Corrected on Sep 15, 2020.
Source: the publisher, via Crossref · checked Oct 22, 2026 · Read the notice
GlobalFungi, a global database of fungal occurrences from high-throughput-sequencing metabarcoding studies
Tomáš Větrovský, Daniel Morais, Petr Kohout and 30 more
Scientific Data · 2020 · CC BY
Abstract
Fungi are key players in vital ecosystem services, spanning carbon cycling, decomposition, symbiotic associations with cultivated and wild plants and pathogenicity. The high importance of fungi in ecosystem processes contrasts with the incompleteness of our understanding of the patterns of fungal biogeography and the environmental factors that drive those patterns. To reduce this gap of knowledge, we collected and validated data published on the composition of soil fungal communities in terrestrial environments including soil and plant-associated habitats and made them publicly accessible through a user interface at https://globalfungi.com . The GlobalFungi database contains over 600 million observations of fungal sequences across > 17 000 samples with geographical locations and additional metadata contained in 178 original studies with millions of unique nucleotide sequences (sequence variants) of the fungal internal transcribed spacers (ITS) 1 and 2 representing fungal species and genera. The study represents the most comprehensive atlas of global fungal distribution, and it is framed in such a way that third-party data addition is possible.
Full text
From PubMed Central, U.S. National Library of Medicine, as current on Oct 22, 2026. Paragraph numbers are ours, so an answer can point at one.
Background & Summary
Fungi play fundamental roles in the ecosystem processes across all terrestrial biomes. As plant symbionts, pathogens or major decomposers of organic matter they substantially influence plant primary production, carbon mineralization and sequestration, and act as crucial regulators of the soil carbon balance,. The activities of fungal communities contribute to the production of clean water, food, and air and the suppression of disease-causing soil organisms. Soil fungal biodiversity is thus increasingly recognized to provide services critical to food safety and human health.
It is of high importance to determine how environmental factors affect the diversity and distribution of fungal communities. So far, only a few studies have focused on fungal distribution and diversity on global scale–. Importantly, these single survey studies focused either on a limited number of biomes,, fairly narrow groups within the fungal kingdom, or were restricted only to fungi inhabiting soil. Although individual studies have the advantage of standardized methodology across their whole dataset, their limitation is in the limited sampling efforts in space and time that do not allow general conclusions on distribution of fungal taxa. On the other hand, since the advent of high-throughput-sequencing methods, large amounts of sequencing data on fungi from terrestrial environments accumulated along with metadata across numerous studies and allow interesting analyses when combined. As an example of this approach, the meta-analysis of 36 papers made it possible to map global diversity of soil fungi collected in >3000 samples and indicated that climate is an important factor for the global distribution of soil fungi. This approach clearly demonstrated the utility of a meta-study approach to address fungal biogeography, ecology and diversity. In addition, the compilation of these data demonstrated the fact that symbiotic mycorrhizal fungi that aid cultivated and wild plants to access nutrients, are more likely to be affected by rapid changes of climate than other guilds of fungi, including plant pathogens and helped to identify which fungi tend to follow alien plants invading new environments.
Here, we have undertaken a comprehensive collection and validation of data published on the composition of fungal communities in terrestrial environments including soil and plant-associated habitats. This approach enabled us to construct the GlobalFungi database containing, on March 16, 2020, over 110 million unique sequence variants (i.e., unique nucleotide sequences) of the fungal nuclear ribosomal internal transcribed spacers (ITS) 1 and 2, covering > 17 000 samples contained in 178 original studies (Fig. 1). The ITS region has been used as molecular marker because it is a universal barcode for fungi.The dataset of sequence variant frequencies across samples, accompanied by metadata retrieved from published papers and in global climate databases is made publicly available at https://globalfungi.com. To achieve the goal to make published data findable, accessible, interoperable and reusable, the user interface at the above address allows the users to search for individual sequences, fungal species hypotheses, species or genera, to get a visual representation of their distribution in the environment and to access and download sequence data and metadata. In addition, the user interface also allows authors to submit data from studies not yet covered and in this way to help to build the resource for the community of researchers in systematics, biogeography, and ecology of fungi.
