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Diversity increases yield but reduces harvest index in crop mixtures

Abstract

Resource allocation to reproduction is a critical trait for plant fitness1,2. This trait, called harvest index in the agricultural context3,4,5, determines how plant biomass is converted to seed yield and consequently financial revenue from numerous major staple crops. While plant diversity has been demonstrated to increase plant biomass6,7,8, plant diversity effects on seed yield of crops are ambiguous9 and dependent on the production syndrome10. This discrepancy might be explained through changes in the proportion of resources invested in reproduction in response to changes in plant diversity, namely through changes in species interactions and microenvironmental conditions11,12,13,14. Here, we show that increasing crop plant diversity from monocultures over two- to four-species mixtures increased annual primary productivity, resulting in overall higher plant biomass and, to a lesser extent, higher seed yield in mixtures compared with monocultures. The difference between the two responses to diversity was due to a reduced harvest index of the eight tested crop species in mixtures, possibly because their common cultivars have been bred for maximum performance in monoculture. While crop diversification provides a sustainable measure of agricultural intensification15, the use of currently available cultivars may compromise larger gains in seed yield. We therefore advocate regional breeding programmes for crop varieties to be used in mixtures that should exploit complementarity16 among crop species.

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Fig. 1: Seed yield response to crop diversity.
Fig. 2: Crop plant diversity effects on seed yield and vegetative biomass.
Fig. 3: Harvest index of crop species in response to plant diversity and country.
Fig. 4: Relationship of the harvest index of eight crop species with plant functional traits.

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Data availability

The data that support the findings of this study and the corresponding R-code are available at the public repository Zenodo (https://doi.org/10.5281/zenodo.4750856).

References

  1. Weiner, J. Plant Reproductive Ecology: Patterns and Strategies (Oxford Univ. Press, 1988).

  2. Ashman, T. L. & Schoen, D. J. How long should flowers live? Nature 371, 788–791 (1994).

    Article  CAS  Google Scholar 

  3. Donald, C. M. The breeding of crop ideotypes. Euphytica 17, 385–403 (1968).

    Article  Google Scholar 

  4. Unkovich, M., Baldock, J. & Forbes, M. Variability in harvest index of grain crops and potential significance for carbon accounting: examples from Australian agriculture. Adv. Agron. 105, 173–219 (2010).

    Article  Google Scholar 

  5. Tamagno, S., Sadras, V. O., Ortez, O. A. & Ciampitti, I. A. Allometric analysis reveals enhanced reproductive allocation in historical set of soybean varieties. Field Crop Res. 248, 107717 (2020).

    Article  Google Scholar 

  6. Hector, A. et al. Plant diversity and productivity experiments in European grasslands. Science 286, 1123–1127 (1999).

    Article  CAS  PubMed  Google Scholar 

  7. Grace, J. B. et al. Integrative modelling reveals mechanisms linking productivity and plant species richness. Nature 529, 390–393 (2016).

    Article  CAS  PubMed  Google Scholar 

  8. Huang, Y. et al. Impacts of species richness on productivity in a large-scale subtropical forest experiment. Science 362, 80–83 (2018).

    Article  CAS  PubMed  Google Scholar 

  9. Letourneau, D. K. et al. Does plant diversity benefit agroecosystems? A synthetic review. Ecol. Appl. 21, 9–21 (2011).

    Article  PubMed  Google Scholar 

  10. Li, C. et al. Syndromes of production in intercropping impact yield gains. Nat. Plants 6, 653–660 (2020).

    Article  PubMed  Google Scholar 

  11. McConnaughay, K. D. M. & Coleman, J. S. Biomass allocation in plants: ontogeny or optimality? A test along three resource gradients. Ecology 80, 2581–2593 (1999).

    Article  Google Scholar 

  12. Bonser, S. P. & Aarssen, L. W. Allometry and plasticity of meristem allocation throughout development in Arabidopsis thaliana. J. Ecol. 89, 72–79 (2001).

    Article  Google Scholar 

  13. Reekie, E. G. & Bazzaz, F. A. Reproductive Allocation in Plants (Elsevier Academic Press, 2005).

  14. Wang, T. H., Zhou, D. W., Wang, P. & Zhang, H. X. Size-dependent reproductive effort in Amaranthus retroflexus: the influence of planting density and sowing date. Can. J. Bot. 84, 485–492 (2006).

