TY - JOUR
T1 - Scale-dependent diversity–biomass relationships can be driven by tree mycorrhizal association and soil fertility
AU - Mao, Zikun
AU - van der Plas, Fons
AU - Corrales, Adriana
AU - Anderson-Teixeira, Kristina J.
AU - Bourg, Norman A.
AU - Chu, Chengjin
AU - Hao, Zhanqing
AU - Jin, Guangze
AU - Lian, Juyu
AU - Lin, Fei
AU - Li, Buhang
AU - Luo, Wenqi
AU - McShea, William J.
AU - Myers, Jonathan A.
AU - Shen, Guochun
AU - Wang, Xihua
AU - Yan, En Rong
AU - Ye, Ji
AU - Ye, Wanhui
AU - Yuan, Zuoqiang
AU - Wang, Xugao
N1 - Funding Information:
National Natural Science Foundation of China, Grant/Award Number: 31961133027; Strategic Priority Research Program of the Chinese Academy of Sciences, Grant/Award Number: XDB31030000; Key Research Program of Frontier Sciences, Chinese Academy of Sciences, Grant/Award Number: ZDBS‐LY‐DQC019; K. C. Wong Education Foundation; Special Research Assistant Project of the Chinese Academy of Sciences, Grant/Award Number: 2022000056; Major Program of the Institute of Applied Ecology, Chinese Academy of Sciences, Grant/Award Number: IAEMP202201; Chengjin Chu was funded by the National Natural Science Foundation of China, Grant/Award Number: 31925027; the General Program of China Postdoctoral Science Foundation, Grant/Award Number: 2021M703397; Zuoqiang Yuan was funded by the National Natural Science Foundation of China, Grant/Award Number: 32171581; the Smithsonian Institution; the National Science Foundation, Grant/Award Number: DEB 1557094 Funding information
Funding Information:
We are grateful to Jean‐Philippe Lessard, Kerri Crawford, Maarja Öpik, Leho Tedersoo, Nico Eisenhauer, Olga Ferlian, Jonathan Chase, Daniel Johnson, Mingyue Jin, and all participants of the 2019 Smithsonian ForestGEO Workshop in Singapore and the anonymous reviewers for their helpful comments and suggestions in improving this manuscript. We also thank the Smithsonian ForestGEO network and field workers who collected data in the plots used here. This work was financially supported by the National Natural Science Foundation of China (Grant 31961133027), the Strategic Priority Research Program of the Chinese Academy of Sciences (Grant XDB31030000), the Key Research Program of Frontier Sciences, Chinese Academy of Sciences (Grant ZDBS‐LY‐DQC019), the K. C. Wong Education Foundation, the General Program of China Postdoctoral Science Foundation (2021M703397), the Special Research Assistant Project of the Chinese Academy of Sciences (2022000056), and the Major Program of the Institute of Applied Ecology, Chinese Academy of Sciences (IAEMP202201). Chengjin Chu was funded by the National Natural Science Foundation of China (31925027). Zuoqiang Yuan was funded by the National Natural Science Foundation of China (32171581). Funding for the data collections was provided by many organizations, including the Smithsonian Institution, the National Science Foundation (DEB 1557094), the National Zoological Park, the HSBC Climate Partnership, the International Center for Advanced Renewable Energy and Sustainability (I‐CARES) at Washington University in St. Louis, and the Tyson Research Center.
Publisher Copyright:
© 2023 The Ecological Society of America.
