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. 2012 Dec;6(12):2199-218.
doi: 10.1038/ismej.2012.84. Epub 2012 Aug 2.

Significant and persistent impact of timber harvesting on soil microbial communities in Northern coniferous forests

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Significant and persistent impact of timber harvesting on soil microbial communities in Northern coniferous forests

Martin Hartmann et al. ISME J. 2012 Dec.

Erratum in

  • ISME J. 2012 Dec;6(12):2320

Abstract

Forest ecosystems have integral roles in climate stability, biodiversity and economic development. Soil stewardship is essential for sustainable forest management. Organic matter (OM) removal and soil compaction are key disturbances associated with forest harvesting, but their impacts on forest ecosystems are not well understood. Because microbiological processes regulate soil ecology and biogeochemistry, microbial community structure might serve as indicator of forest ecosystem status, revealing changes in nutrient and energy flow patterns before they have irreversible effects on long-term soil productivity. We applied massively parallel pyrosequencing of over 4.6 million ribosomal marker sequences to assess the impact of OM removal and soil compaction on bacterial and fungal communities in a field experiment replicated at six forest sites in British Columbia, Canada. More than a decade after harvesting, diversity and structure of soil bacterial and fungal communities remained significantly altered by harvesting disturbances, with individual taxonomic groups responding differentially to varied levels of the disturbances. Plant symbionts, like ectomycorrhizal fungi, and saprobic taxa, such as ascomycetes and actinomycetes, were among the most sensitive to harvesting disturbances. Given their significant ecological roles in forest development, the fate of these taxa might be critical for sustainability of forest ecosystems. Although abundant bacterial populations were ubiquitous, abundant fungal populations often revealed a patchy distribution, consistent with their higher sensitivity to the examined soil disturbances. These results establish a comprehensive inventory of bacterial and fungal community composition in northern coniferous forests and demonstrate the long-term response of their structure to key disturbances associated with forest harvesting.

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Figures

Figure 1
Figure 1
Abundance versus dispersion plots of bacterial (left) and fungal (right) OTUs across all samples. Colors denote OTUs that were significantly associated on the basis of indicator species analysis (q <0.1) with either forest site or soil horizon (location indicators, open green circles) or with OM removal or soil compaction (treatment indicators, closed red circles); non significant OTUs are shown as open black circles. Some treatment indicators were also location indicators.
Figure 2
Figure 2
Principal coordinate analysis (PCO) ordinations of bacterial (a, c) and fungal (b, d) communities based on relative abundances of OTUs. Upper panels (a, b): ordinations of total samples from both organic (ORG) and mineral (MIN) soil horizons at six sites in both the SBS and IDF biogeoclimatic zones. Lower panels (c, d): separate ordinations for each soil horizon in each biogeoclimatic zone, with symbols for each site identified in panel c. Variance explained by each PCO axis is given in parentheses.
Figure 3
Figure 3
Canonical analysis of principal coordinates (CAP) ordinations of bacterial (a, c) and fungal (b, d) communities based on relative abundances of OTUs. These constrained ordinations show maximized differences among the different levels of OM removal (a, b) and soil compaction (c, d). Classification success rates for each treatment group are given in parentheses. Levels of OM removal: reference plots (REF), green circles; OM1, light-red triangles; OM2, red squares; and OM3, dark-red diamonds. Levels of soil compaction: reference plots (REF), green circles; no compaction (C0), light-blue triangles; moderate compaction (C1), blue squares; and severe compaction (C2), dark-blue diamonds. The canonical correlation (δ2) of each CAP axis is given in parentheses. TraceQ_m′HQ_m test statistics are given at the bottom of each ordination.
Figure 4
Figure 4
CAP ordinations of major fungal and bacterial phyla based on relative abundances of OTUs. These constrained ordinations show maximized differences among the different levels of OM removal. Levels of OM removal are represented by symbols and colors as in Figure 3. Classification success rates for each treatment group are given in parentheses. TraceQ_m′HQ_m test statistics are given at the bottom of each ordination.
Figure 5
Figure 5
Simpson's evenness (E1/D) of the bacterial (a, b) and fungal (c, d) communities based on OTUs. Indices were normalized within each site relative to the reference plots. Panels a and c compare evenness among different levels of OM removal with no compaction. Values are displayed as treatment-specific averages including s.e. Different letters indicate significant differences based on one-way ANOVA (F-test and P-value) followed by Fisher's least significant difference test (P <0.05). Panels b and d compare evenness within the 3 × 3 factorial design of OM removal and soil compaction, excluding the reference plots. Significant differences among a priori defined that groups were evaluated using factorial analysis of variance (F-test and P-value) followed by a desirability approach.
Figure 6
Figure 6
Indicator tree showing the taxonomy and taxon-treatment association strength of all 168 fungal species significantly associated with OM removal. Color ranges identify phyla within the tree. Legend colors identify circles. Diameters of black circles in the most inner ring represent the square-root transformed abundance of the corresponding species in the overall community. Diameters of the remaining circles represent the relative, significant (q <0.01) association strength between the corresponding species and the OM removal treatments identified by color. The putative lifestyle of each species is indicated in square brackets and was predicted based on available literature as listed in Supplementary Table S3. AMF, arbuscular mycorrhizal fungi; Ca, Carnivore; Co, Coprophile; E, endophyte; EMF, ectomycorrhizal fungi; P, pathogen/parasite; S, saprobe; U, unknown status. The full interactive tree is accessible at http://itol.embl.de/external.cgi?tree=128189114252250313147317530.
Figure 7
Figure 7
Indicator tree showing the taxonomy and taxon-treatment association strength of all 83 bacterial genera significantly associated with OM removal. Color ranges identify phyla (and proteobacterial classes) within the tree. Legend colors identify circles. Diameters of black circles in the innermost ring represent the square-root transformed abundance of the corresponding genera in the overall community. Diameters of the remaining circles represent the relative, significant (q <0.01) association strength between the corresponding genus and the OM removal treatments identified by color. The full interactive tree is accessible at http://itol.embl.de/external.cgi?tree=128189114252273613147321440.

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