This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
Sea Level Rise and Climate: Impacts on the Greater Everglades Ecosystem and Restoration
The Greater Everglades Ecosystem covers much of south Florida, and the highest areas are only a few meters above sea level. Predictions of sea level rise and changes in storm intensity for the 21st century are particularly concerning to the urban population of Miami and the east coast, but also represent a challenge to Everglades National Park and Biscayne National Park resource managers. The Greater Everglades Ecosystem is undergoing a large-scale restoration effort and decisions need to be made that will affect the system for the next 20 to 30 years. Our project is designed to examine responses of the ecosystem to past sea level and climate changes to better understand coastal resiliency.
Project Lead: G. Lynn Wingard
FBGC Project Members: Miriam Jones, Bethany Stackhouse, Sarah Bergstresser, Kristen Hoefke, Bryan Landacre, Christopher Bernhardt
Other USGS Project Members: Andre Daniels, Marci Marot
Collaborator: Anna Wachnicka (FIU / SFWMD)
The urban and natural landscapes of south Florida are vulnerable to flooding from sea level rise and coastal storm surges for several reasons, including low elevation, lack of topographic relief to promote drainage, and a water table that is at or very close to the land surface. With the current rate of relative sea level rise in south Florida estimated to be between 2.4-3.7 mm/year and rising, it is vital for urban planners and resource managers to understand how vulnerable the coast is to retreat and inundation.
Understanding how the natural (pre-human alteration) environment of south Florida has responded to previous changes in sea level and climate variability is an important first step to predicting what will happen over the next century. What factors make the coast more resilient? What are the most important drivers of coastal change? What is the role of mangroves and coastal vegetation in coastal resiliency? The answers to these questions can be found by studying the record preserved in sediment cores collected throughout south Florida. The layers in the cores are analyzed for physical and biological clues that tell us how the environment has changed over time. The sequence of changes seen in the cores provides information about the factors that drive these changes, such as fluctuations in storm frequency or strength, increased or decreased sea level, or loss of key species such as mangroves and sea grass beds.
An important part of interpreting past environmental history in cores is understanding how physical and biological processes interact in the present and what are the ecological requirements of key species. By studying the present, we are better able to interpret the past record in the cores, which in turn can give us insights into what the future will look like. An especially important factor in coastal change in south Florida are hurricanes, and since 1888 twenty-one major hurricanes (category 3 or above on the Saffir-Simpson scale) have made landfall within an approximately 100-mile radius of Florida Bay, where many of our cores are located. Detailed scientific investigations have been conducted following a few of these storms, and this information provides us with a means to look at the decadal-scale impacts of storms on the coastline. In September 2017, Hurricane Irma passed just west of our field sites, giving us a first-hand look at the immediate impact of storms on the mangrove coastline. By combining our observations of ongoing changes in the coastline with the 3000 to 5000 year record preserved in our cores, we are providing resource managers and urban planners with a better understanding of the natural processes of coastal change, the rates of response of the system to these changes, and what factors contribute to coastal resiliency.
Below are other science projects associated with this project.
Determining Target Salinity Values for Restoration of the Estuaries of the Greater Everglades
Below are databases associated with this project.
2008 - Present Ecosystem History of South Florida's Estuaries Database (ver. 2.0, June 2022)
Below are multimedia items associated with this project.
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
In Photo: Interior mudflat on Jim Foot Key covered with saline water, April 2019. Stumps of dead mangroves (reportedly damaged by Hurricane Donna in 1960 (Craighead, 1962)) are visible projecting from the water. Shadowed areas below the water are underwater grasses typically found in Florida Bay, now growing inside
In Photo: Interior mudflat on Jim Foot Key covered with saline water, April 2019. Stumps of dead mangroves (reportedly damaged by Hurricane Donna in 1960 (Craighead, 1962)) are visible projecting from the water. Shadowed areas below the water are underwater grasses typically found in Florida Bay, now growing inside
In Photo: Juvenile mangroves on eastern berm of Jim Foot Key, April 2019. Mangroves are intermingled with saltwort, the dominant live vegetation on the damaged berms, and standing dead mangroves. Grid is 25 cm high. The question is whether these trees will mature fast enough to protect the berm from rising sea level.
In Photo: Juvenile mangroves on eastern berm of Jim Foot Key, April 2019. Mangroves are intermingled with saltwort, the dominant live vegetation on the damaged berms, and standing dead mangroves. Grid is 25 cm high. The question is whether these trees will mature fast enough to protect the berm from rising sea level.
