Get 20M+ Full-Text Papers For Less Than $1.50/day. Start a 14-Day Trial for You or Your Team.

Learn More →

Links between fear of humans, stress and survival support a non-random distribution of birds among urban and rural habitats

Links between fear of humans, stress and survival support a non-random distribution of birds... www.nature.com/scientificreports OPEN Links between fear of humans, stress and survival support a non-random distribution of birds received: 24 November 2014 Accepted: 31 July 2015 among urban and rural habitats Published: 08 September 2015 1 2,3 3,4 5 Natalia Rebolo-Ifrán , Martina Carrete , Ana Sanz-Aguilar , Sol Rodríguez-Martínez , 3 6 6,† 3 Sonia Cabezas , Tracy A. Marchant , Gary R. Bortolotti & José L. Tella Urban endocrine ecology aims to understand how organisms cope with new sources of stress and maintain allostatic load to thrive in an increasingly urbanized world. Recent research efforts have yielded controversial results based on short-term measures of stress, without exploring its fitness effects. We measured feather corticosterone (CORT , reflecting the duration and amplitude of glucocorticoid secretion over several weeks) and subsequent annual survival in urban and rural burrowing owls. This species shows high individual consistency in fear of humans (i.e., flight initiation distance, FID), allowing us to hypothesize that individuals distribute among habitats according to their tolerance to human disturbance. FIDs were shorter in urban than in rural birds, but CORT levels did not differ, nor were correlated to FIDs. Survival was twice as high in urban as in rural birds and links with CORT varied between habitats: while a quadratic relationship supports stabilizing selection in urban birds, high predation rates may have masked CORT -survival relationship in rural ones. These results evidence that urban life does not constitute an additional source of stress for urban individuals, as shown by their near identical CORT values compared with rural conspecifics supporting the non-random distribution of individuals among habitats according to their behavioural phenotypes. Urbanization is one of the most prevailing and lasting forms of habitat change occurring worldwide and causing the loss of biodiversity through local extinction processes . Nevertheless, species greatly vary in their responses to these severe changes in the environment; while most are unable to occupy these new habitats (termed as urban avoiders), others are able to persist (urban adapters) or even reach higher 2,3 densities in urban than in rural areas (urban exploiters) . This interspecific variability has encouraged the study of the ecological and life history traits that allow some species to thrive in urban environ- ments. Using birds as study subjects, recent comparative works have successfully related variability in 4 5 6 environmental tolerance , life-history traits and inter-individual variability in behavior to the different responses of species to urbanization. In addition to interspecific approaches, research on how individ- uals respond to and cope with urbanization as well as on the associated physiological and behavioral Departamento de Ecología, Genética y Evolución & IEGEBA-CONICET, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Buenos Aires, Argentina. Department of Physical, Chemical and Natural Systems, Universidad Pablo de Olavide, Sevilla, Spain. Department of Conservation Biology, Estación Biológica de Doñana, CSIC Sevilla, Spain. Instituto Mediterráneo de Estudios Avanzados, IMEDEA (CSIC-UIB), Miquel Marqués 21, E-07190 Esporles, Islas Baleares, Spain. Department of Biology, Biochemistry and Pharmacy, Universidad Nacional del Sur, Bahía Blanca, Argentina. Department of Biology, University of Saskatchewan, 112 Science Place, Saskatoon, SK S7N 5E2, Canada. Deceased. Correspondence and requests for materials should be addressed to M.C. (email: martina@ebd.csic.es) Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 1 www.nature.com/scientificreports/ 7,8 mechanisms should help us to understand the observed patterns . Challenges and opportunities asso- 9 10 11 ciated with urbanization include changes in resource availability , predation risk , conspecific density , 12 6 new competitors and human disturbance , as well as other perturbations such as light pollution and 13,14 the artificial elevation of natural noise levels (e.g. ). All of these factors are potential causes of stress that may ae ff ct the fitness of individuals, and how they are able to deal with stress may explain their ability to cope with urban challenges and opportunities and, ultimately, the different responses of species to urbanization . To properly understand whether urbanization represents an opportunity or a challenge for individu- als, it is essential to understand how individuals actually perceive their environment. The endocrine sys- tem is a primary candidate for this purpose, given its role in mediating the physiological and behavioral responses of organisms to the environment. Recent efforts, within the nascent field of urban endocrine ecology, have been devoted to understanding the functional role of the hypothalamic–pituitary–adre- nal (HPA) axis in mediating responses to urbanization . Measures of glucocorticoids - mostly baseline corticosterone (CORT) and stress-induced CORT - have been used to estimate the allostatic load (i.e., the cumulative current and anticipated energetic demands on an organism) experienced by urban and rural individuals of the same species . More than 20 studies, mostly on birds, have been conducted in recent years; however, no consistent patterns have been revealed for differences in allostatic load between urban and rural conspecifics . The fact that similar proportions of studies showed higher, lower, and similar circulating CORT levels in urban vs. non-urban birds may be related to methodological issues (the short-term nature of blood CORT measurements and variability in the life stages of individuals measured), but also to the fact that challenges faced by some species in urban habitats may represent opportunities for others . Therefore, more research is needed to understand the changes in allostatic load of individuals associated with urban life, as well as their uninvestigated fitness consequences of these changes . Here, we deal with two open questions highlighted by Bonier in her recent review: 1) Do hormo- nal responses regulate behavioral adaptation to urban environments, such as reduced flight initiation distances (FID)? and 2) Are hormone-fitness relationships ae ff cted by urbanization? We approach these questions in the light that modulated sensitivity of the HPA axis may play a central role in allowing urban birds to maintain foraging, breeding, and other essential behaviors in the face of frequent expo- 7 6 sure to human disturbance . Studying a contemporary process of urbanization, Carrete & Tella found that inter-individual variability in the fear of humans (experimentally measured as FID of individuals when approached by a human) could explain why some species thrive successfully in urban habitats. We focus here on one of these species, the burrowing owl (Athene cunicularia), an urban exploiter which 6,11 shows higher abundance and density in urban than in nearby rural habitats . Burrowing owls showed high within-individual consistencies in FID throughout their lifespan in both urban and rural habitats (repeatability > 0.90 ), suggesting that the lower FID of urban birds does not arise from habituation but 6,16 from the selection of individuals able to cope with constant human disturbance . Thus, if individual’s behavioural phenotypes match well with the differential levels of human disturbance in the areas where they settle to breed -as posit by the human disturbance habitat selection and the habitat-matching dispersal hypotheses, urban birds should not perceive their habitat as more stressful than that of rural ones. We therefore predict no differences in the allostatic load between urban and rural individuals nor a relationship with their FIDs. The majority of studies utilizing levels of CORT as indicator of the allostatic load of individuals have been conducted using instantaneous blood samples, which can be particularly informative when characterizing the functioning of the HPA response and understanding an individual’s physiological state at the instant of sampling. However, the time frame of such samples is limited, so integrated measures of glucocorticoids have been developed and applied to ecological contexts , nota- bly CORT in feathers (CORT ). This biomarker, whose time frame is significantly longer than that of blood, has been related to diverse ecological factors, suggesting that it integrates CORT secretion in general, globally expressing the response of individuals to different sources of environmental variation . Importantly, CORT levels increase in feathers when individuals are exposed to long-term stressors , as could be expected if urban life actually represents a sustained source of stress for urban individuals. It has been also suggested that CORT could be used as a metric to study carry-over effects . In fact, two 23,24 recent studies showed links between CORT and survival in two bird species . er Th efore, we examined the relationships between CORT levels and subsequent survival, predicting a negative relationship according to the corticosterone-fitness hypothesis independent of the habitat in the area where they set- tled. For these purposes, we individually marked a number of urban and rural breeding owls, measured their FID and CORT , and closely monitored them for their survival until the next breeding season. Our results fully support our first predictions, but also show complex relationships between CORT and sur- vival that may be related to ecological constraints (i.e, predation pressure) other than human disturbance. Results Fear of humans and stress. According to previous studies, urban burrowing owls showed significantly shorter FIDs than their rural conspecifics (urban birds: mean = 18.29 m, SE = 1.05, n = 72; rural birds: mean = 54.51 m, SE = 3.83, n = 49), even while controlling for the slightly shorter -although not statis- tically significant- FIDs in males (mean = 31.19 m, SE = 3.49, n = 56) than in females (mean = 34.48 m, SE = 3.12, n = 65) (Table  1). However, this closer interaction with humans does not suppose an Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 2 www.nature.com/scientificreports/ Dependent Independent Independent variable variables F df P Dependent variable variables F df P (log)FID Habitat 115.20 1, 118 0.0001 (log)CORT Habitat 0.34 1, 116 0.5591 Sex 1.45 1, 118 0.2311 Sex 3.62 1, 116 0.0594 Year 0.28 1, 116 0.5953 FID 0.38 1, 116 0.5398 2 2 Adjusted-R : 0.49 Adjusted-R : 0.003 Table 1. Models obtained to compare FID and feather CORT (CORT ) levels between urban and rural birds (n = 121 individuals). Figure 1. Relationships between feather CORT (CORT ) and FID of urban (grey dots) and rural (white dots) adult burrowing owls. In the external margins of the plot, we included the boxplots for FID and CORT of rural (n = 49) and urban (n = 72) birds. extra-source of stress, as urban birds showed nearly identical CORT concentrations than rural ones (urban birds: mean = 9.61 pg/mm, SE = 0.38, n = 72; rural birds: mean = 9.57 pg/mm, SE = 0.33, n = 49, Fig.  1). CORT did not differ between habitat types even when controlling for year and the slightly and marginally significant lower CORT concentrations found in males (mean = 9.01 pg/mm, SE = 0.29, n = 56) than in females (mean = 10.10 pg/mm, SE = 0.40, n = 65; Table  1). Moreover, CORT concen- trations were not related to individual FIDs, either when considering all birds together (Table  1) or when taking into account potential differences between habitats (interaction habitat *FID: F = 0.05, 1,115 p = 0.82; Fig.  1). Stress and survival. e g Th oodness-of-fit of the general model fitted the data adequately ( χ = 2, df = 5, p = 0.85). We started model selection by testing the effects of time and habitat type on resighting (p) and survival (φ ) probabilities (Table 2). The best model (Model 1, Table 