Abstract
Growing evidence has shown that, apart from local environmental factors, changes in landscape-level factors by accelerated land-use change can also shape soil pathogenic fungal diversity. However, the global representativeness of such patterns remains unclear. Here, we assess how pathogenic fungal diversity in 511 soil samples worldwide responds to landscape factors, including landscape complexity index based on eight landscape metrics and quantity of different land cover types across six spatial scales (i.e., surrounding landscape, 250 m to 10,000 m radii from the sampling coordinate). We find that while soil variables explain over half of the variance, pathogenic fungal alpha diversity increases with landscape complexity and crop cover proportion, but decreases with grass and tree cover proportion, together explaining 23.4% of the total variance. Landscape factors have weaker impacts on beta diversity, explaining 13.0% of the variance. Across spatial scales, grassland ecosystems exhibit increasingly stronger responses to landscape variables compared to forest ecosystems. Landscape factors have a higher relative contribution to root-associated fungi than leaf/fruit/seed-associated fungi. Our results emphasize the importance of local factors and the complementary role of landscape patterns in shaping global soil pathogenic fungal distributions, highlighting scale-dependent effects across ecosystems and fungal functional groups.
Data availability
The raw sequencing data generated in this study have been deposited in the NCBI Sequence Read Archive (SRA) under accession code PRJNA1045969. The source data underlying all figures are available on Figshare at https://doi.org/10.6084/m9.figshare.26377660.v5. All other data supporting the findings of this study are provided in the Supplementary Information.
Code availability
The code that support the findings of this study are openly available on figshare at https://doi.org/10.6084/m9.figshare.26377660.v5.
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Acknowledgements
We thank all the people who helped in sampling and experiment processes and volunteering researchers from the networks of ILTER (https://www.ilter.network) and eLTER (https://elter-ri.eu). We also thank all the landowners for the access to their lands. We thank JiaJia Liu for his contribution to the research idea and manuscript revision, as well as supporting Y.L. for participation in the iSBio project. We thank Yuanyuan Huang, Shengen Liu for advice on data analysis. We acknowledge funding from the German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig of the German Research Foundation (FZT118, 202548816), and from The Swedish Research Council for Environment, Agricultural sciences and Spatial Planning (Formas, grant no. 2020-02339). Sequencing was financed by the German Research Foundation (DFG, BU 941/32-1 | EI 862/27-1 | HE 8266/4-1 | KU 1367/14-1 | WE 6579/2-1 to F.B., N.E., A.H.-B., K.Kü., C.-E.W.). Sequence data analysis was performed at the High-Performance Computing (HPC) Cluster EVE, a joint effort of both the Helmholtz Centre for Environmental Research-UFZ and the German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, whose administrators are thanked for excellent support. Moreover, we acknowledge support by the DFG grants EI 862/29-1 and EI 862/31-1 (to N.E.). Y.L. acknowledges funding from China Scholarship Council (202106100117). F.T.M. acknowledges support by the King Abdullah University of Science and Technology (KAUST) and the KAUST Climate and Livability Initiative. G.W. acknowledges financial support by the Austrian National Science Fund (FWF, grant no. P31669). A.G. acknowledges Fondecyt 1201643 & FB210006 & ICN2021_044. Zs.K. acknowledges the MATE Research Excellence Program MATE-K/1011–32/2024). M.B. acknowledges the Scientific Grant Agency VEGA (Grant No. 2/0045/22). K.L. acknowledges support to the H.J. Andrews Experimental Forest and Long Term Ecological Research (LTER) program under NSF grant LTER8 DEB-2025755. A.S.F.A. acknowledges CNPq-Brazil for his Fellowship of Research (grant 301755/2022-1). Funding was provided by CNPq-Brazil (Grant No. 304636/2022-3) to A.C. A.P. and M.C. acknowledge that this work has benefited from the equipment and framework of the COMP-HUB and COMP-R Initiatives, funded by the ‘Departments of Excellence’ program of the Italian Ministry for University and Research (MIUR, 2018-2022 and MUR, 2023-2027). L.v.d.B., R.C. and R.M. thank Conaf (Chile) and Comunidad Agricola Quebrada de Talca (Chile), and were supported by DFG (Priority Program SPP-1803 ‘EarthShape: Earth Surface Shaping by Biota’, TI 338/14-1 and BA 3843/6-1). L.v.d.B. thanks additional support from ANID PIA/ACT 210038. A.I.S. acknowledges the FCT—Foundation for Science and Technology, I.P. through the individual project CEECIND/00962/2017 (DOI: 10.54499/CEECIND/00962/2017/CP1459/CT0008), for the financial support to CESAM under the project/grant UID/50006 + LA/P/0094/2020 (doi.org/10.54499/LA/P/0094/2020). A.R.G. and R.L.M. are grateful to CNPq-Brazil (PELD—Grant No. 441610/2016-1) for supporting this study. H.J. and F.Z. thank the Galapagos National Park Directorate and the Ecuadorian Ministry of Environment, Water and Ecological Transition for their support and for issuing permit numbers MAE-DNB-CM-2016-0043 and 006-2021-EXP-CM-FAU-DBI/MAAE. This publication is contribution number 2664 of the Charles Darwin Foundation for the Galapagos Islands. P.P. was supported by the long-term research development project RVO 67985939 (Czech Academy of Sciences). S.M.T.