Tree regeneration retards decomposition in a temperate mountain soil
after forest gap disturbance
Mathias Mayer
*
, Bradley Matthews, Christoph Rosinger, Hans Sand
en, Douglas L. Godbold,
Klaus Katzensteiner
Institute of Forest Ecology, Department of Forest and Soil Sciences, University of Natural Resources and Life Sciences Vienna (BOKU), Peter-Jordan Straße 82,
1190 Wien, Austria
article info
Article history:
Received 23 March 2017
Received in revised form
26 July 2017
Accepted 10 September 2017
Keywords:
Forest disturbance
Heterotrophic soil respiration
Soil carbon loss
Soil CO
2
efflux
Soil enzymes
Soil organic matter
abstract
Disturbances significantly affect the carbon (C) cycle of forest ecosystems. Surviving trees from an un-
derstory layer are recognized to play an important role in post-disturbance C dynamics. However, their
influence on decomposition of soil organic matter (SOM), an important ecosystem C pool, has yet to be
rigorously investigated. Over four consecutive years, we investigated the effects of advance spruce
regeneration on decomposition processes in a mountain soil after forest gap disturbance. Gap distur-
bance was accomplished by clear cut harvest and decomposition was assessed by combining measure-
ments of soil CO
2
efflux, heterotrophic respiration, soil enzymes activity, and mass loss from
standardized litter bags. Soil CO
2
efflux showed no response to gap formation, independent of whether
regeneration was present or absent, indicating that reduced autotrophic respiration was offset by
accelerated heterotrophic respiration from decomposing microbes. Incubation studies revealed no effects
of gap disturbance on heterotrophic respiration and its temperature sensitivity under controlled lab
conditions. Since potential enzyme activities, at a given temperature, did not respond to gap formation
either, it appears that neither C nor other nutrient limitations of the decomposing microbes changed in
this SOM-rich mountain forest soil after disturbance. Mass loss of standardized litter was ~5% higher after
gap formation in plots without regeneration, while under the regeneration it remained at control stand
levels. Our findings indicate that canopy removal by gap disturbance lead to an increase in decompo-
sition, primarily due to warmer soil conditions. However, an established regeneration retards decom-
position due to its modulating effect on soil temperature. Our study therefore shows that facilitating
regeneration pre-disturbance can reduce post-disturbance soil C losses from decomposition.
© 2017 Published by Elsevier Ltd.
1. Introduction
Forests of the northern hemisphere store large amounts of
carbon (C) and thus represent a globally important C sink (Goodale
et al., 2002; Luyssaert et al., 2010). Natural and man-made distur-
bances can, however, significantly alter the C balance and the C
sequestration potential of these ecosystems (Kowalski et al., 2004;
Kurz et al., 2008; Amiro et al., 2010; Paul-Limoges et al., 2015).
Beside the changes in ecosystem CO
2
fluxes associated with
photosynthesis and autotrophic respiration, disturbances can
impact heavily on the CO
2
efflux coupled to the decomposition of
soil organic matter (SOM). Although disturbance type (e.g. clear cut
harvest, bark beetle attack, fire), severity (e.g. single tree mortality,
stand replacing mortality), and time since disturbance (e.g. weeks,
decades) might influence decomposition differently, recent meta-
analyses have shown that disturbances generally cause long-
lasting C losses from forest soils (Nave et al., 2010; Thom and
Seidl, 2015; Zhang et al., 2015). If, and to what extent a decrease
in soil C stocks is actually related to altered decomposition rates
and/or changes in C input to soil is, however, still uncertain (Yanai
et al., 2003; Spielvogel et al., 2006; Christophel et al., 2015).
Furthermore, how the post-disturbance soil C pool is influenced by
surviving sub-canopy trees has yet to be addressed in detail.
Live tree legacies are of considerable importance for ecosystem
resilience (Seidl et al., 2014). Surviving trees from a sub-canopy
layer (e.g. seedlings and saplings from regeneration, sub-
* Corresponding author. Tel.: 0043 1 47654 91243.
E-mail addresses: mathias_mayer@gmx.at (M. Mayer), bradley.matthews@boku.
ac.at (B. Matthews), christoph.rosinger@boku.ac.at (C. Rosinger), hans.sanden@
boku.ac.at (H. Sand en), douglas.godbold@boku.ac.at (D.L. Godbold), klaus.
katzensteiner@boku.ac.at (K. Katzensteiner).
Contents lists available at ScienceDirect
Soil Biology & Biochemistry
journal homepage: www.elsevier.com/locate/soilbio
https://doi.org/10.1016/j.soilbio.2017.09.010
0038-0717/© 2017 Published by Elsevier Ltd.
Soil Biology & Biochemistry 115 (2017) 490e498