2) included a temporal effect on resighting probability, which was relatively high (p = 0.81, 95% CI = 0.68–0.89) and did not vary mean between habitats. However, survival differed between habitats, being more than twice as high in urban (φ = 0.59) as in rural (φ = 0.25) individuals (Fig. 2). Models including additional temporal effects on sur - vival had Δ AIC c > 2 and much lower Akaike weights (Table 2). Consequently, we selected the structure of this model to test for CORT effects on subsequent annual survival. e eff Th ect of CORT on survival was retained in model selection (Table  3). The best supported model in terms of AICc (Model 1a, Table  3) showed that survival decreased with CORT levels in rural birds (logit φ = 1.851 (CI: −1.846–5-548)–0.382 (CI: − 0.815–0.052)*CORT ) while it exhibited a rural f quadratic relationship in urban ones (logit φ = − 4.547 (CI: − 8.424–− 0.671) + 0.917 (CI: 0.189– urban 1.644)*CORT –0.034 (CI: − 0.065–− 0.004)*CORT ). However, the confidence interval for the beta esti - f f mate corresponding to the linear slope of rural birds included zero, indicating a non-significant effect. In fact, a more parsimonious model without this effect was equivalent in terms of AICc ( Δ AIC c = 1.90, Table 3), indicating that CORT had a non-detectable effect on the survival of rural birds but a significant quadratic relationship in urban owls (logit φ = − 4.646 (CI: − 8.493–− 0.798) + 0.927 (CI: 0.205– urban 1.650)*CORT –0.034 (CI: −0.065–− 0.004)*CORT ). Accordingly, ∆AICc between models 1b and 1i (no f f CORT effect on survival of rural and urban birds) was 5.38 (Table  3), supporting the CORT -survival f f relationship in urban birds (Fig. 3). Therefore, in addition to habitat differences, CORT had a significant effect on the survival of urban birds, with probabilities of survival being higher at intermediate CORT levels (Fig. 3). Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 3 www.nature.com/scientificreports/ Model Model structure AICc ΔAICc w NP deviance 1 φ (habitat) p (time) 409.229 0.00 0.528 8 392.702 2 φ (habitat × time) p (time) 411.303 2.07 0.187 17 374.985 3 φ (habitat + time) p (time) 412.345 3.12 0.111 13 384.987 φ (habitat × time) p 4 412.794 3.56 0.089 18 374.193 (habitat + time) φ (habitat × time) p 5 414.613 5.38 0.036 14 385.040 (habitat) 6 φ (habitat × time) p (.) 414.754 5.52 0.033 13 387.396 7 φ (habitat × time) p (time) 416.156 6.93 0.017 20 372.938 8 φ (.) p (time) 433.641 24.41 0.000 7 419.232 9 φ (t) p (time) 434.354 25.12 0.000 11 411.376 Table 2. Modeling survival (φ) and recapture probabilities (p) of 183 adult burrowing owls. AICc: Akaike’s information criterion adjusted for effective sample size, ΔAICc: AICc difference between the current model and that with the lowest AICc value; w : Akaike’s weight, NP: number of estimable parameters, deviance: relative deviance. Model notation: “+”: parallel variation, additive effect; “x”: interaction; “.” = constant (i.e. no effects considered); “habitat” = different parameters for urban and rural birds; “time” = between year differences. Figure 2. Estimates of annual survival (mean and 95% CI) obtained for 109 urban and 74 rural adult burrowing owls. Model φ φ AICc ΔAICc w NP deviance urban rural i 1a CORT + CORT CORT 403.89 0.00 0.39 13 376.54 f f f 1b CORT + CORT — 405.79 1.90 0.15 12 380.63 f f 2 2 1c CORT + CORT CORT + CORT 406.07 2.18 0.13 14 376.50 f f f f 1d CORT CORT 406.31 2.41 0.12 12 381.15 f f 1e — CORT 406.95 3.06 0.08 11 383.98 1f CORT — 408.33 4.43 0.04 11 385.35 1g CORT CORT + CORT 408.48 4.58 0.04 13 381.12 f f f 1h — fCORT+ fCORT 409.12 5.23 0.03 12 383.96 1i — — 409.28 5.38 0.03 10 388.46 Table 3. Modeling feather CORT (CORT ) ee ff cts on subsequent annual survival ( φ) of urban (n = 109) and rural (n = 74) adult burrowing owls. In all models, resighting probabilities (p) varied over time and survival aer fir ft st year of CORT sampling was considered to be constant over time and different for rural and urban birds. Model notation: “-”: constant (i.e. no CORT effect); CORT : linear CORT effect; f f f CORT + CORT : quadratic CORT effect. All other notations as in Table 1. f f f Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 4 www.nature.com/scientificreports/ Figure 3. Distribution of feather CORT (CORT ) concentrations measured in urban (n = 109, black bars) and rural (n = 74, grey bars) burrowing owls. Overlapped, we show the relationship between CORT and the estimated immediate survival of urban owls (black line, 95% CI depicted as dashed lines). There was not a significant relationship for rural individuals (see Results). Discussion Human disturbance and stress in urban and rural birds. With the accelerating pace of anthro- pogenic global change, understanding how organisms cope with these changes is an urgent task. Traditionally, the most adverse human activities for fauna have been related to natural landscape mod- ification. However, a growing number of studies are now showing that human presence per se can be 7,21 important in modifying animal activities and distributions through behavioral changes . Indeed, it has been proposed that the ability of certain species to thrive in urban habitats, the most populated habitats worldwide, can be attributed to their high interindividual variability in fear of humans, such that only tame individuals (i.e., those with the lowest fear of humans compared to their conspecifics) can success - 6,15,17 fully occupy these areas . Our result showing shorter FIDs in urban than in rural burrowing owls are 15,17 thus not novel, but in line with previous studies on this species and with others showing the same pattern of higher tolerance towards humans in urban individuals in a variety of birds species . Although this pattern was considered a result of habituation to human disturbance in the absence of individu- al-based studies , the long-term monitoring of individually marked burrowing owls demonstrated that FID remains largely unchanged across their lifespan , thus supporting the idea that behavioral differ - 6,16,27 ences between urban and rural conspecifics are more likely a consequence of selective processes . Urbanized areas may be selecting for individuals with coping styles able to deal with urban challenges, 27–31 human presence included . Coping styles (so called behavioral syndromes or personalities) are rel- atively stable combinations of behavioral and physiological traits that confer differential fitness con - sequences under divergent environmental conditions . Different studies have demonstrated a genetic basis for the expression of behavioral and physiological components of individual coping styles , such that selective pressures associated with urban life can have long-lasting ecological but also evolutionary consequences. In fact, a recent study on urban and rural dark-eyed juncos (Junco hyemalis) supports the role of selection instead of drift or founder effects to explain the lower FID shown by urban birds . We aimed here to determine whether hormonal responses of individuals to stress are related to their tolerance to human disturbance, to deepen our understanding of the potential selection of individuals able to cope with urban habitats. Attending to the above arguments, we should not expect a relationship between FID and CORT nor differences in CORT between urban and rural individuals. If individuals f f choose to breed in urban habitats or in rural sites with different levels of human disturbance according to their tolerance to humans , all individuals should perceive similar amounts of stress in regards to human disturbance. Our results fully support these predictions. However, they may also be interpreted as another piece to the puzzling results obtained to date, which cannot discern a clear pattern of differ - 7,34 ences in allostatic load between urban and rural birds . Remarkably, two experimental studies found that urban birds raised in a common garden showed attenuated CORT responses to handling stress when 27,28 compared to their wildland counterparts , supporting their higher tolerance to human disturbance. On the other hand, the accumulation of apparently contradictory results, even obtained from a single species, might at least partially stem from methodological issues and variability in sources of stress among species . Regarding methodological issues, both baseline and stress-induced CORT concentra- tions are short-term measures of HPA activity that have oen ft been obtained at different life stages of the studied species . Studies conducted to date have shown no consistent patterns in the within-individual repeatability of these hormonal traits even when measured within a single life history stage and habitat, 22,35,36 37 suggesting that they are rather plastic traits . This makes their biological interpretation difficult , including the assessment of differences in allostatic load between urban and rural individuals . In our Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 5 www.nature.com/scientificreports/ case, CORT deposited in feathers reflects the duration and amplitude of glucocorticoid secretion during 20,21,38 the entire period of feather growth within a single life-history stage, which could span several weeks (see Methods). Both the duration and amplitude of HPA activity are important determinants of CORT , so direct correlations between plasma and feather CORT may not always be expected, especially if the elevation in plasma CORT is relatively modest and brief . However, if urban life actually represents a sustained source of stress for individuals, it is not expected to be a short-live but a long-live stressor which should promote sustained plasma CORT levels for a period long enough to elevate CORT . Estimates of within-individual consistency in CORT across years are low , indicating it is a plastic hormonal trait that reflects variations in log-term sources of stress and that it could be used to study 22 23,24 carry-over effects . In fact, CORT correlates with subsequent annual survival (see below), thus sug- gesting that it reflects a relatively long-term exposure of individuals to all of the sources of stress that they encounter, and that it could be a more reliable tool for assessing the effects of urbanization on allostatic load than short-term blood CORT measurements. Regarding variability in sources of stress, Bonier compiled a variety of biotic and abiotic factors associated with urbanization that could lead to both positive and negative changes in allostatic load. Among them, there are no apparent changes in temperature and food availability that could ae ff ct urban owls. Low food availability may cause chronic stress in animals . However, the trophic niche, as assessed through stable isotopes, is nearly identical between urban and rural burrowing owls, and there is a high prey availability in both kinds of habitats (Carrete & Tella, unpublished data). Artificial light should not disturb owls, and in any case may facilitate their foraging at night. Preliminary results suggest that exposure to parasites and diseases neither differ between urban and rural burrowing owls (Carrete & Tella, unpublished data). In addition, the increased breeding densities in urban habitats is not expected to increase allostatic load, since this is a non-territorial species and its mating behavior has been shown to be unae ff cted by these high densities . Interspecific competition is not expected to increase; the only ecologically similar species preying on the same range of prey (the American falcon Falco sparverius) is much scarcer than burrowing owls both in urban and rural areas . Therefore, the only factors that appar - ently differ are a higher human disturbance and much lower predation risk (see below) in urban than in rural areas. Attending to these sources of stress, an explanation alternative to the selection of individuals related to their fear of humans may explain the identical concentrations of CORT in urban and rural owls. That is, our results may reflect a replacement of stressful factors, i.e. predators in rural habitats by humans in urban ones. e Th frequency of exposure to these stressors is however very different: most pre- dation events of