Anthropogenic noise is associated with telomere length and carotenoid-based coloration in free-living nestling songbirds

https://doi.org/10.1016/j.envpol.2020.114032Get rights and content

Highlights

  • Loud noise was related to short telomeres among small, but not large, brood members.

  • Variance in noise levels was associated with carotenoid-based plumage traits.

  • Carotenoid hue was positively related to telomere length.

  • Noise levels were not correlated with body mass, hatching success or fledging success.

  • Detecting deleterious effects of noise may depend on identifying sensitive groups.

Abstract

Growing evidence suggests that anthropogenic noise has deleterious effects on the behavior and physiology of free-living animals. These effects may be particularly pronounced early in life, when developmental trajectories are sensitive to stressors, yet studies investigating developmental effects of noise exposure in free-living populations remain scarce. To elucidate the effects of noise exposure during development, we examined whether noise exposure is associated with shorter telomeres, duller carotenoid-based coloration and reduced body mass in nestlings of a common urban bird, the great tit (Parus major). We also assessed how the noise environment is related to reproductive success. We obtained long-term measurements of the noise environment, over a ∼24-h period, and characterized both the amplitude (measured by LAeq, LA90, LA10, LAmax) and variance in noise levels, since more stochastic, as well as louder, noise regimes might be more likely to induce stress. In our urban population, noise levels varied substantially, with louder, but less variable, noise characteristic of areas adjacent to a highway. Noise levels were also highly repeatable, suggesting that individuals experience consistent differences in noise exposure. The amplitude of noise near nest boxes was associated with shorter telomeres among smaller, but not larger, brood members. In addition, carotenoid chroma and hue were positively associated with variance in average and maximum noise levels, and average reflectance was negatively associated with variance in background noise. Independent of noise, hue was positively related to telomere length. Nestling mass and reproductive success were unaffected by noise exposure. Results indicate that multiple dimensions of the noise environment, or factors associated with the noise environment, could affect the phenotype of developing organisms, that noise exposure, or correlated variables, might have the strongest effects on sensitive groups of individuals, and that carotenoid hue could serve as a signal of early-life telomere length.

Introduction

Anthropogenic environments present organisms with complex mosaics of highly developed and less disturbed habitat, in which novel stressors are experienced (Gaston et al., 2013; Swaddle et al., 2015; Bauerová et al., 2017). Anthropogenic noise is one such stressor that may seriously interfere with animal behaviors, with cascading effects on health status and fitness (Barber et al., 2010; Kight and Swaddle, 2011; Swaddle et al., 2015; Shannon et al., 2016; Kleist et al., 2018). In habitats with high levels of anthropogenic noise, sounds and signals no longer propagate in the same way through the environment, with implications for foraging, vigilance, and communication (Leonard and Horn, 2005, 2008; Quinn et al., 2006; Kight and Swaddle, 2011; Narango and Rodewald, 2016). Moreover, innocuous anthropogenic noises may be perceived as stressors, and consistent activation of stress responses may result in chronic stress and pathology (Blickley et al., 2012; Tennessen et al., 2014; Kleist et al., 2018).

Exposure to loud noise may affect animals across life history stages (Francis and Barber, 2013), and may have particularly strong effects early in life, when the phenotype remains sensitive to organizational effects (Metcalfe and Monaghan, 2001; Monaghan, 2008). A growing number of studies on developing animals document effects of noise exposure on phenotypic traits, including body condition, oxidative status, glucocorticoid and haptoglobin levels, and growth and metabolic rates (Potvin and MacDougall-Shackleton, 2015; Brischoux et al., 2017; Davies et al., 2017; Raap et al., 2017; Injaian et al., 2018a, b). However, the mechanisms underlying phenotypic effects of early-life stress exposure in general, and anthropogenic noise exposure in particular, remain poorly understood.

