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. 2025 Jun 13;11(24):eadt5743.
doi: 10.1126/sciadv.adt5743. Epub 2025 Jun 13.

Mycorrhizal symbioses and tree diversity in global forest communities

Feng Jiang  1 Xucai Pu  1 Bernhard Schmid  1   2 Peter B Reich  3   4   5 Jingjing Liang  6 Akane O Abbasi  6 Jesús Aguirre-Gutiérrez  7   8 Angelica Maria Almeyda Zambrano  9 Jan Altman  10   11 Juan Gabriel Álvarez-González  12 Luciana F Alves  13 Bienvenu H K Amani  14   15 Christian Ammer  16 Gerardo A Aymard  17   18 Naveen Babu Kanda  19 Meredith L Bastian  20   21 Jean-Francois Bastin  22 Marijn Bauters  23 Pascal Boeckx  24 Svetlana N Bondarchuk  25 Alexander Bondarev  26 Francis Q Brearley  27 Sophie Brennan  28 Jaime Briseño-Reyes  29 Eben N Broadbent  30 Goran Češljar  31 Han Y H Chen  32   33 Chelsea Chisholm  34 WookJin Choi  6 Emil Cienciala  35   36 Connie J Clark  37 Alessio Collalti  38   39 José Javier Corral-Rivas  29 Javid Ahmad Dar  40   41 Selvadurai Dayanandan  42 Sergio de-Miguel  43   44 Ashaq Ahmad Dar  45 Géraldine Derroire  46 Ilija Djordjevic  47 Tran Van Do  48 Jiří Doležal  10   49 Aurélie Dourdain  46 Teresa Eyre  50 Adandé Belarmain Fandohan  51 Lorenzo Frizzera  52 Roberto Cazzolla Gatti  53 Damiano Gianelle  52 M Socorro González Elizondo  54 Elisa Grieco  38 David J Harris  55 Andy Hector  56 Bruno Hérault  57   58 Cang Hui  59   60 Nobuo Imai  61 Andrzej M Jagodziński  62   63 Chengjun Ji  1 Lin Jiang  64 Carlos A Joly  65   66 Viktor N Karminov  67 Kuswata Kartawinata  68 Justin N Kassi  69 Elizabeth Kearsley  23 Gunnar Keppel  70 Mohammed Latif Khan  71 Carine Klauberg  72 Kirill A Korznikov  10   73 Subashree Kothandaraman  40   41 Florian Kraxner  74 Leonid Krivobokov  75 Dmitry Kucher  76 Amit Kumar  77   78 Anna Kvashnina  79 Gaia Vaglio Laurin  80 Rodrigo Vieira Leite  81   82 Moses B Libalah  83   84 Ekaterina S Lonkina  85 Huicui Lu  86 Shan Luo  87   88 Yuan Luo  1 Emma Mackintosh  89 Andrew R Marshall  90   91 Rodolfo Vásquez Martínez  92 Radim Matula  93 William McDonald  94 Ayyappan Narayanan  19 María Guadalupe Nava-Miranda  95   96 Jagadeesan Naveenkumar  45 Abel Monteagudo Mendoza  92   97 Stanisław Miścicki  98 Tatyana Moskalyuk  99 Liudmila Mukhortova  75 Sharif A Mukul  100   101 Gert-Jan Nabuurs  102   103 Victor J Neldner  50 Radovan Nevenic  104 Anny E N'Guessan  105 Michael Ngugi  50 Alain Paquette  106 Elena I Parfenova  75 Marc Parren  103 Narayanaswamy Parthasarathy  45 Pablo L Peri  107 Sebastian Pfautsch  108 Maria T F Piedade  109 Galina Polyakova  75 Axel Dalberg Poulsen  55 John R Poulsen  110 Hans Pretzsch  111 Mirco Rodeghiero  52 Ervan Rutishauser  112 Purabi Saikia  113 Philippe Saner  114 Dmitry Schepaschenko  74 Jochen Schöngart  115 Eric B Searle  32 Douglas Sheil  103 Zehao Shen  1 Stephanie Shooner  116   117 Anatoly Shvidenko  74   75 Carlos A Silva  118 Plinio Sist  119 Ferry Slik  120 Wenqi Song  1 Alexandre F Souza  121 Krzysztof Stereńczak  122 Somaiah Sundarapandian  45 Martin Svátek  123 Miroslav Svoboda  93 Zhiyao Tang  1 Natalia Targhetta  115 Nadja Tchebakova  75 Elena Tikhonova  124 Liam Trethowan  125 Daniel José Vega-Nieva  29 Hans Verbeeck  23 Simone A Vieira  126 Camille Volle  127 Anna S Vozmishcheva  128 Foma K Vozmitel  79   129 Hua-Feng Wang  130 Shaopeng Wang  1 Xiangping Wang  131 Florian Wittmann  132 Chengyang Zheng  1 Biao Zhu  1 Irié Casimir Zo-Bi  133 Jingyun Fang  1   134 Zhiheng Wang  1
Affiliations

Mycorrhizal symbioses and tree diversity in global forest communities

Feng Jiang et al. Sci Adv. .