    Article  Google Scholar 

  15. Gurr, G. M. et al. Multi-country evidence that crop diversification promotes ecological intensification of agriculture. Nat. Plants 2, 16014 (2016).

    Article  PubMed  Google Scholar 

  16. Li, C. et al. Yield gain, complementarity and competitive dominance in intercropping in China: a meta-analysis of drivers of yield gain using additive partitioning. Eur. J. Agron. 113, 125987 (2020).

    Article  CAS  Google Scholar 

  17. Tilman, D. et al. Diversity and productivity in a long-term grassland experiment. Science 294, 843–845 (2001).

    Article  CAS  PubMed  Google Scholar 

  18. Loreau, M. & Hector, A. Partitioning selection and complementarity in biodiversity experiments. Nature 412, 72–76 (2001).

    Article  CAS  PubMed  Google Scholar 

  19. Li, L., Tilman, D., Lambers, H. & Zhang, F. S. Plant diversity and overyielding: insights from belowground facilitation of intercropping in agriculture. New Phytol. 203, 63–69 (2014).

    Article  PubMed  CAS  Google Scholar 

  20. Brooker, R. W. et al. Improving intercropping: a synthesis of research in agronomy, plant physiology and ecology. New Phytol. 206, 107–117 (2015).

    Article  PubMed  Google Scholar 

  21. Martin-Guay, M. O., Paquette, A., Dupras, J. & Rivest, D. The new green revolution: sustainable intensification of agriculture by intercropping. Sci. Total Environ. 615, 767–772 (2018).

    Article  CAS  PubMed  Google Scholar 

  22. Bazzaz, F. A., Chiariello, N. R., Coley, P. D. & Pitelka, L. F. Allocating resources to reproduction and defense. Bioscience 37, 58–67 (1987).

    Article  Google Scholar 

  23. Hartnett, D. C. Size-dependent allocation to sexual and vegetative reproduction in 4 clonal composites. Oecologia 84, 254–259 (1990).

    Article  CAS  PubMed  Google Scholar 

  24. Vega, C. R. C., Sadras, V. O., Andrade, F. H. & Uhart, S. A. Reproductive allometry in soybean, maize and sunflower. Ann. Bot. 85, 461–468 (2000).

    Article  Google Scholar 

  25. Gifford, R. M., Thorne, J. H., Hitz, W. D. & Giaquinta, R. T. Crop productivity and photoassimilate partitioning. Science 225, 801–808 (1984).

    Article  CAS  PubMed  Google Scholar 

  26. Andrade, F. H. et al. Kernel number determination in maize. Crop Sci. 39, 453–459 (1999).

    Article  Google Scholar 

  27. Milla, R., Osborne, C. P., Turcotte, M. M. & Violle, C. Plant domestication through an ecological lens. Trends Ecol. Evol. 30, 463–469 (2015).

    Article  PubMed  Google Scholar 

  28. Niklas, K. J. Plant Allometry: The Scaling of Form and Process (Univ. of Chicago Press, 1994).

  29. Echarte, L. & Andrade, F. H. Harvest index stability of Argentinean maize hybrids released between 1965 and 1993. Field Crop Res. 82, 1–12 (2003).

    Article  Google Scholar 

  30. Weiner, J., Campbell, L. G., Pino, J. & Echarte, L. The allometry of reproduction within plant populations. J. Ecol. 97, 1220–1233 (2009).

    Article  Google Scholar 

  31. Sugiyama, S. & Bazzaz, F. A. Size dependence of reproductive allocation: the influence of resource availability, competition and genetic identity. Funct. Ecol. 12, 280–288 (1998).

    Article  Google Scholar 

  32. Weiner, J. Allocation, plasticity and allometry in plants. Perspect. Plant Ecol. 6, 207–215 (2004).

    Article  Google Scholar 

  33. Weiner, J. et al. Is reproductive allocation in Senecio vulgaris plastic? Botany 87, 475–481 (2009).

    Article  Google Scholar 

  34. Schmid, B. & Weiner, J. Plastic relationships between reproductive and vegetative mass in Solidago altissima. Evolution 47, 61–74 (1993).

