Abstract

AbstractDeadwood is an important legacy structure in managed forests, providing continuity in shelter and resource availability for many organisms and acting as a vehicle by which nutrients can be passed from one stand to the next following a harvest. Despite existing at the interface between below‐ and above‐ground systems, however, much remains unknown about the role woody debris plays in linking these zones. Moreover, it remains untested whether the accelerative effects of wood‐feeding insects on wood decomposition influence tree growth or nutritional status in forests. In this study, we added different quantities of pine logs to the bases of saplings in two‐year‐old loblolly pine (Pinus taeda L.) plantations in Mississippi, USA. We included a treatment in which subterranean termites (Blattodea: Rhinotermitidae: Reticulitermes) were excluded from logs to determine how these insects affect the release of nutrients from wood and, in turn, tree growth. After 51 months of decomposition, we quantified below‐ground effects by measuring microbial biomass, plant‐available forms of N, and ectomycorrhizal diversity associated with fine tree roots. Meanwhile, above‐ground measurements focused on the elemental concentrations in decomposing wood either protected or unprotected from termites and tree metrics related to growth and nutrient status. We found additions of wood to significantly increase nitrate and potential net nitrification relative to reference treatments but detected no significant effects on tree growth, needle nitrogen concentrations, or ectomycorrhizal diversity. Soil nitrate and potential net nitrification were higher under protected vs. unprotected logs, and plant‐available forms of N were mostly more abundant short distances away from both protected and unprotected logs than directly under them. The wood of logs protected from termites had significantly lower concentrations of most elements compared to that of unprotected logs, largely due to the large amounts of soil imported into unprotected logs by termites. Termite exclusion had no measurable effect on tree growth, nutritional status, or ectomycorrhizal diversity, however. Our findings indicate that deadwood and termites both contribute to the spatial heterogeneity of soil properties but may have limited short‐term local effects on tree growth. Longer‐term studies and studies on less fertile sites are needed.

Highlights

  • The challenge of ecological forestry is to balance the demand for timber products with the desire to protect natural processes and associated biodiversity (Seymour and Hunter 1999)

  • There were no significant differences for all other soil parameters (100% water-holding capacity (WHC), pH, mineralizable C, microbial N, microbial C, microbial C:N, and Dissolved organic N (DON); see Fig. 2)

  • What to do with woody debris created during a logging operation remains an important question for forest managers, especially today with growing demand for woody biofuels (Eisenbies et al 2009, Tilman et al 2009) and concerns about wildfire risk (Graham et al 2004, Agee and Skinner 2005)

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Summary

Introduction

The challenge of ecological forestry is to balance the demand for timber products with the desire to protect natural processes and associated biodiversity (Seymour and Hunter 1999). Areas of overlap within which management decisions can potentially help satisfy both objectives are of great practical interest. One such area concerns deadwood and the dual role it plays in supporting a large fraction of forest biodiversity (~20–30% of all forest animal species, for example, Stokland et al 2012) and acting as a long-term source of nutrients (Laiho and Prescott 2004, Palviainen et al 2010). With a growing interest in removing woody debris for biofuel production (Eisenbies et al 2009, Tilman et al 2009, Pare and Thiffault 2016) as well as fuel reduction treatments to reduce wildfire risks (Graham et al 2004, Agee and Skinner 2005), research is needed to develop a more holistic basis for any decision concerning these legacy structures (Franklin et al 2007) in managed forests

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