Impacts of Sea Level Rise on the Everglades Mangrove Forest

A Comparative GIS Study 2006-2011

Introduction

Mangroves forests are an integral part of the Florida coastline and Everglades ecosystem

Mangroves are highly productive ecosystems that serve as an estuarine habitat for a multitude of fish, bird, mammal and other species in Everglades National Park (1). The three species of mangrove that are common to intertidal zones of South Florida, the Caribbean, and the Gulf of Mexico are black mangrove (Avicennia germinans), white mangrove (Laguncularia racemosa), and red mangrove (Rhizophora mangle) (2). All three species are present in the Everglades National Park mangrove forest, which is one of the largest continuous mangrove forests in United States (10).

Mangrove forests help reduce the impacts of coastal erosion and storm surge from extreme weather events such as hurricanes and tsunamis (17). They are biogeochemically important to protection of other Everglades ecosystems and to the surrounding region due to their capacity to accumulate sediment, nutrients and contaminants and their ability to capture and store carbon (24). Mangroves serve as critical breeding habitat and nursery grounds for numerous crustaceans, fish, birds, reptiles (1, 14).

Juvenile lemon shark swimming through mangroves. Photo credit: https://ocean.si.edu/ocean-life/sharks-rays/young-lemon-shark-swims-through-mangroves

Research has indicated inland migration of Everglades mangrove forests during the late Holocene due to sea level rise

Multiple studies have indicated that sea level rise and warming waters during the late Holocene (period of last 11,700 years, including the present) have effectively drowned mangroves living directly on the shoreline (1, 6, 8, 12, 13, 20). The same studies also found that mangrove forests have expanded in size and migrated inland, with other types of estuarine wetland covering areas that were previously inhabited by mangroves (1, 2, 3, 6, 7, 10, 14, 15, 18, 20, 23, 24, 28). This was clearly shown in a time series Landsat study of Everglades National Park from 1985-2017 where there was a total cumulative increase of mangrove coverage of 10.2%, with coastal decreases in mangrove coverage in years of hurricanes (10).

Since mangroves are halophytes, they are able to tolerate changes in salinity and tidal stress, making them more readily able to adapt to changing habitat conditions caused by sea level rise and salt water intrusion (2). Mangroves have been observed to be able to build up peat soil with some levels of sea level rise, managing additional saltwater intrusion for a time; as sea level rise accelerates, salt water overwhelms both the mangroves and the ecosystems they protect (22, 1). As sea levels continue to rise over time, saturation occurs and salinity conditions increase in coastal areas, resulting in mangroves to migrate inland into areas of the Everglades that were previously freshwater marsh ecosystems and other types of wetlands habitats.

Mangroves in Everglades National Park. Photo credit: https://www.fondriest.com/news/carbon-everglades-national-park-mangroves-valued-billions.htm  

The Everglades are especially vulnerable to sea level rise

The recent Comprehensive Everglades Restoration Plan notes that the Everglades are especially vulnerable to sea level rise since its flat landscape is only about a 5 cm increase in elevation per linear kilometer inland (23). With this topography and changes in salinity that occur with sea level rise, different types of wetland habitat, such as sawgrass marsh, have been observed to migrate seaward as mangroves have migrated inland (7, 23, 27). It is estimated that the mangrove forest within the Everglades has moved inland at least 3 km on average due to sea level rise since the 1940s (23). Studies that modeled future sea level rise impacts using GIS data showed that under continued sea level rise conditions, freshwater marsh habitat will continue to decrease by 20-30% and mangroves will migrate approximately 15 km inland (6).