Abstract

Unraveling the mechanisms underlying the maintenance of species diversity is a central pursuit in ecology. It has been hypothesized that ectomycorrhizal (EcM) in contrast to arbuscular mycorrhizal fungi can reduce tree species diversity in local communities, which remains to be tested at the global scale. To address this gap, we analyzed global forest inventory data and revealed that the relationship between tree species richness and EcM tree proportion varied along environmental gradients. Specifically, the relationship is more negative at low latitudes and in moist conditions but is unimodal at high latitudes and in arid conditions. The negative association of EcM tree proportion on species diversity at low latitudes and in humid conditions is likely due to more negative plant-soil microbial interactions in these regions. These findings extend our knowledge on the mechanisms shaping global patterns in plant species diversity from a belowground view.

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Figures

Fig. 1.
Fig. 1.. Hypothetical relationships between the proportion of EcM tree individuals in a community and tree species richness; and forest plot data used to test the predictions.
(A to C) Species richness can show a negative (only includes a negative first order term, hypothesis 1, or EcM dominance hypothesis), symmetrically unimodal (includes both linear and quadratic terms but the absolute coefficients of both terms have similar magnitude, hypothesis 2, or mycorrhizal mixture hypothesis), or asymmetrically unimodal (the absolute value of quadratic term being larger than that of the first-order term, hypothesis 3, or integrated hypothesis) relationship with the proportion of EcM trees. (D) The global pattern of the proportion of EcM tree species based on stem abundance in our forest plot dataset (N = 4090). The green background on the map indicates forest regions classified by (43). (E) Raw relationship between the proportion of EcM tree individuals and tree species richness using the generalized linear model without controlling for covariates (r2 = 0.59).
Fig. 2.
Fig. 2.. Effects of EcM tree proportion interacting with absolute latitude and aridity on tree species richness.
(A) Standardized coefficients of generalized linear model, open and solid circles indicate nonsignificant and significant relationships (P < 0.05); (B to D) relationships between EcM tree proportion and tree species richness across gradients of absolute latitudes and aridity (aridity index = 0.5, 1.2, and 2); lines are predicted species richness (log10 back-transformed) after controlling for covariates; the ranges of species richness differ among these panels due to variations in the aridity index. EcM and EcM2 indicate linear and quadratic proportions of EcM trees; AI, aridity index; soil clay, soil clay content. Lat_abs, absolute latitude.
Fig. 3.
Fig. 3.. The relative importance of predictors in explaining tree species richness in random forest models.
(A) Global model (N = 4,090, r2 = 0.88); (B) boreal model (N = 579, r2 = 0.55); (C) temperate model (N = 2,457, r2 = 0.80); (D) tropical model (N = 1,054, r2 = 0.75).
Fig. 4.
Fig. 4.. Direct and indirect effects of environmental variables on species richness in forest communities.
(A) Global model; (B) boreal model; (C) temperate model; (D) tropical model. The goodness of fit for structural equation models is indicated by the Fisher’s C value with P > 0.05 suggesting good fit of models and no missing paths. Brown and blue solid lines represent significantly positive and negative relationships (P < 0.05), respectively. Dashed gray lines represent nonsignificant relationships (P ≥ 0.05). Arrow width is proportional to strength if there is a significant relationship. SR, species richness; EcM and EcM2 indicate the linear and quadratic proportions of ectomycorrhizal trees; MAT, mean annual temperature; AI, aridity index; soil N, total soil nitrogen. The path from the linear to the quadratic proportion of ectomycorrhizal trees must be included in the model by piecewiseSEM package (72) due to their mathematical relationship (not causality). Paths linking environmental variables to EcM2 were removed because they were not significant. Including all potential paths in the models would also prevent the calculation of Fisher’s C. *P < 0.05, **P < 0.01, ***P < 0.001.

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