Abstract

The pace of environmental and socioeconomic change over the past 100 years has been rapid. Changes in fire regimes, climate, and land use have shaped the structure and function of most forest ecosystems, including oak (Quercus spp. L.) forests in the eastern United States. New stressors such as air pollution and invasive species have contributed to and interacted with climate and fire to alter current forest conditions. While changing fire regimes have altered species composition of the current forest, oak regeneration is constrained by many factors that may affect future forests. Over the remainder of the twenty-first century, an accelerating pace of climate and socioeconomic changes will influence the future range of variation in Eastern oak forests. Some of these impacts will be direct, such as changes in tree growth rates, while other impacts will be indirect, such as new disturbance regimes. While it is likely that fire will be important in shaping oak forests in the twenty-first century, it is less clear exactly what that role will be. For example, it is uncertain whether our current scientific knowledge on the use of prescribed fire in oak forests will be applicable under novel climate and changing socioeconomic conditions. We propose that the combination of climate change, wildfire, and other disturbances will create stand conditions that favor oaks with or without management. However, management intervention (e.g., prescribed fire, thinning, or a combination) could reduce wildfire hazard, particularly in the wildland-urban interface, and create more desirable stand conditions that are resilient to future stressors such as changing precipitation patterns and warmer temperatures.

Highlights

  • We propose that the combination of climate change, wildfire, and other disturbances will create stand conditions that favor oaks with or without management

  • Both of these concepts have been challenged because the rapid pace of environmental changes will create novel conditions in which historical reference conditions are not appropriate and desired future conditions are not achievable (Hobbs et al 2014, Golladay et al 2015, Hanberry et al 2015)

  • In the case of oak restoration, using prescribed fire could be viewed as an example of congruence among historical reference conditions, desired future conditions, and achievable future conditions

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Summary

INTRODUCTION

With a reduction in widespread fire and other disturbances, more mesophytic, shade-tolerant, and fire-sensitive species have taken advantage of these wetter conditions over the past century, with some suggestion that changes in the structure of the canopy and litter promotes a self-perpetuating mesic environment that provides a competitive advantage (Abrams 2005, Nowacki and Abrams 2008, Alexander and Arthur 2010, Kreye et al 2013) Whether these changes will be sufficient to offset the impacts of drier and warmer conditions projected for the future is unknown. In eastern US oak forests, mesophytic species (e.g., Acer spp., Liriodendron tulipifera, and Nyssa spp.) are typically isohydric, diffuse-porous, whereas oaks are anisohydric, ring-porous (Table 1) These differences in stomatal conductance and xylem anatomy influence whole-tree transpiration rates, with significantly greater water use by diffuse-porous species than ring-porous species under the same climatic and environ-

Nyssa sylvatica Marshall
CONCLUSIONS
Findings
LITERATURE CITED
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