Other variables exacerbate impacts of sea level rise on mangroves in the Everglades

Research provides evidence for the overall resilience of tidal wetlands that can adapt with saline fluctuations in response to sea level rise, including mangrove forests, and the resulting landward migration of mangroves may be how tidal wetland habitats are adapting in order to continue to persist in the Everglades (3). Studies further indicate that other variables such as hurricanes, temperature, increased atmospheric CO2 and precipitation have exacerbated the impacts of mangrove migration due to sea level rise (1, 10, 13, 14, 23). Mangrove forests and other wetland ecosystems of the Everglades National Park have also been impacted by other external stressors such as hydrological modifications for flood control and agricultural runoff impacts. (11, 22)

The purpose of this study is to investigate the impacts of sea level rise on the mangrove forest of Everglades National Park using GIS data

Study Area

Click on Study Area marker above to expand map and view Study Area information.

Methods and Results

Landsat data was retrieved from Earth Explorer for study analysis. Photo Credit: https://earthexplorer.usgs.gov/

An in-depth literature review was conducted to examine the impacts of sea level rise on Everglades National Park, Southern Florida, and other areas with similar topographic and climate conditions with large mangrove forests. To analyze the impacts of sea level rise on the mangrove forest of Everglades National Park over time, Landsat 5 datasets from 2006 and Landsat 7 datasets from 2011 were downloaded from from USGS Earth Explorer and clipped to the Everglades National Park boundary (25, 26, 5). Landsat data from 2006 and 2011 were selected for comparison due to availability of data with similar seasonality to limit variability in precipitation and vegetation health. Landsat data and NOAA Sea Level Rise Viewer data were used to perform various analyses in ArcGIS Pro 2.7 to evaluate migration and health of mangrove habitat over time in comparison to sea level rise, including:

  • Vegetation Analysis Combination Banding
  • Unsupervised and Supervised Classifications
  • NDVI
  • NPS Mangrove Habitat layer comparison (4)
  • Raster Calculator to Generate Supervised Classification and NDVI Difference Images
  • Reclassification of Difference Images to Generate Change/No Change Images

NOAA Sea Level Data from Sea Level Rise Viewer

Examining Sea Level Rise within the Everglades National Park Study Area

Current mean higher high water levels in NOAA Sea Level Rise Viewer were used to determine sea level rise impacts to the Everglades mangrove forest.

Sea Level Rise and Potential Coastal Flooding

This map displays sea level rise data and potential coastal flooding in the Everglades National Park area from NOAA's Sea Level Rise Viewer.

Sea level rise has impacted coastal areas within the Everglades National Park study area and will likely be further impacted by coastal flooding, as indicated in blue.

Potential Marsh Migration Due to Sea Level

Many studies have shown the migration of different types of marshes in the Everglades due to sea level rise, including inland migration of the mangrove forest. NOAA Sea Level Rise Viewer marsh migration data shows evidence of this migration, including mangrove forest data that is included in areas shown in magenta. Notice that the magenta overlaps with the dark blue area indicating the marsh ecosystem will be impacted by sea level rise and migration or accretion over time, depending on severity of flooding.

Mapping Confidence in Sea Level Rise Data

This NOAA Sea Level rise map displays the confidence in sea level rise data. The yellow areas with strong confidence in sea level rise corresponds with mangrove habitat in the study area.

Mangrove Habitat Analyses of Landsat Data in ArcGIS Pro 2.7

2006 Landsat 5 RGB Image

To further analyze the impacts of sea level change on the mangrove forest of Everglades National Park over time, Landsat datasets for two different years were downloaded from USGS Earth Explorer. This image is a 2006 Landsat 5 RGB image for South Florida clipped to the Everglades National Park boundary. Cloud cover can be seen in white, areas with heavy vegetation (including mangroves) can be see in dark green.

2011 Landsat 7 RGB Image

This image is a 2011 Landsat 7 RGB image for South Florida clipped to the Everglades National Park boundary. Again, areas with heavy vegetation (including mangroves) can be see in dark green, and other types of vegetation and other land cover (such as bare land) in tan and reddish tones.

2006 Landsat 5 Vegetation Analysis

To get a better understanding of where vegetation and mangrove habitat existed within the Everglades, a vegetation analysis was performed using band combinations specific to Landsat to highlight peak vegetation vigor and biomass content and shorelines. Areas with high coastal biomass and peak vigor can be seen in red. Water areas can be seen in blue.

