The Florida
Everglades are a “limestone plateau that is the southeastern extension of the
North American continent (Brown, et al., 2006, p. 255). They are the only
subtropical wetlands in North America. The Everglades are home to a diverse
number of species and interdependent ecosystems. Today, due to human modification,
the Florida Everglades occupies half of the original area it did a century ago
(SFWMD, 2011). “Coastal prairie, pine flatwoods and hardwood hammocks have all
been sacrificed in the name of progress” (Rocus & Mazzotti, 1996, p. 1).
Historically,
the Everglades relied on a natural flow of water from Orlando down through the
Florida Bay (see figure to the left). Originally, the water sheet flow was derived
primarily from rainfall and contained little nutrients. The Everglades were
considered “oligotrophic (nutrient poor)” (Brown, et al., 2006, p. 256).
These
seasonal changes allowed for a high diversity of flora and fauna, while
regulating animal cycles (Brown, et al., 2006). Most of south Florida was
considered uninhabitable swamp.
Increasing
populations drove the efforts to drain marshlands for agricultural conversion,
flood control and urban development. To accomplish those goals, the federal
government developed a system of manmade canals. The natural flow of the water
in the Everglades is now entirely controlled by these canals, levees and pump
stations (Brown, et al., 2006).
Along with
these canal systems, exotic trees were introduced to aid in the draining of the
marshlands; specifically the Australian punk tree (Melaleuca quinquenervia).
These trees have a very high dispersal rate and turned the marshlands into a
forest (Beringer, 2011).
One obvious
consequence of altering the water cycles in the Everglades is the decline in
wading bird populations. “Many species are dependent on the natural water cycle
to signal nesting and breeding times and to provide sufficient food supplies”
(Rocus & Mazzotti, 1996, p. 2). Ninety percent of bird populations have
declined in the Everglades. Wading birds play an important role in the
ecological fitness of this ecosystem. They redistribute nutrients, create tree
islands, and affect the demographics of fish and invertebrate populations
through predation (Frederick, et al., 2008).
Stay tuned next week (part two) for a continuing look at the Florida Everglades and biodiversity loss due to changing water tables.
References:
Arrieta, Diane, 2012. Excerpt from unpublished class paper, Impact of humans on biodiversity. University of Edinburgh.
Beringer, Joe, 2004. Conserving biodiversity in South Florida. [online]: Miami University. Available at: http://jrscience.wcp.muohio.edu/filedcourse04/PapersMarineEcologyArticles/Whathav ew edoneWhattodonow.html. [18 November, 2011].
Brown, Mark T., Cohen, Mathew J., Bardi, Eliana & Ingwersen, Wesley W., 2006. Species diversity in the Florida Everglades, USA: A systems approach to calculating biodiversity. Aquatic Sciences, [online] 68, pp. 254-277. Available through: SpringerLink [12 November, 2011].
Frederick, Peter, Gawlik, Dale E., Ogden, John C., Cook, Mark. I. & Lusk Michael, 2008. The White Ibis and Wood Stork as indicators for restoration of the everglades ecosystem. Ecological Indicators, [online] 9:6, pp. s83-s95. Available through: ScienceDirect [10 November, 2011].
South Florida Water Management District (SFWMD), 2011. America’s Everglades. [online] Available at: http://my.sfwmd.gov/portal/xweb%20and%restoring/americas%20everglades [21 November, 2011].
Rocus, Denise & Mazolli, Frank J.,1996. Threats to Florida’s Biodiversity, [online]: University of Florida IFAS Extension. Available at: http://edis.ifas.edu/uw107. [8 November, 2011].
image credit: United States Geological Service. n.d. Illustration. Available at: http://sofia.usgs.gov/publications/circular/1182/index.html [22 November, 2011].
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