adult burrowing owls occur within their burrow nests (authors’ unpub. data), and thus their few encounters with predators would not cause chronic stress (or “sustained physiological stress ”) but rather their death; meanwhile, urban birds are constantly facing human presence. Demographic experiments have demonstrated that sustained exposure to predators (or their cues) can have associ- ated physiological stress effects (eg, elevation of glucocorticoid levels) with long-term consequences on birth and survival in free-living animals . Therefore, it seems unreasonable to think that successful city dwellers can live with the permanent activation of their HPA axis due to daily encounters with humans. u Th s, it is more likely that a permanent perturbation factor like human disturbance would be selecting 6,17 for those individuals that are able to better tolerate humans . Stress and survival. Studies examining relationships between glucocorticoid levels and survival in 42,43 vertebrates, including birds (e.g. ), showed no less puzzling results than the assessment of variability in allostatic load between rural and urban birds, oer ff ing controversial support to the corticostrone-fitness 25,37 hypothesis . The variety of responses found between baseline and stress-induced CORT and survival in birds could also be at least partially related to the short-term nature of these hormonal traits and to 25,37 the variability of the life history stages at which they were measured . Two recent studies measuring CORT as a longer term, integrated measure of avian stress physiology have found negative relation- ships with overwinter survival in two avian species (house sparrows Passer domesticus and north- ern common eiders Somateria mollissima borealis ). To our knowledge, ours is the first study assessing differences in CORT-survival relationships between urban and rural individuals, showing contrasting patterns. CORT showed a quadratic relationship with survival in urban owls, a pattern previously found for baseline CORT in cliff swallows Petrochelidon pyrrhonota that indicates stabilizing rather than directional mortality selection favoring intermediate CORT levels . Although few studies examined non-linear CORT-survival relationships, stabilizing selection makes sense since acute short-term CORT secretion mediates rapid behavioural and physiological modifications that benefit immediate survival, while prolonged stressful situations lead to a long-term allostatic overload that may have detrimental 25,41 consequences compromising survival . Survival probabilities of rural owls were less than half that of urban ones, and contrary to the lat- ter they were unrelated to their CORT levels. We have strong evidence to suggest that these different patterns result from differences in predation pressure. A lower predation risk is generalized for urban birds , and high predation rates in rural habitats explain differences in breeding densities and the main life-history parameters (breeding success, dispersal) in our study species (Rebolo-Ifrán et al., in prep; authors unpublish data). As breeding burrowing owls have few opportunities to escape from predators entering their deep burrow nests (authors’ unpubl. data), the high rates of predation-caused mortality should be random with respect to their CORT levels and could mask any relationship between CORT f f Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 6 www.nature.com/scientificreports/ and survival in rural owls. Our contrasting results comparing urban and rural birds illustrate how differ - ent CORT-survival patterns can be obtained within a single species, population, and life-history stage , and how difficult their interpretation can be in the absence of a sufficient knowledge of the ecological constraints modelling the demography of the studied species. Conclusions Our results suggest that urban life does not increase the physiological stress experienced by individuals, supporting the hypothesis that individuals select breeding habitats according to their tolerance to human 6,15 disturbance as a major challenge faced in urban habitats . This scenario is in agreement with the adaptive or matching-habitat dispersal hypothesis, which implies a non-random dispersal of individuals 18 44 resulting in a match between phenotype and environment , a hypothesis thus far scarcely explored . Moreover, the higher survival rates (this study) and breeding success (Rebolo-Ifrán et al., in prep) of urban birds have surely contributed to the higher breeding densities currently found in the urban habi- tat , that together with the high philopatry and the non-random dispersal of individuals between urban and rural habitats generates a genetic structuring of the population (Carrete et al. in prep.). Much more research is however needed before we can generalize these results to the many other species that are successfully thriving in urbanized habitats. Material and Methods Study system and field procedures. We conducted our study in a ca. 5,400 km area of natu- ral grasslands, pastures, cereal crops and urban areas surrounding the city of Bahía Blanca (Buenos Aires, Argentina), where burrowing owls nest in burrows excavated by the owls themselves or by mam- 11,15,17 mals . We surveyed this population between 2006 and 2013, monitoring a total of 1,501 different nests. We defined as urban nests (n = 545) those excavated by owls in private and public gardens, spaces among houses, curbs of streets and along large avenues in the city. Nests are usually within 10–100 m of inhabited buildings. Rural nests (n = 956) were located in the surrounding expanses of natural grasslands and pastures devoted to wide-ranging livestock and low-intensive cereal crops, where human presence and activities are minimal . There is no clear habitat interface between urban and rural habitats, since urbanized areas are immediately surrounded by rural ones. For this study, we captured 183 different breeding adults in 2006, 2008 and 2009 (74 in rural and 109 in urban nests) during the chick-rearing period (late November to early January). Birds were marked with plastic rings with a unique alphanumeric code that could be read at a distance using a telescope. Blood samples (0.1 ml) were collected for molecular sexing (see ), while one external tail feather was plucked for CORT determination (see below). Resightings of marked birds were obtained during inten- sive population monitoring from 2007 to 2012, surveying all known breeding sites as well as areas of suitable habitat not previously occupied to detect new breeding sites. We were able to experimentally measure flight initiation distance (FID, i.e. the distance at which individuals flee when approached by a human), of 121 out of the 183 individuals sampled for CORT , 15,17 following the standard protocol used in previous studies . Briefly, all FIDs were also measured during the chick-rearing period, by walking towards focal individuals following a direct trajectory, with no obstacles blocking the bird and the observer and at a constant speed of 0.5 m/s. FIDs were measured in fine weather, avoiding the hottest hours of the day, and rainy or windy days. All tested owls were undisturbed and resting close to or at the entrance of their nests during daytime. The distance between the observer and the flushing bird was measured using a laser telemeter (range: 10–1300 m) or counting paces for distances of less than 10 m. We used for analyses both single and average values of FID (when more than one measure was obtained from a single individual in the same or different years), given that this behavior is highly repeatable within breeding seasons (r = 0.84–0.92) and across the lifespan 15,17 (r = 0.90–0.96) of burrowing owls . Feather corticosterone. We estimated the stress experienced by birds by measuring CORT con- centration in feathers following Bortolotti et al. . Contrary to blood measures, CORT reflects the HPA activity of an individual within a time frame of days or weeks (depending on the moult speed of the studied species). Thus, this hormonal trait integrates not only the intensity of the physiological response but also how long CORT is elevated within the bloodstream, and the frequency of exposure to stress- 20,21,38 ors . In the burrowing owl, no information is available about the growth rate of feathers and growth bars are not conspicuous as in other species (authors’ unpublished data). Estimates for other owls show that flight feathers can growth 1.9–3.1 mm/day , so a typical 95 mm tail feather from a burrowing owl may be fully grown aer c ft a. 30–50 days. Although this may not be an accurate estimation, CORT can reflect the stress experienced by individuals during a time frame of at least 3–4 weeks corresponding to the pre-breeding moult period of adult birds. Burrowing owls are sedentary and breeders stay in their territories along the year in the study area (author’s unpubl. data). Therefore, the studied individuals were potentially exposed to the same stressors associated to their territories across the annual cycle. To quantify CORT , we first measured the length of each feather aer r ft emoving the calamus . Then we cut the feather vanes into small pieces (<5 mm) with scissors and placed in a glass vial with 10 mL 20,38 of methanol (HPLC grade, VWR International, Mississauga, ON) for CORT extraction .Vials were placed in a sonicating water bath at room temperature for 30 min, followed by incubation at 50 °C Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 7 www.nature.com/scientificreports/ overnight in a shaking water bath. Using vacuum filtration, the methanol containing the hormones was separated from the feathers. Vials with the methanol extract were placed open in a 50 °C water bath in a fume hood under air until they were completely dry. When the evaporation of the samples was complete, the extract residues were reconstituted in 600 mL of phosphate buffer system (0.05 M, pH 7.6) and fro- zen at − 20 °C until CORT measurement by radioimmunoassay. We assessed the extraction efficiency by including feather samples spiked with a small amount (c. 4000 dpm) of 3H-corticosterone. The coefficient of variation for five different batches ranges from 5.31 (within essay) to 8.32 (between essays). Greater than 92% of the radioactivity was recoverable in the reconstituted samples. CORT values are expressed 20,38 as a function of feather length (pg mm-1) following Bortolotti et al. . Statistical analysis. We used generalized linear models (GLM, using the identity link function and normal error distribution) to assess if FID (log-transformed) differed between our sampled rural and urban breeding owls, while controlling for sex, a result that was previously found using different data- 6,15,17 sets of individuals . We were able to sample both members of the breeding pair in only 25% of the territories, so we could not control for a potential territory effect fitted as a random term. However, a previous study conducted in the same owl population, using larger sample sizes, showed just a slight effect of territory and results were nearly identical when it was not fitted as a random term . The year(s) when FID was measured for each individual was not controlled for given the high consistency in this behavioural trait across the lifespan of individuals (see above). The same GLM structure was then used for assessing differences in CORT (log-transformed) between urban and rural birds and its relationship with FID, while controlling for potential sources of variability (sex and sampling year). In this case, we controlled for sampling year since CORT of individuals may vary across years due to yearly variations in the kind and intensity of sources of stress . All models were fitted using R 3.0.3. Survival analysis. We analyzed encounter histories of the 183 individuals sampled in 2006, 2008 and 2009 and resighted (or not) from 2007 to 2012 to test for habitat and CORT effects on survival. This monitoring period is longer than the average lifespan of adult burrowing owls , and no individuals changed breeding habitat (urban or rural) during the study. Survival (φ ) and resighting probabilities (p) were estimated simultaneously by maximum-likelihood procedures and models were built using the program MARK . We conducted capture-recapture analyses in two steps: first we tested for temporal and habitat effects on both resighting and survival probabilities; then, we selected the best structure of the parameters to specifically test for CORT effects on subsequent survival probabilities (i.e, only first year survival aer s ft ampling was modeled as a function of the CORT covariate, including linear and quadratic effects). Exploratory analyses did not detect a sex effect on survival or resighting probabilities, nor was there a strong sex effect on CORT (see results), so we did not include sex in final models to avoid overparameterization. The goodness-of-fit of the general Cormack-Jolly-Seber model by group (i.e, urban and rural birds; φ p ) was assessed using program U-CARE 2.3.2 . Model selection was based t*g t*g on Akaike’s Information Criterion adjusted for the effective sample size (AICc ). Models differing less than 2 AICc points were considered equivalent . We also calculated for each model the Akaike weight (w), as an index of its relative plausibility . Ethic statements. Capture, banding and FID measures of Burrowing owls were conducted under permits and following the protocols approved by the Argentinean wildlife agency (22500-4102/09), the Ethic Committee of CSIC (CEBA-EBD-11-28), and the owners of private properties, in accordance with the approved guidelines. References 1. McKinney, M. L. Urbanization as a major cause of biotic homogenization. Biol. Conserv. 