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. 2020 Aug 11;15(8):e0237368.
doi: 10.1371/journal.pone.0237368. eCollection 2020.

Patient propagules: Do soil archives preserve the legacy of fungal and prokaryotic communities?

Affiliations

Patient propagules: Do soil archives preserve the legacy of fungal and prokaryotic communities?

Gian Maria Niccolò Benucci et al. PLoS One. .

Abstract

Soil archives are an important resource in agronomic and ecosystem sciences. If microbial communities could be reconstructed from archived soil DNA, as prehistoric plant communities are reconstructed via pollen data, soil archive resources would assume even greater value for reconstructing land-use history, forensic science, and biosphere modelling. Yet, the effects of long-term soil archival on the preservation of microbial DNA is still largely unknown. To address this, we assessed the capacity of high-throughput sequencing (Illumina MiSeq) of ITS (internal transcribed spacer) and prokaryotic 16S rRNA genes for reconstructing soil microbial communities across a 20 years time-series. We studied air-dried soil archives and fresh soil samples taken from Populus bioenergy and deciduous forest research plots at the Kellogg Biological Station. Habitat and archival time explained significant amounts of variation in soil microbial α- and β-diversity both in fungal and prokaryotic communities. We found that microbial richness, diversity, and abundance generally decreased with storage time, but varied between habitat and taxonomic groups. The high relative abundance of ectomycorrhizal species including Hebeloma and Cortinarius detected in older soil archives raises questions regarding traits such as long-term persistence and viability of ectomycorrhizal propagules in soils, with relevance to forest health and ecosystem succession. Talaromyces, Paecilomyces and Epicoccum spp. were detected in fresh and across 20-year-old archived soils and were also cultured from these soils demonstrating their long-term spore viability. In summary, we found that microbial DNA in air-dried soils archived over the past 20 years degraded with time, in a manner that differed between soil types and phylogenetic groups of microbes.

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Conflict of interest statement

The authors have declared that no competing interests exist.

Figures

Fig 1
Fig 1
Fungal (A) and prokaryotic (B) rarefied richness boxplots (n = 3) in Experiment 1, Experiment 2, and Experiment 3 (See M&M for details). Plots are faceted by DF (deciduous forest) and PS (Populus stand) habitats. Red diamonds represent the mean of the distribution.
Fig 2
Fig 2. Best models of rarefied richness variation according to storage time (Exp1).
Points represent samples of fungal (A) and prokaryotic communities (C) in DF (deciduous forest) habitat and fungal (B) and prokaryotic (D) communities in PS (Populus stand) habitat.
Fig 3
Fig 3. Non-Metric Multidimensional Scaling (NMDS) and Canonical Analysis Of Principal Coordinates (CAP) ordinations.
Plots for fungal (A, C) and (B, D) prokaryotic communities are shown. Analyses were performed on even-depth normalized read abundance and bray-curtis distance.
Fig 4
Fig 4. Heatmap of relative abundance and OTU richness of all the fungal classes detected in DF (deciduous forest) and PS (Populus stand) soils after increasing storage years.
Taxon relative abundance was square root transformed to improved visibility. Black indicates zero relative abundance or absent taxa. For taxa marked with * subphylum was used instead of Class incertae sedis.
Fig 5
Fig 5. Heatmap of relative abundance and OTU richness of only the mycorrhizal (A), pathogenic (B), and endophytic (C) fungal genera after increasing storage years.
Plots are faceted by DF (deciduous forest) and PS (Populus stand) soils. Taxon relative abundance was square root transformed to improved visibility. Black indicates zero relative abundance or absent taxa.
Fig 6
Fig 6. Taxonomic turnover and compositional changes in fungal and prokaryotic communities.
Total OTU turnover, OTU gained and OTU dropped, for fungal (A) and prokaryotic (B) communities in both DF (deciduous forest) and PS (Pupulus stand), and compositional community changes described by Euclidean distances in fungal (C) and prokaryotic (D) communities in DF and PS.

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Grants and funding

This research was supported through AgBioResearch NIFA, projects MICL02416 and MICL08541, and the Great Lakes Bioenergy Research Center, U.S. Department of Energy, Office of Science, Office of Biological and Environmental Research, under award number DE-SC0018409.
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