2006 Landsat 5 Vegetation Analysis

Like the 2006 Landsat data, a vegetation analysis was performed on the 2011 Landsat data using band combinations to highlight peak vegetation vigor and biomass content and shorelines. Areas with high coastal biomass and peak vigor can be seen in red. Water areas can be seen in blue.

2006 Landsat 5 Supervised Classification

To further determine change in mangrove forest cover that may be related to sea level rise, a supervised classification of both Landsat images was performed. Different types of land cover classes are visualized as the following: water in blue, mangrove habitat in sawgrass/seagrass in brown, clouds in light gray, shadows in dark gray, vegetation/wetlands in green, and barren land in magenta. Mangroves (in yellow), can be observed along the coastline. Some mangrove habitat may have been classified as vegetation.

2011 Landsat 7 Supervised Classification

The supervised classification of the 2011 Landsat 7 image used the same types of land cover classes as the 2006 Landsat 5 image supervised classification: water in blue, mangrove habitat in sawgrass/seagrass in brown, clouds in light gray, shadows in dark gray, vegetation/wetlands in green, and barren land in magenta. Mangrove habitat (in yellow), along the coastline notably expanded in size, and also migrated inland. Sawgrass/seagrass land cover expanded and migrated into coastal areas where mangroves had been dominant. Barren land cover areas inland also increased.

2006 LandSat5 NDVI Custom Stretch

To measure the health of vegetation over time, the Normalized Difference Vegetation Index was calculated from the visible and near-infrared light that is reflected from vegetation. Healthy vegetation can be seen in green, while less healthy to unhealthy or scarce vegetation can be seen in yellow to red. In 2006, NDVI shows the Everglades area to have largely healthy vegetation with large areas of green, and some areas of less healthy vegetation that correspond with bare ground cover from the supervised classification. It should be noted that some areas in red correspond with cloud cover.

2011 LandSat7 NDVI Custom Stretch

In 2011, NDVI showed a change in the health of vegetation in the Everglades. Areas that were found to be largely classified as mangrove habitat appear healthy (in green). Other inland land cover areas appear to have decreased in vegetation health, including areas that were classified as sawgrass/seagrass habitat that migrated towards the coast. Areas with poor health also include those classified as barren land cover. Coastal water areas appear red due to lack of vegetation.

NDVI Difference

This image is the calculated raster image between the 2006 NDVI and 2011 NDVI, showing the change in vegetation health over time. It was reclassified to create a change/no change image.

Comparing Images with Present Mangrove Forest

Supervised Classification Change/No Change 2006-2011

Differences between land use classes were calculated using image attribute tables and the raster calculator to visualize the difference in a change/no change image. The areas in red show land cover that changed in class between 2006-2011, and areas in yellow show land cover that had no change.

To compare the change of land cover with the overall change mangrove habitat over time, the current mangrove habitat layer from Esri was added (in green with 50% transparency) to the supervised classification change/no change layer. Though some of the areas near the coast overlap with areas of no change (yellow), many of the areas that are inland overlap with areas of change (red).

Swipe to view compare change from 2006-2011 with mangrove habitat layer

NDVI Change/No Change 2006-2011

To better interpret the calculated difference between the 2006 and 2011 NDVI analyses, the NDVI change image was reclassified to show only change or no change in vegetation health. There was a significant amount of change in vegetation health across the entire Everglades area, including the mangrove habitat area.

When comparing the current mangrove habitat layer (50% transparency in green) to the NDVI change/no change image, it appears that current mangrove habitat is located in areas that did not experience a change in vegetation health.

Swipe to view compare change from 2006-2011 with mangrove habitat layer

Results Displayed in ArcGIS Maps

Maps were created in ArcGIS Pro to compare and contrast results.