PY - 2023/5
Y1 - 2023/5
N2 - Diversity–biomass relationships (DBRs) often vary with spatial scale in terrestrial ecosystems, but the mechanisms driving these scale-dependent patterns remain unclear, especially for highly heterogeneous forest ecosystems. This study explores how mutualistic associations between trees and different mycorrhizal fungi, i.e., arbuscular mycorrhizal (AM) vs. ectomycorrhizal (EM) association, modulate scale-dependent DBRs. We hypothesized that in soil-heterogeneous forests with a mixture of AM and EM tree species, (i) AM and EM tree species would respond in contrasting ways (i.e., positively vs. negatively, respectively) to increasing soil fertility, (ii) AM tree dominance would contribute to higher tree diversity and EM tree dominance to greater standing biomass, and that as a result (iii) mycorrhizal associations would exert an overall negative effect on DBRs across spatial scales. To empirically test these hypotheses, we collected detailed tree distribution and soil information (e.g., nitrogen, phosphorus, organic matter, pH) from seven temperate and subtropical AM–EM mixed forest megaplots (16–50 ha). Using a spatial codispersion null model and structural equation modeling, we identified the relationships among AM or EM tree dominance, soil fertility, tree species diversity, and biomass and, thus, DBRs across 0.01- to 1-ha scales. We found the first evidence overall supporting the three aforementioned hypotheses in these AM–EM mixed forests: (i) In most forests, with increasing soil fertility, tree communities changed from EM-dominated to AM-dominated; (ii) increasing AM tree dominance had an overall positive effect on tree diversity and a negative effect on biomass, even after controlling for soil fertility and number of trees. Together, (iii) the changes in mycorrhizal dominance along soil fertility gradients weakened the positive DBR observed at 0.01- to 0.04-ha scales in nearly all forests and drove negative DBRs at 0.25- to 1-ha scales in four out of seven forests. Hence, this study highlights a soil-related mycorrhizal dominance mechanism that could partly explain why, in many natural forests, biodiversity–ecosystem functioning (BEF) relationships shift from positive to negative with increasing spatial scale.
AB - Diversity–biomass relationships (DBRs) often vary with spatial scale in terrestrial ecosystems, but the mechanisms driving these scale-dependent patterns remain unclear, especially for highly heterogeneous forest ecosystems. This study explores how mutualistic associations between trees and different mycorrhizal fungi, i.e., arbuscular mycorrhizal (AM) vs. ectomycorrhizal (EM) association, modulate scale-dependent DBRs. We hypothesized that in soil-heterogeneous forests with a mixture of AM and EM tree species, (i) AM and EM tree species would respond in contrasting ways (i.e., positively vs. negatively, respectively) to increasing soil fertility, (ii) AM tree dominance would contribute to higher tree diversity and EM tree dominance to greater standing biomass, and that as a result (iii) mycorrhizal associations would exert an overall negative effect on DBRs across spatial scales. To empirically test these hypotheses, we collected detailed tree distribution and soil information (e.g., nitrogen, phosphorus, organic matter, pH) from seven temperate and subtropical AM–EM mixed forest megaplots (16–50 ha). Using a spatial codispersion null model and structural equation modeling, we identified the relationships among AM or EM tree dominance, soil fertility, tree species diversity, and biomass and, thus, DBRs across 0.01- to 1-ha scales. We found the first evidence overall supporting the three aforementioned hypotheses in these AM–EM mixed forests: (i) In most forests, with increasing soil fertility, tree communities changed from EM-dominated to AM-dominated; (ii) increasing AM tree dominance had an overall positive effect on tree diversity and a negative effect on biomass, even after controlling for soil fertility and number of trees. Together, (iii) the changes in mycorrhizal dominance along soil fertility gradients weakened the positive DBR observed at 0.01- to 0.04-ha scales in nearly all forests and drove negative DBRs at 0.25- to 1-ha scales in four out of seven forests. Hence, this study highlights a soil-related mycorrhizal dominance mechanism that could partly explain why, in many natural forests, biodiversity–ecosystem functioning (BEF) relationships shift from positive to negative with increasing spatial scale.
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U2 - 10.1002/ecm.1568
DO - 10.1002/ecm.1568
M3 - Research Article
AN - SCOPUS:85150419359
SN - 0012-9615
VL - 93
JO - Ecological Monographs
JF - Ecological Monographs
IS - 2
M1 - e1568
ER -