Abstract
A long-standing but poorly tested hypothesis in plant ecology and evolution is that biotic interactions play a more important role in producing and maintaining species diversity in the tropics than in the temperate zone. A core prediction of this hypothesis is that tropical plants deploy a higher diversity of phytochemicals within and across communities because they experience more herbivore pressure than temperate plants. However, simultaneous comparisons of phytochemical diversity and herbivore pressure in plant communities from the tropical to the temperate zone are lacking. Here we provide clear support for this prediction by examining phytochemical diversity and herbivory in 60 tree communities ranging from species-rich tropical rainforests to species-poor subalpine forests. Using a community metabolomics approach, we show that phytochemical diversity is higher within and among tropical tree communities than within and among subtropical and subalpine communities, and that herbivore pressure and specialization are highest in the tropics. Furthermore, we show that the phytochemical similarity of trees has little phylogenetic signal, indicating rapid divergence between closely related species. In sum, we provide several lines of evidence from entire tree communities showing that biotic interactions probably play an increasingly important role in generating and maintaining tree diversity in the lower latitudes.
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Data availability
The MS data (.mzML) have been deposited in the MassIVE public repository and are available under accession number MSV000092950. The datasets analysed in the current study, including the molecular network, sample–sample chemical structural and compositional similarity, plot-species-abundance community data, phytochemical richness and the phylogenetic tree of 206 tree species, are available via Figshare at https://doi.org/10.6084/m9.figshare.22758269 (ref. 69).
Code availability
The R code used in the current study is available via Figshare at https://doi.org/10.6084/m9.figshare.22758269 (ref. 69).
References
Hillebrand, H. On the generality of the latitudinal diversity gradient. Am. Nat. 163, 192–211 (2004).
Willig, M. R., Kaufman, D. M. & Stevens, R. D. Latitudinal gradients of biodiversity: pattern, process, scale, and synthesis. Annu. Rev. Ecol. Evol. Syst. 34, 273–309 (2003).
Gentry, A. H. Tree species richness of upper Amazonian forests. Proc. Natl Acad. Sci. USA 85, 156–159 (1988).
Valencia, R. et al. in Tropical Forest Diversity and Dynamism: Findings from a Large-Scale Plot Network (eds Losos, E. C. & Leigh, E. G.) 609–628 (Univ. Chicago Press, 2004).
Dobzhansky, T. Evolution in the tropics. Am. Sci. 38, 209–221 (1950).
Fischer, A. G. Latitudinal variations in organic diversity. Evolution 14, 64–81 (1960).
Janzen, D. H. Herbivores and the number of tree species in tropical forests. Am. Nat. 104, 501–528 (1970).
Connell, J. H. in Dynamics of Numbers in Populations (eds Den Boer, P. J. & Gradwell, G. R.) 298–312 (PUDOC, 1971).
Ehrlich, P. R. & Raven, P. H. Butterflies and plants—a study in coevolution. Evolution 18, 586–608 (1964).
Van Valen, L. The red queen. Am. Nat. 111, 809–810 (1977).
Coley, P. D. & Kursar, T. A. On tropical forests and their pests. Science 343, 35–36 (2014).
Zvereva, E. L. & Kozlov, M. V. Latitudinal gradient in the intensity of biotic interactions in terrestrial ecosystems: sources of variation and differences from the diversity gradient revealed by meta-analysis. Ecol. Lett. 24, 2506–2520 (2021).
Roslin, T. et al. Higher predation risk for insect prey at low latitudes and elevations. Science 356, 742–744 (2017).
Moles, A. T. & Ollerton, J. Is the notion that species interactions are stronger and more specialized in the tropics a zombie idea? Biotropica 48, 141–145 (2016).
Coley, P. D. & Barone, J. A. Herbivory and plant defenses in tropical forests. Annu. Rev. Ecol. Evol. Syst. 27, 305–335 (1996).
Schemske, D. W., Mittelbach, G. G., Cornell, H. V., Sobel, J. M. & Roy, K. Is there a latitudinal gradient in the importance of biotic interactions? Annu. Rev. Ecol. Evol. Syst. 40, 245–269 (2009).
