Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2014 Sep;8(9):1920-31.
doi: 10.1038/ismej.2014.37. Epub 2014 Mar 27.

When the forest dies: the response of forest soil fungi to a bark beetle-induced tree dieback

Affiliations

When the forest dies: the response of forest soil fungi to a bark beetle-induced tree dieback

Martina Stursová et al. ISME J. 2014 Sep.

Abstract

Coniferous forests cover extensive areas of the boreal and temperate zones. Owing to their primary production and C storage, they have an important role in the global carbon balance. Forest disturbances such as forest fires, windthrows or insect pest outbreaks have a substantial effect on the functioning of these ecosystems. Recent decades have seen an increase in the areas affected by disturbances in both North America and Europe, with indications that this increase is due to both local human activity and global climate change. Here we examine the structural and functional response of the litter and soil microbial community in a Picea abies forest to tree dieback following an invasion of the bark beetle Ips typographus, with a specific focus on the fungal community. The insect-induced disturbance rapidly and profoundly changed vegetation and nutrient availability by killing spruce trees so that the readily available root exudates were replaced by more recalcitrant, polymeric plant biomass components. Owing to the dramatic decrease in photosynthesis, the rate of decomposition processes in the ecosystem decreased as soon as the one-time litter input had been processed. The fungal community showed profound changes, including a decrease in biomass (2.5-fold in the litter and 12-fold in the soil) together with the disappearance of fungi symbiotic with tree roots and a relative increase in saprotrophic taxa. Within the latter group, successive changes reflected the changing availability of needle litter and woody debris. Bacterial biomass appeared to be either unaffected or increased after the disturbance, resulting in a substantial increase in the bacterial/fungal biomass ratio.

PubMed Disclaimer

Figures

Figure 1
Figure 1
Montane P. abies forest at Site A before (spring 2008) and after a tree dieback caused by a bark beetle invasion in summer 2008. After 2 years, the dead trees were still covered with bark and retained most of their branches (2010). Four years after the initial damage, much of the dead wood and bark had fallen to the ground (2012).
Figure 2
Figure 2
Nutrient composition, microbial biomass and enzyme activity in the litter and organic soil of a P. abies forest before and after a tree dieback caused by a bark beetle invasion. The data represent the means of three replicates with standard errors. Statistically significant differences among seasons are indicated by different letters. Right-hand axis displays variables indicated in red; abbreviations: Nmin – mineral N, Norg – organic N, NAGase – N-acetylglucosaminidase.
Figure 3
Figure 3
Phylogenetic assignment of fungal ITS sequences from a P. abies forest before and after a tree dieback caused by a bark beetle invasion. The data represent mean values from three study sites.
Figure 4
Figure 4
Principal component analysis of the relative abundances of fungal ITS sequences corresponding to dominant fungal genera in the litter and soil of a P. abies forest before and after a tree dieback caused by a bark beetle invasion. Sampling season loadings and environmental variables are indicated. All genera with ⩾0.5% abundance in ⩾3 samples were considered. Fungal genera with significant differences in abundance among years are underlined. Root symbiotic fungi are indicated in green, root endophytes in black and lichens in gray. DN, dissolved N; C/N, C/N ratio; bG, β-glucosidase; EC, endocellulase; Lac, laccase; NAG, N-acetylglucosaminidase; PME, phosphatase; PLFAB, bacterial PLFA; PLFAF, fungal PLFA; B/F, bacterial/fungal biomass ratio. Bottom panels show relative abundances of ecophysiological groups of fungi and selected fungal genera; data represent means (standard errors omitted for clarity).

References

    1. Adams HD, Macalady AK, Breshears DD, Allen CD, Stephenson NL, Saleska SR, Huxman TE, McDowell Ng. Climate-induced tree mortality: Earth system consequences. Eos, Trans Amer Geophys Union. 2010;91:153–154.
    1. Baldrian P, Kolařík M, Štursová M, Kopecký J, Valášková V, Větrovský T, et al. Active and total microbial communities in forest soil are largely different and highly stratified during decomposition. ISME J. 2012;6:248–258. - PMC - PubMed
    1. Baldrian P, Větrovský T, Cajthaml T, Dobiášová P, Petránková M, Šnajdr J, et al. Estimation of fungal biomass in forest litter and soil. Fungal Ecol. 2013;6:1–11.
    1. Bače R, Svoboda M, Pouska V, Janda P, Červenka J. Natural regeneration in Central-European subalpine spruce forests: which logs are suitable for seedling recruitment. Forest Ecol Manag. 2012;266:254–262.
    1. Bouget C, Duelli P. The effects of windthrow on forest insect communities: a literature review. Biol Conserv. 2004;118:281–299.

Publication types