Data selection
We explored papers fitting with a main criterion, i.e., high-throughput sequencing for the analysis of fungal communities thanks to the ITS region, and that were published up to the beginning of 2019; in total, we explored 843 papers. The following selection criteria were used for the inclusion of samples (and, consequently, studies) into the dataset: (1) samples came from terrestrial biomes of soil, dead or live plant material (e.g., soil, litter, rhizosphere soil, topsoil, lichen, deadwood, root, and shoot) and were not subject to experimental treatment that artificially modifies the fungal community composition (e.g., temperature or nitrogen increase experiment, greenhouse controlled experiment were excluded); (2) the precise geographic location of each sample was recorded and released using GPS coordinates; (3) the whole fungal community was subject to amplicon sequencing (studies using group-specific primers were excluded); (4) the internal transcribed spacer regions (ITS1, ITS2, or both) were subject to amplification; (5) sequencing data (either in fasta with phred scores reported or fastq format) were publicly available or provided by the authors of the study upon request, and the sequences were unambiguously assigned to samples; (6) the samples could be assigned to biomes according to the Environment Ontology (http://www.ontobee.org/ontology/ENVO). In total, 178 publications contained samples that matched our criteria.
Processing of sequencing data
For the processing of data, see Fig. 2 and Code Availability section. Raw datasets from 178 studies, covering 17 242 individual samples were quality filtered by removing all sequences with the mean quality phred scores below 20. Each sequence was labelled using the combination of a sample ID and sequence ID, and the full ITS1 or ITS2 fungal region was extracted using Perl script ITSx v1.0.11. ITS extraction resulted in a total of 416 291 533 full ITS1 and 231 278 756 full ITS2 sequences. The extracted ITS sequences were classified according to the representative sequence of the closest UNITE species hypothesis (SH) using BLASTn, using the SH created considering a 98.5% similarity threshold (BLASTDBv5, general release 8.1 from 2.2.2019). A sequence was classified to the best best hit SH only when the following thresholds were met: e-value < 10e−50, sequence similarity > = 98.5%. All representative sequences annotated as nonfungal were discarded. All representative sequences classified to any fungal SH and all unclassified sequences were used to build database library of unique nucleotide sequences (sequence variants). The number of sequence variants accessible through the database is 113 423 871.
Sample metadata
Sample metadata were collected from the published papers and/or public repositories where they were submitted by the authors. In some cases, metadata were obtained from the authors of individual studies upon request. The samples were assigned to continents, countries, and specific locations when available, and all sites were categorized into biomes following the classification of Environment Ontology to a maximum achievable depth for each sample. The complete list of metadata included in the database is presented in Table 1.
In addition to the metadata provided by the authors of each study, we also extracted bioclimatic variables from the global CHELSA and WorldClim 2 databases for each sample based on its GPS location. Since the results based on CHELSA and WorldClim 2 were comparable, we decided to include those from CHELSA, because precipitation patterns are better captured in the CHELSA dataset, in particular for mountain sites.
For each sequence variant that was classified to SH, fungal species name and genus name was retrieved from the UNITE database, when available.
Data Records
The raw sequencing reads used to create the database are available at different locations (see Table 2).
The database contains two data types: sequence variants (individual nucleotide sequences) and samples. For each sequence variant, the following information is stored: sequence variant code, identification of samples where sequence variant occurs and the number of observations, the SH of best hit (when available), fungal species name (when available), fungal genus name (when available). For each sample, metadata information is stored (Table 1). Sequence data and metadata are accessible at Figshare (GlobalFungi_ITS_variants.zip, GlobalFungi_metadata.xlsx). All database content is accessible using a public graphical user interface at https://globalfungi.com.
Technical Validation
The technical validation included the screening of the data sources, sequencing data and data reliability. Regarding the data source screening, the data sources (published papers) were screened to fulfil the criteria outlined in the Methods section. The dataset was thoroughly checked for duplicates, and for all records that appeared in multiple publications, only the first original publication of the dataset was considered as a data source. Considering sequence quality, we have only utilized those primer pairs that are generally accepted to target general fungi (see Online-Only Table 1),. Sequences were quality filtered by removing all sequences with the mean quality phred scores below 20 and sequences that did not represent complete ITS1 or ITS2 after extraction or those that were identified as chimeric by the ITS extraction software were removed. All representative sequences where the BLASTn search against the UNITE database resulted in a nonfungal organism, were discarded.