Ali, J. G. & Agrawal, A. A. Specialist versus generalist insect herbivores and plant defense. Trends Plant Sci. 17, 293–302 (2012).
Carmona, D., Lajeunesse, M. J. & Johnson, M. T. J. Plant traits that predict resistance to herbivores. Funct. Ecol. 25, 358–367 (2011).
Jones, C. G. & Firn, R. D. On the evolution of plant secondary chemical diversity. Phil. Trans. R. Soc. Lond. B. 333, 273–280 (1991).
Endara, M. J., Forrister, D. L. & Coley, P. D. The evolutionary ecology of plant chemical defenses: from molecules to communities. Annu. Rev. Ecol. Evol. Syst. 54, 107–127 (2023).
Kessler, A. & Kalske, A. Plant secondary metabolite diversity and species interactions. Annu. Rev. Ecol. Evol. Syst. 49, 115–138 (2018).
Wang, S., Alseekh, S., Fernie, A. R. & Luo, J. The structure and function of major plant metabolite modifications. Mol. Plant 12, 899–919 (2019).
Iason, G. R., Dicke, M. & Hartley, S. E. The Ecology of Plant Secondary Metabolites: From Genes to Global Processes (Cambridge Univ. Press, 2012).
Sedio, B. E. Recent breakthroughs in metabolomics promise to reveal the cryptic chemical traits that mediate plant community composition, character evolution and lineage diversification. N. Phytol. 214, 952–958 (2017).
Wetzel, W. C. & Whitehead, S. R. The many dimensions of phytochemical diversity: linking theory to practice. Ecol. Lett. 23, 16–32 (2020).
Sedio, B. E., Parker, J. D., McMahon, S. M. & Wright, S. J. Comparative foliar metabolomics of a tropical and a temperate forest community. Ecology 99, 2647–2653 (2018).
Defossez, E. et al. Spatial and evolutionary predictability of phytochemical diversity. Proc. Natl Acad. Sci. USA 118, e2013344118 (2021).
Forrister, D. L. et al. Diversity and divergence: evolution of secondary metabolism in the tropical tree genus Inga. N. Phytol. 237, 63–642 (2023).
Qian, L. S., Chen, J. H., Deng, T. & Sun, H. Plant diversity in Yunnan: current status and future directions. Plant Divers. 42, 281–291 (2020).
Zhu, H. & Tan, Y. H. Flora and vegetation of Yunnan, southwestern China: diversity, origin and evolution. Diversity 14, 340 (2022).
Sedio, B. E., Boya P, C. A. & Rojas Echeverri, J. C. A protocol for high-throughput, untargeted forest community metabolomics using mass spectrometry molecular networks. Appl. Plant Sci. 6, e1033 (2018).
GNPS: Global Natural Products Social Molecular Networking. UCSD https://gnps.ucsd.edu (2023).
Wang, M. X. et al. Sharing and community curation of mass spectrometry data with Global Natural Products Social Molecular Networking. Nat. Biotechnol. 34, 828–837 (2016).
Aron, A. T. et al. Reproducible molecular networking of untargeted mass spectrometry data using GNPS. Nat. Protoc. 15, 1954–1991 (2020).
Kim, H. W. et al. NPClassifier: a deep neural network-based structural classification tool for natural products. J. Nat. Prod. 84, 2795–2807 (2021).
Chao, A. et al. An attribute-diversity approach to functional diversity, functional beta diversity, and related (dis)similarity measures. Ecol. Monogr. 89, e01343 (2019).
Swenson, N. G. Functional and Phylogenetic Ecology in R (Springer, 2014).
Kraft, N. J. B. et al. Disentangling the drivers of β diversity along latitudinal and elevational gradients. Science 333, 1755–1758 (2011).
Wang, X. Z. et al. Niche differentiation along multiple functional-trait dimensions contributes to high local diversity of Euphorbiaceae in a tropical tree assemblage. J. Ecol. 110, 2731–2744 (2022).
Labandeira, C. C., Wilf, P., Johnson, K. R. & Marsh, F. Guide to insect (and other) damage types on compressed plant fossils v.3.0. figshare https://doi.org/10.6084/m9.figshare.16571441.v1 (2007).