One mechanism that may link later-life fitness effects to early-life stress exposure is telomere loss. Telomeres are conserved repeats of nucleotide sequences that cap chromosomes and protect coding DNA from damage and malfunction (Monaghan and Haussmann, 2006; Haussmann et al., 2012; Monaghan, 2014). Telomeres shorten upon cellular division, with rapid rates occurring during development in association with rapid growth (Heidinger et al., 2012). Once reduced beyond a threshold length, telomere shortening triggers cellular senescence. Shorter telomeres have been related to stress exposure, increased biomolecular aging rates, and pathology (Monaghan, 2014 for review). On a related vein, faster shortening of telomeres is correlated with disease and lower survival prospects (Haussmann et al., 2005; Heidinger et al., 2012; Boonekamp et al., 2014; Wilbourn et al., 2018).

Early-life noise exposure may also affect other condition-dependent traits, such as plumage pigmentation, with potential later-life effects on mating and reproductive success. Carotenoid-based pigmentation is a common sexually-selected trait in vertebrates, which is responsible for red, yellow and orange coloration in integumentary tissues (McGraw, 2006). Carotenoids must be obtained from the diet, since they cannot be synthesized de novo by animals (Isaksson, 2009), and may serve as antioxidants, meaning that depositing carotenoids in the skin or feathers may tradeoff against combating oxidative stress (Alonso-Alvarez et al., 2004, 2008; McGraw, 2006). Thus, increased stress levels associated with noise exposure may reduce the intensity of carotenoid-based coloration. Moreover, if carotenoid-based coloration is sensitive to stressors, such as loud noise, then coloration may serve as a visual signal of associated declines in physiological state, such as telomere loss and reduced body condition. Indeed, the role of carotenoids as antioxidants is debated, but their condition-dependence is well-established, and researchers have proposed that carotenoid-based pigmentation could serve as a bioindicator trait for environmental stress exposure (Hill, 1991, 1995; Eeva et al., 1998; McGraw, 2006).

Past studies demonstrate that early-life stress associated with factors such as sibling competition (Nettle et al., 2013, 2015; Stier et al., 2015), environmental conditions at high elevations (Stier et al., 2016), and nutritional stress (Nettle et al., 2017), can accelerate telomere shortening during development. In addition, great tit (Parus major) nestlings in urban areas were found to have shorter telomeres than those in rural areas (Salmón et al., 2016). Finally, three recent studies report negative effects of anthropogenic noise exposure on the telomere length of young birds (Meillère et al., 2015; Dorado-Correa et al., 2018; Injaian et al., 2019).

However, the association between early-life noise exposure and the expression of carotenoid-based pigmentation remains unexplored. Moreover, noise environments are multidimensional, and past studies have incompletely captured this complexity since they generally rely on single types of manipulations or short-term measurements of noise amplitude, thus ignoring patterns of temporal variance in noise (Gill et al., 2015). In addition to the amplitude of noise, variance in the noise environment may also significantly affect the phenotypic traits of animals, with ramifications for community dynamics and fitness. More variable noise regimes may be more likely to activate stress responses and result in phenotypic changes that have fitness consequences, whereas organisms might more readily habituate to consistent noise regimes (Blickley et al., 2012; Gill et al., 2015; Injaian et al., 2018b).

We explored the hypothesis that exposure to anthropogenic noise negatively affects telomere length, carotenoid-based pigmentation, and body mass in great tit (Parus major) nestlings, and also assessed the potential for duller carotenoid-based pigmentation to signal telomere shortening and reduced body mass. We obtained relatively long-term measurements of the noise environment (across an ∼24-h period), comprehensively quantified the noise environment during the nestling period, and assessed whether more variable, or well as louder noise environments, have deleterious effects on nestlings. In addition, we evaluated whether phenotypic associations with the noise environment are modified by a variable that may affect susceptibility to environmental stress, nestling size rank within a brood. Nestling size rank has been shown to affect competitive dynamics (Nettle et al., 2013), and we previously found that nestling size rank was associated with shorter telomere length in nestling great tits, whereas nestling sex and mass were not (Grunst et al., 2019a). Finally, we tested the hypothesis that reproductive success is reduced in loud, or variable, noise environments.

