting events like the June 21 storm’s impact on Lake Superior.

June 23, 2025
by GLERL Communications Team
Comments Off on Great Lakes Water Levels Down from Record Highs of 2017-2020

Great Lakes Water Levels Down from Record Highs of 2017-2020

Monthly lake-wide water levels on the Lake Michigan-Huron system showing declines in lake water levels over the past five years. Source: Great Lakes Water Level Dashboard, NOAA Great Lakes Environmental Research Laboratory, https://www.glerl.noaa.gov/data/wlevels/dashboard/.

Great Lakes water levels have taken a dip over the last few years. Only a few years ago, we were fielding questions related to record high water levels on each of the lakes. Now, as water levels return to near and sometimes even below average, the question arises: why the dramatic shift from very high water levels to the relatively lower water levels we are seeing now?

First, it is important to look at the current water levels in the context of the very long historical record of Great Lakes water levels. The historical record, which is officially coordinated by federal agencies in the U.S. and Canada, dates back to 1918. The NOAA Great Lakes Water Level Dashboard is a useful tool to explore this coordinated data. Here is where monthly mean water levels were in May 2025, relative to this long record back to 1918:

  • Lake Superior was about 2 inches below last year and almost 4 inches below its long-term average level for May, but about 20 inches above the record low May level. The overall range since 1918 is close to 4 ft.
  • Lake Michigan-Huron was about 8 inches below last year and close to 6 inches below its long-term average level for May, but 25 inches above the record low May level. The overall range since 1918 is a little over 6 ft.
  • Lake Erie was about 6 inches below last year, but 5 inches above its long-term average level for May and 40 inches above the record low May level. The overall range since 1918 is about 6.5 ft.
  • Lake Ontario was about 1 inch above last year, but close to 2 inches below its long-term average level for May. The Lake Ontario May level was about 35 inches above the record low May level. The overall range since 1918 is a little over 7 ft.

In the context of the long historical record, these recent levels are not so different from long term averages, but what is remarkable is how much change seen in Great Lakes water levels since 2020. We observed record high water levels on each lake at some point between 2017 and 2020. During that period, impacts included coastal flooding and property damage from erosion. When water levels are much below average, on the other hand, impacts include ecosystem changes and loss of wetland area, reduced capacity for shipping drafts, and changes to waterfront access and aesthetics.

Why did water levels come down?

Great Lakes water level changes on seasonal and longer timescales are the result of the combined influence of precipitation falling over the lake, runoff into the lake, and evaporation from the lake surface. We refer to the combination of these three factors as net basin supply (NBS). When the net inflow to a lake is more than the lake outflow, water levels will go up, and vice versa.

Components of Net Basin Supply to a Great Lake, including inflow, runoff, precipitation, evaporation, and outflow.
Components of Net Basin Supply to a Great Lake. Source: NOAA Great Lakes Environmental Research Laboratory flickr, https://www.flickr.com/photos/noaa_glerl/.

At a seasonal timescale, the lakes generally follow a pattern of lower levels during the winter months and higher water levels during the summer or early fall. During the winter, precipitation falls as snow and accumulates on land. In the spring, melting snow and precipitation falling as rain add water to the lakes, causing water levels to rise. Then, in the fall and early winter, when cold air enters the region, the temperature difference between warmer water and cooler air results in increased evaporation, driving water levels back down for the winter. When we see longer periods of high precipitation and/or low evaporation rates, we can expect increasing water levels, whereas during extended periods of low precipitation and/or high evaporation rates, we can expect water levels to decline.

Graphic showing how Great Lakes levels change with each season from winter low to spring rise, summer peak, and fall decline.
Great Lakes seasonal water level cycle. Source: NOAA Great Lakes Environmental Research Laboratory flickr, https://www.flickr.com/photos/noaa_glerl/.

High water levels were sustained over a multi-year period ending in 2020, largely a result of a sequence of years with very high precipitation. In fact, the five years ending in April 2020 were the wettest 5 years on record for the Great Lakes since the late 1890s. After 2020, precipitation was considerably less than during the 5-year period ending in 2020. Below is a graphic of annual precipitation since 1895 from NOAA Climate at a Glance.

Graph of Great Lakes Basin Annual Precipitation from 1895 to 2025
Great Lakes Basin Annual Precipitation from 1895 to 2025. Source: NOAA National Centers for Environmental information, Climate at a Glance: Regional Time Series, published May 2025, retrieved on May 12, 2025 from https://www.ncei.noaa.gov/access/monitoring/climate-at-a-glance/regional/time-series.

