Abstract

Environmental change and habitat fragmentation will affect population densities for many species. For those species that have locally adapted to persist in changed or stressful habitats, it is uncertain how density dependence will affect adaptive responses. Anurans (frogs and toads) are typically freshwater organisms, but some coastal populations of green treefrogs (Hyla cinerea) have adapted to brackish, coastal wetlands. Tadpoles from coastal populations metamorphose sooner and demonstrate faster growth rates than inland populations when reared solitarily. Although saltwater exposure has adaptively reduced the duration of the larval period for coastal populations, increases in densities during larval development typically increase time to metamorphosis and reduce rates of growth and survival. We test how combined stressors of density and salinity affect larval development between salt‐adapted (“coastal”) and nonsalt‐adapted (“inland”) populations by measuring various developmental and metamorphic phenotypes. We found that increased tadpole density strongly affected coastal and inland tadpole populations similarly. In high‐density treatments, both coastal and inland populations had reduced growth rates, greater exponential decay of growth, a smaller size at metamorphosis, took longer to reach metamorphosis, and had lower survivorship at metamorphosis. Salinity only exaggerated the effects of density on the time to reach metamorphosis and exponential decay of growth. Location of origin affected length at metamorphosis, with coastal tadpoles metamorphosing slightly longer than inland tadpoles across densities and salinities. These findings confirm that density has a strong and central influence on larval development even across divergent populations and habitat types and may mitigate the expression (and therefore detection) of locally adapted phenotypes.

Highlights

  • Habitat quality is in a state of flux worldwide due to climate change, urbanization, and other anthropogenic disturbances (Grimm et al, 2013; Pereira et al, 2010)

  • In the high-density treatment, both coastal and inland tadpoles from freshwater and saltwater treatments had approximately 25% lower survival, 2.86-fold slower growth rates, and were 66% older at metamorphosis relative to the lowdensity treatments. These findings demonstrate that the form and strength of density dependence are conserved across divergent amphibian populations. These findings are consistent with the strong negative effects of crowding on population demographics and life history strategy that have been identified in other studies (Brook & Bradshaw, 2006; McCoy, 2007; Vonesh & De la Cruz, 2002), and suggest that biotic factors have a strong and central influence in larval development across divergent populations and habitat types

  • Previous work demonstrated that coastal tadpoles have faster growth rates and metamorphosed younger than inland frogs when reared solitarily (Albecker & McCoy, 2019), but in this study, we find that differences in larval growth rates and time to metamorphosis between coastal and inland populations were eliminated

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Summary

Introduction

Habitat quality is in a state of flux worldwide due to climate change, urbanization, and other anthropogenic disturbances (Grimm et al, 2013; Pereira et al, 2010). Concomitant changes in the quality and contiguity of habitats increase the likelihood that populations of affected species will inhabit unfavorable patches that alter population growth and dispersal rates. These effects may be impactful for species that use spatially circumscribed habitat patches (e.g., ponds) or that occur in spatially structured population networks (Cushman, 2006; Keinath et al, 2017). Populations that reside in habitats that become abiotically unsuitable will typically decline to extirpation (Grimm et al, 2013; Stuart et al, 2004), unless they are able to locally adapt to the altered environmental conditions via evolutionary rescue (Bell, 2017; Gomulkiewicz & Holt, 1995; Holt, 2011). The third phase occurs as the equilibrium abundances begin to increase above the stochastic extinction thresholds as a result of an increase in the frequency of adaptive alleles in the population (Carlson, Cunningham, & Westley, 2014)

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