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Conclusions
Visual survey is relatively unbiased by diver avoidance. Thus could be used in areas with good water clarity to monitor prop-root fish abundance and composition.
Fish are very patchy in prop-root habitat such that not all areas are of equal value. Some areas may more essential than others requiring special protection. These need to be better identified.
Inshore areas have poor habitat quality, shallow depths and narrow fringe, that is not conducive to harboring large numbers of higher trophic level species. Additional freshwater is unlikely to increase this capacity.
References
Ley, J.A., C.C. McIvor, and C.L. Montague. 1999. Fishes in mangrove prop-root habitats of northeastern Florida Bay: distinct assemblages across an estuarine gradient. Est. Coastal Shelf Sci. 48: 701-723.
Lorenz, J.J. 1999. The response of fishes to physiochemical changes in the mangroves of northeast Florida Bay. Estuaries 22: 500-517.
Serafy, JE, K.C. Lindeman, T.E. Hopkins, and J.S. Ault. 1997. Effects of freshwater canal discharge on fish assemblages in a subtropical bay: field and laboratory observations. Mar. Ecol. Prog. Ser. 160: 161-172.
Smith III, T.J. and M.B. Robblee. 1994. Relationships of sport fisheries catches in Florida Bay to freshwater inflow from the Everglades. Bull. Mar. Sci. 54(3): 1084.
Thayer, G.W., D.R. Colby, and W.F. Hettler. 1987. Utilization of the red mangrove prop root habitat by fishes in south Florida. Mar. Ecol. Prog. Ser. 35: 25-38.
Acknowledgments
Funds for this project were provided by the U.S. Department of Interior, South Florida Ecosystem Restoration Program, Critical Ecosystems Studies Initiative. We would like to thank the Everglades National Park for providing permits, laboratory facilities, and accommodations. Additional support was provided by the NOAA/UNCW National Undersea Research Center and the NOAA Florida Keys National Marine Sanctuary.
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