Figure 1F. Mangrove rivulus are common in mangrove forests along Shark River, and are distributed, seemingly independent of site salinity. (bar graph)

Figure 2F. Frillfin gobies are common in mangrove forests along Shark River, and their distribution is closely correlated with site salinity. (bar graph)

Figure 3F. Simplified plot from cluster analysis of fish samples collected from replicate mudflats (brown shading) and forests (green shading) in the Big Sable Creek complex.

Figure 4F. Log jams in headwater creeks of the Big Sable Creek complex appear to be favored habitat for diamondback terrapins in this system.

Figure 1V. Mangrove forest and barren mud flat located in the Big Sable Creek region of Everglades National Park.

Figure 2V. Percent cover of herbaceous vegetation on North Dump Key, Florida Bay. (bar graph)

Figure 3V. Log-log (base 10) relationship of total dry biomass as a function of diameter at breast height for three species of mangroves in Florida. (graph)

Figure 4V. Concentrations of ammonium (mean ± 1 standard deviation) in the sediment along a transect from the edge of a coastal tidal river, into a sawgrass prairie. Data are shown for two depths in the sediment (30 and 60cm) and for two seasons (summer and winter). (bar graph)

Figure 5V. Relationships between stem density and sediment porewater iron concentration for Avicennia and Rhizophora. (graph)

Figure 1H. Relationships of stage anomalies at gauge P33 in central Shark River slough in Everglades National Park and sediment porewater salinity anomalies at three locations downstream from P33. (graph)

Figure 2H. Relationship between water level (stage) change and sediment surface elevation for freshwater and saltwater wetlands. (graph)