For data reliability, the geographic location represented by the GPS coordinates was validated first. For each sample set, the geographic location of the sample described in the text of the study was confronted with the location on the map. For those samples where disagreement was recorded (e.g., terrestrial samples positioned in the ocean or located in another region than described in the text), the authors of each study were asked for correction. Studies or samples that could not be reconciled in this way were excluded from the database. The quality of sample metadata was checked and if they were outside the acceptable range (such as content of elements or organic matter > 100%), these invalid metadata were removed.
Usage Notes
The user interface at https://globalfungi.com enables the users to access the database in several ways (Fig. 3). In the taxon search, it is possible to search for genera or species of fungi or for the 98.5% SH species hypotheses of UNITE, contained in the general release 8.1 from 2.2.2019. The search results open the options to download the corresponding SH or the corresponding sequence variants. It is also possible to view a breakdown of samples by type, biome, mean annual temperature, mean annual precipitation, pH, and continents. The results also contain an interactive map of the taxon distribution with relative abundances of sequences of the taxon across samples and a list of samples with metadata. Several modes of filtering of results are available as well.
In the sequence search, it is possible to search for multiple nucleotide sequences by choosing if the result will be the exact match or a BLAST result. The BLAST option gives the possibility to retrieve the sequence variant best hit in the database, or, when only one sequence is submitted, it is possible to display multiple ranked high score hits among the sequence variants.
It is also possible to open individual studies and access their content. Finally, in the Geosearch, users can select a group of samples on the map, with a range of tools, and retrieve data for these samples (such as the FASTA file with all occurring sequence variants).
Importantly, the database is intended to grow, both by the continuing activity of the authors and by using the help of the scientific community. For that, the “Submit your study” section of the web interface enabling the submission of studies not yet represented is available to users. The submission tool guides the submitting person through the steps where details about the publication, samples, sample metadata and sequences are sequentially submitted. The submitted data will be used to update the database twice a year after processing and validation by the authors. Thus, users submitting their data, besides a precious contribution to mycological progress, will benefit from making their data accessible to the international scientific community in an easily accessible form and increasing the visibility of their results. Users can also maximize their visibility by approving to add their name and affiliation to the online list of collaborators and/or to the GlobalFungi Group Author’ list that will be mentioned in future publications describing the database content, its development, or metastudies using the whole database.
Among the possible uses of the GlobalFungi Database, fungal ecologists will be able to link fungal diversity data with the panel of collected metadata, which should allow them to determine the environmental factors driving the fungal diversity. This kind of study can be done at different geographic levels, from country scale up to the entire world, and for all the fungal communities or by focusing on some ecosystem compartments. This should lead to a better understanding of the biogeography of the fungal diversity. Větrovský et al. brought interesting findings by doing this for soil fungal communities at the scale of the globe. The evolutionary biologists could study, for example, the effect of global change on the fungal diversity by comparing the natural versus anthropogenic biomes. In addition to focus on the fungal diversity, some studies could trigger specific fungi. Thus, mycologists could determine the biogeography of one specific fungal species. They could also determine the composition of the fungal communities associated with the focused species and detect some potential recurrent fungal associations. The GlobalFungi Database could also speed up the progress in fungal taxonomy by highlighting the existence of a high number of fungal sequences not currently assigned to species along with environmental metadata promoting thus the interest in their description.
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Zhang T, Wang NF, Liu HY, Zhang YQ, Yu LY. Soil pH is a key determinant of soil fungal community composition in the Ny-Alesund region, Svalbard (High Arctic). Front. Microbiol. 2016;7:227.
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Gehring CA, et al. Cheatgrass invasion alters the abundance and composition of dark septate fungal communities in sagebrush steppe. Botany. 2016;94:481-491.
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Li Y, et al. Changes of soil microbial community under different degraded gradients of alpine meadow. Agric. Ecosyst. Environ. 2016;222:213-222.
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Cox F, Newsham KK, Bol R, Dungait JA, Robinson CH. Not poles apart: Antarctic soil fungal communities show similarities to those of the distant Arctic. Ecol. Lett. 2016;19:528-536.
