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a cause of barrier migration on the Core Banks in <br />North Carolina (Riggs and Ames 2003, Gutierrez et <br />al. 2009) (Figure 3 -11). Maritime forests and shrub <br />communities have been identified as highly sensitive <br />habitats in the NC WAP. These habitats are mainly <br />found along barrier islands and the mainland coast <br />on stabilized upper dunes and flats protected from <br />salt spray. These habitats are important breeding and <br />migration stopover points for many migratory birds, <br />and key breeding areas for declining populations of <br />the eastern painted buntings, as well as for several <br />snake species (NC WAP). All of the barrier island <br />maritime forest /shrub communities occur in very <br />dynamic environments and will be susceptible to sea <br />level rise. <br />Coastal wetlands are also highly vulnerable to sea <br />level rise, and loss of this habitat has the poten- <br />tial to adversely affect a number of priority species <br />listed in the NC WAP. Estimates suggest there are <br />between 3.1 and 3.9 million acres of wetland in <br />Photo: North Carolina Derision of Coastal Management <br />pp/)6qP�" / %E(% /: /E ",° ll:l(y' 1(,ll('( f E(G l(,l <br />(le�i�)c r (," )i (, (f( }c/ a l%'t�u/i ''/// (,r Cb /Z'He <br />,jxrF ie, ,lr(ll ire f , ')e1' C IAA l., <br />coastal North Carolina, including marshes, swamps, <br />forested wetlands, pocosins, and other wetland habi- <br />tats (Street et al. 2005). Vertical accretion rates in <br />North Carolina have been able to keep up with the <br />rate of sea level rise (Feldman et al. 2009), however <br />there are some wetlands that have been unable to <br />vertically accrete at a pace to match current rates <br />of sea level rise. Feldman et al. (2009) suggest that <br />North Carolinas lower coastal plain fringe wetlands <br />may not survive with the 10 mm per year of relative <br />sea level rise scenario described by Day et al. (2005) <br />for the Mississippi Delta region. Pocosin wetlands <br />generally accrete at a rate of approximately one to <br />two mm per year when in their natural state (Craft <br />and Richardson 1998 and Moorhead and Brin- <br />son 1995 in Feldman et al. 2009). Human altered <br />drainage patterns appear to be limiting their verti- <br />cal accretion, which, in combination with saltwater <br />intrusion, could cause subsidence and conversion <br />to open water (Pearsall and Poulter 2005). As sea <br />level rises further and waters with higher salt content <br />reach the Albemarle- Pamlico peninsula, the ability of <br />peat -based wetlands to keep up is unlikely (Box 3 -3, <br />Feldman et al. 2009). Higher scenarios of sea level <br />rise may lead to an increase in inlets and segmen- <br />tation or disintegration of barrier islands leading, <br />potentially resulting in a change from a non -tidal to <br />a tidal regime with increased salinity. These changes <br />would fundamentally alter the structure of current <br />ecosystems and would lead to increased erosion and <br />impacts on wetlands (Riggs and Ames 2003). <br />Chapter 3: Projected Impacts of Climate Change in North Carolina 71 <br />