Section snippets

Study species and site

We studied the effects of noise exposure in a nest box population of great tits on and near the University of Antwerp’s Campus Drie Eiken (CDE; Wilrijk, Belgium; 51°9′44″N, 4°24′15″E). This population contains ∼150 nest boxes and has been studied since 1997 (e.g. Van Duyse et al., 2000, 2005; Rivera-Gutierrez et al., 2010, 2012; Raap et al., 2016a, b, 2017; Vermeulen et al., 2016). Great tits are a model species for studies of ecology and evolution, and are successful urban colonizers that

Variation and repeatability in noise

LAeq, LA10, LA90, and LAmax were higher at Highway nest boxes relative to at Campus or Rekreatief nest boxes (Fig. 2.; Tables S1 and S2). Noise variables at Campus nest boxes were higher than in the Rekreatief, with the exception of LA90 (Fig. 2.; Table S2). See Tables S3 and S4 for a comparison of noise levels during the day (615–2045) and night (2100–600).

Variance in LAeq, LA10, and LAmax were higher on Campus relative to near the Highway (Fig. 3.; Tables S1 and S2). Variance in LAmax was

Discussion

Our study suggests that variation in the noise environment within the urban matrix may affect telomere loss and acquisition of carotenoid-based plumage coloration in great tit nestlings. With respect to telomere dynamics, we found shorter RTL in loud noise environments among small brood members. With respect to carotenoid-based coloration, carotenoid chroma and hue were higher in noise environments characterized by higher variance in average and maximum noise levels, and average reflectance was

Data availability

Data is available in the Dryad Digital Repository (https://doi.org/10.5061/dryad.d51c59zz9).

CRediT authorship contribution statement

Melissa L. Grunst: Conceptualization, Formal analysis, Writing - original draft. Andrea S. Grunst: Writing - review & editing, Methodology. Rianne Pinxten: Project administration, Supervision, Writing - review & editing. Marcel Eens: Project administration, Supervision, Writing - review & editing.

Declaration of competing interest

The authors declare that there are no conflicts of interest.

Acknowledgements

We thank Geert Eens, Peter Scheys, Bert Thys, and Susan Grunst for aid during fieldwork. The University of Antwerp, FWO Flanders, and European Commission (to MLG: Marie Skłodowska-Curie fellowship: 799667; to ASG, FWO grant ID: 1.2I35.17N; to RP and ME: FWO project ID: G0A3615N and G052117N) supported this study.

References (94)

  • T. Raap et al.

    Early life exposure to artificial light at night affects the physiological condition: an experimental study on the ecophysiology of free-living nestling songbirds

    Environ. Pollut.

    (2016)
  • H.F. Rivera-Gutierrez et al.

    Multiple signals for multiple messages: great tit, Parus major, song signals age and survival

    Anim. Behav.

    (2010)
  • H.F. Rivera-Gutierrez et al.

    Tuning and fading voices in songbirds: age-dependent changes in two acoustic traits across the life span

    Anim. Behav.

    (2012)
  • J.P. Swaddle et al.

    A framework to assess evolutionary responses to anthropogenic light and sound

    Trends Ecol. Evol.

    (2015)
  • E. Van Duyse et al.

    Simultaneous treatment with an aromatase inhibitor and an anti-androgen decreases the likelihood of dawn song in free-living male great tits. Parus major

    Horm. Behav.

    (2005)
  • C. Alonso-Alvarez et al.

    An experimental test of the dose-dependent effect of carotenoids and immune activation on sexual signals and antioxidant activity

    Am. Nat.

    (2004)
  • C. Alonso-Alvarez et al.

    The oxidative handicap hypothesis and the carotenoid allocation trade-off

    J. Evol. Biol.

    (2008)
  • M. Andersson et al.

    Quantifying color

  • E. Atema et al.

    GAPDH as a control gene to estimate genome copy number in great tits, with cross-amplification in blue tits

    Ardea

    (2013)
  • J.R. Barber et al.

    The costs of chronic noise exposure for terrestrial organisms

    Trends Ecol. Evol.

    (2010)
  • D. Bates et al.

    Fitting linear mixed-effects models using lme4

    J. Stat. Software

    (2015)
  • C. Biard et al.

    Growing in cities: an urban penalty for wild birds? a study of phenotypic differences between urban and rural great tit chicks (Parus major)

    Front. Ecol. Evol.