127, 247–260 (2006). 2. Kark, S., Iwaniuk, A., Schalimtzek, A. & Banker, E. Living in the city: can anyone become an urban exploiter? J. Biogeogr. 34, 638–651 (2007). 3. McKinney, M. L. Urbanization, Biodiversity, and Conservation. BioScience 52, 883–890 (2002). 4. Bonier, F., Martin, P. R. & Wingfield, J. C. Urban birds have broader environmental tolerance. Biol. Lett. 3, 670–3 (2007). 5. Sol, D., González-Lagos, C., Moreira, D. & Maspons, J. Urbanisation tolerance and the loss of avian diversity. Ecol. Lett. 17, 942–950 (2014). 6. Carrete, M. & Tella, J. L. Inter-individual variability in fear of humans and relative brain size of the species are related to contemporary urban invasion in birds. PLoS One 6, e18859 (2011). 7. Bonier, F. Hormones in the city: endocrine ecology of urban birds. Horm. Behav. 61, 763–772 (2012). 8. Sol, D., Lapiedra, O. & González-Lagos, C. Behavioural adjustments for a life in the city. Anim. Behav. 85, 1101–1112 (2013). 9. Chace, J. F. & Walsh, J. J. Urban effects on native avifauna: a review. Lands. Urban Plan . 74, 46–69 (2006). 10. Díaz, M. et al. The geography of fear: a latitudinal gradient in anti-predator escape distances of birds across Europe. PloS one 8, e64634 (2013). 11. Rodriguez-Martínez, S., Carrete, M., Roques, S., Rebolo-Ifrán, N. & Tella, J. L. High urban breeding densities do not disrupt genetic monogamy in a bird species. PLoS One 9, e91314 (2014). 12. Hernández-Brito, D., Carrete, M., Popa-Lisseanu, A., Ibáñez, C. & Tella, J. L. Crowding in the city: losing and winning competitors of an invasive bird. PLoS One 9, e100593 (2014). 13. Slabbekoorn, H. & Peet, M. Birds sing at higher pitch in urban noise. Nature 424, 26 (2003). 14. Da Silva, A., Samplonius, J. M., Schlicht, E., Valcu, M. & Kempenaers, B. Artificial night lighting rather than traffic noise ae ff cts the daily timing of dawn and dusk singing in common European songbirds. Behav. Ecol. 25, 1037–1047 (2014). Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 8 www.nature.com/scientificreports/ 15. Carrete, M. & Tella, J. L. High individual consistency in fear of humans throughout the adult lifespan of rural and urban burrowing owls. Sci. Rep. 3, 3524 (2013). 16. Møller, A. P. Behavioural and ecological predictors of urbanization. In Avian urban ecology (ed. D. Gil & H. Brumm), pp. 54–68. Oxford: Oxford University Press (2014). 17. Carrete, M. & Tella, J. L. Individual consistency in flight initiation distances in burrowing owls: a new hypothesis on disturbance- induced habitat selection. Biol. Lett. 6, 167–70 (2010). 18. Edelaar, P. & Bolnick, D. I. Non-random gene flow: an underappreciated force in evolution and ecology. Trends Ecol. Evol. 27, 659–665 (2012). 19. Sheriff, M. J., Dantzer, B., Delehanty, B., Palme, R. & Boonstra, R. Measuring stress in wildlife: techniques for quantifying glucocorticoids. Oecologia 166, 869–887 (2011). 20. Bortolotti, G. R., Marchant, T. A., Blas, J. & German, T. Corticosterone in feathers is a long-term, integrated measure of avian stress physiology. Funct. Ecol. 22, 494–500 (2008). 21. Fairhurst, G. D., Marchant, T., Soos, C., Machin, K. & Clark, R. G. Experimental relationships between levels of corticosterone in plasma and feathers in a free-living bird. J. Exp. Biol. 216, 4071–4081 (2013). 22. Legagneux, P. et al. Does Feather Corticosterone Reflect Individual Quality or External Stress in Arctic-Nesting Migratory Birds? Plos One 8, e82644 (2013). 23. Koren, L. et al. Non-breeding feather concentrations of testosterone, corticosterone and cortisol are associated with subsequent survival in wild house sparrows. Proc. R. Soc. B Biol. Sci. 279, 1560–1566 (2012). 24. Harms, N. J. et al. Feather corticosterone reveals effect of moulting conditions in the autumn on subsequent reproductive output and survival in an Arctic migratory bird. Proc. R. Soc. B Biol. Sci. 282, 20142085 (2015). 25. Bonier, F., Martin, P. R., Moore, I. T. & Wingfield, J. C. Do baseline glucocorticoids predict fitness? Trends Ecol. Evol. 24, 634–42 (2009). 26. Blumstein, D. Attention, habituation, and antipredator behaviour: implications for urban birds. In Avian urban ecology (ed. D. Gil & H. Brumm), pp. 41–53. Oxford: Oxford University Press (2014). 27. Atwell, J. W. et al. Boldness behavior and stress physiology in a novel urban environment suggest rapid correlated evolutionary adaptation. Behav. Ecol. 23, 960–969 (2012). 28. Partecke, J., Schwabl, I. & Gwinner, E. Stress and the city: urbanization and its effects on the stress physiology in European blackbirds. Ecology 87, 1945–52 (2006). 29. Evans, J., Boudreau, K. & Hyman, J. Behavioural syndromes in urban and rural populations of song sparrows. Ethology 116, 588–595 (2010). 30. Bókony, V., Kulcsár, A., Tóth, Z. & Liker, A. Personality traits and behavioral syndromes in differently urbanized populations of house sparrows (Passer domesticus). PLoS One 7, e36639 (2012). 31. Miranda, A. C., Schielzeth, H., Sonntag, T. & Partecke, J. Urbanization and its effects on personality traits: a result of microevolution or phenotypic plasticity? Glob. Chang. Biol. 19, 2634–2644 (2013). 32. Coppens, C. M., de Boer, S. F. & Koolhaas, J. M. Coping styles and behavioural flexibility: towards underlying mechanisms. Philos. Trans. R. Soc. Lond. B. Biol. Sci. 365, 4021–8 (2010). 33. Øverli, Ø. et al. Evolutionary background for stress-coping styles: relationships between physiological, behavioral, and cognitive traits in non-mammalian vertebrates. Neurosci. Biobehav. Rev. 31, 396–412 (2007). 34. Partecke, J. Mechanisms of phenotypic responses following colonization of urban areas: from plastic to genetic adaptation. In Avian urban ecology (ed. D. Gil & H. Brumm), pp. 131–142. Oxford: Oxford University Press (2014). 35. Ouyang, J. Q., Hau, M. & Bonier, F. Within seasons and among years: when are 840 corticosterone levels repeatable? Horm. Behav. 60, 559–564 (2011). 36. Baugh, A. T., van Oers, K., Dingemanse, N. J. & Hau, M. Baseline and stress-induced glucocorticoid concentrations are not repeatable but covary within individual great tits (Parus major). Gen. Comp. Endocrinol. 208, 154–163 (2014). 37. Crespi, E. J., Williams, T. D., Jessop, T. S. & Delehanty, B. Life history and the ecology of stress: how do glucocorticoid hormones influence life-history variation in animals? Funct. Ecol. 27, 93–106 (2013). 38. Bortolotti, G. R., Marchant, T. A., Blas, J. & Cabezas, S. Tracking stress: localization, deposition and stability of corticosterone in feathers. J. Exp. Biol. 212, 1477–1482 (2009). 39. Clinchy, M., Zanette, L., Boonstra, R., Wingfield, J. C. & Smith, J. N. Balancing food and predator pressure induces chronic stress in songbirds. Proc. R. Soc. B Biol. Sci. 271, 2473–2479 (2004). 40. Clinchy, M., Sheriff, M. J. & Zanette, L. Y. Predator-induced stress and the ecology of fear. Funct. Ecol. 27, 56–65 (2013). 41. Wingfield, J. C. e Th comparative biology of environmental stress: behavioural endocrinology and variation in ability to cope with novel, changing environments. Anim. Behav. 85, 1127–1133 (2013). 42. Brown, C. R., Brown, M. B., Raouf, S. A., Smith, L. C. & Wingfield, J. C. Effects of endogenous steroid hormone levels on annual survival in cliff swallows. Ecology 86, 1034–1046 (2005). 43. Blas, J., Bortolotti, G. R., Tella, J. L., Baos, R. & Marchant, T. A. Stress response during development predicts fitness in a wild, long-lived vertebrate. Proc. Nat. Acad. Sci. USA 104, 8880–8884 (2007). 44. Camacho, C., Canal, D. & Potti, J. Nonrandom dispersal drives phenotypic divergence within a bird population. Ecol. Evol. 3, 4841–4848 (2013). 45. Wood, H. B. Growth bars in feathers. Auk 67, 486–491 (1950). 46. Bortolotti, G. R. Flaws and pitfalls in the chemical analysis of feathers: bad news-good news for avian chemoecology and toxicology Ecol. Appl. 20, 1766–1774 (2010). 47. Lebreton, J. D., Burnham, K. P., Clobert, J. & Anderson, D. R. Modeling Survival and Testing Biological Hypotheses Using Marked Animals: A Unified Approach with Case Studies. Ecol. Monogr. 62, 67–118 (1992). 48. White, G. C. & Burnham, K. P. Program MARK: survival estimation from populations of marked animals. Bird Study 46, 120–139 (1999). 49. Choquet, R., Lebreton, J. D., Gimenez, O., Reboulet, A. M. & Pradel, R. U-CARE: Utilities for performing goodness of t fi tests and manipulating Capture-Recapture data. Ecography 32, 1071–1074 (2009). 50. Burnham, K. P. & Anderson, D. R. Model selection and multimodel inference: a practical Information-Theoretic Approach. 2nd ed. New York: Springer-Verlag (2002). Acknowledgements We thank N. Lois, S. Briones, M. Santillán, P. Laiolo, M. de la Riva, N. Tella-Carrete, and M. Vázquez for their help in capturing and monitoring owls over the years. Field work was conducted under permits from Argentinean wildlife agencies and the owners of private properties. We thank G.D. Fairhurst for discussion of results. This work was supported by Canal Sur TV, Fundación Repsol, Project CGL2012- 31888 from MEC, and COOPA20049 from CSIC (Spain). N.R.I. and S.R.M. were supported by CONICET Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 9 www.nature.com/scientificreports/ (Argentina), M.C. by a Ramón y Cajal contract (RYC-2009-04860), and A. S.A. by the JCI-2011-09085 fellowship. Author Contributions N.R.-I., M.C., G.R.B. and J.L.T. conceived the idea. N.R.-I., M.C., A.S.-A., S.R.-M., S.C., T.A.C. and J.L.T. collected and analysed the data. N.R.-I., M.C., A.S.-A. and J.L.T. wrote the paper. N.R.-I., M.C., A.S.-A., S.R.-M., S.C., T.A.C., G.R.B. and J.L.T. discussed the results and commented on the manuscript. Additional Information Competing financial interests: e a Th uthors declare no competing financial interests. How to cite this article: Rebolo-Ifrán, N. et al. Links between fear of humans, stress and survival support a non-random distribution of birds among urban and rural habitats. Sci. Rep. 5, 13723; doi: 10.1038/srep13723 (2015). This work is licensed under a Creative Commons Attribution 4.0 International License. The images or other third party material in this article are included in the article’s Creative Com- mons license, unless indicated otherwise in the credit line; if the material is not included under the Creative Commons license, users will need to obtain permission from the license holder to reproduce the material. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/ Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 10 http://www.deepdyve.com/assets/images/DeepDyve-Logo-lg.png Scientific Reports Springer Journals

Links between fear of humans, stress and survival support a non-random distribution of birds among urban and rural habitats

Loading next page...