-T. was supported by an Australian Research Council DECRA Fellowship (DE210101029). I.D. thanks UNILEVER and EKATERRA for sponsoring tea bags. I.F. acknowledges support by Scientific Council of the University of Nyíregyháza. T.M.U. was supported through the Nucleu Program as part of the 2022–2027 National Research, Development and Innovation Plan, funded by MCID, project no. PN23020401, contract no. 7N/03.01.2023. C.A.G. was funded by the Portuguese Foundation for Science and Technology, as part of Project SoilRecon (PTDC/BIA-CBI/2340/2020). Q.P. thanks the Walloon forest service (Service Public de Wallonie-Département de la Nature et des Forêts) for its financial support to the installation and maintenance of the FORBIO-Gedinne site through the 5-year research programme ‘Accord-cadre de recherches et de vulgarisation forestières’. A.St. and P.B.R. acknowledge the National Science Foundation, Biological Integration Institutes grant NSF-DBI-2021898. I.O. and K.Kr. were supported by the Estonian Research Council grant PRG916. C.B. and H.C.S. were supported by projects AdaptForGrazing (02/C05-i03/2021.PPRR-C05-i03-I-000035), SustInAfrica (EU H2020 R&I GA 861924), and Portuguese National Funds through ‘Fundação para a Ciência e Tecnologia’ (FCT) within the cE3c Unit funding (DOI:10.54499/UIDB/00329/2020). G.G. was supported by the grant DEB 0620910, 1831952 and 2425484 from the National Science Foundation as part of the Luquillo LTER. The U.S. Forest Service (Department of Agriculture) and University of Puerto Rico gave additional support. P.F. was supported by the Swedish Research Council FORMAS (2020-01100). S.L. was supported by the Integrated Monitoring Programme contract 221-22-006 financed by the Swedish Environmental Protection Agency. Financial support was provided by the EU Horizon 2020 project eLTER PLUS (grant 871128) to P.H. M.Di. receives financial support from the Swiss Federal Office of the Environment. S.K.-R. was supported by Novo Nordisk Foundation grant NNF20OC0059948. P.D.T. was supported by the GreenMount project (PN-IV-P2-2.1-TE-2023-0726), funded by UEFISCDI Romania. S.E.V. was supported by an Australian Research Council Linkage project, LP190100844. H.K. and K.H. were supported by the Grant-in-Aid for Scientific Research (B) (17H03835 to H.K. and 19H02999 to K.H.) from Japan Society for the Promotion of Science. C.C. was supported by the Long-Term Ecological Research project (2006–2025), Ministry of Agriculture, Taiwan. R.G.G. was supported by a grant (PR3/23-30823) from Complutense University. U.H. and M.Frei. received financial support by the German Research Foundation (DFG) Infrastructure Priority Program 1374 “Biodiversity-Exploratories” (HA 4597/6-4). H.B. and S.T. acknowledge the support by the BEF-China platform and the Deutsche Forschungsgemeinschaft (DFG, German Research Foundation)—35758305 (FOR891); 319936945 (GRK2324).
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Y.L., N.E., G.P., A.H.-B., K.Kü., C.-E.W., F.B., and C.A.G. conceived and designed the study. Y.L., X.L., Y.C., and C.A.G. performed the data analyses. Y.L. wrote the first draft of the manuscript with support by C.A.G. and N.E., and all authors contributed greatly to the final manuscript. N.E., G.P., A.H.-B., K.Kü., C.-E.W., F.B., Q.B., M.C.R., and S.S. worked on laboratorial analyses and data compiling. Site coordination and soil sampling were contributed by A.S.F.A., B.F., F.T.M., M.V., L.v.d.B., Q.P., M.Di., G.W., A.G., C.B., H.M., K.F., E.C.A., A.A., M.B., H.B., A.C., R.C., M.C., R.C.G., C.C., C.T.C., M.Da., E.A.D., M.-A.d.G., C.D., V.D.C., L.D.M., I.D., S.D., T.E., I.F., P.F., M.Frei., M.Fren., R.G.G., S.G., M.G., G.G., A.R.G., P.H., U.H., T.His., T.Hiu., E.H., K.H., H.J., J.J.J., M.J.K.-S., S.K.-R., Zs.K., K.Kr., H.K., K.L., J.L., S.L., V.M., R.L.M., F.M.-D., I.M., V.O., I.O., A.P., W.C.P., P.L.P., R.M., A.P., P.P., M.P., C.R., P.B.R., M.C.R., M.Schä., M.Scha., A.Sc., J.S., H.C.S., A.I.S., S.S., A.St., M.T., Z.T., S.M.T.-T., S.T., P.D.T., T.M.U., S.E.V., A.V., J.V., D.V., M.Wa., M.We., and F.Z.
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Lu, Y., Eisenhauer, N., Patoine, G. et al. Landscape effects on global soil pathogenic fungal diversity across spatial scales.
Nat Commun (2026). https://doi.org/10.1038/s41467-025-67929-5
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DOI: https://doi.org/10.1038/s41467-025-67929-5
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