Kursar, T. A. et al. Linking bioprospecting with sustainable development and conservation: the Panama case. Biodivers. Conserv. 16, 2789–2800 (2007).
Kursar, T. A. et al. The evolution of antiherbivore defenses and their contribution to species coexistence in the tropical tree genus Inga. Proc. Natl Acad. Sci. USA 106, 18073–18078 (2009).
Song, X. Y. et al. Different environmental factors drive tree species diversity along elevation gradients in three climatic zones in Yunnan, southern China. Plant Divers. 43, 433–443 (2021).
Song, X. Y., Nakamura, A., Sun, Z. H., Tang, Y. & Cao, M. Elevational distribution of adult trees and seedlings in a tropical montane transect, Southwest China. Mt. Res. Dev. 36, 342–354 (2016).
Endara, M. J. et al. Divergent evolution in antiherbivore defences within species complexes at a single Amazonian site. J. Ecol. 103, 1107–1118 (2015).
Richards, L. A. et al. Phytochemical diversity drives plant–insect community diversity. Proc. Natl Acad. Sci. USA 112, 10973–10978 (2015).
Salazar, D. et al. Origin and maintenance of chemical diversity in a species-rich tropical tree lineage. Nat. Ecol. Evol. 2, 983–990 (2018).
Chambers, M. C. et al. A cross-platform toolkit for mass spectrometry and proteomics. Nat. Biotechnol. 30, 918–920 (2012).
Sedio, B. E., Rojas Echeverri, J. C., Boya P, C. A. & Wright, S. J. Sources of variation in foliar secondary chemistry in a tropical forest tree community. Ecology 98, 616–623 (2017).
Oksanen, J. et al. vegan: community ecology package. R package v.2.6-4 CRAN https://CRAN.R-project.org/package=vegan (2022).
Magneville, C. et al. mFD: an R package to compute and illustrate the multiple facets of functional diversity. Ecography 2022, e05904 (2022).
Millar, R. B., Anderson, M. J. & Tolimieri, N. Much ado about nothings: using zero similarity points in distance–decay curves. Ecology 92, 1717–1722 (2011).
Graco-Roza, C. et al. Distance decay 2.0—a global synthesis of taxonomic and functional turnover in ecological communities. Glob. Ecol. Biogeogr. 31, 1399–1421 (2022).
Anderson, M. J. et al. Navigating the multiple meanings of β diversity: a roadmap for the practicing ecologist. Ecol. Lett. 14, 19–28 (2011).
Haan, J. & Avery, M. ciTools: confidence or prediction intervals, quantiles, and probabilities for statistical models. R package v.0.6.1 CRAN https://CRAN.R-project.org/package=ciTools (2020).
Kurokawa, H. et al. Plant characteristics drive ontogenetic changes in herbivory damage in a temperate forest. J. Ecol. 110, 2772–2784 (2022).
Katabuchi, M. LeafArea: an R package for rapid digital image analysis of leaf area. Ecol. Res. 30, 1073–1077 (2015).
Laliberté, E. & Legendre, P. A distance-based framework for measuring functional diversity from multiple traits. Ecology 91, 299–305 (2010).
Carvalho, M. R. et al. Insect leaf-chewing damage tracks herbivore richness in modern and ancient forests. PLoS ONE 9, e94950 (2014).
Smith, D. M. & Nufio, C. R. Levels of herbivory in two Costa Rican rain forests: implications for studies of fossil herbivory. Biotropica 36, 318–326 (2004).
Azevedo-Schmidt, L., Meineke, E. K. & Currano, E. D. Insect herbivory within modern forests is greater than fossil localities. Proc. Natl Acad. Sci. USA 119, e2202852119 (2022).
Wang, X. Z. et al. Phytochemical diversity impacts herbivory in a tropical rainforest tree community. Ecol. Lett. 26, 1898–1910 (2023).
Bates, D., Maechler, M., Bolker, B. & Walker, S. Fitting linear mixed-effects models using lme4. J. Stat. Softw. 67, 1–48 (2015).