 
/lp/springer-journals/links-between-fear-of-humans-stress-and-survival-support-a-non-random-Q9R8SdS3MR

References (55)

Publisher
Springer Journals
Copyright
Copyright © 2015 by The Author(s)
Subject
Science, Humanities and Social Sciences, multidisciplinary; Science, Humanities and Social Sciences, multidisciplinary; Science, multidisciplinary
eISSN
2045-2322
DOI
10.1038/srep13723
Publisher site
See Article on Publisher Site

Abstract

www.nature.com/scientificreports OPEN Links between fear of humans, stress and survival support a non-random distribution of birds received: 24 November 2014 Accepted: 31 July 2015 among urban and rural habitats Published: 08 September 2015 1 2,3 3,4 5 Natalia Rebolo-Ifrán , Martina Carrete , Ana Sanz-Aguilar , Sol Rodríguez-Martínez , 3 6 6,† 3 Sonia Cabezas , Tracy A. Marchant , Gary R. Bortolotti & José L. Tella Urban endocrine ecology aims to understand how organisms cope with new sources of stress and maintain allostatic load to thrive in an increasingly urbanized world. Recent research efforts have yielded controversial results based on short-term measures of stress, without exploring its fitness effects. We measured feather corticosterone (CORT , reflecting the duration and amplitude of glucocorticoid secretion over several weeks) and subsequent annual survival in urban and rural burrowing owls. This species shows high individual consistency in fear of humans (i.e., flight initiation distance, FID), allowing us to hypothesize that individuals distribute among habitats according to their tolerance to human disturbance. FIDs were shorter in urban than in rural birds, but CORT levels did not differ, nor were correlated to FIDs. Survival was twice as high in urban as in rural birds and links with CORT varied between habitats: while a quadratic relationship supports stabilizing selection in urban birds, high predation rates may have masked CORT -survival relationship in rural ones. These results evidence that urban life does not constitute an additional source of stress for urban individuals, as shown by their near identical CORT values compared with rural conspecifics supporting the non-random distribution of individuals among habitats according to their behavioural phenotypes. Urbanization is one of the most prevailing and lasting forms of habitat change occurring worldwide and causing the loss of biodiversity through local extinction processes . Nevertheless, species greatly vary in their responses to these severe changes in the environment; while most are unable to occupy these new habitats (termed as urban avoiders), others are able to persist (urban adapters) or even reach higher 2,3 densities in urban than in rural areas (urban exploiters) . This interspecific variability has encouraged the study of the ecological and life history traits that allow some species to thrive in urban environ- ments. Using birds as study subjects, recent comparative works have successfully related variability in 4 5 6 environmental tolerance , life-history traits and inter-individual variability in behavior to the different responses of species to urbanization. In addition to interspecific approaches, research on how individ- uals respond to and cope with urbanization as well as on the associated physiological and behavioral Departamento de Ecología, Genética y Evolución & IEGEBA-CONICET, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Buenos Aires, Argentina. Department of Physical, Chemical and Natural Systems, Universidad Pablo de Olavide, Sevilla, Spain. Department of Conservation Biology, Estación Biológica de Doñana, CSIC Sevilla, Spain. Instituto Mediterráneo de Estudios Avanzados, IMEDEA (CSIC-UIB), Miquel Marqués 21, E-07190 Esporles, Islas Baleares, Spain. Department of Biology, Biochemistry and Pharmacy, Universidad Nacional del Sur, Bahía Blanca, Argentina. Department of Biology, University of Saskatchewan, 112 Science Place, Saskatoon, SK S7N 5E2, Canada. Deceased. Correspondence and requests for materials should be addressed to M.C. (email: martina@ebd.csic.es) Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 1 www.nature.com/scientificreports/ 7,8 mechanisms should help us to understand the observed patterns . Challenges and opportunities asso- 9 10 11 ciated with urbanization include changes in resource availability , predation risk , conspecific density , 12 6 new competitors and human disturbance , as well as other perturbations such as light pollution and 13,14 the artificial elevation of natural noise levels (e.g. ). All of these factors are potential causes of stress that may ae ff ct the fitness of individuals, and how they are able to deal with stress may explain their ability to cope with urban challenges and opportunities and, ultimately, the different responses of species to urbanization . To properly understand whether urbanization represents an opportunity or a challenge for individu- als, it is essential to understand how individuals actually perceive their environment. The endocrine sys- tem is a primary candidate for this purpose, given its role in mediating the physiological and behavioral responses of organisms to the environment. Recent efforts, within the nascent field of urban endocrine ecology, have been devoted to understanding the functional role of the hypothalamic–pituitary–adre- nal (HPA) axis in mediating responses to urbanization . Measures of glucocorticoids - mostly baseline corticosterone (CORT) and stress-induced CORT - have been used to estimate the allostatic load (i.e., the cumulative current and anticipated energetic demands on an organism) experienced by urban and rural individuals of the same species . More than 20 studies, mostly on birds, have been conducted in recent years; however, no consistent patterns have been revealed for differences in allostatic load between urban and rural conspecifics . The fact that similar proportions of studies showed higher, lower, and similar circulating CORT levels in urban vs. non-urban birds may be related to methodological issues (the short-term nature of blood CORT measurements and variability in the life stages of individuals measured), but also to the fact that challenges faced by some species in urban habitats may represent opportunities for others . Therefore, more research is needed to understand the changes in allostatic load of individuals associated with urban life, as well as their uninvestigated fitness consequences of these changes . Here, we deal with two open questions highlighted by Bonier in her recent review: 1) Do hormo- nal responses regulate behavioral adaptation to urban environments, such as reduced flight initiation distances (FID)? and 2) Are hormone-fitness relationships ae ff cted by urbanization? We approach these questions in the light that modulated sensitivity of the HPA axis may play a central role in allowing urban birds to maintain foraging, breeding, and other essential behaviors in the face of frequent expo- 7 6 sure to human disturbance . Studying a contemporary process of urbanization, Carrete & Tella found that inter-individual variability in the fear of humans (experimentally measured as FID of individuals when approached by a human) could explain why some species thrive successfully in urban habitats. We focus here on one of these species, the burrowing owl (Athene cunicularia), an urban exploiter which 6,11 shows higher abundance and density in urban than in nearby rural habitats . Burrowing owls showed high within-individual consistencies in FID throughout their lifespan in both urban and rural habitats (repeatability > 0.90 ), suggesting that the lower FID of urban birds does not arise from habituation but 6,16 from the selection of individuals able to cope with constant human disturbance . Thus, if individual’s behavioural phenotypes match well with the differential levels of human disturbance in the areas where they settle to breed -as posit by the human disturbance habitat selection and the habitat-matching dispersal hypotheses, urban birds should not perceive their habitat as more stressful than that of rural ones. We therefore predict no differences in the allostatic load between urban and rural individuals nor a relationship with their FIDs. The majority of studies utilizing levels of CORT as indicator of the allostatic load of individuals have been conducted using instantaneous blood samples, which can be particularly informative when characterizing the functioning of the HPA response and understanding an individual’s physiological state at the instant of sampling. However, the time frame of such samples is limited, so integrated measures of glucocorticoids have been developed and applied to ecological contexts , nota- bly CORT in feathers (CORT ). This biomarker, whose time frame is significantly longer than that of blood, has been related to diverse ecological factors, suggesting that it integrates CORT secretion in general, globally expressing the response of individuals to different sources of environmental variation . Importantly, CORT levels increase in feathers when individuals are exposed to long-term stressors , as could be expected if urban life actually represents a sustained source of stress for urban individuals. It has been also suggested that CORT could be used as a metric to study carry-over effects . In fact, two 23,24 recent studies showed links between CORT and survival in two bird species . er Th efore, we examined the relationships between CORT levels and subsequent survival, predicting a negative relationship according to the corticosterone-fitness hypothesis independent of the habitat in the area where they set- tled. For these purposes, we individually marked a number of urban and rural breeding owls, measured their FID and CORT , and closely monitored them for their survival until the next breeding season. Our results fully support our first predictions, but also show complex relationships between CORT and sur- vival that may be related to ecological constraints (i.e, predation pressure) other than human disturbance. Results Fear of humans and stress. According to previous studies, urban burrowing owls showed significantly shorter FIDs than their rural conspecifics (urban birds: mean = 18.29 m, SE = 1.05, n = 72; rural birds: mean = 54.51 m, SE = 3.83, n = 49), even while controlling for the slightly shorter -although not statis- tically significant- FIDs in males (mean = 31.19 m, SE = 3.49, n = 56) than in females (mean = 34.48 m, SE = 3.12, n = 65) (Table  1). However, this closer interaction with humans does not suppose an Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 2 www.nature.com/scientificreports/ Dependent Independent Independent variable variables F df P Dependent variable variables F df P (log)FID Habitat 115.20 1, 118 0.0001 (log)CORT Habitat 0.34 1, 116 0.5591 Sex 1.45 1, 118 0.2311 Sex 3.62 1, 116 0.0594 Year 0.28 1, 116 0.5953 FID 0.38 1, 116 0.5398 2 2 Adjusted-R : 0.49 Adjusted-R : 0.003 Table 1. Models obtained to compare FID and feather CORT (CORT ) levels between urban and rural birds (n = 121 individuals). Figure 1. Relationships between feather CORT (CORT ) and FID of urban (grey dots) and rural (white dots) adult burrowing owls. In the external margins of the plot, we included the boxplots for FID and CORT of rural (n = 49) and urban (n = 72) birds. extra-source of stress, as urban birds showed nearly identical CORT concentrations than rural ones (urban birds: mean = 9.61 pg/mm, SE = 0.38, n = 72; rural birds: mean = 9.57 pg/mm, SE = 0.33, n = 49, Fig.  1). CORT did not differ between habitat types even when controlling for year and the slightly and marginally significant lower CORT concentrations found in males (mean = 9.01 pg/mm, SE = 0.29, n = 56) than in females (mean = 10.10 pg/mm, SE = 0.40, n = 65; Table  1). Moreover, CORT concen- trations were not related to individual FIDs, either when considering all birds together (Table  1) or when taking into account potential differences between habitats (interaction habitat *FID: F = 0.05, 1,115 p = 0.82; Fig.  1). Stress and survival. e g Th oodness-of-fit of the general model fitted the data adequately ( χ = 2, df = 5, p = 0.85). We started model selection by testing the effects of