GLERL research is advancing seasonal to annual water level forecasts

The NOAA Great Lakes Environmental Research Laboratory (GLERL) hydrology team, including partners from the University of Michigan’s Cooperative Institute for Great Lakes Research (CIGLR), conducts research focused on better understanding and predicting the key factors driving seasonal and longer changes in Great Lakes water levels (primarily precipitation, evaporation, and runoff). The forecast tools produced by the GLERL-CIGLR team contributes to the official 6 month forecast of Great Lakes water levels produced by coordination between the U.S. Army Corps of Engineers and Environment and Climate Change Canada each month. The GLERL-CIGLR team is currently developing a next generation prediction system for subseasonal to annual water supply forecasts. This system will transition to sustained operations at the U.S. Army Corps of Engineers for application to seasonal water level forecast products. This new forecast system is being developed using machine learning approaches to predict subseasonal to annual precipitation, evaporation, and runoff based on the NOAA operational Climate Forecast System. The integration of atmospheric science, hydrology, data science, and research engagement creates a forecast of Great Lakes water levels that meets end user needs.

Resources

NOAA GLERL Great Lakes Water Levels
NOAA Great Lakes Regional Collaboration Network
U.S. Army Corps of Engineers Great Lakes Water Information
Cooperative Institute for Great Lakes Research, Great Lakes Forecasting

May 8, 2025
by GLERL Communications Team
Comments Off on Great Lakes Ice Cover Near Average for the 2025 Season

Great Lakes Ice Cover Near Average for the 2025 Season

Each spring, NOAA’s Great Lakes Environmental Research Laboratory (GLERL) conducts an analysis of how Great Lakes ice conditions progressed throughout the previous winter. This analysis, which compares the past winter’s conditions to historical trends, helps us understand the key factors that influence ice formation, how ice conditions have changed over time, and how we might predict future ice cover. Ice cover data is highly valued because it plays a critical role in both the ecology and economy of the Great Lakes region. Lake ice affects everything from snowfall and fishery populations to recreational activities and the multibillion-dollar commercial shipping industry.

The 2024-2025 winter Great Lakes ice season stayed close to long term normals following the near historic low ice levels seen in the 2023-2024 winter (Figure 1). One way that GLERL tracks ice cover is by looking at the daily percentage of ice cover across the Great Lakes, calculated by determining the area of the Great Lakes that are covered by ice and dividing that by the total surface area of the lakes. The daily percentage of ice covering each of the Great Lakes this winter is shown in the figure below.

Figure 1. Individual graphs of the percentage of ice cover of Lake Superior, Michigan, Huron, Erie, Ontario, and for all of the Great Lakes for the 2025 season.

However, despite colder temperatures than last winter, most of the lakes stayed slightly below long term averages on a daily basis through the season. Figure 2 shows 2025 daily ice cover percentages compared to 2024 ice cover values and other past seasons. Note that the 2025 ice season had an increase in ice cover compared to last year, but it did not approach record levels.

Figure 2. Daily ice cover percentage for the Great Lakes basin for 2024 (green line), 2025 (purple line) and the other years in the record 1973-2023 (blue).

Each of the Great Lakes responds differently to seasonal changes due to unique physical characteristics—particularly their size and depth. Deeper lakes, for example, retain heat longer and may experience delayed or reduced ice cover compared to shallower ones. Similarly, larger surface areas can influence how wind and air temperature affect ice formation. Figure 3 illustrates the differences between lakes by showing the size and depth of each lake. 

Figure 3. Size comparison of length and depth for the individual Great Lakes. Graphic courtesy of Michigan Sea Grant.

Let’s compare ice cover between Lake Michigan and Lake Erie. Lake Michigan, with its relatively deep basin, tends to warm and cool more slowly than shallower Erie. As a result, Lake Michigan experiences a more gradual formation of ice and typically has lower overall ice cover. In contrast, Lake Erie, the shallowest of the Great Lakes, loses heat more quickly and develops ice cover earlier in the season. As a result, Lake Erie quickly covers with ice when air temperatures stay below freezing.

