Elsevier

Animal Behaviour

Volume 136, February 2018, Pages 31-39
Animal Behaviour

Experimental anthropogenic noise impacts avian parental behaviour, nestling growth and nestling oxidative stress

https://doi.org/10.1016/j.anbehav.2017.12.003Get rights and content

Highlights

  • Tree swallow nestlings and adults were exposed to traffic noise during breeding.

  • Noise-exposed nestlings had decreased body size and increased oxidative stress.

  • Noise exposure caused delayed fledging, but no difference in nestling survival.

  • Negative nestling impacts are not explained by differences in parental behaviour.

  • Our results suggest direct noise effects on nestlings.

Human-produced noise, from transport, urbanization and industry, is widespread. Studies of noise pollution show a wide range of effects on birds, such as alterations in communication, parental behaviour, physiology and reproductive success. These human-induced changes are likely to have long-term impacts, such as altered nestling physiology and survival, as well as reduced local population size. Further experimental field studies that simultaneously investigate the effects of noise exposure on avian behaviour, physiology and reproductive success are needed. Here, we used an experimental field study to investigate impacts of short-term traffic noise exposure on parental behaviour (i.e. vigilance and feeding rate), nestling body size and oxidative stress (as measured by oxidative status) and nestling fledging success in tree swallows, Tachycineta bicolor. Our results show negative consequences of traffic noise exposure, despite a relatively modest playback regime (6 h, every other day). Adults in noise-exposed territories were less vigilant earlier in the nestling period and fed at a higher rate later in the nestling period, compared to controls. However, increased feeding rate in noise-exposed nests did not compensate for noise impacts on nestlings: noise-exposed nestlings were smaller and had higher oxidative status, compared to control nestlings. Noise-exposed nestlings took longer to fledge, but we found no effect of noise on fledging success. These results highlight the potential long-term consequences of short-term noise exposure (decreased nestling size and increased oxidative status) and add to a growing body of literature, showing that noise pollution can negatively impact birds through both direct and indirect pathways.

Section snippets

General Field Methods

From April to June 2015, we monitored tree swallow activity at 30 nestboxes in Davis, CA (15 in Putah Creek Riparian Reserve and 15 in South Fork Preserve). Nestboxes were mounted to metal poles approximately 1.5 m above ground. They were checked every other day to record egg laying, incubation, hatching and fledging dates; thus, all phenological dates have an associated error of 1 day. Once incubation began, each nest was alternately assigned to the ‘noise’ (N = 15) or ‘control’ (N = 15) treatment,

Parental Behaviour

For feeding rate, we found an interaction effect between noise and nestling age, such that over time, feeding rate increased more in the noise treatment (i.e. greater slope), compared to the control (Table 1, Fig. 2a). For adult vigilance behaviour, we also found that noise interacted with nestling age and brood size (Table 1). Adults exposed to control conditions decreased vigilance with increased nestling age (Fig. 2b) and brood size, while vigilance for noise-exposed adults remained

Discussion

Overall, our results show negative impacts of traffic noise exposure during development, despite a relatively modest noise playback regime (6 h, every other day). We found that noise exposure during the nestling period altered adult behaviour, reduced nestling body size and increased nestling oxidative stress, compared to individuals exposed to control conditions. We did not find a difference in fledging success between noise and control treatments. Although our overall measure of reproductive

Acknowledgments

First, we thank the City of Davis for permitting our use of the South Fork Preserve and UC Davis for the use of Putah Creek Riparian Reserve. We thank M. Clapp, A. Krakauer, R. Logsdon, A. Perry, J. Phillips and B. Walsh for input on experimental design, as well as A. Bird, T. Hahn, C. Jones, A. Munson and A. Sih for helpful comments on the manuscript. We also thank our undergraduate field interns, without whom this research would not have been possible. Finally, we thank M. Vitousek for

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