time and habitat type on resighting (p) and survival (φ ) probabilities (Table 2). The best model (Model 1, Table 2) included a temporal effect on resighting probability, which was relatively high (p = 0.81, 95% CI = 0.68–0.89) and did not vary mean between habitats. However, survival differed between habitats, being more than twice as high in urban (φ = 0.59) as in rural (φ = 0.25) individuals (Fig. 2). Models including additional temporal effects on sur - vival had Δ AIC c > 2 and much lower Akaike weights (Table 2). Consequently, we selected the structure of this model to test for CORT effects on subsequent annual survival. e eff Th ect of CORT on survival was retained in model selection (Table  3). The best supported model in terms of AICc (Model 1a, Table  3) showed that survival decreased with CORT levels in rural birds (logit φ = 1.851 (CI: −1.846–5-548)–0.382 (CI: − 0.815–0.052)*CORT ) while it exhibited a rural f quadratic relationship in urban ones (logit φ = − 4.547 (CI: − 8.424–− 0.671) + 0.917 (CI: 0.189– urban 1.644)*CORT –0.034 (CI: − 0.065–− 0.004)*CORT ). However, the confidence interval for the beta esti - f f mate corresponding to the linear slope of rural birds included zero, indicating a non-significant effect. In fact, a more parsimonious model without this effect was equivalent in terms of AICc ( Δ AIC c = 1.90, Table 3), indicating that CORT had a non-detectable effect on the survival of rural birds but a significant quadratic relationship in urban owls (logit φ = − 4.646 (CI: − 8.493–− 0.798) + 0.927 (CI: 0.205– urban 1.650)*CORT –0.034 (CI: −0.065–− 0.004)*CORT ). Accordingly, ∆AICc between models 1b and 1i (no f f CORT effect on survival of rural and urban birds) was 5.38 (Table  3), supporting the CORT -survival f f relationship in urban birds (Fig. 3). Therefore, in addition to habitat differences, CORT had a significant effect on the survival of urban birds, with probabilities of survival being higher at intermediate CORT levels (Fig. 3). Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 3 www.nature.com/scientificreports/ Model Model structure AICc ΔAICc w NP deviance 1 φ (habitat) p (time) 409.229 0.00 0.528 8 392.702 2 φ (habitat × time) p (time) 411.303 2.07 0.187 17 374.985 3 φ (habitat + time) p (time) 412.345 3.12 0.111 13 384.987 φ (habitat × time) p 4 412.794 3.56 0.089 18 374.193 (habitat + time) φ (habitat × time) p 5 414.613 5.38 0.036 14 385.040 (habitat) 6 φ (habitat × time) p (.) 414.754 5.52 0.033 13 387.396 7 φ (habitat × time) p (time) 416.156 6.93 0.017 20 372.938 8 φ (.) p (time) 433.641 24.41 0.000 7 419.232 9 φ (t) p (time) 434.354 25.12 0.000 11 411.376 Table 2. Modeling survival (φ) and recapture probabilities (p) of 183 adult burrowing owls. AICc: Akaike’s information criterion adjusted for effective sample size, ΔAICc: AICc difference between the current model and that with the lowest AICc value; w : Akaike’s weight, NP: number of estimable parameters, deviance: relative deviance. Model notation: “+”: parallel variation, additive effect; “x”: interaction; “.” = constant (i.e. no effects considered); “habitat” = different parameters for urban and rural birds; “time” = between year differences. Figure 2. Estimates of annual survival (mean and 95% CI) obtained for 109 urban and 74 rural adult burrowing owls. Model φ φ AICc ΔAICc w NP deviance urban rural i 1a CORT + CORT CORT 403.89 0.00 0.39 13 376.54 f f f 1b CORT + CORT — 405.79 1.90 0.15 12 380.63 f f 2 2 1c CORT + CORT CORT + CORT 406.07 2.18 0.13 14 376.50 f f f f 1d CORT CORT 406.31 2.41 0.12 12 381.15 f f 1e — CORT 406.95 3.06 0.08 11 383.98 1f CORT — 408.33 4.43 0.04 11 385.35 1g CORT CORT + CORT 408.48 4.58 0.04 13 381.12 f f f 1h — fCORT+ fCORT 409.12 5.23 0.03 12 383.96 1i — — 409.28 5.38 0.03 10 388.46 Table 3. Modeling feather CORT (CORT ) ee ff cts on subsequent annual survival ( φ) of urban (n = 109) and rural (n = 74) adult burrowing owls. In all models, resighting probabilities (p) varied over time and survival aer fir ft st year of CORT sampling was considered to be constant over time and different for rural and urban birds. Model notation: “-”: constant (i.e. no CORT effect); CORT : linear CORT effect; f f f CORT + CORT : quadratic CORT effect. All other notations as in Table 1. f f f Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 4 www.nature.com/scientificreports/ Figure 3. Distribution of feather CORT (CORT ) concentrations measured in urban (n = 109, black bars) and rural (n = 74, grey bars) burrowing owls. Overlapped, we show the relationship between CORT and the estimated immediate survival of urban owls (black line, 95% CI depicted as dashed lines). There was not a significant relationship for rural individuals (see Results). Discussion Human disturbance and stress in urban and rural birds. With the accelerating pace of anthro- pogenic global change, understanding how organisms cope with these changes is an urgent task. Traditionally, the most adverse human activities for fauna have been related to natural landscape mod- ification. However, a growing number of studies are now showing that human presence per se can be 7,21 important in modifying animal activities and distributions through behavioral changes . Indeed, it has been proposed that the ability of certain species to thrive in urban habitats, the most populated habitats worldwide, can be attributed to their high interindividual variability in fear of humans, such that only tame individuals (i.e., those with the lowest fear of humans compared to their conspecifics) can success - 6,15,17 fully occupy these areas . Our result showing shorter FIDs in urban than in rural burrowing owls are 15,17 thus not novel, but in line with previous studies on this species and with others showing the same pattern of higher tolerance towards humans in urban individuals in a variety of birds species . Although this pattern was considered a result of habituation to human disturbance in the absence of individu- al-based studies , the long-term monitoring of individually marked burrowing owls demonstrated that FID remains largely unchanged across their lifespan , thus supporting the idea that behavioral differ - 6,16,27 ences between urban and rural conspecifics are more likely a consequence of selective processes . Urbanized areas may be selecting for individuals with coping styles able to deal with urban challenges, 27–31 human presence included . Coping styles (so called behavioral syndromes or personalities) are rel- atively stable combinations of behavioral and physiological traits that confer differential fitness con - sequences under divergent environmental conditions . Different studies have demonstrated a genetic basis for the expression of behavioral and physiological components of individual coping styles , such that selective pressures associated with urban life can have long-lasting ecological but also evolutionary consequences. In fact, a recent study on urban and rural dark-eyed juncos (Junco hyemalis) supports the role of selection instead of drift or founder effects to explain the lower FID shown by urban birds . We aimed here to determine whether hormonal responses of individuals to stress are related to their tolerance to human disturbance, to deepen our understanding of the potential selection of individuals able to cope with urban habitats. Attending to the above arguments, we should not expect a relationship between FID and CORT nor differences in CORT between urban and rural individuals. If individuals f f choose to breed in urban habitats or in rural sites with different levels of human disturbance according to their tolerance to humans , all individuals should perceive similar amounts of stress in regards to human disturbance. Our results fully support these predictions. However, they may also be interpreted as another piece to the puzzling results obtained to date, which cannot discern a clear pattern of differ - 7,34 ences in allostatic load between urban and rural birds . Remarkably, two experimental studies found that urban birds raised in a common garden showed attenuated CORT responses to handling stress when 27,28 compared to their wildland counterparts , supporting their higher tolerance to human disturbance. On the other hand, the accumulation of apparently contradictory results, even obtained from a single species, might at least partially stem from methodological issues and variability in sources of stress among species . Regarding methodological issues, both baseline and stress-induced CORT concentra- tions are short-term measures of HPA activity that have oen ft been obtained at different life stages of the studied species . Studies conducted to date have shown no consistent patterns in the within-individual repeatability of these hormonal traits even when measured within a single life history stage and habitat, 22,35,36 37 suggesting that they are rather plastic traits . This makes their biological interpretation difficult , including the assessment of differences in allostatic load between urban and rural individuals . In our Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 5 www.nature.com/scientificreports/ case, CORT deposited in feathers reflects the duration and amplitude of glucocorticoid secretion during 20,21,38 the entire period of feather growth within a single life-history stage, which could span several weeks (see Methods). Both the duration and amplitude of HPA activity are important determinants of CORT , so direct correlations between plasma and feather CORT may not always be expected, especially if the elevation in plasma CORT is relatively modest and brief . However, if urban life actually represents a sustained source of stress for individuals, it is not expected to be a short-live but a long-live stressor which should promote sustained plasma CORT levels for a period long enough to elevate CORT . Estimates of within-individual consistency in CORT across years are low , indicating it is a plastic hormonal trait that reflects variations in log-term sources of stress and that it could be used to study 22 23,24 carry-over effects . In fact, CORT correlates with subsequent annual survival (see below), thus sug- gesting that it reflects a relatively long-term exposure of individuals to all of the sources of stress that they encounter, and that it could be a more reliable tool for assessing the effects of urbanization on allostatic load than short-term blood CORT measurements. Regarding variability in sources of stress, Bonier compiled a variety of biotic and abiotic factors associated with urbanization that could lead to both positive and negative changes in allostatic load. Among them, there are no apparent changes in temperature and food availability that could ae ff ct urban owls. Low food availability may cause chronic stress in animals . However, the trophic niche, as assessed through stable isotopes, is nearly identical between urban and rural burrowing owls, and there is a high prey availability in both kinds of habitats (Carrete & Tella, unpublished data). Artificial light should not disturb owls, and in any case may facilitate their foraging at night. Preliminary results suggest that exposure to parasites and diseases neither differ between urban and rural burrowing owls (Carrete & Tella, unpublished data). In addition, the increased breeding densities in urban habitats is not expected to increase allostatic load, since this is a non-territorial species and its mating behavior has been shown to be unae ff cted by these high densities . Interspecific competition is not expected to increase; the only ecologically similar species preying on the same range of prey (the American falcon Falco sparverius) is much scarcer than burrowing owls both in urban and rural areas . Therefore, the only factors that appar - ently differ are a higher human disturbance and much lower predation risk (see below) in urban than in rural areas. Attending to these sources of stress, an explanation alternative to the selection of individuals related to their fear of humans may explain the identical concentrations of CORT in urban and rural owls. That is, our results may reflect a replacement of stressful factors, i.e. predators in rural habitats by