In addition to the vegetation analysis performed using Landsat band combinations and the supervised classification, an unsupervised classification was performed. Areas in the vegetation analyses that indicated vegetation corresponded heavily with areas classified as mangrove land cover in the unsupervised classifications. The unsupervised classification also showed an inland migration of mangrove habitat, as well as an expansion and coastal migration of sawgrass/seagrass, and increase of bare ground cover.

Overall land cover change as calculated between the two images:

Water: -23.05%

Vegetation: -10%

Mangrove habitat: 21.2%

Bare ground: 4.44%

Sea grass: 10.16%

As was found in the unsupervised classification, the mangrove habitat land cover area expanded in size and migrated inland. The sawgrass/seagrass area also expanded, and migrating into areas that historically have been primarily mangrove forest. Barren land cover also expanded, which also corresponds with the NDVI analyses and change in vegetation health in the same areas.

Overall land cover change as calculated between the two images:

Water: 38.4%

Barren: 14.9%

Vegetation/Wetlands: -68.9%

Seagrass: 219%

Clouds: 101%

Mangroves: 88.4%

Shadows: -21.4%

Mapping the different the Normalized Difference Vegetation Index analyses together, it is clear there is a significant reduction in healthy vegetation between 2006-2011 in the Everglades. Areas of healthy vegetation that remain in 2011 overlap with areas of mangrove forest, and areas that have decreased in vegetation overlap with changes inland to land cover classes that include decreases in wetlands, increases in sawgrass/seagrass, and increases in barren land.

Change/no change images that were derived from both the supervised classification and NDVI difference images show change in red. Between 2006-2011, there was a significant amount of change in land cover in the Everglades (most of the land within the boundary experienced a change in land cover). There was also a significant amount of change in vegetation health between 2006-2011, whether the change was an increase or decrease. When the change/no change images are compared with current mangrove habitat (in transparent green), it appears that mangrove habitat overlaps with areas of change in the supervised classification image and areas of no change in the NDVI image.

Discussion

Does sea level rise have an impact on mangrove habitat in the Everglades?

Similar to the results presented in previous research, results from this study indicate that sea level rise impacts the mangrove forest within the Everglades National Park. According to NOAA sea level rise data, areas of mangrove forest habitat are impacted by sea level rise and marsh migration. Between the years of 2006 to 2011, the areas of mangrove land cover increased based on both unsupervised and supervised classification analyses. Mangrove land cover also migrated inland based on these same analyses.

As mangrove habitat within the park boundary expanded inland over time, mangroves appear to be moving into areas historically inhabited by other types of vegetation. Land cover change comparisons with the current mangrove forest area indicate that the mangrove forest exists in areas that have changed land cover class over time, and continues to move. Similarly, in coastal areas once inhabited by mangroves, other wetland marsh habitats such as sawgrass have increased , confirming previous research from other studies. From 2006-2011, wetland areas of vegetation decreased within the Everglades, while barren land cover areas increased. Based on previous research, both are a likely result of sea level rise impacts and salt water intrusion, or other hydrological impacts from recent flood control modifications.

Aerial view of Everglades National Park. Photo credit: AdobeStock_356530515.jpeg (Everglades National Park)

Mangrove forest land cover increased during the study period, and the health of the mangroves seemed to remain consistent over time as indicated by NDVI analyses. Despite mangroves maintaining health during the study period, health of other wetland communities including sawgrass marsh declined. Inland vegetation declined the greatest along with an increase in barren land cover. NDVI analyses indicated a decrease in overall health of Everglades vegetation during the study period, likely due to sea level rise and other variables, as was described in previous research. When changes in vegetation health were compared to the current mangrove forest, mangrove areas corresponded primarily with areas of no change over time, confirming their adaptability to changing conditions within the Everglades despite migration and sea level rise impacts.

Considerations that impact the results of the study

This study only compared two years of Landsat data (although a study in the literature review with Landsat data from 1985-2017 and had similar conclusions) (10). The analysis was limited to consideration of sea level rise and vegetation health, and did not consider other variables that could impact mangroves including hurricanes, precipitation, temperature and atmospheric CO2. Sampling error in supervised classifications should also be considered, along with the acknowledgment that there may have been classes that were not identified or included.