This winter season began with warm water temperatures across the Great Lakes, with little-to-no ice coverage in December. However, temperatures dropped in January and Lake Erie saw above normal ice from late January to early March (Figure 4). Lake Erie, the smallest and shallowest lake, lost heat relatively quickly while the larger lakes didn’t reach the temperatures needed for ice generation until later in the season, or only over smaller portions of the lake. 

Figure 4. Daily ice percentage for Lake Erie for 2025 (black line), long term average (red) and the other years in the record 1973-2024 (blue).

Why did Ice Percentages Peak in Late February?

The first three weeks of February were cold, with below average air temperatures allowing ice to build. A shift occurred during the 4th week of February when above normal air temperatures were recorded across the Great Lakes, reversing ice growth. Figure 5 shows the air temperatures since January 1st, 2025 for select cities across the Great Lakes. The shift from cold, below normal temperatures to warm, above normal temperatures during the 4th week of February is evident at each location, regardless of geography.

Figure 5. Temperature graphics for January 1st through April 1st, 2025 at Detroit, MI (upper left), Chicago, IL (upper right), Marquette, MI (lower left), and Buffalo, NY (lower right). Observed temperatures in 2025 are shown in dark blue, with the normal temperature ranges shaded in tan.

Seasonal Averages: A look at the numbers

The 2024-25 annual maximum ice cover is compared to the long term average in the table below, showing that overall, maximum ice cover was close to average this season.

Table 1. Annual Maximum Ice Cover (%).

The average ice coverage between January and March is shown in the table below in comparison to the full season annual max ice cover above. Ice cover was typically below average.

Table 2. Average Ice Cover from January to March (%).

The number of days with ice coverage greater than 10% is shown. The majority of lakes and the basin-wide total both indicate that this winter was slightly below long term averages.

Table 3. Number of Days of Ice Cover Duration Greater than 10%.

The tables below show how this past winter ranked with respect to records from the previous 51 years. Much of the data indicates that ice cover in general was slightly below average.

Basin-WideSuperiorMichiganHuronErieOntario
28th36th26th21st10th23rd
Table 4. Maximum Ice Percentage (%) Annual Ranking 1973 through 2025.

Basin-WideSuperiorMichiganHuronErieOntario
38th38th37th38th29th24th
Table 5. Ice Duration (Number of Days > 10%) Annual Ranking 1973 through 2025.

Basin-WideSuperiorMichiganHuronErieOntario
36th39th36th36th25th28th
Table 6. Average Ice Cover (Jan-Feb-Mar) Annual Ranking 1973 through 2025

What was happening globally that played a role in determining ice cover in the Great Lakes?

During the winter, ice cover on the Great Lakes is influenced by four large-scale climate patterns from the Atlantic and Pacific: the North Atlantic Oscillation (NAO), the Atlantic Multidecadal Oscillation (AMO), the El Niño-Southern Oscillation (ENSO), and the Pacific Decadal Oscillation (PDO). These patterns describe conditions that can lead to above average or below average temperatures in the Great Lakes, depending on their position. In February, both the AMO and PDO drove strong and steady warming during the entire ice season – except for the month of February. February was marked by below-average air temperatures, including a 16-day streak of colder than normal weather in the middle of the month. While the NAO stayed near normal, while ENSO was in a cooling phase. On February 22, the ENSO-induced cooling caused ice cover to briefly peak at 52% but conditions quickly warmed, which correlates with the status of global climate patterns at that time (the 3rd warmest February). The strong warming effects from AMO and PDO meant the brief increase in ice cover linked to ENSO didn’t last long. GLERL predicted at mid-December and mid-January a similar but slightly higher range of maximum ice cover (between 53–66%) than occurred. These predictions are provided each year by a statistical ice coverage model based on the four climate patterns.

April 24, 2025
by GLERL Communications Team
Comments Off on Seining Season: Studying the Future of Great Lakes Whitefish

Seining Season: Studying the Future of Great Lakes Whitefish

Each spring biologists from the NOAA Great Lakes Environmental Research Laboratory (GLERL) head out to the beaches along Lake Michigan to check in on juvenile lake whitefish. This popular, mild-tasting native species is the most popular commercial fish in the Great Lakes. Our scientists use special nets to count juvenile whitefish and keep tabs on how these fish are faring as the Great Lakes change. Numbers show that the species has declined dramatically, and GLERL is working to determine what is causing this.

What is a Lake Whitefish?