humans in urban ones. e Th frequency of exposure to these stressors is however very different: most pre- dation events of adult burrowing owls occur within their burrow nests (authors’ unpub. data), and thus their few encounters with predators would not cause chronic stress (or “sustained physiological stress ”) but rather their death; meanwhile, urban birds are constantly facing human presence. Demographic experiments have demonstrated that sustained exposure to predators (or their cues) can have associ- ated physiological stress effects (eg, elevation of glucocorticoid levels) with long-term consequences on birth and survival in free-living animals . Therefore, it seems unreasonable to think that successful city dwellers can live with the permanent activation of their HPA axis due to daily encounters with humans. u Th s, it is more likely that a permanent perturbation factor like human disturbance would be selecting 6,17 for those individuals that are able to better tolerate humans . Stress and survival. Studies examining relationships between glucocorticoid levels and survival in 42,43 vertebrates, including birds (e.g. ), showed no less puzzling results than the assessment of variability in allostatic load between rural and urban birds, oer ff ing controversial support to the corticostrone-fitness 25,37 hypothesis . The variety of responses found between baseline and stress-induced CORT and survival in birds could also be at least partially related to the short-term nature of these hormonal traits and to 25,37 the variability of the life history stages at which they were measured . Two recent studies measuring CORT as a longer term, integrated measure of avian stress physiology have found negative relation- ships with overwinter survival in two avian species (house sparrows Passer domesticus and north- ern common eiders Somateria mollissima borealis ). To our knowledge, ours is the first study assessing differences in CORT-survival relationships between urban and rural individuals, showing contrasting patterns. CORT showed a quadratic relationship with survival in urban owls, a pattern previously found for baseline CORT in cliff swallows Petrochelidon pyrrhonota that indicates stabilizing rather than directional mortality selection favoring intermediate CORT levels . Although few studies examined non-linear CORT-survival relationships, stabilizing selection makes sense since acute short-term CORT secretion mediates rapid behavioural and physiological modifications that benefit immediate survival, while prolonged stressful situations lead to a long-term allostatic overload that may have detrimental 25,41 consequences compromising survival . Survival probabilities of rural owls were less than half that of urban ones, and contrary to the lat- ter they were unrelated to their CORT levels. We have strong evidence to suggest that these different patterns result from differences in predation pressure. A lower predation risk is generalized for urban birds , and high predation rates in rural habitats explain differences in breeding densities and the main life-history parameters (breeding success, dispersal) in our study species (Rebolo-Ifrán et al., in prep; authors unpublish data). As breeding burrowing owls have few opportunities to escape from predators entering their deep burrow nests (authors’ unpubl. data), the high rates of predation-caused mortality should be random with respect to their CORT levels and could mask any relationship between CORT f f Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 6 www.nature.com/scientificreports/ and survival in rural owls. Our contrasting results comparing urban and rural birds illustrate how differ - ent CORT-survival patterns can be obtained within a single species, population, and life-history stage , and how difficult their interpretation can be in the absence of a sufficient knowledge of the ecological constraints modelling the demography of the studied species. Conclusions Our results suggest that urban life does not increase the physiological stress experienced by individuals, supporting the hypothesis that individuals select breeding habitats according to their tolerance to human 6,15 disturbance as a major challenge faced in urban habitats . This scenario is in agreement with the adaptive or matching-habitat dispersal hypothesis, which implies a non-random dispersal of individuals 18 44 resulting in a match between phenotype and environment , a hypothesis thus far scarcely explored . Moreover, the higher survival rates (this study) and breeding success (Rebolo-Ifrán et al., in prep) of urban birds have surely contributed to the higher breeding densities currently found in the urban habi- tat , that together with the high philopatry and the non-random dispersal of individuals between urban and rural habitats generates a genetic structuring of the population (Carrete et al. in prep.). Much more research is however needed before we can generalize these results to the many other species that are successfully thriving in urbanized habitats. Material and Methods Study system and field procedures. We conducted our study in a ca. 5,400 km area of natu- ral grasslands, pastures, cereal crops and urban areas surrounding the city of Bahía Blanca (Buenos Aires, Argentina), where burrowing owls nest in burrows excavated by the owls themselves or by mam- 11,15,17 mals . We surveyed this population between 2006 and 2013, monitoring a total of 1,501 different nests. We defined as urban nests (n = 545) those excavated by owls in private and public gardens, spaces among houses, curbs of streets and along large avenues in the city. Nests are usually within 10–100 m of inhabited buildings. Rural nests (n = 956) were located in the surrounding expanses of natural grasslands and pastures devoted to wide-ranging livestock and low-intensive cereal crops, where human presence and activities are minimal . There is no clear habitat interface between urban and rural habitats, since urbanized areas are immediately surrounded by rural ones. For this study, we captured 183 different breeding adults in 2006, 2008 and 2009 (74 in rural and 109 in urban nests) during the chick-rearing period (late November to early January). Birds were marked with plastic rings with a unique alphanumeric code that could be read at a distance using a telescope. Blood samples (0.1 ml) were collected for molecular sexing (see ), while one external tail feather was plucked for CORT determination (see below). Resightings of marked birds were obtained during inten- sive population monitoring from 2007 to 2012, surveying all known breeding sites as well as areas of suitable habitat not previously occupied to detect new breeding sites. We were able to experimentally measure flight initiation distance (FID, i.e. the distance at which individuals flee when approached by a human), of 121 out of the 183 individuals sampled for CORT , 15,17 following the standard protocol used in previous studies . Briefly, all FIDs were also measured during the chick-rearing period, by walking towards focal individuals following a direct trajectory, with no obstacles blocking the bird and the observer and at a constant speed of 0.5 m/s. FIDs were measured in fine weather, avoiding the hottest hours of the day, and rainy or windy days. All tested owls were undisturbed and resting close to or at the entrance of their nests during daytime. The distance between the observer and the flushing bird was measured using a laser telemeter (range: 10–1300 m) or counting paces for distances of less than 10 m. We used for analyses both single and average values of FID (when more than one measure was obtained from a single individual in the same or different years), given that this behavior is highly repeatable within breeding seasons (r = 0.84–0.92) and across the lifespan 15,17 (r = 0.90–0.96) of burrowing owls . Feather corticosterone. We estimated the stress experienced by birds by measuring CORT con- centration in feathers following Bortolotti et al. . Contrary to blood measures, CORT reflects the HPA activity of an individual within a time frame of days or weeks (depending on the moult speed of the studied species). Thus, this hormonal trait integrates not only the intensity of the physiological response but also how long CORT is elevated within the bloodstream, and the frequency of exposure to stress- 20,21,38 ors . In the burrowing owl, no information is available about the growth rate of feathers and growth bars are not conspicuous as in other species (authors’ unpublished data). Estimates for other owls show that flight feathers can growth 1.9–3.1 mm/day , so a typical 95 mm tail feather from a burrowing owl may be fully grown aer c ft a. 30–50 days. Although this may not be an accurate estimation, CORT can reflect the stress experienced by individuals during a time frame of at least 3–4 weeks corresponding to the pre-breeding moult period of adult birds. Burrowing owls are sedentary and breeders stay in their territories along the year in the study area (author’s unpubl. data). Therefore, the studied individuals were potentially exposed to the same stressors associated to their territories across the annual cycle. To quantify CORT , we first measured the length of each feather aer r ft emoving the calamus . Then we cut the feather vanes into small pieces (<5 mm) with scissors and placed in a glass vial with 10 mL 20,38 of methanol (HPLC grade, VWR International, Mississauga, ON) for CORT extraction .Vials were placed in a sonicating water bath at room temperature for 30 min, followed by incubation at 50 °C Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 7 www.nature.com/scientificreports/ overnight in a shaking water bath. Using vacuum filtration, the methanol containing the hormones was separated from the feathers. Vials with the methanol extract were placed open in a 50 °C water bath in a fume hood under air until they were completely dry. When the evaporation of the samples was complete, the extract residues were reconstituted in 600 mL of phosphate buffer system (0.05 M, pH 7.6) and fro- zen at − 20 °C until CORT measurement by radioimmunoassay. We assessed the extraction efficiency by including feather samples spiked with a small amount (c. 4000 dpm) of 3H-corticosterone. The coefficient of variation for five different batches ranges from 5.31 (within essay) to 8.32 (between essays). Greater than 92% of the radioactivity was recoverable in the reconstituted samples. CORT values are expressed 20,38 as a function of feather length (pg mm-1) following Bortolotti et al. . Statistical analysis. We used generalized linear models (GLM, using the identity link function and normal error distribution) to assess if FID (log-transformed) differed between our sampled rural and urban breeding owls, while controlling for sex, a result that was previously found using different data- 6,15,17 sets of individuals . We were able to sample both members of the breeding pair in only 25% of the territories, so we could not control for a potential territory effect fitted as a random term. However, a previous study conducted in the same owl population, using larger sample sizes, showed just a slight effect of territory and results were nearly identical when it was not fitted as a random term . The year(s) when FID was measured for each individual was not controlled for given the high consistency in this behavioural trait across the lifespan of individuals (see above). The same GLM structure was then used for assessing differences in CORT (log-transformed) between urban and rural birds and its relationship with FID, while controlling for potential sources of variability (sex and sampling year). In this case, we controlled for sampling year since CORT of individuals may vary across years due to yearly variations in the kind and intensity of sources of stress . All models were fitted using R 3.0.3. Survival analysis. We analyzed encounter histories of the 183 individuals sampled in 2006, 2008 and 2009 and resighted (or not) from 2007 to 2012 to test for habitat and CORT effects on survival. This monitoring period is longer than the average lifespan of adult burrowing owls , and no individuals changed breeding habitat (urban or rural) during the study. Survival (φ ) and resighting probabilities (p) were estimated simultaneously by maximum-likelihood procedures and models were built using the program MARK . We conducted capture-recapture analyses in two steps: first we tested for temporal and habitat effects on both resighting and survival probabilities; then, we selected the best structure of the parameters to specifically test for CORT effects on subsequent survival probabilities (i.e, only first year survival aer s ft ampling was modeled as a function of the CORT covariate, including linear and quadratic effects). Exploratory analyses did not detect a sex effect on survival or resighting probabilities, nor was there a strong sex effect on CORT (see results), so we did not include sex in final models to avoid overparameterization. The goodness-of-fit of the general Cormack-Jolly-Seber model by group (i.e, urban and rural birds; φ p ) was assessed using program U-CARE 2.3.2 . Model selection was based t*g t*g on Akaike’s Information Criterion adjusted for the effective sample size (AICc ). Models differing less than 2 AICc points were considered equivalent . We also calculated for each model the Akaike weight (w), as an index of its relative plausibility . Ethic statements. Capture, banding and FID measures of Burrowing owls were conducted under permits and following the protocols approved by the Argentinean wildlife agency (22500-4102/09), the Ethic Committee of CSIC (CEBA-EBD-11-28), and the owners of private properties, in accordance with the approved guidelines. References 1. McKinney, M. L. Urbanization as a major cause of biotic homogenization. Biol. Conserv. 