Conclusion

The Everglades mangrove forest is an important natural resource that needs to be protected to help mitigate the impacts of sea level rise and climate change

As sea levels rise, mitigation efforts should be taken to prevent further flooding of coastal mangrove forests to avoid further inundation from saltwater intrusion. Since mangroves serve as a coastal buffer to erosion and storm surge, and they absorb nutrients and contaminants that otherwise would filter into the Everglades ecosystem, it is crucial that the loss of coastal mangrove forest cover is attenuated as sea level continues to rise. It is also important to consider as overall vegetation health of the Everglades National Park has declined over time, with salt water intrusion from sea level rise being a key factor.

Picture Credit: AdobeStock_405377962.jpeg (Everglades National Park)

Environmental management of the Everglades will need to adapt as mangroves and other tidal wetlands adapt

As the mangrove forests migrate, preservation efforts should continue and adapt as the mangrove forest area adapts with sea level rise over time. Research has shown that the mangrove forest of Everglades National Park has migrated inland in response to sea level rise, as this study also indicates. Other types of plant ecosystems have migrated seaward, like sawgrass marsh. Both have implications for plant and animal species living in those ecosystems, and for the Everglades ecosystem as a whole.

Sea level rise and the migration of mangroves also has significant consequences on the freshwater balance of the Everglades. Environmental managers of the park will need to consider sea level rise and climate change impacts in their management decisions for restoration, conservation, and preservation efforts. The current Comprehensive Everglades Restoration Plan includes plans to improve bringing freshwater distribution to the Everglades region for habitat restoration purpose, with considerations to combat saltwater intrusion from sea level rise (23).

Further research needs to be done to fully understand the impacts of temperature, hurricanes, and precipitation in concert with sea level rise

Previous research indicated that the impacts of sea level rise could be further exacerbated by variables such as temperature, hurricanes, precipitation and atmospheric CO2 (1, 10, 13, 14, 23). Impacts of climate change will likely cause fluctuations in many of these variables that should be considered along with sea level rise to fully understand the adaptability of the Everglades mangrove forest to sea level rise and other climate impacts. With the importance of the mangrove as buffer, filter, and habitat, further determining the stability and adaptability of the mangrove forest of Everglades National Park to the impacts of climate change may prove critical to mitigating the impacts of sea level rise for its ecosystem and the surrounding region.

Sunset at Everglades National Park. Photo credit: AdobeStock_112157455.jpeg (Everglades National Park)

References

1.    Alongi, D. M. (2015). The impact of climate change on mangrove forests. Current Climate Change Reports, 1(1), 30-39. doi:10.1007/s40641-015-0002-x

2.    Doyle, T. (1994, January 01). Predicting future mangrove forest migration in the Everglades under rising sea level. Retrieved April 30, 2021, from https://pubs.er.usgs.gov/publication/fs03003

3.    Enwright, N. M., Griffith, K. T., & Osland, M. J. (2016). Barriers to and opportunities for landward migration of coastal wetlands with sea-level rise. Frontiers in Ecology and the Environment, 14(6), 307-316. doi:10.1002/fee.1282

4.    ESRI. U.S. Mangrove_Florida. Produced 2014. Web. April 21, 2021  https://services1.arcgis.com/B4MnusZHL3vmqU3t/arcgis/rest/services/Mangrove_Florida/FeatureServe 

5.    ESRI. U.S. Everglades National Park Boundary. Produced 2014. Web. April 21, 2021  https://services.arcgis.com/FvF9MZKp3JWPrSkg/arcgis/rest/services/Everglades_national_park_boundaries_WFL1/FeatureServer 

6.    Flower, H., Rains, M., & Fitz, C. (2017). Visioning the FUTURE: SCENARIOS modeling of the Florida Coastal Everglades. Environmental Management, 60(5), 989-1009. doi:10.1007/s00267-017-0916-2

