Matthew Peters
United States Department of Agriculture
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Gen. Tech. Rep. NRS-146. Newtown Square, PA: U.S. Department of Agriculture, Forest Service, Northern Research Station. 310 p. | 2015
Patricia R. Butler; Louis R. Iverson; Frank R. Thompson; Leslie A. Brandt; Stephen D. Handler; Maria Janowiak; Christopher W. Swanston; Kent Karriker; Jarel L. Bartig; Stephanie J. Connolly; William D. Dijak; Scott Bearer; Steve Blatt; Andrea Brandon; Elizabeth Byers; Cheryl Coon; Tim Culbreth; Jad Daly; Wade Dorsey; David Ede; Chris Euler; Neil Gillies; David M. Hix; Catherine Johnson; Latasha Lyte; Stephen Matthews; Dawn McCarthy; Dave Minney; Daniel Murphy; Claire O’Dea
Forest ecosystems in the Central Appalachians will be affected directly and indirectly by a changing climate over the 21st century. This assessment evaluates the vulnerability of forest ecosystems in the Central Appalachian Broadleaf Forest-Coniferous Forest-Meadow and Eastern Broadleaf Forest Provinces of Ohio, West Virginia, and Maryland for a range of future climates. Information on current forest conditions, observed climate trends, projected climate changes, and impacts on forest ecosystems was considered by a multidisciplinary panel of scientists, land managers, and academics in order to assess ecosystem vulnerability to climate change. Appalachian (hemlock)/northern hardwood forests, large stream floodplain and riparian forests, small stream riparian forests, and spruce/fir forests were determined to be the most vulnerable. Dry/mesic oak forests and dry oak and oak/pine forests and woodlands were determined to be least vulnerable. Projected changes in climate and the associated impacts and vulnerabilities will have important implications for economically valuable timber species, forest-dependent wildlife and plants, recreation, and long-term natural resource planning.
Archive | 2014
Matthew Peters; Louis R. Iverson; Stephen N. Matthews
Droughts are common in virtually all U.S. forests, but their frequency and intensity vary within forest ecosystems (Hanson and Weltzin 2000). Accounting for the long-term influence of droughts within a region is difficult due to variations in the spatial extent and intensities over a period. Therefore, we created a cumulative drought severity index (CDSI) (Fig. 1) for the United States using weighted monthly frequencies of Palmer Drought Severity Index values reported at climate divisions for the periods 1960 to 1986 and 1987 to 2013 (National Climate Data Center 2014, Palmer 1965). The occurrences of severe conditions (index value of -3.0 to -3.9) receive a weight of 2 and extreme (index value of = -4.0) receive a weight of 3 to reflect the increased magnitude of these events.
Archive | 2017
Leslie A. Brandt; Abigail Derby Lewis; Lydia Scott; Lindsay Darling; Robert T. Fahey; Louis R. Iverson; David J. Nowak; Allison R. Bodine; Andrew Bell; Shannon Still; Patricia R. Butler; Andrea Dierich; Stephen D. Handler; Maria Janowiak; Stephen N. Matthews; Jason W. Miesbauer; Matthew Peters; Anantha Prasad; Douglas Stotz; Christopher W. Swanston
The urban forest of the Chicago Wilderness region, a 7-million-acre area covering portions of Illinois, Indiana, Michigan, and Wisconsin, will face direct and indirect impacts from a changing climate over the 21st century. This assessment evaluates the vulnerability of urban trees and natural and developed landscapes within the Chicago Wilderness region to a range of future climates. We synthesized and summarized information on the contemporary landscape, provided information on past climate trends, and illustrated a range of projected future climates. We used this information to inform models of habitat suitability for trees native to the area. Projected shifts in plant hardiness and heat zones were used to understand how nonnative species and cultivars may tolerate future conditions. We also assessed the adaptability of planted and naturally occurring trees to stressors that may not be accounted for in habitat suitability models such as drought, flooding, wind damage, and air pollution. The summary of the contemporary landscape identifies major stressors currently threatening the urban forest of the Chicago Wilderness region. Major current threats to the region?s urban forest include invasive species, pests and disease, land-use change, development, and fragmentation. Observed trends in climate over the historical record from 1901 through 2011 show a temperature increase of 1 ?F in the Chicago Wilderness region. Precipitation increased as well, especially during the summer. Mean annual temperature is