Scott M. Pearson (Presenter), Mars
Hill College
Monica G. Turner, University of Wisconsin
Paul Bolstad, University of Minnesota
The abundance and spatial pattern of forest community types can affect
ecosystem function and the persistence of populations of native species.
A recent paper by Wear and Bolstad (Ecosystems 1:575-594) projected
forest cover change to 2030 using econometric models for four study
areas in NC and VA. We combined maps of forest cover for four time
periods (1950, 1970, 1990, and projections for 2030) for the same study
areas with maps of potential forest types to measure changes in the
abundance and spatial pattern of forest community types: northern hardwoods,
cove hardwoods, mixed hardwoods, and oak-pine. The maps of potential
forest types were derived from spatially explicit topographic information
(e.g., elevation, land form, aspect). Forests increased all four study
areas between 1950 and 1990. The abundance of cove hardwoods, mixed
hardwoods, and oak-pine showed the greatest amount of change. Increases
in forest cover were accompanied by reduced fragmentation of habitats,
as measured by increases in forest patch size and decreases in the number
of patches. The density of buildings within the forest also increased
during the study period. The most dramatic increases were observed
in the Cane Creek watershed, which is near Asheville, NC. Grayson County,
VA, the most rural study area, showed the least amount of change in
building density. While increases in forest cover will provide additional
habitat for native species, increases in building density within forests
may offset these gains for some species.
Workshop IV: Terrestrial
Ecosystems