Lake whitefish from Lake Ontario. Note smaller body size of top and bottom fish. November 2000. Credit: J. Hoyle, Ontario Ministry of Natural Resources.

Lake whitefish (Coregonus clupeaformis) are a native species to the Great Lakes that are a popular and valuable commercial fish. Related to salmon and trout, they are prized for their exceptional flavor and are economically valuable to the Great Lakes. They live and feed in the benthic zone of the lakes – in the dark, cool depths near the lake bottom. Lake whitefish prefer cool water and spend much of their time offshore except during the spawning run in late fall where they migrate to shallow reefs, rocky channels, and rivers to lay their eggs. Eggs then overwinter in those locations and hatch in the early spring, when the larval fish begin looking for food. Their diet historically consisted of an energy-rich, shrimp-like amphipod called diporeia. However, diporeia have been in drastic decline in the Great Lakes over the past several decades, so lake whitefish must find poorer quality food such as mussels, other invertebrates, and small fish to eat.

Why are Lake Whitefish Popular?

Lake whitefish have long been an important commercial fishery in the Great Lakes. According to the Michigan Sea Grant, in 2020 they made up 89 percent of the catch in Michigan commercial fisheries and 95 percent of the sales. Well known for their mild flavor they are likely to end up on restaurant menus throughout the Great Lakes region and beyond. They also support a popular recreational fishery for ice anglers on Green Bay, where over 110,00 fish are caught annually, as well as smaller recreational fisheries around piers throughout the Great Lakes.

Lake whitefish caught by ice fisher Jeff Elliott, biologist with the NOAA Great Lakes Environmental Research Laboratory. Credit: Jeff Elliott.

What is Affecting the Status of Whitefish Populations?

Lake whitefish are showing a decline throughout much of the Great Lakes, especially in the main basin of Lake Michigan. According to the Great Lakes Fishery Commission, commercial harvest in the early 1990s was around 8 million pounds a year, but by 2020, harvests had declined to just above 2 million pounds a year. Recruitment describes the critical process through which fish populations regenerate themselves by laying eggs, producing larval fish that can thrive when conditions and food supplies are optimal before transitioning to mature fish that become desirable for catch. Researchers from GLERL along with partners from other agencies and tribes are working to identify what factors are affecting whitefish recruitment, and identify any recruitment bottlenecks that are contributing to the decline of whitefish populations.

Lake whitefish life cycle: it takes 5 to 7 years for a whitefish to mature to adulthood. Credit: Michigan Sea Grant. https://www.michiganseagrant.org/topics/ecosystems-and-habitats/native-species-and-biodiversity/lake-whitefish/

How are We Investigating Whitefish Recruitment?

Beach seine net being deployed by biologists from NOAA’s Great Lakes Environmental Research Laboratory in Grand Haven, Michigan. Credit: NOAA/GLERL.

After hatching in late winter, larval lake whitefish spend their time in the nearshore areas of the lakes. They need a steady supply of food in order to thrive and grow, typically eating zooplankton in the water. Researchers are able to capture larval fish for studies in this habitat by manually pulling a seine net along the beach. The seine is a 150 foot long mesh net that is pulled out from the beach and then manually worked back towards the shore. Any fish captured in the seine are concentrated to the back of the net for easier sorting.

Biologists from the Great Lakes Environmental Research Laboratory seining for larval lake whitefish in Muskegon, Michigan. Credit: NOAA/GLERL.

Spottail shiners, banded killifish, round gobies, and emerald shiners are all common bycatch species; those are counted and returned to the water. Any whitefish captured are counted, measured, and their diet is analyzed by examining their stomach contents under a microscope. Additionally, lake and weather conditions are recorded, such as water temperature, dissolved oxygen, pH, substrate, wave height, wind speed and direction. A zooplankton sample is also taken to allow researchers to compare what’s in the water to what the whitefish have eaten to estimate how much food is available to them.

Larval lake whitefish caught by GLERL biologists in a seine net. Credit: NOAA/GLERL.

Biologists at GLERL’s Lake Michigan Field Station in Muskegon, MI have been using seine nets to sample larval whitefish on the beaches near Muskegon, Grand Haven, and Montague every spring since 2014. This long term dataset is important for understanding the health of the fishery as it takes whitefish five to seven years to recruit to full adulthood. Once larval whitefish have been captured at each site and examined in the laboratory, GLERL biologists can study ecological changes that are happening over time to understand how likely young fish will be recruited to adult stages and become part of the commercial fishery.