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Bergottini VM, et al. Exploring the diversity of the root-associated microbiome of Ilex paraguariensis St. Hil. (Yerba Mate). Appl. Soil Ecol. 2017;109:23-31.
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Moussa TA, Al-Zahrani HS, Almaghrabi OA, Abdelmoneim TS, Fuller MP. Comparative metagenomics approaches to characterize the soil fungal communities of western coastal region, Saudi Arabia. PLoS One. 2017;12:e0185096.
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Goldmann K, et al. Divergent habitat filtering of root and soil fungal communities in temperate beech forests. Sci. Rep. 2016;11:31439.
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Liu C, et al. The influence of soil properties on the size and structure of bacterial and fungal communities along a paddy soil chronosequence. Eur. J. Soil Biol. 2016;76:9-18.
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Smith ME, et al. Investigating niche partitioning of ectomycorrhizal fungi in specialized rooting zones of the monodominant leguminous tree Dicymbe corymbosa. New Phytol. 2017;215:443-453.
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Vannette RL, Leopold DR, Fukami T. Forest area and connectivity influence root-associated fungal communities in a fragmented landscape. Ecology. 2016;97:2374-2383.
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Zhou X, et al. Rhizospheric fungi and their link with the nitrogen-fixing Frankia harbored in host plant Hippophae rhamnoides L. J. Basic Microbiol. 2017;57:1055-1064.
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Glassman SI, Wang IJ, Bruns TD. Environmental filtering by pH and soil nutrients drives community assembly in fungi at fine spatial scales. Mol. Ecol. 2017;26:6960-6973.
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Cline LC, Schilling JS, Menke J, Groenhof E, Kennedy PG. Ecological and functional effects of fungal endophytes on wood decomposition. Funct. Ecol. 2018;32:181-191.
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Johansen RB, et al. A native and an invasive dune grass share similar, patchily distributed, root-associated fungal communities. Fungal Ecol. 2016;23:141-155.
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Zhang S, Chen X, Zhong Q, Huang Z, Bai Z. Relations among epiphytic microbial communities from soil, leaves and grapes of the grapevine. Front. Life Sci. 2017;10:73-83.
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Fernandez CW, et al. Ectomycorrhizal fungal response to warming is linked to poor host performance at the boreal-temperate ecotone. Glob. Change Biol. 2017;23:1598-1609.
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Zhang Z, et al. Fungal communities in ancient peatlands developed from different periods in the Sanjiang Plain, China. PLoS One. 2017;12:e0187575.
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Gomes SI, Merckx VS, Saavedra S. Fungal-host diversity among mycoheterotrophic plants increases proportionally to their fungal-host overlap. Ecol. Evol. 2017;7:3623-3630.
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Zhou X, et al. Conversion from long-term cultivated wheat field to Jerusalem artichoke plantation changed soil fungal communities. Sci. Rep. 2017;7:41502.
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Gomes SI, Aguirre‐Gutiérrez J, Bidartondo MI, Merckx VS. Arbuscular mycorrhizal interactions of mycoheterotrophic Thismia are more specialized than in autotrophic plants. New Phytol. 2017;213:1418-1427.
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Tian H, et al. Changes in soil microbial communities after 10 years of winter wheat cultivation versus fallow in an organic-poor soil in the Loess Plateau of China. PLoS One. 2017;12:e0184223.
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Gourmelon V, et al. Environmental and geographical factors structure soil microbial diversity in New Caledonian ultramafic substrates: a metagenomic approach. PLoS One. 2016;11:e0167405.
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Younginger BS, Ballhorn DJ. Fungal endophyte communities in the temperate fern Polystichum munitum show early colonization and extensive temporal turnover. Am. J. Bot. 2017;104:1188-1194.
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Kamutando CN, et al. Soil nutritional status and biogeography influence rhizosphere microbial communities associated with the invasive tree Acacia dealbata. Sci. Rep. 2017;7:6472.
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Anthony MA, Frey SD, Stinson KA. Fungal community homogenization, shift in dominant trophic guild, and appearance of novel taxa with biotic invasion. Ecosphere. 2017;8:e01951.