projected to increase by 2.3 to 8.2 ?F by the end of the century, with temperature increases across all seasons. Projections for precipitation show an increase in winter and spring precipitation, and summer and fall precipitation projections vary by model. Species distribution modeling for native species suggests that suitable habitat may decrease for 11 primarily northern species and increase or become newly suitable for 40 species. An analysis of tree species vulnerability that combines model projections, shifts in hardiness and heat zones, and adaptive capacity showed that 15 percent of the trees currently present in the region have either moderate-high or high vulnerability to climate change, and many of those trees with low vulnerability are invasive species. We developed a process for self-assessment of urban forest vulnerability that was tested by urban forestry professionals from four municipalities, three park districts, and three forest preserve districts in the region. The professionals generally rated the impacts of climate change on the places they managed as moderately negative, mostly driven by the potential effects of extreme storms and heavy precipitation on trees in the area. The capacity of forests to adapt to climate change ranged widely based on economic, social, and organizational factors, as well as on the diversity of species and genotypes of trees in the area. These projected changes in climate and their associated impacts and vulnerabilities will have important implications for urban forest management, including the planting and maintenance of street and park trees, management of natural areas, and long-term planning. will have important implications for urban forest management, including the planting and maintenance of street and park trees, management of natural areas, and long-term planning.
Archive | 2013
Matthew Peters; Louis R. Iverson; Anantha Prasad; steve Matthews
Fine-scale soil (SSURGO) data were processed at the county level for 37 states within the eastern United States, initially for use as predictor variables in a species distribution model called DISTRIB II. Values from county polygon files converted into a continuous 30-m raster grid were aggregated to 4-km cells and integrated with other environmental and site condition values for use in the DISTRIB II model. In an effort to improve the prediction accuracy of DISTRIB II over our earlier version of DISTRIB, fine-scale soil attributes replaced those derived from coarse-scale soil (STATSGO) data. The methods used to prepare and process the SSURGO data are described and geoprocessing scripts are provided.
Archive | 2018
Stephen N. Matthews; Louis R. Iverson; Matthew Peters; Anantha Prasad
The maps and tables presented here represent potential variability of projected climate change across the conterminous United States during three 30-year periods in this century and emphasizes the importance of evaluating multiple signals of change across large spatial domains. Maps of growing degree days, plant hardiness zones, heat zones, and cumulative drought severity depict the potential for markedly shifting conditions and highlight regions where changes may be multifaceted across these metrics. In addition to the maps, the potential change in these climate variables are summarized in tables according to the seven regions of the fourth National Climate Assessment to provide additional regional context. Viewing these data collectively further emphasizes the potential for novel climatic space under future projections of climate change and signals the wide disparity in these conditions based on relatively near-term human decisions of curtailing (or not) greenhouse gas emissions.
Ecosphere | 2017
Louis R. Iverson; Todd F. Hutchinson; Matthew Peters; Daniel A. Yaussy
Archive | 2013
Louis R. Iverson; Matthew Peters; Stephen Matthews; Anantha Prasad
Archive | 2010
Louis R. Iverson; Anantha Prasad; Stephen Matthews; Matthew Peters; Coeli Hoover
In: Parra, Gregory; Lance, David; Mastro, Victor; Reardon, Richard; Benedict, Chuck, comps. 2011 emerald ash borer national research and technology development meeting; 2011 October 12-13; Wooster, OH. FHTET-2011-06. Morgantown, WV; U.S. Department of Agriculture, Forest Service, State and Private Forestry, Forest Health Protection, Forest Health Technology Enterprise Team: 63-64. | 2011
Louis R. Iverson; Anantha Prasad; Kathleen S. Knight; Daniel A. Herms; Stephen Matthews; Matthew Peters; Annemarie Smith; Robert P. Long
Archive | 2012
Volker Bahn; Stephen Matthews; Xavier Morin; Louis R. Iverson; Anatha Prasad; Matthew Peters; Jens-Christian Svenning; Brian J. McGill