Higher Trophic Levels Overwhelm Climate Change Impacts on Terrestrial Ecosystem Functioning
RESEARCH ARTICLE
Higher Trophic Levels Overwhelm Climate
Change Impacts on Terrestrial Ecosystem
Functioning
Shannon L. Pelini1, Audrey M. Maran1, Angus R. Chen2¤a, Justine Kaseman1,2¤b, Thomas
W. Crowther3*
a11111
1 Department of Biological Sciences, Bowling Green State University, Bowling Green, OH, 43403, United
States of America, 2 Harvard Forest, Harvard University, Petersham, MA, 01366, United States of America,
3 School of Forestry and Environmental Studies, Yale University, New Haven, CT, 06511, United States of
America
¤a Current address: US Geological Survey, Dededo, 96912, Guam
¤b Current address: Freelance writing, Brooklyn, NY, 11233, USA
*
OPEN ACCESS
Citation: Pelini SL, Maran AM, Chen AR, Kaseman
J, Crowther TW (2015) Higher Trophic Levels
Overwhelm Climate Change Impacts on Terrestrial
Ecosystem Functioning. PLoS ONE 10(8): e0136344.
doi:10.1371/journal.pone.0136344
Editor: Andrea Belgrano, Swedish University of
Agricultural Sciences, SWEDEN
Received: May 22, 2015
Accepted: July 31, 2015
Published: August 20, 2015
Copyright: © 2015 Pelini et al. This is an open
access article distributed under the terms of the
Creative Commons Attribution License, which permits
unrestricted use, distribution, and reproduction in any
medium, provided the original author and source are
credited.
Data Availability Statement: Data are available on
the Harvard Forest data archive (accession number
hf113) at http://harvardforest.fas.harvard.edu/harvardforest-data-archive and on the Long Term Ecological
Research Network, doi:10.6073/pasta/
be0b964a5caedb3f9c89006eba29cbf7.
Funding: Funding was provided by United States
National Science Foundation Long Term Ecological
Research (DBI 10-03938) and Research Experiences
for Undergraduates (DBI 1459519) awards to
Harvard Forest. SLP received funds from the Building
Strength Program at Bowling Green State University.
TWC received funds from Yale University's Climate
Abstract
Forest floor food webs play pivotal roles in carbon cycling, but they are rarely considered in
models of carbon fluxes, including soil carbon dioxide emissions (respiration), under climatic warming. The indirect effects of invertebrates on heterotrophic (microbial and invertebrate) respiration through interactions with microbial communities are significant and will be
altered by warming. However, the interactive effects of invertebrates and warming on heterotrophic respiration in the field are poorly understood. In this study we combined field and
common garden laboratory approaches to examine relationships between warming, forest
floor food web structure, and heterotrophic respiration. We found that soil animals can overwhelm the effects of warming (to 5 degrees Celsius above ambient) on heterotrophic respiration. In particular, the presence of higher trophic levels and burrowing detritivores strongly
determined heterotrophic respiration rates in temperate forest soils. These effects were,
however, context-dependent, with greater effects in a lower-latitude site. Without isolating
and including the significant impact of invertebrates, climate models will be incomplete, hindering well-informed policy decisions.
Introduction
There is a critical need to improve estimates of future soil CO2 emissions (soil respiration, RS),
which are 10 × greater than those generated by the burning of fossil fuels [1], and the potential
feedbacks of the emissions to climate change. The impacts of increasing temperatures on
microbes, which, along with plant roots are the primary contributors to RS, are included in
determination of soil-climate change feedbacks [2–5]. While the direct contribution of other
soil and litter-dwelling organisms (e.g., invertebrate detritivores, vertebrate predators) to the
heterotrophic component of RS (i.e., RH) is presumed to be small relative to that of microbes,
PLOS ONE | DOI:10.1371/journal.pone.0136344 August 20, 2015
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Soil Macroinvertebrates Drive Carbon Release
and Energy Institute and the British Ecological
Society. The authors thank Rob Dunn, Aaron Ellison,
Nick Gotelli, and Nate Sanders for allowing use of the
warming chambers, funded by United States
Department of Energy Program for Ecosystem
Research (DE-FG02-08ER64510). The funders had
no role in study design, data collection and analysis,
decision to publish, or preparation of the manuscript.
Competing Interests: The authors have declared
that no competing interests exist.
the indirect effects of climate change on RH through animal-microbe interactions have not
been sufficiently explored. Indeed, the absence of soil animals, particularly invertebrates, has
been highlighted as a major limitation to current climate and carbon cycling models and management practices [6–10].
Soil food webs are dominated by invertebrates, which govern decomposition rates and soil
structure via their interactions with microbial communities [11–17]. Direct trophic effects of
invertebrates can regulate microbial activity in some regions [18,19], but the indirect effects
generally enhance microbial growth and respiration. That is, by shredding litter [15,17,20,21]
and moving soil [11,12,22,23], invertebrate engineers have the potential to stimulate microbial
growth and nutrient mineralization [24].
Temperate forests harbor a variety of organisms that also have the capacity to drive cascading effects on microbial activity. However, there is mixed support for top-down trophic cascades on RH via invertebrate predation [25,26]. Best and Welsh [27] demonstrated that
salamanders affect forest leaf litter retention by regulating invertebrate populations, but the
impacts on microbes and RH remain unknown. The potential for cascading effects on RH needs
to be explored further because multiple studies have shown that warming strengthens the
effects of predators on lower trophic levels and nutrient cycling in other food webs [21,28,29].
Invertebrates are highly responsive to climatic change [reviewed in 30]. Because invertebrates are ectotherms, the rates and magnitudes of predation and engineering should increase
with temperature, at least until thermal thresholds are exceeded or competitive interactions
shift [31]. The effects of warming on invertebrate activity may be magnified if soil invertebrates
increase movement throughout the soil [32]. Based on this pattern, our understanding of RH
responses to warming remains incomplete until we consider the indirect effects of warming
mediated through invertebrates.
In this study we examined relationships between warming, forest floor food web structure,
and RH. We combined field and common garden laboratory experiments to separate indirect
from direct and individual from community structure responses to warming on RH. More specifically, using open-top warming chambers at Harvard Forest and Duke Forest, we evaluated
the effects of (1) warming on food web structure-RH interactions, (2) macroinvertebrate communities shaped by different warming scenarios on RH, a (...truncated)