How are Larval Whitefish Doing?

Captured larval lake whitefish swimming in container. Credit: NOAA/GLERL.

During most years, larval fish numbers have been low in GLERL sampling in southeast Lake Michigan, indicating there will be fewer fish to grow to adult life phases than historical numbers show. Furthermore, even during the years when catch numbers were highest, there was little evidence in subsequent surveys of mature whitefish by the Michigan Department of Natural Resources that these fish survived to adulthood, reflecting poor recruitment. One reason may be that these fish do not have enough food to quickly grow beyond the larval stage (where they are vulnerable to predators or starvation). GLERL’s diet analyses indicate that larval lake whitefish require certain types and sizes of food at different phases of life. In order to thrive, larval whitefish and the right types of food (i.e., different species of zooplankton or larger prey) have to be in synchrony in order for the whitefish to successfully survive and grow into their next stage of life. Many factors can affect this harmony, including competitors such as invasive mussels, predators, and how winter and spring weather conditions are suitable for both plankton and fish larvae. GLERL’s research is used by fishery managers to determine how to manage sustainable and profitable fisheries in Lake Michigan and the other Great Lakes. Beach seining surveys of larval whitefish have become a critical clue on why fishery catches have dropped in the Great Lakes. This study is very important to fishery managers who are working to ensure Great Lakes fisheries are sustainable and profitable, and people are able to enjoy whitefish on their table for many years to come.

March 24, 2025
by GLERL Communications Team
Comments Off on Following the Great Lakes’ Most Unwanted

Following the Great Lakes’ Most Unwanted

GLANSIS Database Keeps Tabs on Biological Invaders

The mouth of an invasive sea lamprey, one of the most notorious Great Lakes invasive species. Photo credit: Dave Brenner, Michigan Sea Grant.

The Great Lakes are one of the most unique freshwater ecosystems in the world – but are also heavily threatened by biological invaders. Aquatic invasive and nuisance species are the plants and animals from other regions of the globe that accidentally get brought to the Great Lakes, potentially destroying the local ecosystem. Many species pose a significant threat to the Great Lakes environment and economy, from sea lamprey that devastate prized fisheries, zebra mussels that encrust underwater infrastructure, and aquatic weeds that entangle boat motors and swimmers alike. There are nearly 200 nonindigenous aquatic species currently present in the Great Lakes, many of which have significant environmental and socioeconomic impacts, and keeping track of them across the region is a daunting task. The Great Lakes Aquatic Nonindigenous Species Information System (GLANSIS) is designed to meet this challenge, providing a “one-stop shop” for comprehensive information about aquatic invaders.

GLANSIS is based out of NOAA’s Great Lakes Environmental Research Laboratory (GLERL) and is the Great Lakes hub of the USGS Nonindigenous Aquatic Species (NAS) database. According to Acting GLERL Director Dr. Jesse Feyen, “GLERL experts have long studied the impacts of current and potential invaders in the Great Lakes. As the long-standing home for GLANSIS, our goal is to get the message out about the significant risks they pose.” With funding from the Great Lakes Restoration Initiative (GLRI), the site provides the best available information to limit the introduction, spread, and impact of aquatic invasive species in the Great Lakes. GLANSIS provides a comprehensive set of tools including species profiles, a custom-generated list of invaders, a mapping tool, risk assessments, and more. While GLANSIS was originally designed for use by scientists and environmental managers, this publicly-accessible tool is used by teachers, students, anglers, property owners, and anyone who wants to learn more about stopping invasive species in the Great Lakes. Citizens and stakeholders can help protect their local waterways by learning how to recognize, report, and stop the spread of aquatic invasive species.

The Great Lakes’ Most Unwanted

As of 2025, GLANSIS maintains species profiles of 192 nonindigenous aquatic species that are successfully reproducing and overwintering in the Great Lakes, including fish, plants, invertebrates, algae, and even parasites and diseases. GLANSIS conducts a thorough risk assessment process on all species which facilitates direct comparisons of their impacts, as shown in a recent paper on the top 10 most impactful invaders published in the Journal of Great Lakes Research.