    Article  PubMed  Google Scholar 

  35. Schmid, B. & Pfisterer, A. B. Species vs community perspectives in biodiversity experiments. Oikos 100, 620–621 (2003).

    Article  Google Scholar 

  36. Lipowsky, A. et al. Plasticity of functional traits of forb species in response to biodiversity. Perspect. Plant Ecol. Evol. Syst. 17, 66–77 (2015).

    Article  Google Scholar 

  37. Abakumova, M., Zobel, K., Lepik, A. & Semchenko, M. Plasticity in plant functional traits is shaped by variability in neighbourhood species composition. New Phytol. 211, 455–463 (2016).

    Article  CAS  PubMed  Google Scholar 

  38. Zhu, J. Q., van der Werf, W., Anten, N. P. R., Vos, J. & Evers, J. B. The contribution of phenotypic plasticity to complementary light capture in plant mixtures. New Phytol. 207, 1213–1222 (2015).

    Article  PubMed  Google Scholar 

  39. Niklaus, P. A., Baruffol, M., He, J. S., Ma, K. P. & Schmid, B. Can niche plasticity promote biodiversity-productivity relationships through increased complementarity? Ecology 98, 1104–1116 (2017).

    Article  PubMed  Google Scholar 

  40. Eziz, A. et al. Drought effect on plant biomass allocation: a meta-analysis. Ecol. Evol. 7, 11002–11010.

  41. Joshi, J. et al. Local adaptation enhances performance of common plant species. Ecol. Lett. 4, 536–544 (2001).

    Article  Google Scholar 

  42. Li, J. et al. Variations in maize dry matter, harvest index, and grain yield with plant density. Agron. J. 107, 829–834 (2015).

    Article  Google Scholar 

  43. Gou, F., van Ittersum, M. K., Wang, G. Y., van der Putten, P. E. L. & van der Werf, W. Yield and yield components of wheat and maize in wheat-maize intercropping in the Netherlands. Eur. J. Agron. 76, 17–27.

  44. Isbell, F. et al. Quantifying effects of biodiversity on ecosystem functioning across times and places. Ecol. Lett. 21, 763–778.

  45. Roscher, C. & Schumacher, J. Positive diversity effects on productivity in mixtures of arable weed species as related to density–size relationships. J. Plant Ecol. 9, 792–804 (2016).

    Article  Google Scholar 

  46. Roscher, C. et al. Overyielding in experimental grassland communities – irrespective of species pool or spatial scale. Ecol. Lett. 8, 419–429.

  47. Isbell, F. et al. High plant diversity is needed to maintain ecosystem services. Nature 477, 199–202 (2011).

    Article  CAS  PubMed  Google Scholar 

  48. Schmid, B., Baruffol, M., Wang, Z. & Niklaus, P. A. A guide to analyzing biodiversity experiments. J. Plant Ecol. 10, 91–110.

  49. Rosenthal, R. & Rosnow, R. L. Contrast Analysis: Focused Comparisons in the Analysis of Variance (Cambridge Univ. Press, 2010).

  50. Díaz-Sierra, R., Verwijmeren, M., Rietkerk, M., de Dios, V. R. & Baudena, M. A new family of standardized and symmetric indices for measuring the intensity and importance of plant neighbour effects. Methods Ecol. Evol. 8, 580–591 (2017).

    Article  Google Scholar 

  51. Poorter, H. & Garnier, E. in Handbook of Functional Plant Ecology (eds Pugnaire, F. I. & Valladares, F.) 81–120 (Marcel Dekker, 1999).

  52. Grime, J. P. Evidence for existence of 3 primary strategies in plants and its relevance to ecological and evolutionary theory. Am. Nat. 111, 1169–1194 (1977).

    Article  Google Scholar 

  53. Wilson, P. J., Thompson, K. & Hodgson, J. G. Specific leaf area and leaf dry matter content as alternative predictors of plant strategies. New Phytol. 143, 155–162 (1999).

    Article  Google Scholar 

  54. Poorter, H., Niinemets, U., Poorter, L., Wright, I. J. & Villar, R. Causes and consequences of variation in leaf mass per area (LMA): a meta-analysis. New Phytol. 182, 565–588 (2009).