Jin, Y. & Qian, H. V. PhyloMaker: an R package that can generate very large phylogenies for vascular plants. Ecography 42, 1353–1359 (2019).
Adams, D. C. A generalized K statistic for estimating phylogenetic signal from shape and other high-dimensional multivariate data. Syst. Biol. 63, 685–697 (2014).
Simon, P. B., Theodore Garland, J. R. & Anthony, R. I. Testing for phylogenetic signal in comparative data: behavioral traits are more labile. Evolution 57, 717–745 (2003).
Letunic, I. & Bork, P. Interactive Tree of Life (iTOL) v5: an online tool for phylogenetic tree display and annotation. Nucleic Acids Res. 49, W293–W296 (2021).
R Core Team. R: A Language and Environment for Statistical Computing (R Foundation for Statistical Computing, 2022). https://www.R-project.org/
Sun, L. et al. Tree phytochemical diversity and herbivory are higher in the tropics. figshare https://doi.org/10.6084/m9.figshare.22758269 (2024).
Acknowledgements
This research was supported by the NSFC China–US Dimensions of Biodiversity Grant (DEB: no. 32061123003 to M.C.); the National Natural Science Foundation of China (grant nos. 32201318 to L.S. and 31870410 to J.Y.); the Chinese Academy of Sciences Youth Innovation Promotion Association (grant no. Y202080 to J.Y.); the Distinguished Youth Scholar of Yunnan (grant no. 202101AV070005 to J.Y.); the Ten Thousand Talent Plans for Young Top-Notch Talents of Yunnan Province (grant no. YNWR-QNBJ-2018-309 to J.Y.); a Postdoctoral Fellowship of Xishuangbanna Tropical Botanical Garden, CAS, to L.S.; the Postdoctoral Science Foundation of Yunnan Province to L.S.; the 14th Five-Year Plan of the Xishuangbanna Tropical Botanical Garden, Chinese Academy of Sciences (grant nos. XTBG-1450101 and E3ZKFF2B01 to J.Y.); and an NSF US–China Dimensions of Biodiversity Grant (DEB: no. 2124466) to N.G.S. We acknowledge support from Xishuangbanna Station for Tropical Rain Forest Ecosystem Studies, Ailaoshan Station for Subtropical Forest Ecosystem Studies and Lijiang Forest Ecosystem Research Station. We thank the Molecular Biology Experiment Center in Germplasm Bank of Wild Species, Chinese Academy of Sciences, for facilitating the extraction of plant metabolites, and the State Key Laboratory of Phytochemistry and Plant Resources in West China, Chinese Academy of Sciences, for performing the UHPLC–MS/MS analysis. We thank J. Wang, C. Xu, P. Song, T. Liang and many local residents for their assistance in collecting leaf samples. We also thank J. Yang, H. Liu and Y. Tan for their kind assistance during extracting plant metabolites and metabolite analysis.
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J.Y., L.S. and N.G.S. designed the study. M.C. set up the forest inventory plots. L.S., X.Z., Y.H. and X.W. collected and processed the metabolomics data. L.S., Y.H. and X.W. collected and processed the leaf samples. L.S. and J.Y. analysed the data with input from all authors. J.Y., N.G.S. and L.S. wrote the paper. All authors provided feedback on the final version of the paper.
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Extended data
Extended Data Fig. 1 Observed phytochemical alpha diversity for seven biosynthetic pathway categories within each climatic zone (tropical, sub-tropical and sub-alpine) with diverse q exponents (Qorder = 0, 1, 2).