In Photo: Berm of Jim Foot Key about 1.5 years after Hurricane Irma. The red circle indicates the same position as shown in the April 2014 photo. The mature mangrove trees have not recovered from the storm.
In Photo: Berm of Jim Foot Key about 1.5 years after Hurricane Irma. The red circle indicates the same position as shown in the April 2014 photo. The mature mangrove trees have not recovered from the storm.
In Photo: Eastern berm of Jim Foot Key, April 2019. This photo taken from Florida Bay, looking in toward the center of the island (now covered in water). The arrow points toward a breach in the berm, first noted in 2014, but the cut has deepened significantly after Hurricane Irma, and the island interior
In Photo: Eastern berm of Jim Foot Key, April 2019. This photo taken from Florida Bay, looking in toward the center of the island (now covered in water). The arrow points toward a breach in the berm, first noted in 2014, but the cut has deepened significantly after Hurricane Irma, and the island interior
In Photo: The red circle indicates the same position as shown in the April 2014 photo. The mangroves have lost all their leaves and the berm is significantly thinner following the storm.
In Photo: The red circle indicates the same position as shown in the April 2014 photo. The mangroves have lost all their leaves and the berm is significantly thinner following the storm.
In Photo: View south/southeast along eastern shoreline in April 2014 shows a dense berm of mangrove trees. The bay is not visible.
In Photo: View south/southeast along eastern shoreline in April 2014 shows a dense berm of mangrove trees. The bay is not visible.
Below are publications associated with this project.
Climate, sea level, and people - Changing South Florida's mangrove coast
Impacts of Hurricane Irma on Florida Bay Islands, Everglades National Park, U.S.A.
Rapid inundation of the southern Florida coastline despite low relative sea-level rise rates during the late-Holocene
The role of paleoecology in restoration and resource management—The past as a guide to future decision-making: Review and example from the Greater Everglades Ecosystem, U.S.A
Application of molluscan analyses to the reconstruction of past environmental conditions in estuaries
Biological indicators of changes in water quality and habitats of the coastal and estuarine areas of the Greater Everglades Ecosystem; Chapter 11
Estimates of natural salinity and hydrology in a subtropical estuarine ecosystem: implications for Greater Everglades restoration
Integrated conceptual ecological model and habitat indices for the southwest Florida coastal wetlands
Impact of Late Holocene climate variability and anthropogenic activities on Biscayne Bay (Florida, U.S.A.): Evidence from diatoms
Florida Bay salinity and Everglades wetlands hydrology circa 1900 CE: A compilation of paleoecology-based statistical modeling analyses
Application of a weighted-averaging method for determining paleosalinity: a tool for restoration of south Florida's estuaries
Climate variability during the Medieval Climate Anomaly and Little Ice Age based on ostracod faunas and shell geochemistry from Biscayne Bay, Florida
The Greater Everglades Ecosystem covers much of south Florida, and the highest areas are only a few meters above sea level. Predictions of sea level rise and changes in storm intensity for the 21st century are particularly concerning to the urban population of Miami and the east coast, but also represent a challenge to Everglades National Park and Biscayne National Park resource managers. The Greater Everglades Ecosystem is undergoing a large-scale restoration effort and decisions need to be made that will affect the system for the next 20 to 30 years. Our project is designed to examine responses of the ecosystem to past sea level and climate changes to better understand coastal resiliency.
Project Lead: G. Lynn Wingard
FBGC Project Members: Miriam Jones, Bethany Stackhouse, Sarah Bergstresser, Kristen Hoefke, Bryan Landacre, Christopher Bernhardt
Other USGS Project Members: Andre Daniels, Marci Marot
Collaborator: Anna Wachnicka (FIU / SFWMD)
The urban and natural landscapes of south Florida are vulnerable to flooding from sea level rise and coastal storm surges for several reasons, including low elevation, lack of topographic relief to promote drainage, and a water table that is at or very close to the land surface. With the current rate of relative sea level rise in south Florida estimated to be between 2.4-3.7 mm/year and rising, it is vital for urban planners and resource managers to understand how vulnerable the coast is to retreat and inundation.
