Abstract

Ecology, biogeography and conservation biology, among other disciplines, often rely on species identity, distribution and abundance to perceive and explain patterns in space and time. Yet, species are not independent units in the way they interact with their environment. Species often perform similar roles in networks and their ecosystems, and at least partial redundancy or difference of roles might explain co-existence, competitive exclusion or other patterns reflected at the community level. Therefore, considering species traits, that is, the organisms’ functional properties that interact with the environment, might be of utmost importance in the study of species relative abundances. Several descriptive measures of diversity, such as the species-area relationship (SAR) and the species abundance distribution (SAD), have been used extensively to characterize the communities and as a possible window to gain insight into underlying processes shaping and maintaining biodiversity. However, if the role of species in a community is better assessed by their functional attributes, then one should also study the SAR and the SAD by using trait-based approaches, and not only taxonomic species. Here we merged species according to their similarity in a number of traits, creating functional units, and used these new units to study the equivalent patterns of the SAR and of the SAD (functional units abundance distributions - FUADs), with emphasis on their spatial scaling characteristics. This idea was tested using data on arthropods collected in Terceira island, in the Azorean archipelago. Our results showed that diversity scales differently depending on whether we use species or functional units. If what determines species communities’ dynamics is their functional diversity, then our results suggest that we may need to revaluate the commonly assumed patterns of species diversity and, concomitantly, the role of the underlying processes.

Highlights

  • Species diversity, or biodiversity, encompasses several scales, from the genetic to that of species, populations and ecosystem functions (Wilcox, 1984; United Nations Environment Programme [UNEP], 1992)

  • The obvious difference between the two curves is that the functional units-area relationships (FUAR) in a log-log plot starts exhibits a plateau, showing clear signs of starting to “saturate,” while the traditional species-area curve reveals the typical straight line in a log-log plot, that is the number of taxonomic species keeps increasing until the very last transect considered

  • Under the premise that functional units have a more meaningful correspondence with the underlying processes of maintenance and generation of species diversity (Tilman, 2001), we applied several procedures commonly used on studies of communities but using, instead of taxonomical species, functional units, that is, entities resulting from aggregating species with identical traits

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Summary

Introduction

Biodiversity, encompasses several scales, from the genetic (phylogenetic diversity at the species level) to that of species (taxonomic diversity), populations and ecosystem functions (functional diversity) (Wilcox, 1984; United Nations Environment Programme [UNEP], 1992). One of the major goals of ecology is to describe this diversity at different spatial and temporal scales and seek for the processes shaping and maintaining it. Species do not exist in isolation, they interact with each other and are influenced, and influence, abiotic processes in the environments where they exist. A major challenge is to connect the description of taxonomic diversity with the processes by which species interact with their environments. Functional diversity has the potential to link these two views of a community (Asner et al, 2017). Our main purpose here is to study patterns of functional diversity using tools commonly used to assess patterns of species taxonomic diversity with an emphasis on its scaling properties

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