7.    Foster, A. T., III, Tiling-Range, G., & Jones, J. (2013, July 24). Dynamics of mangrove-marsh ecotones in subtropical coastal wetlands: Fire, sea-level rise, and water levels. Retrieved April 30, 2021, from  https://pubs.er.usgs.gov/publication/70047188            

8.    Geselbracht, L., Freeman, K., Kelly, E., Gordon, D., & Birch, A. (2013). Retrospective Analysis and Sea Level Rise Modeling of Coastal Habitat Change in Charlotte Harbor to Identify Restoration and Adaptation Priorities. Florida Scientist, 76(2), 328-355. doi:https://www.jstor.org/stable/24321887

9.    Gramling, C. (2019, August 21). A freshwater, saltwater tug-of-war is eating away at the everglades. Retrieved May 14, 2021, from https://www.sciencenews.org/article/florida-everglades-freshwater-saltwater-sea-level-rise

10. Han, X., Feng, L., Hu, C., & Kramer, P. (2018). Hurricane‐Induced changes in the Everglades National Park Mangrove Forest: Landsat observations between 1985 and 2017. Journal of Geophysical Research: Biogeosciences, 123(11), 3470-3488. doi:10.1029/2018jg004501

11. Jerath, M., Bhat, M., Rivera-Monroy, V. H., Castañeda-Moya, E., Simard, M., & Twilley, R. R. (2016). The role of ECONOMIC, policy, and ecological factors in estimating the value of carbon stocks in Everglades mangrove forests, South Florida, USA. Environmental Science & Policy, 66, 160-169. doi:10.1016/j.envsci.2016.09.005

12. Jones, M., Wingard, G., Stackhouse, B., Keller, K., Willard, D., Marot, M., . . . Bernhardt, C. (2019, July 19). Rapid inundation of southern Florida Coastline despite low relative sea-level Rise rates during the late-Holocene. Retrieved April 30, 2021, from https://www.nature.com/articles/s41467-019-11138-4

13. Koch MS;Coronado C;Miller MW;Rudnick DT;Stabenau E;Halley RB;Sklar FH;. (n.d.). Climate change projected effects on coastal foundation communities of the GREATER Everglades using a 2060 scenario: Need for a new management paradigm. Retrieved April 30, 2021, from https://pubmed.ncbi.nlm.nih.gov/25312295/

14. Krauss, K. W., From, A. S., Doyle, T. W., Doyle, T. J., & Barry, M. J. (2011). Sea-level rise and landscape change INFLUENCE Mangrove encroachment onto Marsh in the ten Thousand Islands region of Florida, USA. Journal of Coastal Conservation, 15(4), 629-638. doi:10.1007/s11852-011-0153-4

15. Krauss, K. W., McKee, K. L., Lovelock, C. E., Cahoon, D. R., Saintilan, N., Reef, R., & Chen, L. (2013). How mangrove forests adjust to rising sea level. New Phytologist, 202(1), 19-34. doi:10.1111/nph.12605

16. Kumaran, K. P., Limaye, R. B., & Padmalal, D. (2013). Mangrove responses to climate change along the southwestern coast of India during Holocene: Evidence from palynology and geochronology. Climate Change and Island and Coastal Vulnerability, 217-238. doi:10.1007/978-94-007-6016-5_15

17. Mangroves to the rescue! (n.d.). Retrieved April 30, 2021, from https://www.nps.gov/features/ever/climatechange/ever702/#:~:text=Mangroves%20are%20the%20first%20responders,Center%20and%20Everglades%20National%20Park.&text=Higher%20temperatures%20and%20more%20carbon,to%20stimulate%20growth%20in%20mangroves.

