Cornus florida L. is one of the most numerous tree species in the Eastern United States (US). Multiple studies have reported localized declines in C. florida populations following the introduction of the destructive fungus Discula destructiva Redlin (dogwood anthracnose), but few, if any, have documented changes in C. florida populations across the species' entire natural range. Thus, a current assessment of the C. florida population in the Eastern US and implications for future sustainability is warranted. Our study's goal was to present C. florida population estimates across the natural range of the species (Little, 1971)
IntroductionCornus florida L. (flowering dogwood) is widely distributed across the eastern landscape of the United States (US) and is one of the most common understory trees in North America (Jenkins & White, 2002). Little (1971) describes the C. florida geographical distribution as covering the majority of the Eastern US from northern Florida and the Gulf Coast to southern Michigan and New England and extending as far west as eastern Oklahoma and eastern Texas. Although C. florida is an important member of the eastern deciduous forest, the species has been and is currently experiencing localized and regional declines. Cornus florida declines have largely been attributed to an imported fungus (Britton, 1994). The fungus Discula destructiva Redlin (dogwood anthracnose) (Mielke & Langdon, 1986;Redlin, 1991; Chellimi et al., 1992) has been identified as responsible for considerable C. florida mortality throughout the East, particularly in the Appalachian ecoregion .Botanical surveys conducted throughout the 20 th Century have documented the abundance of C. florida in the Eastern US (Hiers & Evans, 1997). Measures of high relative density and elevated importance values prior to D. destructiva infestation were reported by Hannah (1993) in North Carolina, Quarterman et al. (1972) in Tennessee, Muller (1982) in Kentucky, Carr and Banas (2000) in Virginia, and Sherald et al. (1996) in Maryland. Moreover, C. florida has been documented as a common component of second-growth hardwood stands (Orwig & Abrams, 1994;Jenkins & Parker, 1998), as an important understory component of old-growth forests (McCune et al., 1988;Goebel & Hix, 1996), and is also reported to be a significant source of calcium, in the form of leaf litter, in the surface horizons of some forest soils (Thomas, 1969;Hepting, 1971).Multiple studies (Hiers & Evans, 1997;Schwegman et al., 1998; Williams & Moriarty, 1999;McEwan et al., 2000) have reported substantial C. florida mortality at local scales across its natural biological range following local colonization by D. destructiva, the causal agent for dogwood anthracnose (Redlin, 1991). While numerous studies have quantified local losses of C. florida (Sherald et al., 1996;Hiers & Evans, 1997;Schwegman et al., 1998; Williams & Moriarty, 1999;Carr & Banas, 2000;McEwan et al., 2000) specifically attributed to D. destructiva, few, if any, studies have quantified large-scale losses acr...