    (2017)
  • R. Bleiweiss

    Novel chromatic and structural biomarkers of diet in carotenoid-bearing plumage

    Proc. Roy. Soc. Lond. B

    (2004)
  • R. Bleiweiss

    Variation in ultraviolet reflectance by carotenoid-bearing feathers of tanagers (Thraupini: emberizinae: Passeriformes)

    Biol. J. Linn. Soc.

    (2005)
  • J.L. Blickley et al.

    Experimental chronic noise is related to elevated fecal corticosteroid metabolites in lekking male greater sage-grouse (Centrocercus urophasianus)

    PloS One

    (2012)
  • J.J. Boonekamp et al.

    Nestling telomere shortening, but not telomere length, reflects developmental stress and predicts survival in wild birds

    Proc. Roy. Soc. Lond. B

    (2014)
  • F. Brischoux et al.

    Traffic noise decreases nestlings’ metabolic rates in an urban exploiter

    J. Avian Biol.

    (2017)
  • P.A. Cotton et al.

    Chick begging strategies in relation to brood hierarchies and hatching asynchrony

    Am. Nat.

    (1999)
  • F. Criscuolo et al.

    Real-time quantitative PCR assay for measurement of avian telomeres

    J. Avian Biol.

    (2009)
  • T. Dauwe et al.

    Melanin- and carotenoid-dependent signals of great tits (Parus major) relate differently to metal pollution

    Naturwissenschaften

    (2008)
  • S. Davies et al.

    Stressful city sounds: glucocorticoid responses to experimental traffic noise are environmentally dependent

    Biol. Lett.

    (2017)
  • A.M. Dorado-Correa et al.

    Timing matters: traffic noise accelerates telomere loss rate differently across developmental stages

    Front. Zool.

    (2018)
  • H.L. Dugdale et al.

    Heritability of telomere variation: it’s all about the environment!

    Phil. Trans. R. Soc. B.

    (2018)
  • T. Eeva et al.

    Air pollution fades the plumage of the Great Tit

    Funct. Ecol.

    (1998)
  • C.D. Francis et al.

    A framework for understanding noise impacts on wildlife: an urgent conservation priority

    Front. Ecol. Environ.

    (2013)
  • I. Galván

    Plumage coloration can be perceived as a multiple condition-dependent signal by Great Tits Parus major

    Ibis

    (2010)
  • K.J. Gaston et al.

    The ecological impacts of nighttime light pollution: a mechanistic approach

    Biol. Rev.

    (2013)
  • S.A. Gill et al.

    Toward a broader characterization of anthropogenic noise and its effects on wildlife

    Behav. Ecol.

    (2015)
  • A.S. Grunst et al.

    Age-dependent relationships between multiple sexual pigments and condition in males and females

    Behav. Ecol.

    (2014)
  • A.S. Grunst et al.

    Phaeomelanin- and carotenoid-based pigmentation reflect oxidative status in two populations of the yellow warbler (Setophaga petechia)

    Behav. Ecol. Sociobiol.

    (2014)
  • M.L. Grunst et al.

    Pigment-specific relationships between feather corticosterone levels and sexual coloration

    Behav. Ecol.

    (2014)
  • M.L. Grunst et al.

    Carotenoid- but not melanin-based plumage coloration is negatively related to metal exposure and proximity to the road in an urban songbird

    Environ. Pollut.

    (2019)
  • C. Guarnaccia et al.

    A comparison between traffic noise experimental data and predictive models results

    Int. J. Mech.

    (2011)
  • W. Halfwerk et al.

    Negative impacts of traffic noise on avian reproductive success

    J. Appl. Ecol.

    (2011)
  • W. Halfwerk et al.

    Noise affects nest-box choice of 2 competing songbird species, but not their reproduction

    Behav. Ecol.

    (2016)
  • M.F. Haussmann et al.

    Longer telomeres associated with higher survival in birds

    Biol. Lett.

    (2005)
  • M.F. Haussmann et al.

    Embryonic exposure to corticosterone modifies the juvenile stress response, oxidative stress and telomere length

    Proc. Roy. Soc. Lond. B.

    (2012)
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