18. Meeder, J., & Parkinson, R. (2018, March 01). SE saline EVERGLADES TRANSGRESSIVE sedimentation in response to Historic acceleration in Sea-level Rise: A viable marker for the base of the Anthropocene? Retrieved April 30, 2021, from https://meridian.allenpress.com/jcr/article-abstract/34/2/490/28021

19. NOAA Sea Level Rise Viewer. (2020). Retrieved April 30, 2021, from https://coast.noaa.gov/slr/

20. Rising sea levels could Accelerate Florida Bay Mangrove Loss. (n.d.). Retrieved April 30, 2021, from https://www.usgs.gov/news/rising-sea-levels-could-accelerate-florida-bay-mangrove-loss

21. Sarhan, M., & Tawfik, R. (2018). The Economic Valuation of Mangrove Forest Ecosystem Services. The George Wright Forum, 35(3), 341-549.

22. Sea level rise could make mangrove forests even saltier. (n.d.). Retrieved April 30, 2021, from https://www.usgs.gov/center-news/sea-level-rise-could-make-mangrove-forests-even-saltier

23. Stabenau, E., Engel, V., Sadle, J., & Pearlstine, L. (2011). (Pdf) sea-level rise: Observations, impacts, and proactive ... Retrieved April 30, 2021, from https://www.researchgate.net/publication/286374988_Sea-level_rise_Observations_impacts_and_proactive_measures_in_Everglades_National_park

24. University, Rutgers. (2020, June 04). Mangrove trees won't Survive sea-level rise by 2050 if emissions aren't cut. Retrieved April 30, 2021, from  https://www.sciencedaily.com/releases/2020/06/200604152109.htm 

25. U.S. Geological Survey (USGS) Earth Resources Observation and Science (EROS) Center. 9/11/2006. Landsat ETM+ SLC-off - Path: 15 Row: 42 for Scene: LT05L1TP0154220111110201683001T1. Remote-Sensing Image. NASA EOSDIS Land Processes DAAC, USGS Earth Resources Observation and Science (EROS) Center, Sioux Falls, South Dakota (https://lpdaac.usgs.gov), accessed 3/21/2021, at <https://earthexplorer.usgs.gov/>

26. U.S. Geological Survey (USGS) Earth Resources Observation and Science (EROS) Center. 11/10/2011. Landsat ETM+ SLC-off - Path: 15 Row: 42 for Scene: LT05L1TP0154220111110201683001T1. Remote-Sensing Image. NASA EOSDIS Land Processes DAAC, USGS Earth Resources Observation and Science (EROS) Center, Sioux Falls, South Dakota (https://lpdaac.usgs.gov), accessed 3/21/2021, at <https://earthexplorer.usgs.gov/>

27. Willard, D. A., & Bernhardt, C. E. (2011). Impacts of past climate and sea level change on Everglades Wetlands: Placing a century of Anthropogenic change into A late-Holocene Context. Climatic Change, 107(1-2), 59-80. doi:10.1007/s10584-011-0078-9

28.  Yao, Q., & Liu, K. (2017). Dynamics of Marsh-mangrove ecotone since the Mid-holocene: A palynological study of Mangrove encroachment and sea level rise in the SHARK river Estuary, florida. PLOS ONE, 12(3). doi:10.1371/journal.pone.0173670

Johns Hopkins University

Environmental Applications of GIS

Juvenile lemon shark swimming through mangroves. Photo credit: https://ocean.si.edu/ocean-life/sharks-rays/young-lemon-shark-swims-through-mangroves

Mangroves in Everglades National Park. Photo credit: https://www.fondriest.com/news/carbon-everglades-national-park-mangroves-valued-billions.htm  

Landsat data was retrieved from Earth Explorer for study analysis. Photo Credit: https://earthexplorer.usgs.gov/

Aerial view of Everglades National Park. Photo credit: AdobeStock_356530515.jpeg (Everglades National Park)

Picture Credit: AdobeStock_405377962.jpeg (Everglades National Park)

Sunset at Everglades National Park. Photo credit: AdobeStock_112157455.jpeg (Everglades National Park)

Swipe to view compare change from 2006-2011 with mangrove habitat layer

Swipe to view compare change from 2006-2011 with mangrove habitat layer