(a) terpenoids (n = 20 in tropical zone, n = 20 in sub-tropical zone, n = 20 in sub-alpine zone, for one of q exponents), (b) shikimates and phenylpropanoids (n = 20 in tropical zone, n = 20 in sub-tropical zone, n = 20 in sub-alpine zone, for one of q exponents), (c) polyketides (n = 20 in tropical zone, n = 20 in sub-tropical zone, n = 20 in sub-alpine zone, for one of q exponents), (d) alkaloids (n = 20 in tropical zone, n = 20 in sub-tropical zone, n = 20 in sub-alpine zone, for one of q exponents), (e) fatty acids (n = 20 in tropical zone, n = 20 in sub-tropical zone, n = 17 in sub-alpine zone, for one of q exponents), (f) amino acids/peptides (n = 18 in tropical zone, n = 19 in sub-tropical zone, n = 12 in sub-alpine zone, for one of q exponents), (g) carbohydrates (n = 17 in tropical zone, n = 20 in sub-tropical zone, n = 17 in sub-alpine zone, for one of q exponents). In all panels, the significance of difference of phytochemical alpha diversity across forest type pairs were tested using a one-way ANOVA with a post-hoc Tukey test. In boxplots: the centre line represents the median; the lower and upper hinges correspond to the 25th and 75th percentiles; the lower and upper whiskers extend to the lowest and highest points to a limit of 1.5× the interquartile range from the closest hinge.
Extended Data Fig. 2 Observed phytochemical beta diversity for seven biosynthetic pathway categories within each climatic zone (tropical, sub-tropical and sub-alpine) with diverse q exponents (Qorder = 0, 1, 2).
(a) terpenoids (n = 190 in tropical zone, n = 190 in sub-tropical zone, n = 190 in sub-alpine zone, for one of q exponents), (b) shikimates and phenylpropanoids (n = 190 in tropical zone, n = 190 in sub-tropical zone, n = 190 in sub-alpine zone, for one of q exponents), (c) polyketides (n = 190 in tropical zone, n = 190 in sub-tropical zone, n = 190 in sub-alpine zone, for one of q exponents), (d) alkaloids (n = 190 in tropical zone, n = 190 in sub-tropical zone, n = 190 in sub-alpine zone, for one of q exponents), (e) fatty acids (n = 190 in tropical zone, n = 190 in sub-tropical zone, n = 136 in sub-alpine zone, for one of q exponents), (f) amino acids/peptides (n = 153 in tropical zone, n = 171 in sub-tropical zone, n = 66 in sub-alpine zone, for one of q exponents), (g) carbohydrates (n = 136 in tropical zone, n = 190 in sub-tropical zone, n = 136 in sub-alpine zone, for one of q exponents). In all panels, the significance of difference of phytochemical beta diversity across forest type pairs were tested using a one-way ANOVA with a post-hoc Tukey test. In boxplots: the centre line represents the median; the lower and upper hinges correspond to the 25th and 75th percentiles; the lower and upper whiskers extend to the lowest and highest points to a limit of 1.5× the interquartile range from the closest hinge.
Extended Data Fig. 3 Distance-decay curves for the whole plant specialized metabolites with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 4 Distance-decay curves for the plant specialized metabolites on terpenoids with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 5 Distance-decay curves for the plant specialized metabolites on shikimates and phenylpropanoids with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 6 Distance-decay curves for the plant specialized metabolites on polyketides with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue), sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 7 Distance-decay curves for the plant specialized metabolites on alkaloids with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 8 Distance-decay curves for the plant specialized metabolites on fatty acids with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 9 Distance-decay curves for the plant specialized metabolites on amino acids/ peptides with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
Extended Data Fig. 10 Distance-decay curves for the plant specialized metabolites on carbohydrates with diverse q exponents of 0, 1, 2.
The rate of decay (slope) and corresponding significance level were estimated by regressing the chemical similarity against elevational distance via generalized linear model with link log and a quasi-binomial family. The trend lines represent linear fits from regressions, and coloured shaded areas indicate 95% confidence interval (CI) of the prediction. Colours denote whole study region (grey), tropical zone (red), sub-tropical zone (blue) and sub-alpine zone (yellow). Panels, a, d, g and j show the slope of the relationship when q exponents is 0. Panels, b, e, h and k. show the slope of the relationship when q exponents is 1. Panels, c, f, i and l show the slope of the relationship when q exponents is 2.
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Sun, L., He, Y., Cao, M. et al. Tree phytochemical diversity and herbivory are higher in the tropics. Nat Ecol Evol 8, 1426–1436 (2024). https://doi.org/10.1038/s41559-024-02444-2
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DOI: https://doi.org/10.1038/s41559-024-02444-2