    Article  PubMed  Google Scholar 

  55. Lavorel, S. & Grigulis, K. How fundamental plant functional trait relationships scale-up to trade-offs and synergies in ecosystem services. J. Ecol. 100, 128–140 (2012).

    Article  Google Scholar 

  56. Conti, G. & Díaz, S. Plant functional diversity and carbon storage – an empirical test in semi‐arid forest ecosystems. J. Ecol. 101, 18–28 (2013).

    Article  CAS  Google Scholar 

  57. R Core Team. R: A Language and Environment for Statistical Computing (R Foundation for Statistical Computing, 2019); https://www.r-project.org/

  58. Lüdecke, D. ggeffects: Tidy data frames of marginal effects from regression models. J. Open Source Softw. 3, 772 (2018).

    Article  Google Scholar 

  59. Lüdecke, D. sjPlot: data visualization for statistics in social science. Zenodo https://doi.org/10.5281/zenodo.1308157 (2018).

Download references

Acknowledgements

This work was financially supported by the Swiss National Science Foundation (no. PPOOP3_170645 to C.S.). J.C. was supported by the China Scholarship Council. We thank C. Barriga Cabanillas, E. P. Carbonell, H. Ramos Marcos, E. Hidalgo Froilán, A. García-Astillero Honrado, R. Hüppi and S. Baumgartner for field assistance.

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Contributions

C.S. and J.C. conceptualized the study. C.S. designed the experiment with input from B.S. N.E., L.S. and C.S. carried out the experiment. C.S., B.S. and J.C. analysed the data. J.C. and C.S. wrote the paper with input from B.S., N.E., L.S. and H.S.

Corresponding author

Correspondence to Christian Schöb.

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The authors declare no competing interests.

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Peer review information Nature Plants thanks Wopke van der Werf and the other, anonymous, reviewer(s) for their contribution to the peer review of this work.

Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Extended data

Extended Data Fig. 1 Vegetative biomass responses to crop diversity.

Average vegetative biomass (in g m-2) of eight monocultures, 24 different 2- and 16 different 4-species mixtures planted with eight different annual crop species in 0.25 m2 plots in Switzerland and Spain. Data are mean and 95% CI. n = 762 plots. The statistical analyses (type-I analysis of variance of a linear mixed model and significance tested with the Satterthwaite approximation method) show significant effects of country [F(1,20.7) = 195.8, P = 5.23×10-12], country × diversity [F(1,677.5) = 8.1, P = 0.004], country × species number [F(1,679.2) = 5.9, P = 0.015], and marginally significant effects of diversity [F(1,45.1) = 3.7, P = 0.062] on vegetative biomass. See Extended Data Fig. 2 for seed yield and vegetative biomass data of each species in monocultures and 2- and 4-species mixtures in Switzerland and Spain.

Extended Data Fig. 2 Crop plant diversity effects on seed yield and vegetative biomass of each species.

Average seed yield (a) and vegetative biomass (b) per species (in g m-2) of eight monocultures, 24 different 2- and 16 different 4-species mixtures planted with eight different annual crop species in 0.25 m2 plots in Switzerland and Spain. Data are mean and 1 SE based on raw data. To facilitate interpretation, data were extrapolated so that the values reflect the area of 1 m2 covered by the species in the community of interest. n = 2284 species in plots for seed yield and n = 2275 species in plots for vegetative biomass.

Extended Data Fig. 3 Crop plant diversity effects on seed yield and vegetative biomass.

Seed yield and vegetative biomass increases (in g m-2) compared with monocultures averaged over 24 different 2- and 16 different 4-species mixtures, respectively. For the complementarity effect (a) n = 1274 biomass partitions (seed vs vegetative) in plots, for the sampling effect (b) n = 1181 biomass partitions (seed vs vegetative) in plots. Data are mean and 95% CI. See Supporting Information Table 6 for the complete statistical analyses. In Switzerland, complementarity effects contributed 25% more than sampling effects to the net biodiversity effect on seed yield, while in Spain only sampling effects could be detected. Complementarity effects in Switzerland were 59% lower for seed yield than for vegetative biomass. Sampling effects were 70% and 83% lower for seed yield than for vegetative biomass in Spain and Switzerland, respectively.