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Ge ZW, Brenneman T, Bonito G, Smith ME. Soil pH and mineral nutrients strongly influence truffles and other ectomycorrhizal fungi associated with commercial pecans (Carya illinoinensis). Plant Soil. 2017;418:493-505.
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Mirmajlessi SM, et al. Survey of soil fungal communities in Strawberry fields by Illumina amplicon sequencing. Eurasian Soil Sci. 2018;51:682-691.
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Harrison JG, Forister ML, Parchman TL, Koch GW. Vertical stratification of the foliar fungal community in the world’s tallest trees. Am. J. Bot. 2016;103:2087-2095.
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Semenova‐Nelsen TA, Platt WJ, Patterson TR, Huffman J, Sikes BA. Frequent fire reorganizes fungal communities and slows decomposition across a heterogeneous pine savanna landscape. New Phytol. 2019;224:916-927.
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Dean SL, et al. A study of Glycine max (soybean) fungal communities under different agricultural practices. Plant Gene. 2017;11:8-16.
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Kyaschenko J, Clemmensen KE, Hagenbo A, Karltun E, Lindahl BD. Shift in fungal communities and associated enzyme activities along an age gradient of managed Pinus sylvestris stands. ISME J. 2017;11:863-874.
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Tian J, et al. Ecological succession pattern of fungal community in soil along a retreating glacier. Front. Microbiol. 2017;8:1028.
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Oono R, Rasmussen A, Lefèvre E. Distance decay relationships in foliar fungal endophytes are driven by rare taxa. Environ. Microbiol. 2017;19:2794-2805.
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Oono R. A confidence interval analysis of sampling effort, sequencing depth, and taxonomic resolution of fungal community ecology in the era of high-throughput sequencing. PLoS One. 2017;12:e0189796.
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Marín C, et al. Functional land-use change effects on soil fungal communities in Chilean temperate rainforests. J. Soil Sci. Plant Nut. 2017;17:985-1002.
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Siles JA, Margesin R. Seasonal soil microbial responses are limited to changes in functionality at two Alpine forest sites differing in altitude and vegetation. Sci. Rep. 2017;7:2204.
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Kazartsev I, Shorohova E, Kapitsa E, Kushnevskaya H. Decaying Picea abies log bark hosts diverse fungal communities. Fungal Ecol. 2018;33:1-12.
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Peay KG, et al. Convergence and contrast in the community structure of bacteria, fungi and archaea along a tropical elevation-climate gradient. FEMS Microbiol. Ecol. 2017;93:fix045.
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Coleine C, et al. Antarctic cryptoendolithic fungal communities are highly adapted and dominated by Lecanoromycetes and Dothideomycetes. Front. Microbiol. 2018;9:1392.
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Park MS, et al. Diversity of fungi associated with roots of Calanthe orchid species in Korea. J. Microbiol. 2018;56:49-55.
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Glynou K, Nam B, Thines M, Maciá‐Vicente JG. Facultative root-colonizing fungi dominate endophytic assemblages in roots of nonmycorrhizal Microthlaspi species. New Phytol. 2018;217:1190-1202.
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Saitta A, Anslan S, Bahram M, Brocca L, Tedersoo L. Tree species identity and diversity drive fungal richness and community composition along an elevational gradient in a Mediterranean ecosystem. Mycorrhiza. 2018;28:39-47.
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Almario J, et al. Root-associated fungal microbiota of nonmycorrhizal Arabis alpina and its contribution to plant phosphorus nutrition. Proc. Natl. Acad. Sci. USA. 2017;114:E9403-E9412.
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Fernández‐Mendoza F, Fleischhacker A, Kopun T, Grube M, Muggia L. ITS1 metabarcoding highlights low specificity of lichen mycobiomes at a local scale. Mol. Ecol. 2017;26:4811-4830.
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Varenius K, Lindahl BD, Dahlberg A. Retention of seed trees fails to lifeboat ectomycorrhizal fungal diversity in harvested Scots pine forests. FEMS Microbiol. Ecol. 2017;93:fix105.
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He D, et al. Diversity and co-occurrence network of soil fungi are more responsive than those of bacteria to shifts in precipitation seasonality in a subtropical forest. Soil Biol. Biochem. 2017;115:499-510.
