Abstract

While there has been increasing interest in how taxonomic diversity is changing over time, less is known about how long‐term taxonomic changes may affect ecosystem functioning and resilience. Exploring long‐term patterns of functional diversity can provide key insights into the capacity of a community to carry out ecological processes and the redundancy of species’ roles. We focus on a protected freshwater system located in a national park in southeast Germany. We use a high‐resolution benthic macroinvertebrate dataset spanning 32 years (1983–2014) and test whether changes in functional diversity are reflected in taxonomic diversity using a multidimensional trait‐based approach and regression analyses. Specifically, we asked: (i) How has functional diversity changed over time? (ii) How functionally distinct are the community's taxa? (iii) Are changes in functional diversity concurrent with taxonomic diversity? And (iv) what is the extent of community functional redundancy? Resultant from acidification mitigation, macroinvertebrate taxonomic diversity increased over the study period. Recovery of functional diversity was less pronounced, lagging behind responses of taxonomic diversity. Over multidecadal timescales, the macroinvertebrate community has become more homogenous with a high degree of functional redundancy, despite being isolated from direct anthropogenic activity. While taxonomic diversity increased over time, functional diversity has yet to catch up. These results demonstrate that anthropogenic pressures can remain a threat to biotic communities even in protected areas. The differences in taxonomic and functional recovery processes highlight the need to incorporate functional traits in assessments of biodiversity responses to global change.

Highlights

  • In the Anthropocene, changes to global biodiversity are widespread and dynamic, albeit heterogeneous across spatial scales and taxonomic groups (Dornelas et al, 2014; Pilotto et al, 2020)

  • Even when reliable and representative long-­term data are available, investigating biodiversity patterns is not without its challenges, as local biodiversity is indisputably governed by biotic and abiotic interactions and comprises a multitude of different facets, namely taxonomic diversity (TD), phylogenetic diversity (PD), and functional diversity (FD), all of which are important for maintaining ecosystem functioning (Devictor et al, 2010)

  • What is the extent of functional redundancy within the Grosse Ohe macroinvertebrate communities? Owing to the linear increases in TD reported in Baker et al (2021) and our expectations that FD would concurrently increase over time, we hypothesize a low degree of functional redundancy within the macroinvertebrate communities (H4) (Micheli & Halpern, 2005)

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Summary

| INTRODUCTION

In the Anthropocene, changes to global biodiversity are widespread and dynamic, albeit heterogeneous across spatial scales and taxonomic groups (Dornelas et al, 2014; Pilotto et al, 2020). The species deviance from the mean distance to the center of gravity weighted by relative abundance within multidimensional trait spaced,e. The weighted (i.e., species relative abundances) mean distance in multidimensional trait space of individual species to the centroid of all speciesd,h. Owing to the linear increases in TD reported in Baker et al (2021) and our expectations that FD would concurrently increase over time, we hypothesize a low degree of functional redundancy within the macroinvertebrate communities (H4) (Micheli & Halpern, 2005). The standardized abundance classes were converted to the mean abundance of each abundance class (see Baker et al, 2021) Despite these necessary adjustments, there was no significant impact of the count method on the analyzed community metrics, which included compositional and abundance metrics, richness and diversity metrics, tolerance and sensitivity metrics, and functional feeding group proportions (Baker et al, 2021)

| MATERIALS AND METHODS
Findings
| DISCUSSION
| General conclusions and future outlooks
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