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The Ecology of Hydric Hammocks - USGS National Wetlands ...

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cause they are tropical plants confinedmostly to south Flnrida- Noneoccur in abundance and only one, whitestopper, is a tree. Isolated populations<strong>of</strong> this species occur north <strong>of</strong>Lake Okeechobee (Little 1978); one ispresent in hydric hammock in TosohatcheeState Reserve. <strong>The</strong> geographicaldistributions <strong>of</strong> several herbaceousplants common to hydric hammocks,including goldfoot fern andwild c<strong>of</strong>fee, extend north from theCaribbean to central Florida.A striking example <strong>of</strong> the influence<strong>of</strong> a species' range on the composition<strong>of</strong> hydric hammock is cabbage palm, thepredominant tree species in many hydric hammocks. From North Carol i na tonorthern Florida and west across thepanhandle, this species is essentiallyrestricted to the coast (Figure 28).South <strong>of</strong> a line from about Cedar Keyon the gulf coast to St. Augustine onthe Atlantic, cabbage palm rangesFigure 28. Distribution <strong>of</strong> cabbage palm inFlorida (from Little 1978). Asterisks on the insetmap indicate isolated populations <strong>of</strong> cabbagepalm outside <strong>of</strong> its continuous range (from Brown1973).across Florida' s peni nsul a. North <strong>of</strong>this line, a few interior populationsare scattered a1 ong rivers. <strong>Hydric</strong>hammocks in the northern region, forexample in San Felasco Hammock StatePreserve (Tab1 e 5), 1 ack cabbage palm.<strong>The</strong> inland Gulf Hammock site that wesampled (Table 5) is situated at theedge <strong>of</strong> cabbage palm's coastal range.Cabbage palm was absent from much <strong>of</strong>the forest, but it was common, especiallyin the understory, in someparts.Numerous studies have demonstratedor inferred that patterns <strong>of</strong> vegetationin southern forested wetlands arestrongly influenced by flooding(Bedinger 1978; Huffman and Forsythe1981; Wharton et a7. 1982; Leitman eta7. 1983). Frequency, duration,depth, and timing <strong>of</strong> flooding are factorsthat affect the species composition<strong>of</strong> a forested wetland. <strong>The</strong> effects<strong>of</strong> flooding on these communitiesare mediated by physical and chemicalchanges in the soils and varying responsesto the alterations by plantspecies.<strong>The</strong> nature and extent <strong>of</strong> the physicaland chemical processes that followsoil inundation largely depend on theduration <strong>of</strong> submergence and on soilproperties (Ponnamperuma 1984). Whena soil is flooded or saturated, gasexchange between the soil and air isgreatly restricted. <strong>The</strong> slowing <strong>of</strong>gas diffusion is particularly great insoils with high clay content. Oxygensupply to the soil is drastically cut,and roots and microorganisms depletethe oxygen in the soil water veryrapidly. Gases produced by soi 1metabol ism (e.g., carbon dioxide) accumulate.Anaerobic conditions inducea number <strong>of</strong> chemical changes in thesoil, many <strong>of</strong> which are detrimental toplant growth. Nitrate is replaced byammonium, <strong>of</strong>ten less preferred for uptakeand assimilation by plantspecies. Oxidized forms <strong>of</strong> iron, manganese,and sulfur are reduced to potentiallytoxic forms, including sulfides. Ethanol, another potent i a1toxin, is a by-product <strong>of</strong> anaerobicrespiration in most plant roots.

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