Abstract

Functional diversity metrics are increasingly used to augment or replace taxonomic diversity metrics to deliver more mechanistic insights into community structure and function. Metrics used to describe landscape structure and characteristics share many of the same limitations as taxonomy‐based metrics, particularly their reliance on anthropogenically defined typologies with little consideration of structure, management, or function. However, the development of alternative metrics to describe landscape characteristics has been limited. Here, we extend the functional diversity framework to characterize landscapes based on the diversity of resources available across habitats present. We then examine the influence of resource diversity and provenance on the functional diversities of native and exotic avian communities in New Zealand. Invasive species are increasingly prevalent and considered a global threat to ecosystem function, but the characteristics of and interactions between sympatric native and exotic communities remain unresolved. Understanding their comparative responses to environmental change and the mechanisms underpinning them is of growing importance in predicting community dynamics and changing ecosystem function. We use (i) matrices of resource use (species) and resource availability (habitats) and (ii) occurrence data for 62 native and 25 exotic species and 19 native and 13 exotic habitats in 2015 10 × 10 km quadrats to examine the relationship between native and exotic avian and landscape functional diversity. The numbers of species in, and functional diversities of, native and exotic communities were positively related. Each community displayed evidence of environmental filtering, but it was significantly stronger for exotic species. Less environmental filtering occurred in landscapes providing a more diverse combination of resources, with resource provenance also an influential factor. Landscape functional diversity explained a greater proportion of variance in native and exotic community characteristics than the number of habitat types present. Resource diversity and provenance should be explicitly accounted for when characterizing landscape structure and change as they offer additional mechanistic understanding of the links between environmental filtering and community structure. Manipulating resource diversity through the design and implementation of management actions could prove a powerful tool for the delivery of conservation objectives, be they to protect native species, control exotic species, or maintain ecosystem service provision.

Highlights

  • Patterns of species richness and community structure are underpinned by complex interactions between broad-­scale factors relating to the abiotic environment and historical biogeography, and local scale responses to resource availability and species interactions (Montaña, Winemiller, & Sutton, 2013)

  • We show that the number of species in, and functional diversity of, avian communities are influenced by the functional diversity of landscapes, with native and exotic species responding to both the diversity and provenance of resources available

  • While both native and exotic communities display evidence of environmental filtering, these effects are significantly stronger for exotic species

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Summary

| INTRODUCTION

Patterns of species richness and community structure are underpinned by complex interactions between broad-­scale factors relating to the abiotic environment and historical biogeography, and local scale responses to resource availability and species interactions (Montaña, Winemiller, & Sutton, 2013). Many observational studies have shown a generally positive correlation between the species richness of native and exotic communities, suggesting they respond in similar ways to extrinsic factors or environmental filters (Cleland et al, 2004; Levine, 2000) In both native and exotic communities, specialist species are likely to be more sensitive to changes in resource availability than generalists (Butler, Vickery, & Norris, 2007; Clavel, Julliard, & Devictor, 2010), while generalists should be more able to respond positively to the creation of new niches arising from environmental change and become established It has previously been shown that the quantity and quality of resources associated with foraging and reproduction can be used to delineate species’ functional space and that the availability of functional space defined in this way predicts species’ responses to land-­use change (Butler & Norris, 2013; Butler et al, 2007; Wade et al, 2013); in effect, the landscape functional diversity metric presented here reflects the composite functional space available in each quadrat

| METHODS
| DISCUSSION
FD native landscape
Findings
| CONCLUSION
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