Southern Blue Ridge priority conservation areas were identified by The Nature Conservancy through an analysis of matrix forests which identified 83 large blocks that are relatively unfragmented forest (Anderson et al. 2013).  In this analysis a matrix forest was defined as a large area (greater than or equal to 15,000 acres) of heterogeneous, relatively undeveloped forested areas (i.e. areas containing at least 80% deciduous forest, evergreen forest, or forest scrub).  These forests are considered to be large enough to be resistant to the effects of catastrophic events (i.e. hurricanes, tornadoes, ice storms) and resilient enough to return to a positive state of ecological productivity and species composition following disturbances (Anderson and Bernstein 2003). The boundary of each block was delineated by any major fragmenting feature (interstates, railroads, large lakes, etc.). These blocks were then prioritized across the SBR to identify which matrix forest blocks best represented a range of ecological land units (ELU). These ELUs contain combinations of elevation, bedrock geology, and land forms that make them each unique, however some matrix forests are more similar to some than to others. These characteristics create a wide range of environmental conditions often correlated with high biodiversity. Thus through conservation of a wide array of large forest blocks, a wide range of biodiversity will be supported, and it will maintain or improve ecosystem function as changes within the environment occur, including climate disruption. 

 

While these matrix forest blocks are relatively undeveloped, they do contain elements of multiple-use landscapes. The concern with multiple-use landscapes in these areas is that these blocks could contain minor fragmenting features or be managed in such a way that might not support biodiversity (i.e. extraction). These minor fragmenting features are defined as features such as minor roads (county, Forest Service, logging etc.), motorized recreation trails or other landscape features that could impede movement of organisms across the matrix block or downsize habitat. To meet the habitat needs of SBR organisms it is necessary to identify and evaluate unfragmented core forests that will reside within priority matrix forests to be managed for biodiversity.

The goal of this report is to build upon previous analysis of SBR matrix forest blocks using aerial photography and geospatial analysis to identify core forests within each of these blocks.  A core forest is defined as a heterogeneous landscape with minimal (i.e. hiking trails) or no fragmenting features that contain at least 5,000 acre interior forest surrounded by a 100m buffer. The buffer is a part of the core forest which surrounds and protects the 5,000 acre (or larger) interior forest from any multiple-use disturbances (such as off road vehicle trails) that may take place in the matrix forest block. Core forests are a key component in the long-term SBR conservation strategy as they “provide the opportunity for relatively natural processes to occur or be mimicked through management, resulting in a healthy range of structural and compositional forest attributes” (Anderson et al. 2013).