Abstract

While shifts in organismal biology stemming from climate change are receiving increased attention, we know relatively little about how organisms respond to other forms of anthropogenic disturbance. The urban heat island (UHI) effect describes the capture of heat by built structures (e.g. asphalt), resulting in elevated urban temperatures. The UHI is a well-studied phenomenon, but only a handful of studies have investigated trait-based shifts resulting from the UHI, and even fewer have attempted to quantify the magnitude of the UHI experienced at the microclimate scale. Here, using a common urban exploiter, the Western black widow spider (Latrodectus hesperus), we show that the UHI experienced by spiders in July in their urban Phoenix, AZ refuges is 6°C hotter (33°C) than conditions in the refuges of spiders from Sonoran Desert habitat outside of Phoenix’s development (27°C). We then use this field microclimate UHI estimate to compare the development speed, mass gain and mortality of replicate siblings from 36 urban lineages reared at ‘urban’ and ‘desert’ temperatures. We show that extreme heat is slowing the growth of spiderlings and increasing mortality. In contrast, we show that development of male spiders to their penultimate moult is accelerated by 2 weeks. Lastly, in terms of behavioral shifts, UHI temperatures caused late-stage juvenile male spiders to heighten their foraging voracity and late-stage juvenile female spiders to curtail their web-building behavior. Trait-based approaches like the one presented herein help us better understand the mechanisms that lead to the explosive population growth of urban (sometimes invasive) species, possibly at the expense of urban biodiversity. Studies of organismal responses to the present day UHI can be used as informative surrogates that help us grasp the impact that projected climate change will have on biodiversity.

Highlights

  • The impact of human activity on native biodiversity is a critical question that needs to be quantified to minimize the damage we do to ecosystems [1,2]

  • Looking at the effect of this temperature difference on early spiderling development to the 3rd molt, we found that family had a highly significant effect (F33,1010 = 254, p

  • Spiderling mass at day 105 was affected by family (F33,755 = 3.28, p

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Summary

Introduction

The impact of human activity on native biodiversity is a critical question that needs to be quantified to minimize the damage we do to ecosystems [1,2]. Urbanization is a important example of HIREC, as 70% of all humans are expected to live in rapidly expanding urban centers by 2050 (United Nations, 1996). Hemipteran pests seem to thrive as urban environments heat up, developing significantly faster than they do in cooler, less disturbed environments. Despite the growing number of studies showing the profound impacts of human disturbance on arthropod populations, much work is still needed to address the fundamental question of why some arthropods thrive in urban ecosystems, and how that success may compromise urban biodiversity

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