Abstract

Abstract The spatial distributions of biodiversity and people vary across landscapes and are critical to the delivery of ecosystem services and disservices. The high densities of people and often of birds in urban areas lead to frequent human–avian interactions, which can be positive or negative for people's well‐being. The identities of the bird species providing these services or disservices tend to be quite different; however, it is unclear how their abundance and richness covary with human population density, and hence with potential recipients of these services and disservices. We surveyed bird populations in 106 tiles (500 × 500 m) across the 174 km2 of an extended urban area in southern England. From the literature, we identified two groups of species: those associated with positive interactions for human well‐being and those that display behaviours that are negative for human well‐being. We estimated the abundance (adjusted for detection probability) and richness of each group and modelled how they covary with human population density. Aggregation of population estimates for the 35 service and nine disservice species observed revealed 593,128 (95% confidence interval: 541,817–657,046) and 225,491 (200,134–235,066) birds respectively. Across the surveyed tiles, there were 1.09 service and 0.42 disservice birds per person. There was a peaking quadratic relationship between service abundance and human population density, but a negative linear relationship between richness and human density. Conversely, there were positive linear relationships for both abundance and richness of disservice species with human density. The ratio of service to disservice birds shifted from 3.5–1 at intermediate human densities to 1–1 in more densely populated areas. Synthesis and applications. Differences in the distributions of service and disservice species, and the extremely low ratios of birds to people particularly in socioeconomically deprived areas, mean that people there have few opportunities for contact with birds, and the contact they do have is equally likely to be negative as positive for human well‐being. We recommend spatial targeting of improvements in green infrastructure, combined with the targeted provisioning of food and nesting places for service species, to promote positive interactions between birds and people.

Highlights

  • The relationship between the spatial distribution of biodiversity and of people has attracted a good deal of attention (e.g. Gaston, 2005, 2006; Luck, 2007; Sushinsky, Rhodes, Possingham, Gill, & Fuller, 2013; Wilson, Thomas, Fox, Roy, & Kunin, 2004)

  • We found that weekly household income was positively correlated with an increased ratio of cultural service to disservice species (Table 3)

  • Avian abundance and richness changed markedly with spatial variation in human population density, with those birds that provided cultural services showing distinctly different spatial relationships from those providing cultural disservices (Figure 3). These relationships are not a direct consequence of human population density per se, but instead occur indirectly as a result of factors such as urban form (Silva et al, 2015; Tratalos et al, 2007), private and public green space management (Sandström et al, 2006), disturbance (Matlack, 1993) and resource availability (e.g. Gaston et al, 2007), all of which vary along socio-­economic gradients (Davies, Fuller, Dallimer, Loram, & Gaston, 2012)

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Summary

| INTRODUCTION

The relationship between the spatial distribution of biodiversity and of people has attracted a good deal of attention (e.g. Gaston, 2005, 2006; Luck, 2007; Sushinsky, Rhodes, Possingham, Gill, & Fuller, 2013; Wilson, Thomas, Fox, Roy, & Kunin, 2004). Gaston, 2005, 2006; Luck, 2007; Sushinsky, Rhodes, Possingham, Gill, & Fuller, 2013; Wilson, Thomas, Fox, Roy, & Kunin, 2004) This has focussed on the oft-­reported finding at larger geographic scales of broad-­ positive relationships between species richness and the number of people in an area, with negative relationships only appearing at high human densities (e.g. Chown, van Rensburg, Gaston, Rodrigues, & van Jaarsveld, 2003; Evans, Greenwood, & Gaston, 2007; Pautasso, 2007; Tratalos et al, 2007). Blair, 1996; Silva et al, 2015) This suggests that negative relationships between the abundance and richness of birds providing cultural services or disservices and human densities might prevail. Unpacking the spatial relationships between different species, or groups of species, and people in this way is a critical step for informing management recommendations to promote positive interactions between people and birds in urban areas

| MATERIALS AND METHODS
Findings
| DISCUSSION
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