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Mendoza JR, Kok CR, Stratton J, Bianchini A, Hallen-Adams HE. Understanding the mycobiota of maize from the highlands of Guatemala, and implications for maize quality and safety. Crop Prot. 2017;101:5-11.
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Miura T, Sánchez R, Castañeda LE, Godoy K, Barbosa O. Is microbial terroir related to geographic distance between vineyards? Environ. Microbiol. Rep. 2017;9:742-749.
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Zhang J, et al. Distinct large-scale biogeographic patterns of fungal communities in bulk soil and soybean rhizosphere in China. Sci. Total Environ. 2018;644:791-800.
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Sharma-Poudyal D, Schlatter D, Yin C, Hulbert S, Paulitz T. Long-term no-till: A major driver of fungal communities in dryland wheat cropping systems. PLoS One. 2017;12:e0184611.
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Ren C, et al. Differential responses of soil microbial biomass, diversity, and compositions to altitudinal gradients depend on plant and soil characteristics. Sci. Total Environ. 2018;610:750-758.
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Sapkota R, Nicolaisen M. Cropping history shapes fungal, oomycete and nematode communities in arable soils and affects cavity spot in carrot. Agric. Ecosyst. Environ. 2018;257:120-131.
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Schroeder JW, et al. Community composition and diversity of Neotropical root‐associated fungi in common and rare trees. Biotropica. 2018;50:694-703.
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Fan K, Weisenhorn P, Gilbert JA, Chu H. Wheat rhizosphere harbors a less complex and more stable microbial co-occurrence pattern than bulk soil. Soil Biol. Biochem. 2018;125:251-260.
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Montagna M, et al. Differential biodiversity responses between kingdoms (plants, fungi, bacteria and metazoa) along an Alpine succession gradient. Mol. Ecol. 2018;27:3671-3685.
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Schön ME, Nieselt K, Garnica S. Belowground fungal community diversity and composition associated with Norway spruce along an altitudinal gradient. PLoS One. 2018;13:e0208493.
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Thiem D, Piernik A, Hrynkiewicz K. Ectomycorrhizal and endophytic fungi associated with Alnus glutinosa growing in a saline area of central Poland. Symbiosis. 2017;75:17-28.
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Schlatter DC, Kahl K, Carlson B, Huggins DR, Paulitz T. Fungal community composition and diversity vary with soil depth and landscape position in a no-till wheat-based cropping system. FEMS Microbiol. Ecol. 2018;94:fiy098.
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Rasmussen PU, et al. Multiscale patterns and drivers of arbuscular mycorrhizal fungal communities in the roots and root-associated soil of a wild perennial herb. New Phytol. 2018;220:1248-1261.
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Guo J, et al. Soil fungal assemblage complexity is dependent on soil fertility and dominated by deterministic processes. New Phytol. 2019;226:232-243.
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Song H, et al. Tropical forest conversion to rubber plantation in southwest China results in lower fungal beta diversity and reduced network complexity. FEMS Microbiol. Ecol. 2019;95:fiz092.
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Rogers TJ, et al. Exploring variation in phyllosphere microbial communities across four hemlock species. Ecosphere. 2018;9:e02524.
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Marasco R, et al. Rhizosheath microbial community assembly of sympatric desert speargrasses is independent of the plant host. Microbiome. 2018;6:215.
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Bickford WA, Goldberg DE, Kowalski KP, Zak DR. Root endophytes and invasiveness: no difference between native and non‐native Phragmites in the Great Lakes region. Ecosphere. 2018;9:e02526.
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Si P, et al. Rhizosphere microenvironments of eight common deciduous fruit trees were shaped by microbes in Northern China. Front. Microbiol. 2018;9:3147.
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Purahong W, Wu YT, Chen CT, Mapook A. Characterization of the Castanopsis carlesii deadwood mycobiome by Pacbio sequencing of the full-length fungal nuclear ribosomal internal transcribed spacer (ITS). Front. Microbiol. 2019;10:983.
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Geml J, et al. The contribution of DNA metabarcoding to fungal conservation: diversity assessment, habitat partitioning and mapping red-listed fungi in protected coastal Salix repens communities in the Netherlands. PLoS One. 2014;9:e99852.