GLANSIS also hosts data on “watchlist” species – plants, animals, and pathogens that have not yet established lasting populations in the Great Lakes, but have been identified by experts as emerging threats. These include invasive silver and bighead carp, which have caused devastating ecological impacts to native fish and plants as they have expanded through other US waterways, as well as aquarium plants and pets like the self-cloning marbled crayfish, where even a single individual can launch a new invasive population.

Invasive silver carp are not reproducing and overwintering in the Great Lakes – yet. Photo credit: Dan O’Keefe, Michigan Sea Grant.

The GLANSIS team recently brought together more than a dozen invasive species experts for a real-time virtual review to provide new data on more than 50 non-native species that are either already present in the Great Lakes basin or have been identified as an emerging threat. These efforts ensure that the information in the database remains accurate, timely and relevant to environmental managers, educators, and other user groups who rely on GLANSIS for decision-making about aquatic invasive species.

To learn more about GLANSIS and explore the database yourself, visit https://www.glerl.noaa.gov/glansis/ or contact GLANSIS Program Manager Rochelle Sturtevant at rochelle.sturtevant@noaa.gov.

February 26, 2025
by Gabrielle Farina
Comments Off on NOAA GLERL director retires after 40-year career in managing America’s water resources

NOAA GLERL director retires after 40-year career in managing America’s water resources

After more than 40 years of civil service, Deborah Lee, NOAA Great Lakes Environmental Research Laboratory (GLERL) director, is retiring on February 28, 2025. Known for her passion for managing our nation’s water resources, Lee has been a dedicated and innovative steward of our nation’s freshwater, benefiting people, the environment, and the economy.

A GLERL hydrologist at the time, Lee stands at the NOAA GLERL sign with colleagues Frank Quinn, Tom Croley, and Dave Reid in the 1990s.

As an award-winning and nationally recognized engineer and professional hydrologist, Lee’s career was divided between time at NOAA and the U.S. Army Corps of Engineers. Early in her career she served as a hydrologist at NOAA GLERL and then for the NOAA National Weather Service (NWS) Ohio River Forecast Center. Her leadership and management skills grew and were acknowledged during her time with the U.S. Army Corps of Engineers where she served as Chief of the Water Management of the Great Lakes and Ohio River Division and as its Acting Regional Business Director.

Lee is awarded a Superior Civilian Service Award on her last day serving at the U.S. Army Corps of Engineers.

As GLERL director over the past ten years, Lee applied her expertise in the region to create partnerships that accelerated GLERL’s research to application on some of the Great Lakes most pressing issues. She oversaw the transitioning from research to operations of NOAA’s Harmful Algal Bloom (HAB) forecast to NOAA’s National Centers for Coastal Ocean Science, and of the Great Lakes Operational Forecast System (GLOFS) to NOAA’s Center for Operational Oceanographic Products and Services. The GLOFS is used by NWS to predict Great Lakes water levels, temperature, currents and waves in its marine forecasts, and by the U.S. Coast Guard for search and rescue operations. She also fostered GLERL’s ‘Omics program and the important research that predicted the potential impact to the fishery from invasive carp. 

Lee celebrates the 50th anniversary of NOAA’s Great Lakes Environmental Research Laboratory in 2024.

Lee’s legacy reaches far beyond NOAA. First, with her position as Regional Team Lead for NOAA’s Great Lakes Regional Collaboration Team, she represented NOAA in the execution of the binational Great Lakes Water Quality Agreement with Canada and led NOAA’s mission under the Great Lakes Restoration Initiative where she built several successful regional coalitions across the U.S. and Canada and with private industry. Her creativity, adaptability and resilience helped her align these program efforts with NOAA’s vision, mission, and goals in partnering with stakeholders inside and outside of NOAA. She also served as the U.S. Co-chair of the International Joint Commission’s Science Advisory Board’s Research Coordination Committee. Always open to new and challenging assignments, Lee took on the leadership roles as the Co-chair of the Aquatic Nuisance Species Task Force and as Senior Advisor to the National Invasive Species Council.

Lee receives Lifetime Achievement Award from the Environmental & Water Resources Institute of the American Society of Civil Engineers in 2024.

Lee has been recognized with numerous professional awards throughout her career, including The Ohio State University Distinguished Alumni Award, the American Society of Civil Engineers Environmental Water Resources Institute Lifetime Achievement Award and President’s Medal, and nominated by Eminence to the American Academy of Water Resources Engineers.

Join us in thanking Director Lee for her profound impact on NOAA Research and the Great Lakes region throughout her remarkable career!