Simulated effects of climate change, fragmentation, and inter-specific competition on tree species migration in northern Wisconsin, USA

The reproductive success, growth, and mortality rates of tree species in the northern United States will be differentially affected by projected climate change over the next century. As a consequence, the spatial distributions of tree species will expand or contract at differential rates. In addition, human fragmentation of the landscape may limit effective seed dispersal, and inter-specific competition may limit the migration of climate-adapted species, restraining the rate of tree species migration. If the northward migration of tree species adapted to a warmer climate lags behind the rate of climatic change, overall growth rates and aboveground biomass of northern forests may be significantly reduced relative to their potential. We used a spatially interactive forest landscape model, LANDIS-II, that simulates tree species establishment, growth, mortality, succession, and dis- turbance. We simulated multiple scenarios of disturbance and climatic change across a ~15 000 km 2 forested landscape in northwestern Wisconsin, USA. These simulations were used to estimate changes in aboveground live biomass and the spatial distribution of 22 tree species. We observed a reduction in aboveground live biomass relative to the potential biomass for the combined soils and changing climate. We regressed the reduction of potential aboveground biomass against a measure of fragmentation, the initial biomass for 22 tree species, and soil water holding capacity calculated at 3 spatial resolutions. We also regressed the range expansion of 3 individual tree species that are expected to expand their distributions against the same variables. Species migration and range expansion were negatively correlated with fragmentation both in total and for 2 of the 3 species examined in detail. The initial abundances of some tree species were also significant predictors of species migration and range expansion and indicate significant competition between existing species assemblages and more southerly species that are expected to migrate north. In conclusion, the above- ground biomass of northern forests may be limited by interactions among climate change, interspe- cific competition, and fragmentation.

[1]  Vemap Participants Vegetation/ecosystem modeling and analysis project: Comparing biogeography and biogeochemistry models in a continental-scale study of terrestrial ecosystem responses to climate change and CO2 doubling , 1995 .

[2]  Mark W. Schwartz,et al.  Modeling potential future individual tree-species distributions in the eastern United States under a climate change scenario: a case study with Pinus virginiana , 1999 .

[3]  J. R. Wallis,et al.  Some ecological consequences of a computer model of forest growth , 1972 .

[4]  J. Aber,et al.  A generalized, lumped-parameter model of photosynthesis, evapotranspiration and net primary production in temperate and boreal forest ecosystems , 1992, Oecologia.

[5]  A. Prasad,et al.  Potential Changes in Tree Species Richness and Forest Community Types following Climate Change , 2001, Ecosystems.

[6]  D. Mladenoff LANDIS and forest landscape models , 2004 .

[7]  Hong S. He,et al.  INTEGRATION OF GIS DATA AND CLASSIFIED SATELLITE IMAGERY FOR REGIONAL FOREST ASSESSMENT , 1998 .

[8]  M. B. Davis,et al.  Lags in vegetation response to greenhouse warming , 1989 .

[9]  A. Lugo,et al.  Climate Change and Forest Disturbances , 2001 .

[10]  C. Loehle Forest ecotone response to climate change: sensitivity to temperature response functional forms , 2000 .

[11]  James S. Clark,et al.  MOLECULAR INDICATORS OF TREE MIGRATION CAPACITY UNDER RAPID CLIMATE CHANGE , 2005 .

[12]  James S. Clark,et al.  Why Trees Migrate So Fast: Confronting Theory with Dispersal Biology and the Paleorecord , 1998, The American Naturalist.

[13]  E. Davidson,et al.  Estimating regional carbon stocks and spatially covarying edaphic factors using soil maps at three scales , 1993 .

[14]  J. Innes,et al.  A tree and climate assessment tool for modelling ecosystem response to climate change , 2008 .

[15]  George Z. Gertner,et al.  Potential effects of interaction between CO2 and temperature on forest landscape response to global warming , 2007 .

[16]  Mark A. White,et al.  A Quantitative Approach to Developing Regional Ecosystem Classifications , 1996 .

