Abstract:Summary
The generality of increasing diversity of fungi and bacteria across arctic sand dune succession was tested. Microbial communities were examined by high‐throughput sequencing of 16S rRNA genes (bacteria) and internal transcribed spacer (ITS) regions (fungi). We studied four microbial compartments (inside leaf, inside root, rhizosphere and bulk soil) and characterized microbes associated with a single plant species (Deschampsia flexuosa) across two sand dune successional stages (early and late). Bacteria… Show more
“…Some of the changes in relative abundance observed here agree with findings from other studies, such as an increase in Verrucomicrobia (Nemergut et al, 2007) and Acidobacteria (Nemergut et al, 2007;Yarwood and Högberg, 2017) over succession and an abundance of cyanobacteria (Schmidt et al, 2008;Zumsteg et al, 2012;Yarwood and Högberg, 2017) and algae (Kaštovská et al, 2005) in early successional stages. However, some of our results differ from prior studies that show decreases in Actinobacteria (Zumsteg et al, 2012;Poosakkannu et al, 2017) and shifts from Ascomycota to Basiodiomycota (Zumsteg et al, 2012) with succession in alpine and arctic areas, suggesting that succession may proceed differently at different sites even at a broad taxonomic level.…”
Section: Discussioncontrasting
confidence: 99%
“…Recent work suggests that the composition of microbes changes considerably and predictably during primary succession (Nemergut et al, 2007;Tarlera et al, 2008;Roy-Bolduc et al, 2015;Poosakkannu et al, 2017), with certain groups like Actinobacteria and N fixers prevalent in early successional stages, and other groups such as Acidobacteria and mycorrhizal taxa dominating later stages (Rime et al, 2015;Poosakkannu et al, 2017;Yarwood and Högberg, 2017). Much work also suggests that the taxonomic diversity (Nemergut et al, 2007;Tarlera et al, 2008;Brown and Jumpponen, 2014;Rime et al, 2015;Poosakkannu et al, 2017) and functional diversity (Tscherko et al, 2003) of soil bacterial and fungal communities generally increase during succession. However, some studies find decreases, no change, or variable patterns for some or all taxa (Sigler and Zeyer, 2002;Brown and Jumpponen, 2014;Dini-Andreote et al, 2014;Poosakkannu et al, 2017).…”
Section: Introductionmentioning
confidence: 99%
“…Much work also suggests that the taxonomic diversity (Nemergut et al, 2007;Tarlera et al, 2008;Brown and Jumpponen, 2014;Rime et al, 2015;Poosakkannu et al, 2017) and functional diversity (Tscherko et al, 2003) of soil bacterial and fungal communities generally increase during succession. However, some studies find decreases, no change, or variable patterns for some or all taxa (Sigler and Zeyer, 2002;Brown and Jumpponen, 2014;Dini-Andreote et al, 2014;Poosakkannu et al, 2017).…”
While it is well established that microbial composition and diversity shift along environmental gradients, how interactions among microbes change is poorly understood. Here, we tested how community structure and species interactions among diverse groups of soil microbes (bacteria, fungi, non-fungal eukaryotes) change across a fundamental ecological gradient, succession. Our study system is a high-elevation alpine ecosystem that exhibits variability in successional stage due to topography and harsh environmental conditions. We used hierarchical Bayesian joint distribution modeling to remove the influence of environmental covariates on species distributions and generated interaction networks using the residual species-to-species variance-covariance matrix. We hypothesized that as ecological succession proceeds, diversity will increase, species composition will change, and soil microbial networks will become more complex. As expected, we found that diversity of most taxonomic groups increased over succession, and species composition changed considerably. Interestingly, and contrary to our hypothesis, interaction networks became less complex over succession (fewer interactions per taxon). Interactions between photosynthetic microbes and any other organism became less frequent over the gradient, whereas interactions between plants or soil microfauna and any other organism were more abundant in late succession. Results demonstrate that patterns in diversity and composition do not necessarily relate to patterns in network complexity and suggest that network analyses provide new insight into the ecology of highly diverse, microscopic communities.