Extended Data Fig. 4 Harvest index of crops in response to the Home vs Away, Fertilization, Country and Species number (2- vs 4-species mixtures) treatments.

Data are mean and 95% CI. n = 4751 individuals.

Extended Data Fig. 5 Harvest index of the eight crop species planted in communities of different species composition.

Species were abbreviated as: Avena sativa = Av, Triticum aestivum = Tr, Camelina sativa = Ca, Coriandrum sativum = Co, Lens culinaris = Le, Lupinus angustifolius = Lu, Linum usitatissimum = Li and Chenopodium quinoa = Qu. Data are mean and 1 SE. n = 4751 individuals.

Extended Data Fig. 6 Harvest index for eight crop species in their Home vs Away environment.

The harvest index quantifies the proportion of reproductive biomass, that is seed yield, from total aboveground biomass produced by the Spanish cultivars in Spain and the Swiss cultivars in Switzerland (Home) and vice versa (Away). Data are mean and 95% CI. n = 4751 individuals.

Extended Data Fig. 7 The harvest index at the community level in response to plant diversity and country.

Harvest index calculated at the community-level as the ratio between plot-level seed yield and plot-level aboveground biomass (that is the sum of aboveground vegetative biomass and seed yield), irrespective of species. Data shown are mean and 95% CI. n = 762 plots. The contrast of diversity vs mixture is marginally significant as a main effect [F(1,44.9) = 3.05, P = 0.088], and significant in interaction with country [F(1,675.1) = 4.96, P = 0.026], while the contrast between 2- and 4-species mixtures is not significant. Statistical tests were done on a linear mixed effects model with type-I analysis of variance and Satterthwaite approximation.

Extended Data Fig. 8 Layout of the experimental garden in Switzerland.

Monoculture and mixture communities are composed of four planting rows (divided by dashed lines and coloured strips), while plots with single plants are indicated in plain colour corresponding to the crop species. Plots (0.5 × 0.5 m) are delineated with a solid black frame. Beds (20 beds of 7 × 1 m each) are delineated with either a red (= fertilised) or green (= non-fertilised control) frame. Row numbers and column letters between the beds are used to identify each plot. Letters within the plots indicate the ecotype (S = Switzerland, E = Spain) of each crop species.

Extended Data Fig. 9 Layout of the experimental garden in Spain.

Monoculture and mixture communities are composed of four planting rows (divided by dashed lines and coloured strips), while plots with single plants are indicated in plain colour corresponding to the crop species. Plots (0.5 × 0.5 m) are delineated with a solid black frame. Beds (16 beds of 10 × 1 m each) are delineated with either a red (= fertilised) or green (= non-fertilised control) frame. Row numbers and column letters between the beds are used to identify each plot. Letters within the plots indicate the ecotype (S = Switzerland, E = Spain) of each crop species.

Extended Data Fig. 10 Phenological plant development for eight crop species as single plants, in monocultures and in mixtures in Switzerland and Spain.

Boxplots show median (black dot), upper and lower quartile (box), maximum and minimum values (whiskers) and outliers (open circles). Three plant development stages for each of the eight crop species averaged over all treatments per country, per diversity level. The specific development stages are for oat: beginning of tillering, flowering (tip of inflorescence emerged from sheath), seeds with milk texture; for wheat: beginning of tillering, flowering, seeds milk ripe; for lentil: first true leaf unfolded, flowering, full seeds (seeds fill the pod cavities); lupin: stem elongation and bases of several leaves clearly separated from each other, flowering, green pods (septa split and filled with seeds); camelina: first true leaf unfolded, flowering, start of grain formation; linseed: first basal branches expanded, flowering, capsules expanded and seeds formed; coriander: first true coriander leaf unfolded, flowering, formation of green capsules; quinoa: first true leaves unfolded, flower buds in pyramids, start of grain formation.

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Chen, J., Engbersen, N., Stefan, L. et al. Diversity increases yield but reduces harvest index in crop mixtures. Nat. Plants 7, 893–898 (2021). https://doi.org/10.1038/s41477-021-00948-4

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