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Schmidt PA, et al. Illumina metabarcoding of a soil fungal community. Soil Biol. Biochem. 2013;65:128-132.
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Muller LA, Hilger HH. Insights into the effects of serpentine soil conditions on the community composition of fungal symbionts in the roots of Onosma echioides. Soil Biol. Biochem. 2015;81:1-8.
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Wilhelm RC, et al. A metagenomic survey of forest soil microbial communities more than a decade after timber harvesting. Sci. Data. 2017;4:170092.
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Lanzén A, et al. Multi-targeted metagenetic analysis of the influence of climate and environmental parameters on soil microbial communities along an elevational gradient. Sci. Rep. 2016;6:28257.
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Yang T, et al. Soil fungal diversity in natural grasslands of the Tibetan Plateau: associations with plant diversity and productivity. New Phytol. 2017;215:756-765.
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Yang T, et al. Fungal community assemblages in a high elevation desert environment: absence of dispersal limitation and edaphic effects in surface soil. Soil Biol. Biochem. 2017;115:393-402.
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van der Wal A, Gunnewiek PK, de Boer W. Soil-wood interactions: Influence of decaying coniferous and broadleaf logs on composition of soil fungal communities. Fungal Ecol. 2017;30:132-134.
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Sun R, et al. Tillage changes vertical distribution of soil bacterial and fungal communities. Front. Microbiol. 2018;9:699.
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Santalahti M, et al. Reindeer grazing alter soil fungal community structure and litter decomposition related enzyme activities in boreal coniferous forests in finnish lapland. Appl. Soil Ecol. 2018;132:74-82.
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Gałązka A, Grządziel J. Fungal genetics and functional diversity of microbial communities in the soil under long-term monoculture of Maize using different cultivation techniques. Front. Microbiol. 2018;9:76.
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Matsuoka S, Mori AS, Kawaguchi E, Hobara S, Osono T. Disentangling the relative importance of host tree community, abiotic environment and spatial factors on ectomycorrhizal fungal assemblages along an elevation gradient. FEMS Microbiol. Ecol. 2016;92:fiw044.
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Shen Z, et al. Banana Fusarium Wilt disease incidence is influenced by shifts of soil microbial communities under different monoculture spans. Microb. Ecol. 2017;75:739-750.
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Matsuoka S, Ogisu Y, Sakoh S, Hobara S, Osono T. Taxonomic, functional, and phylogenetic diversity of fungi along primary successional and elevational gradients near Mount Robson, British Columbia. Polar Sci. 2018;21:165-171.
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Mundra S, et al. Arctic fungal communities associated with roots of Bistorta vivipara do not respond to the same fine-scale edaphic gradients as the aboveground vegetation. New Phytol. 2015;205:1587-1597.
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Schappe T, et al. The role of soil chemistry and plant neighbourhoods in structuring fungal communities in three Panamanian rainforests. J. Ecol. 2017;105:569-579.
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BioSample. 2017.
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Vaz AB, et al. Using Next-Generation Sequencing (NGS) to uncover diversity of wood-decaying fungi in neotropical atlantic forests. Phytotaxa. 2017;295:1-21.
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Australian Antarctic Data Centre. 2014.
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Ji M, et al. Microbial diversity at Mitchell Peninsula, Eastern Antarctica: a potential biodiversity “hotspot”. Polar Biol. 2016;39:237-249.
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Hartmann M, et al. Significant and persistent impact of timber harvesting on soil microbial communities in Northern coniferous forests. ISME J. 2012;6:2199-2218.
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Rime T, Hartmann M, Frey B. Potential sources of microbial colonizers in an initial soil ecosystem after retreat of an alpine glacier. ISME J. 2016;10:1625-1641.
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Cited by papers we hold 3
- Defining Soilborne Pathogen Complexes Provides a New Foundation for the Effective Management of Faba Bean Root Diseases in Ethiopia · 2025Not checked
- Metagenomes, metatranscriptomes and microbiomes of naturally decomposing deadwood · 2021Not checked
- Unambiguous identification of fungi: where do we stand and how accurate and precise is fungal DNA barcoding? · 2020No notice
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