Understanding how the natural (pre-human alteration) environment of south Florida has responded to previous changes in sea level and climate variability is an important first step to predicting what will happen over the next century. What factors make the coast more resilient? What are the most important drivers of coastal change? What is the role of mangroves and coastal vegetation in coastal resiliency? The answers to these questions can be found by studying the record preserved in sediment cores collected throughout south Florida. The layers in the cores are analyzed for physical and biological clues that tell us how the environment has changed over time. The sequence of changes seen in the cores provides information about the factors that drive these changes, such as fluctuations in storm frequency or strength, increased or decreased sea level, or loss of key species such as mangroves and sea grass beds.
An important part of interpreting past environmental history in cores is understanding how physical and biological processes interact in the present and what are the ecological requirements of key species. By studying the present, we are better able to interpret the past record in the cores, which in turn can give us insights into what the future will look like. An especially important factor in coastal change in south Florida are hurricanes, and since 1888 twenty-one major hurricanes (category 3 or above on the Saffir-Simpson scale) have made landfall within an approximately 100-mile radius of Florida Bay, where many of our cores are located. Detailed scientific investigations have been conducted following a few of these storms, and this information provides us with a means to look at the decadal-scale impacts of storms on the coastline. In September 2017, Hurricane Irma passed just west of our field sites, giving us a first-hand look at the immediate impact of storms on the mangrove coastline. By combining our observations of ongoing changes in the coastline with the 3000 to 5000 year record preserved in our cores, we are providing resource managers and urban planners with a better understanding of the natural processes of coastal change, the rates of response of the system to these changes, and what factors contribute to coastal resiliency.
Below are other science projects associated with this project.
Determining Target Salinity Values for Restoration of the Estuaries of the Greater Everglades
Below are databases associated with this project.
2008 - Present Ecosystem History of South Florida's Estuaries Database (ver. 2.0, June 2022)
Below are multimedia items associated with this project.
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
This video highlights paleoecology and ecosystems restoration science being conducted by the USGS Florence Bascom Geoscience Center (FBGC).
In Photo: Interior mudflat on Jim Foot Key covered with saline water, April 2019. Stumps of dead mangroves (reportedly damaged by Hurricane Donna in 1960 (Craighead, 1962)) are visible projecting from the water. Shadowed areas below the water are underwater grasses typically found in Florida Bay, now growing inside
In Photo: Interior mudflat on Jim Foot Key covered with saline water, April 2019. Stumps of dead mangroves (reportedly damaged by Hurricane Donna in 1960 (Craighead, 1962)) are visible projecting from the water. Shadowed areas below the water are underwater grasses typically found in Florida Bay, now growing inside
In Photo: Juvenile mangroves on eastern berm of Jim Foot Key, April 2019. Mangroves are intermingled with saltwort, the dominant live vegetation on the damaged berms, and standing dead mangroves. Grid is 25 cm high. The question is whether these trees will mature fast enough to protect the berm from rising sea level.
In Photo: Juvenile mangroves on eastern berm of Jim Foot Key, April 2019. Mangroves are intermingled with saltwort, the dominant live vegetation on the damaged berms, and standing dead mangroves. Grid is 25 cm high. The question is whether these trees will mature fast enough to protect the berm from rising sea level.
In Photo: Berm of Jim Foot Key about 1.5 years after Hurricane Irma. The red circle indicates the same position as shown in the April 2014 photo. The mature mangrove trees have not recovered from the storm.
In Photo: Berm of Jim Foot Key about 1.5 years after Hurricane Irma. The red circle indicates the same position as shown in the April 2014 photo. The mature mangrove trees have not recovered from the storm.
In Photo: Eastern berm of Jim Foot Key, April 2019. This photo taken from Florida Bay, looking in toward the center of the island (now covered in water). The arrow points toward a breach in the berm, first noted in 2014, but the cut has deepened significantly after Hurricane Irma, and the island interior
In Photo: Eastern berm of Jim Foot Key, April 2019. This photo taken from Florida Bay, looking in toward the center of the island (now covered in water). The arrow points toward a breach in the berm, first noted in 2014, but the cut has deepened significantly after Hurricane Irma, and the island interior
In Photo: The red circle indicates the same position as shown in the April 2014 photo. The mangroves have lost all their leaves and the berm is significantly thinner following the storm.
In Photo: The red circle indicates the same position as shown in the April 2014 photo. The mangroves have lost all their leaves and the berm is significantly thinner following the storm.
In Photo: View south/southeast along eastern shoreline in April 2014 shows a dense berm of mangrove trees. The bay is not visible.
In Photo: View south/southeast along eastern shoreline in April 2014 shows a dense berm of mangrove trees. The bay is not visible.
Below are publications associated with this project.