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Top-down effects dominate the relationship between plant–herbivorous insect interactions and ecosystem stability


Abstract

Consumptive interactions across trophic levels underpin ecosystem stability. Although theoretical and experimental studies have examined the diversity–stability relationship, empirical evidence linking trophic interactions to ecosystem stability remains limited. Here we evaluate how trophic interactions relate to stability across 430 plant–herbivorous insect networks from temperate and tropical ecosystems. We quantified interaction indicators alongside ecosystem resistance and resilience under drought and wet events. Higher plant diversity was associated with drought resistance but with reduced resilience, and these relationships weakened after accounting for sampling and environmental covariates. In contrast, drought resistance increased with network modularity, whereas resilience decreased with robustness, although these patterns were absent in temperate forests. Diversity and interaction indicators did not predict stability under wet events. Although both directions of trophic interaction–stability relationships were significant, the pathway from trophic interactions to stability (top-down) was stronger than the reverse. Our findings provide large-scale empirical evidence that top-down effects probably dominate the relationship between plant–herbivorous insect interactions and ecosystem stability under climate change.

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Fig. 1: Relationships between plant diversity, trophic interaction indicators and drought resistance or resilience across ecosystem types.
Fig. 2: Relative importance of plant diversity and trophic interactions in drought resistance and resilience.
Fig. 3: Effects of trophic interactions on drought resistance and of drought resistance on trophic interactions.
Fig. 4: Effects of trophic interactions on drought resilience and of drought resilience on trophic interactions.
Fig. 5: Direct effects of trophic interactions on stability and of stability on trophic interactions.

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Data availability

The raw data associated with this study are available from figshare (https://doi.org/10.6084/m9.figshare.32305317; ref. 95). This study also used previously published data available from the Harmonized World Soil Database (https://gaez.fao.org/pages/hwsd), Global Land Evaporation Amsterdam Model (https://www.gleam.eu) and CHELSA database (https://chelsa-climate.org). Source data are provided with this paper.

Code availability

All R scripts for statistical analyses are available from figshare (https://doi.org/10.6084/m9.figshare.32305317; ref. 95).

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Funding

This work was supported by grants from the National Natural Science Foundation of China (32501439), Hebei Provincial Natural Science Foundation (C2024205002) and Science Foundation of Hebei Normal University (L2024B18).

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Y.W., Q.Q. and J.L. conceived of the study idea. Y.W., Q.Q., Z.W. and Y.Z. collected the data. Y.W., Q.Q. and J.F. performed the analyses. The manuscript was drafted by Y.W. and Q.Q. with contributions from J.L., Z.Y. and C.W. All authors contributed critically to the manuscript and gave final approval for publication.

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Yin Wang or Jingze Liu.

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Nature Ecology & Evolution thanks Jörg Albrecht, Yi Li and the other, anonymous, reviewer(s) for their contribution to the peer review of this work. Peer reviewer reports are available.

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Extended data

Extended Data Fig. 1 Relationships between plant diversity, trophic interaction indicators and wet resistance or resilience across ecosystem types.

Circles and error bars represent average parameter estimates (standardized coefficients) and 95% confidence intervals based on linear mixed-effects models: “lmer(stability ~ (1|study ID) + sampling effects + trophic interactions or plant diversity)”. P values represent the probability of type I error based on analysis of variance (two-sided F-test). Values in bold indicate significant (P < 0.05) or marginally significant (0.05 ≤ P < 0.1) effects. The complete results are presented in Supplementary Tables 3 and 6. The numbers in parentheses show sample sizes.

Extended Data Fig. 2 Relative importance of plant diversity and trophic interactions on wet resistance and resilience.

a–f, Relative importance of plant diversity and trophic interactions on wet resistance (a–c) or resilience (d–f) across ecosystem types (temperate forest (a and d), tropical forest (b and e) and savanna (c and f)). The bar plots indicate percentages of explained variance (relative importance) for plant diversity, trophic interactions, covariates and random effects. The marginal R2 (R2m) and conditional R2 (R2c) values represent the proportion of variance explained by all factors without accounting for random effects and accounting for random effects, respectively. It is important to note that variable importance based on hierarchical partitioning can be negative due to multicollinearity96. The numbers in parentheses show sample sizes.

Extended Data Fig. 3 Relationships of plant diversity and trophic interaction indicators across ecosystem types.

a–c, Results from piecewise SEM on the relationships of plant diversity and trophic interaction indicators in temperate forests (a), tropical forests (b) and savannas (c). Alternative SEMs were tested to elucidate the relationships between plant diversity and interaction indicators (Supplementary Fig. 3). The values represent standardized path coefficients. Solid arrows denote significant positive (blue) or negative (red) relationships (P < 0.05; two-sided test). Dashed arrows (grey) denote non-significant paths (P > 0.05; two-sided test). *P < 0.05; **P < 0.01; ***P < 0.001. The numbers in parentheses show sample sizes.

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Wang, Y., Qin, Q., Feng, J. et al. Top-down effects dominate the relationship between plant–herbivorous insect interactions and ecosystem stability.
Nat Ecol Evol (2026). https://doi.org/10.1038/s41559-026-03114-1

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