“…Some of the changes in relative abundance observed here agree with findings from other studies, such as an increase in Verrucomicrobia (Nemergut et al, 2007) and Acidobacteria (Nemergut et al, 2007;Yarwood and Högberg, 2017) over succession and an abundance of cyanobacteria (Schmidt et al, 2008;Zumsteg et al, 2012;Yarwood and Högberg, 2017) and algae (Kaštovská et al, 2005) in early successional stages. However, some of our results differ from prior studies that show decreases in Actinobacteria (Zumsteg et al, 2012;Poosakkannu et al, 2017) and shifts from Ascomycota to Basiodiomycota (Zumsteg et al, 2012) with succession in alpine and arctic areas, suggesting that succession may proceed differently at different sites even at a broad taxonomic level.…”
Section: Discussioncontrasting
confidence: 99%
“…Recent work suggests that the composition of microbes changes considerably and predictably during primary succession (Nemergut et al, 2007;Tarlera et al, 2008;Roy-Bolduc et al, 2015;Poosakkannu et al, 2017), with certain groups like Actinobacteria and N fixers prevalent in early successional stages, and other groups such as Acidobacteria and mycorrhizal taxa dominating later stages (Rime et al, 2015;Poosakkannu et al, 2017;Yarwood and Högberg, 2017). Much work also suggests that the taxonomic diversity (Nemergut et al, 2007;Tarlera et al, 2008;Brown and Jumpponen, 2014;Rime et al, 2015;Poosakkannu et al, 2017) and functional diversity (Tscherko et al, 2003) of soil bacterial and fungal communities generally increase during succession. However, some studies find decreases, no change, or variable patterns for some or all taxa (Sigler and Zeyer, 2002;Brown and Jumpponen, 2014;Dini-Andreote et al, 2014;Poosakkannu et al, 2017).…”
Section: Introductionmentioning
confidence: 99%
“…Much work also suggests that the taxonomic diversity (Nemergut et al, 2007;Tarlera et al, 2008;Brown and Jumpponen, 2014;Rime et al, 2015;Poosakkannu et al, 2017) and functional diversity (Tscherko et al, 2003) of soil bacterial and fungal communities generally increase during succession. However, some studies find decreases, no change, or variable patterns for some or all taxa (Sigler and Zeyer, 2002;Brown and Jumpponen, 2014;Dini-Andreote et al, 2014;Poosakkannu et al, 2017).…”
While it is well established that microbial composition and diversity shift along environmental gradients, how interactions among microbes change is poorly understood. Here, we tested how community structure and species interactions among diverse groups of soil microbes (bacteria, fungi, non-fungal eukaryotes) change across a fundamental ecological gradient, succession. Our study system is a high-elevation alpine ecosystem that exhibits variability in successional stage due to topography and harsh environmental conditions. We used hierarchical Bayesian joint distribution modeling to remove the influence of environmental covariates on species distributions and generated interaction networks using the residual species-to-species variance-covariance matrix. We hypothesized that as ecological succession proceeds, diversity will increase, species composition will change, and soil microbial networks will become more complex. As expected, we found that diversity of most taxonomic groups increased over succession, and species composition changed considerably. Interestingly, and contrary to our hypothesis, interaction networks became less complex over succession (fewer interactions per taxon). Interactions between photosynthetic microbes and any other organism became less frequent over the gradient, whereas interactions between plants or soil microfauna and any other organism were more abundant in late succession. Results demonstrate that patterns in diversity and composition do not necessarily relate to patterns in network complexity and suggest that network analyses provide new insight into the ecology of highly diverse, microscopic communities.
