As a member of the Biodiversity and
As such, these models can serve as important tools for urban planners, wildlife biologists, traditional cultures, and others seeking to manage and conserve natural resources for future generations.
|
|
Roanoke-Tar-Neuse-Cape Fear Ecosystem boundary. National Wildlife Refuges are shown in red. |
Ashton is currently working with the US Fish and Wildlife Service in the RTNCF Ecosystem of North Carolina. The objectives of this 3-year pilot project are 1) to develop population objectives for species and abundance goals for RTNCF natural communities; 2) convert these population/abundance objectives into habitat objectives; 3) map potential conservation areas where deficits exist; and 4) step down population/abundance objectives to individual refuges and partner lands. Thus, each land manager will be able to see how his or her refuge contributes to objectives at broader scales, and can coordinate activities with other partner agencies and land managers to track progress toward meeting ecoregional population and habitat objectives. Further, the confidence intervals that will be provided by the literature and expert opinion will provide more focus on where additional research would be most beneficial.
She will develop examples of three quantitative species distribution modeling scenarios (inductive, deductive, and aquatic), with confidence intervals, for select USFWS Trust Species within the RTNCF ecosystem. Trust Species are those for which the Service has legislative mandate, and include federally-listed threatened and endangered species, interjurisdictional fishes, and migratory birds (USFWS 1999). Inductive models will be developed for terrestrial vertebrate species represented by sufficient point count data within the RTNCF ecosystem region to quantify habitat-specific species density and independently validate the models. This approach is being developed through another pilot project at SE-GAP (Williams & McKerrow 2005, Laurent et al. 2006), which is exploring the data requirements and limitations of various quantitative modeling techniques to define spatial gradients in habitat suitability for six forest bird species in North Carolina. Deductive models will be developed for selected terrestrial vertebrate species that are well-studied, yet for which there are limited point count data within the RTNCF region. The aquatic models will also follow a deductive approach, but will require different spatial datasets and different spatial analyses than the terrestrial deductive models. Expert opinion, literature review, and a Bayesian belief network will provide the foundation for these deductive models.
Laurent, E.J., S.G. Williams, and A.J.
McKerrow. 2006. Developing a
scientifically rigorous framework for enhancing and evaluating vertebrate
models. Gap Analysis Bulletin 15.
Williams, S.G., and A.J. McKerrow.
2005. Refining Southeast regional GAP models for use
in regional bird conservation planning: a pilot project. Gap Analysis Bulletin
13: 8-9.
August
2006
September 2006
October 2006
November 2006
January 2007
May 2007
August 2007
November 2007
February 2008
August 2008
December 2008
November 2009
Article published in 2006 GAP Bulletin 14
Species and Habitats Spreadsheet (xls)
SSP Models and Strategic Habitat Conservation Presentation (ppt)
From Expert-based to Data-based Decision Support for SHC Presentation (ppt)
King Rail and Least Bittern Nest Success 2009 (pdf)
King Rail Bibliography (pdf)
Contact: Dr. C.
Ashton Drew
Regional Habitat Modeler
Biodiversity and Spatial Information Center
Box 7617, North Carolina State University
Raleigh, NC 27695-7617
919-513-0506
FAX 919-515-4454
Last updated: 11 March 2010