Abstract

Foundation species have a major impact on biotic and abiotic processes and create a stable environment for many other species. Eastern hemlock (Tsuga canadensis), a foundation tree species native to North America, is currently declining due to infestation by an invasive insect, the hemlock woolly adelgid (Adelges tsugae). Loss of hemlock canopies can greatly alter the dark, cool, and damp microclimate of hemlock forests. We studied five years of microclimatic changes following logging or girdling (to simulate physical effects of adelgid) of hemlocks in a multi‐hectare‐scale experiment in a New England forest. Both logging and girdling of hemlocks caused large changes in light availability, air and soil temperature, and soil moisture. Even though the impact of logging was more rapid than the effect of gradual hemlock mortality after girdling, the microclimatic changes in these two canopy treatments converged over time. The microclimate in hardwood control plots, which represent the predicted forest composition 50 years after hemlock loss, was intermediate between the two canopy treatments and the hemlock control plots. Our fine‐scale results were generally consistent with average microclimatic effects observed in comparative studies but revealed additional changes in variance and seasonal rhythms, and the importance of stochastic events such as ice storms. The variance in air temperature, but not in soil temperature, greatly increased after loss of hemlock. We also observed a striking saw‐tooth pattern, consisting of a small peak before bud‐break in temperature differentials between hemlock control and the two canopy treatments—likely due to the insulating hemlock canopy preventing snow from melting—followed by a larger difference in temperatures after bud‐break. We expect the ongoing decline of eastern hemlock—due to both infestation and pre‐emptive salvage logging—to greatly impact the microclimate of hemlock forests, as well as the many taxa that are associated with it.

Highlights

  • Biotic and abiotic processes in forest ecosystems often are strongly influenced by the structural or functional characteristics of certain tree species (Ellison et al 2005a)

  • The Harvard Forest Hemlock Removal Experiment (HF-HeRE; Ellison et al 2010) has two types of canopy manipulation applied to 90 × 90m plots; a girdling treatment that mimics slow death by HWA infestation and a logging treatment analogous to a pre-emptive salvage logging operation aimed at extracting income from a forest stand before the adelgid would have arrived

  • We observed in the logged plots an abrupt increase in light availability at the forest floor followed by a decrease in light availability as regrowth commenced

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Summary

Introduction

Biotic and abiotic processes in forest ecosystems often are strongly influenced by the structural or functional characteristics of certain tree species (Ellison et al 2005a). Because foundation tree species often define or control the local microclimate, major changes in abiotic conditions are expected as eastern hemlock declines and is replaced progressively by early successional hardwoods, including birches (Betula spp.), red maples (Acer rubrum L.), and oaks (Quercus spp.) (Orwig et al 2002). These changes in abiotic conditions may be associated with changes in abundance of a number of animal species, including arthropods (Rohr et al 2009, Sackett et al 2011), birds (Tingley et al 2002), and aquatic invertebrates (Snyder et al 2002), as well as with changes in species interactions, successional pathways, and the rates of cycling of energy and nutrients (Orwig et al 2008, Gandhi and Herms 2010)

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