127, 247–260 (2006). 2. Kark, S., Iwaniuk, A., Schalimtzek, A. & Banker, E. Living in the city: can anyone become an urban exploiter? J. Biogeogr. 34, 638–651 (2007). 3. McKinney, M. L. Urbanization, Biodiversity, and Conservation. BioScience 52, 883–890 (2002). 4. Bonier, F., Martin, P. R. & Wingfield, J. C. Urban birds have broader environmental tolerance. Biol. Lett. 3, 670–3 (2007). 5. Sol, D., González-Lagos, C., Moreira, D. & Maspons, J. Urbanisation tolerance and the loss of avian diversity. Ecol. Lett. 17, 942–950 (2014). 6. Carrete, M. & Tella, J. L. Inter-individual variability in fear of humans and relative brain size of the species are related to contemporary urban invasion in birds. PLoS One 6, e18859 (2011). 7. Bonier, F. Hormones in the city: endocrine ecology of urban birds. Horm. Behav. 61, 763–772 (2012). 8. Sol, D., Lapiedra, O. & González-Lagos, C. Behavioural adjustments for a life in the city. Anim. Behav. 85, 1101–1112 (2013). 9. Chace, J. F. & Walsh, J. J. Urban effects on native avifauna: a review. Lands. Urban Plan . 74, 46–69 (2006). 10. Díaz, M. et al. The geography of fear: a latitudinal gradient in anti-predator escape distances of birds across Europe. PloS one 8, e64634 (2013). 11. Rodriguez-Martínez, S., Carrete, M., Roques, S., Rebolo-Ifrán, N. & Tella, J. L. High urban breeding densities do not disrupt genetic monogamy in a bird species. PLoS One 9, e91314 (2014). 12. Hernández-Brito, D., Carrete, M., Popa-Lisseanu, A., Ibáñez, C. & Tella, J. L. Crowding in the city: losing and winning competitors of an invasive bird. PLoS One 9, e100593 (2014). 13. Slabbekoorn, H. & Peet, M. Birds sing at higher pitch in urban noise. Nature 424, 26 (2003). 14. Da Silva, A., Samplonius, J. M., Schlicht, E., Valcu, M. & Kempenaers, B. Artificial night lighting rather than traffic noise ae ff cts the daily timing of dawn and dusk singing in common European songbirds. Behav. Ecol. 25, 1037–1047 (2014). Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 8 www.nature.com/scientificreports/ 15. Carrete, M. & Tella, J. L. High individual consistency in fear of humans throughout the adult lifespan of rural and urban burrowing owls. Sci. Rep. 3, 3524 (2013). 16. Møller, A. P. Behavioural and ecological predictors of urbanization. In Avian urban ecology (ed. D. Gil & H. Brumm), pp. 54–68. Oxford: Oxford University Press (2014). 17. Carrete, M. & Tella, J. L. Individual consistency in flight initiation distances in burrowing owls: a new hypothesis on disturbance- induced habitat selection. Biol. Lett. 6, 167–70 (2010). 18. Edelaar, P. & Bolnick, D. I. Non-random gene flow: an underappreciated force in evolution and ecology. Trends Ecol. Evol. 27, 659–665 (2012). 19. Sheriff, M. J., Dantzer, B., Delehanty, B., Palme, R. & Boonstra, R. Measuring stress in wildlife: techniques for quantifying glucocorticoids. Oecologia 166, 869–887 (2011). 20. Bortolotti, G. R., Marchant, T. A., Blas, J. & German, T. Corticosterone in feathers is a long-term, integrated measure of avian stress physiology. Funct. Ecol. 22, 494–500 (2008). 21. Fairhurst, G. D., Marchant, T., Soos, C., Machin, K. & Clark, R. G. Experimental relationships between levels of corticosterone in plasma and feathers in a free-living bird. J. Exp. Biol. 216, 4071–4081 (2013). 22. Legagneux, P. et al. Does Feather Corticosterone Reflect Individual Quality or External Stress in Arctic-Nesting Migratory Birds? Plos One 8, e82644 (2013). 23. Koren, L. et al. Non-breeding feather concentrations of testosterone, corticosterone and cortisol are associated with subsequent survival in wild house sparrows. Proc. R. Soc. B Biol. Sci. 279, 1560–1566 (2012). 24. Harms, N. J. et al. Feather corticosterone reveals effect of moulting conditions in the autumn on subsequent reproductive output and survival in an Arctic migratory bird. Proc. R. Soc. B Biol. Sci. 282, 20142085 (2015). 25. Bonier, F., Martin, P. R., Moore, I. T. & Wingfield, J. C. Do baseline glucocorticoids predict fitness? Trends Ecol. Evol. 24, 634–42 (2009). 26. Blumstein, D. Attention, habituation, and antipredator behaviour: implications for urban birds. In Avian urban ecology (ed. D. Gil & H. Brumm), pp. 41–53. Oxford: Oxford University Press (2014). 27. Atwell, J. W. et al. Boldness behavior and stress physiology in a novel urban environment suggest rapid correlated evolutionary adaptation. Behav. Ecol. 23, 960–969 (2012). 28. Partecke, J., Schwabl, I. & Gwinner, E. Stress and the city: urbanization and its effects on the stress physiology in European blackbirds. Ecology 87, 1945–52 (2006). 29. Evans, J., Boudreau, K. & Hyman, J. Behavioural syndromes in urban and rural populations of song sparrows. Ethology 116, 588–595 (2010). 30. Bókony, V., Kulcsár, A., Tóth, Z. & Liker, A. Personality traits and behavioral syndromes in differently urbanized populations of house sparrows (Passer domesticus). PLoS One 7, e36639 (2012). 31. Miranda, A. C., Schielzeth, H., Sonntag, T. & Partecke, J. Urbanization and its effects on personality traits: a result of microevolution or phenotypic plasticity? Glob. Chang. Biol. 19, 2634–2644 (2013). 32. Coppens, C. M., de Boer, S. F. & Koolhaas, J. M. Coping styles and behavioural flexibility: towards underlying mechanisms. Philos. Trans. R. Soc. Lond. B. Biol. Sci. 365, 4021–8 (2010). 33. Øverli, Ø. et al. Evolutionary background for stress-coping styles: relationships between physiological, behavioral, and cognitive traits in non-mammalian vertebrates. Neurosci. Biobehav. Rev. 31, 396–412 (2007). 34. Partecke, J. Mechanisms of phenotypic responses following colonization of urban areas: from plastic to genetic adaptation. In Avian urban ecology (ed. D. Gil & H. Brumm), pp. 131–142. Oxford: Oxford University Press (2014). 35. Ouyang, J. Q., Hau, M. & Bonier, F. Within seasons and among years: when are 840 corticosterone levels repeatable? Horm. Behav. 60, 559–564 (2011). 36. Baugh, A. T., van Oers, K., Dingemanse, N. J. & Hau, M. Baseline and stress-induced glucocorticoid concentrations are not repeatable but covary within individual great tits (Parus major). Gen. Comp. Endocrinol. 208, 154–163 (2014). 37. Crespi, E. J., Williams, T. D., Jessop, T. S. & Delehanty, B. Life history and the ecology of stress: how do glucocorticoid hormones influence life-history variation in animals? Funct. Ecol. 27, 93–106 (2013). 38. Bortolotti, G. R., Marchant, T. A., Blas, J. & Cabezas, S. Tracking stress: localization, deposition and stability of corticosterone in feathers. J. Exp. Biol. 212, 1477–1482 (2009). 39. Clinchy, M., Zanette, L., Boonstra, R., Wingfield, J. C. & Smith, J. N. Balancing food and predator pressure induces chronic stress in songbirds. Proc. R. Soc. B Biol. Sci. 271, 2473–2479 (2004). 40. Clinchy, M., Sheriff, M. J. & Zanette, L. Y. Predator-induced stress and the ecology of fear. Funct. Ecol. 27, 56–65 (2013). 41. Wingfield, J. C. e Th comparative biology of environmental stress: behavioural endocrinology and variation in ability to cope with novel, changing environments. Anim. Behav. 85, 1127–1133 (2013). 42. Brown, C. R., Brown, M. B., Raouf, S. A., Smith, L. C. & Wingfield, J. C. Effects of endogenous steroid hormone levels on annual survival in cliff swallows. Ecology 86, 1034–1046 (2005). 43. Blas, J., Bortolotti, G. R., Tella, J. L., Baos, R. & Marchant, T. A. Stress response during development predicts fitness in a wild, long-lived vertebrate. Proc. Nat. Acad. Sci. USA 104, 8880–8884 (2007). 44. Camacho, C., Canal, D. & Potti, J. Nonrandom dispersal drives phenotypic divergence within a bird population. Ecol. Evol. 3, 4841–4848 (2013). 45. Wood, H. B. Growth bars in feathers. Auk 67, 486–491 (1950). 46. Bortolotti, G. R. Flaws and pitfalls in the chemical analysis of feathers: bad news-good news for avian chemoecology and toxicology Ecol. Appl. 20, 1766–1774 (2010). 47. Lebreton, J. D., Burnham, K. P., Clobert, J. & Anderson, D. R. Modeling Survival and Testing Biological Hypotheses Using Marked Animals: A Unified Approach with Case Studies. Ecol. Monogr. 62, 67–118 (1992). 48. White, G. C. & Burnham, K. P. Program MARK: survival estimation from populations of marked animals. Bird Study 46, 120–139 (1999). 49. Choquet, R., Lebreton, J. D., Gimenez, O., Reboulet, A. M. & Pradel, R. U-CARE: Utilities for performing goodness of t fi tests and manipulating Capture-Recapture data. Ecography 32, 1071–1074 (2009). 50. Burnham, K. P. & Anderson, D. R. Model selection and multimodel inference: a practical Information-Theoretic Approach. 2nd ed. New York: Springer-Verlag (2002). Acknowledgements We thank N. Lois, S. Briones, M. Santillán, P. Laiolo, M. de la Riva, N. Tella-Carrete, and M. Vázquez for their help in capturing and monitoring owls over the years. Field work was conducted under permits from Argentinean wildlife agencies and the owners of private properties. We thank G.D. Fairhurst for discussion of results. This work was supported by Canal Sur TV, Fundación Repsol, Project CGL2012- 31888 from MEC, and COOPA20049 from CSIC (Spain). N.R.I. and S.R.M. were supported by CONICET Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 9 www.nature.com/scientificreports/ (Argentina), M.C. by a Ramón y Cajal contract (RYC-2009-04860), and A. S.A. by the JCI-2011-09085 fellowship. Author Contributions N.R.-I., M.C., G.R.B. and J.L.T. conceived the idea. N.R.-I., M.C., A.S.-A., S.R.-M., S.C., T.A.C. and J.L.T. collected and analysed the data. N.R.-I., M.C., A.S.-A. and J.L.T. wrote the paper. N.R.-I., M.C., A.S.-A., S.R.-M., S.C., T.A.C., G.R.B. and J.L.T. discussed the results and commented on the manuscript. Additional Information Competing financial interests: e a Th uthors declare no competing financial interests. How to cite this article: Rebolo-Ifrán, N. et al. Links between fear of humans, stress and survival support a non-random distribution of birds among urban and rural habitats. Sci. Rep. 5, 13723; doi: 10.1038/srep13723 (2015). This work is licensed under a Creative Commons Attribution 4.0 International License. The images or other third party material in this article are included in the article’s Creative Com- mons license, unless indicated otherwise in the credit line; if the material is not included under the Creative Commons license, users will need to obtain permission from the license holder to reproduce the material. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/ Scientific RepoRts | 5:13723 | DOi: 10.1038/srep13723 10

Journal

Scientific ReportsSpringer Journals

Published: Sep 8, 2015

There are no references for this article.