[17]  Steven I. Higgins,et al.  Estimating plant migration rates under habitat loss and fragmentation , 2003 .

[18]  E. Nordheim,et al.  Quantitative classification of a historic northern Wisconsin (U.S.A.) landscape: mapping forests at regional scales , 2002 .

[19]  Thomas Hovestadt,et al.  Forecasting plant migration rates: managing uncertainty for risk assessment , 2003 .

[20]  Mark W. Schwartz,et al.  How fast and far might tree species migrate in the eastern United States due to climate change , 2004 .

[21]  David J. Mladenoff,et al.  Simulating the Effects of Fire Reintroduction Versus Continued Fire Absence on Forest Composition and Landscape Structure in the Boundary Waters Canoe Area, Northern Minnesota, USA , 2005, Ecosystems.

[22]  Hong S. He,et al.  Spatial simulation of forest succession and timber harvesting using LANDIS. , 2000 .

[23]  W. Post,et al.  Development of a linked forest productivity-soil process model , 1985 .

[24]  David M. Cairns,et al.  Effects of dispersal, population delays, and forest fragmentation on tree migration rates , 1997, Plant Ecology.

[25]  Craig Loehle,et al.  Model-based assessments of climate change effects on forests , 1995 .

[26]  T. Crow,et al.  BIOMASS AND PRODUCTION IN THREE CONTIGUOUS FORESTS IN NORTHERN WISCONSIN , 1978 .

[27]  George C. Hurtt,et al.  Reid's Paradox of Rapid Plant Migration Dispersal theory and interpretation of paleoecological records , 1998 .

[28]  A. Prasad,et al.  Potential colonization of newly available tree-species habitat under climate change: An analysis for five eastern US species , 2004, Landscape Ecology.

[29]  J. T. Curtis The Vegetation of Wisconsin: An Ordination of Plant Communities , 1961 .

[30]  B. Huntley,et al.  IMPACTS OF HABITAT FRAGMENTATION AND PATCH SIZE UPON MIGRATION RATES , 2000 .

[31]  R. Farmer Seed Ecophysiology of Temperate and Boreal Zone Forest Trees , 1996 .

[32]  Eric J. Gustafson,et al.  Quantifying Landscape Spatial Pattern: What Is the State of the Art? , 1998, Ecosystems.

[33]  Edward B. Rastetter,et al.  Validating models of ecosystem response to global change , 1996 .

[34]  R. Neilson,et al.  Estimated migration rates under scenarios of global climate change , 2002 .

[35]  David J. Mladenoff,et al.  Eastern Hemlock Regeneration and Deer Browsing in the Northern Great Lakes Region: A Re-examination and Model Simulation , 1993 .

[36]  M. Kellman,et al.  Tree seed dispersal among forest fragments: II. Dispersal abilities and biogeographical controls , 2002 .

[37]  D. Mladenoff,et al.  A forest growth and biomass module for a landscape simulation model, LANDIS: design, validation, and application , 2004 .

[38]  David J. Currie,et al.  Projected Effects of Climate Change on Patterns of Vertebrate and Tree Species Richness in the Conterminous United States , 2001, Ecosystems.

[39]  C. Loehle Height growth rate tradeoffs determine northern and southern range limits for trees , 1998 .

[40]  D. Mladenoff,et al.  A spatially interactive simulation of climate change, harvesting, wind, and tree species migration and projected changes to forest composition and biomass in northern Wisconsin, USA , 2005 .

[41]  J. T. Curtis,et al.  The Vegetation of Wisconsin: An Ordination of Plant Communities. , 1960 .

[42]  Wolfgang Cramer,et al.  The effects of fragmentation and disturbance of rainforest on ground‐dwelling small mammals on the Robertson Plateau, New South Wales, Australia , 1996, Journal of Biogeography.

[43]  Climate Change and Shifts in Potential Tree Species Range Limits in the Great Lakes Region , 2002 .