“…DNA was extracted from the homogenized leaf (100 mg) and root (100 mg) material from each plant using Invisorb Spin Plant Mini Kit (Stratec molecular). We used the M13 system (Mäki et al 2016) for library preparation as described by Poosakkannu et al (2017). In brief, a nested approach was used to amplify the partial 16S rRNA genes; the first round of 16S rRNA amplification was performed with primers 799F (5´-AACMGGATTAGATACCCKG-3´) and 1492R (5´-GGYTACTTGTTACGACTT-3´) which excludes plant chloroplast amplification (Chelius and Triplett 2001).…”
Section: Dna Extraction Library Preparation and Sequencingmentioning
confidence: 99%
“…Distinct factors such as plant part inhabited, host genotype and soil type affect the plantassociated microbial assemblage (Lundberg et al 2012;Edwards et al 2015;Coleman-Derr et al 2016;Robinson et al 2016;Poosakkannu et al 2015;Poosakkannu et al 2017).…”
The effects of arbuscular mycorrhizal (AM) fungi on plant-associated microbes are poorly known. We tested the hypothesis that colonization by an AM fungus affects microbial species richness and microbial community composition of host plant tissues. We grew the grass, Deschampsia flexuosa in a greenhouse with or without the native AM fungus, Claroideoglomus etunicatum. We divided clonally produced tillers into two parts: one inoculated with AM fungus spores and one without AM fungus inoculation (non-mycorrhizal, NM). We characterized bacterial (16S rRNA gene) and fungal communities (internal transcribed spacer region) in surface-sterilized leaf and root plant compartments. AM fungus inoculation did not affect microbial species richness or diversity indices in leaves or roots, but the AM fungus inoculation significantly affected bacterial community composition in leaves. A total of three OTUs in leaves belonging to the phylum Firmicutes positively responded to the presence of the AM fungus in roots. Another six OTUs belonging to the Proteobacteria (Alpha, Beta, and Gamma) and Bacteroidetes were significantly more abundant in NM plants when compared to AM fungus-inoculated plants. Further, there was a significant correlation between plant dry weight and leaf microbial community compositional shift. Also, there was a significant correlation between leaf bacterial community compositional shift and foliar nitrogen content changes due to AM fungus inoculation. The results suggest that AM fungus colonization in roots has a profound effect on plant physiology that is reflected in leaf bacterial community composition.
In desert areas, the process of mobile sandy land changing to semi‐fixed sandy land and eventually to fixed sandy land after undergoing vegetation restoration is inevitable. The presence of shrub patches and herb patches is common in this restoration process. No relevant studies have reported the soil bacterial community characteristics of different vegetation‐type patches (shrub patches and herb patches) under different stages of restoration. Therefore, we utilized long‐established experimental plots to collect soil from 0–20 cm soil layer under shrub patches (dominated by Salix psammophila) and herb patches under different stages of restoration (i.e., mobile sand land, semi‐fixed sand land, and fixed sand land), by determining soil physicochemical properties, enzyme activities, and soil bacterial communities. Our results found that soil bacterial α‐diversity under different restoration stages showed higher shrub patches than herb patches. The dominant bacterial communities (phyla) in shrub patches and herb patches at different recovery stages were Actinobacteria, Proteobacteria, and Bacteroidota. When the mobile sandy land returned to fixed sandy land, the relative abundance of Actinobacteria and Bacteroidota gradually decreased under shrub patches and herb patches, while the relative abundance of Proteobacteria increased significantly. In addition, herb patches significantly increased the relative abundance of bacteria (genus) relative to shrub patches at different stages of recovery. Soil nutrients, soil fine particles, and soil enzyme activities were significantly higher under shrub patches than under herb patches when fixed sandy land due to differences in life form and architecture between shrub patches and herb patches. Based on this, soil bacterial community composition and diversity under shrub patches were driven by more soil properties during the restoration of sandy land. This study complements the dynamic recovery processes and driving mechanisms of soil bacterial community structure under different vegetation patches in sandy areas, especially in the context of global climate change.
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