Jimmy Webb, Conservation Biology (BIOL 834), Spring 2011
General Introduction Wetlands are a vital ecosystem. Wetlands support great biological diversity of species (Russell et al. 2002 and Liner et al. 2008). Even though wetlands contain great diversity, wetlands are often undervalued and overlooked (Russell et al. 2002). Scientists have estimated that approximately 50% of all wetlands have been lost since the colonization on the United States (Lehtinen and Galatowitsch 2001). There has been an estimated loss of 84% of wetlands in the southern states alone over the last 30 years (Russel et al. 2002). Efforts to restore these lost wetlands and the native species that inhabit them continues (Lehtinen and Galatowitsch 2001). These restoration efforts have been evaluated and many deemed unsuccessful for a number of reasons. Hilderbrand et al. (2005) outline some of the methods used to restore wetlands and the short comings of each of these approaches. The methods utilized to restore wetlands in a given area are not a one size fits all as it relates to future successes. Humans inevitably have an impact on any ecosystem they come in contact with. With this in mind, one must manage ecosystems based on the effect that human inflict (Hilderbrand et al. 2005). Hilderbrand et al. (2005) states that conservation of ecosystems after degradation is not enough. For example, “No Net Loss” policy for U.S wetlands have not been effective since losses still exceed gains or are not functionally equal (Dahl and Alford 1996, Zedler 2000a). Attempts to limit further losses of wetlands have failed since wetlands are still disappearing at an alarming rate in spite of the “No Net Loss” policy. Also, the “No Net Loss” policy implies that wetland restoration will be equivalent to the pre-degradation wetland. In reality very few restored wetlands have achieved equivalency to existing wetlands (Zedler
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