Abstract

Male frogs call to attract females for mating and to defend territories from rival males. Female frogs of some species prefer lower-pitched calls, which indicate larger, more experienced males. Acoustic interference occurs when background noise reduces the active distance or the distance over which an acoustic signal can be detected. Birds are known to call at a higher pitch or frequency in urban noise, decreasing acoustic interference from low-frequency noise. Using Bayesian linear regression, we investigated the effect of traffic noise on the pitch of advertisement calls in two species of frogs, the southern brown tree frog (Litoria ewingii) and the common eastern froglet (Crinia signifera). We found evidence that L. ewingii calls at a higher pitch in traffic noise, with an average increase in dominant frequency of 4.1 Hz/dB of traffic noise, and a total effect size of 123 Hz. This frequency shift is smaller than that observed in birds, but is still large enough to be detected by conspecific frogs and confer a significant benefit to the caller. Mathematical modelling predicted a 24% increase in the active distance of a L. ewingii call in traffic noise with a frequency shift of this size. Crinia signifera may also call at a higher pitch in traffic noise, but more data are required to be confident of this effect. Because frog calls are innate rather than learned, the frequency shift demonstrated by L. ewingii may represent an evolutionary adaptation to noisy conditions. The phenomenon of frogs calling at a higher pitch in traffic noise could therefore constitute an intriguing trade-off between audibility and attractiveness to potential mates. © 2009 by the author(s).

Highlights

  • Roads cover a significant and increasing proportion of the earth's landscape

  • The model predicted an average decrease in snout-vent length of 0.034 mm/dB of traffic noise, which corresponds to a decrease of 0.73 mm (2.3%) in snout-vent length between sites with traffic noise levels of 47 and 68 dB(A) L10 18 hr soundpressure level (SPL), respectively (Fig. 5)

  • The lower frequency of the advertisement call of Crinia signifera was predicted to increase with traffic noise, but to a lesser extent: 1.5 Hz/dB of traffic noise

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Summary

Introduction

Roads cover a significant and increasing proportion of the earth's landscape. Many ecological effects of roads have been identified, such as loss and fragmentation of habitat; pollution of air, water, and soil; mortality of animals hit by passing vehicles; and acoustic interference caused by traffic noise (Forman et al 2003, Warren et al 2006). A variety of responses to road-traffic noise has been observed in birds, including singing at a higher pitch; singing louder, i.e., the Lombard effect; and changing diurnal singing patterns to avoid peak traffic periods (e.g., Slabbekoorn and Peet 2003, Brumm 2004, Fuller et al 2007). Sun and Narins (2005) demonstrated that motorcycle noise changed the chorusing behavior of a mixed-species community of frogs, with three species decreasing their calling rates and one species increasing its calling rate in response to the noise. The overall effect was to change the proportion of time each species spent calling, and potentially their relative breeding success (Sun and Narins 2005). Decreases in the species richness and relative abundance of frogs have been observed hundreds of meters away from a highway in eastern Ontario, Canada (Eigenbrod et al 2009)

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