Abstract

A pressing question is whether biodiversity can buffer ecosystem functioning against extreme climate events. However, biodiversity loss is expected to occur due to climate change with severe impacts to tropical forests. Using data from a ca. 15 year-old tropical planted forest, we construct models based on a bootstrapping procedure to measure growth and mortality among different species richness treatments in response to extreme climate events. In contrast to higher richness mixtures, in one-species plots we find growth is strongly regulated by climate events and we also find increasingly higher mortality during a consecutive three year dry event. Based on these results together with indicators of loss of resilience, we infer an effect of diversity on critical slowing down. Our work generates new methods, concepts, and applications for global change ecology and emphasises the need for research in the area of biodiversity-ecosystem functioning along environmental stress gradients.

Highlights

  • Projections of future climate change include higher mean temperatures, water deficit intensity, and more intense El Niño-Southern Oscillation events[1]

  • Normal years are identified based on the climate data over a 21 year period; because of the way standardised precipitation-evapotranspiration index46 (SPEI) is computed there is an unavoidable shifting baseline which depends on the period chosen

  • The effect sizes generated by our growth model are very similar to measures of resistance; our measure is adapted to studying stability in trees because we account for the large individual variation by adopting a bootstrapping procedure to compute both means and variances

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Summary

Introduction

Projections of future climate change include higher mean temperatures, water deficit intensity, and more intense El Niño-Southern Oscillation events[1]. In a recent study[24], the authors found empirical evidence for decreased stability in certain functions from an analysis of species abundances in five different functional groups (i.e. decomposition, carbon sequestration, pollination, pest control, and cultural values) which they posit is due to a weakened insurance capacity They claim that there is a higher risk of failure in these functions under future environmental perturbations, they do not consider perturbations of higher frequency and magnitude. It is posited that the performance of more diverse communities improves relative to that of low diversity communities in stressful environments because of the emergence of interspecific facilitative interactions among individuals[35] Both species-specific (complementarity) and per capita (stress gradient hypothesis) mechanisms suggest a stronger impact of stress events on monocultures than on mixture communities. Separating the background variation in functioning from the signal due to stress means developing an approach to measure stability accounting for this variation

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