Sex-dependent spatial structure of telomere length in a wild
long-lived scavenger
Laura Gangoso,1,† Sergio A. Lambertucci,2 Sonia Cabezas,1,3 Pablo A. E. Alarcón,2,4
Guillermo M. Wiemeyer,4,5 José A. Sanchez-Zapata,6 Guillermo Blanco,7 Fernando Hiraldo,1
and José A. Donázar1
1Estación Biológica de Doñana, CSIC, C/Américo Vespucio s/n, E-41092 Sevilla, Spain
de Biología de la Conservación, Laboratorio Ecotono, INIBIOMA (CONICET-National University of Comahue),
Quintral 1250, Centro Regional Universitario Bariloche, 8400 Bariloche, Argentina
3University of Saskatchewan, 72 Campus Drive, SK S7N 5E2 Saskatoon, Canada
4The Peregrine Fund, 5668 West Flying Hawk Lane, Boise, Idaho 83709 USA
5Jardín Zoológico de la Ciudad de Buenos Aires (CABA), Avenida Sarmiento and Avenida Las Heras, CP1425 Buenos Aires, Argentina
6University Miguel Hernández, Avinguda de la Universitat d’Elx, s/n, E-03202 Alicante, Spain
7National Museum of Natural Sciences, CSIC, C/José Gutiérrez Abascal 2, E-28006 Madrid, Spain
2Grupo
Citation: Gangoso, L., S. A. Lambertucci, S. Cabezas, P. A. E. Alarcón, G. M. Wiemeyer, J. A. Sanchez-Zapata, G. Blanco,
F. Hiraldo, and J. A. Donázar. 2016. Sex-dependent spatial structure of telomere length in a wild long-lived scavenger
Ecosphere 7(10):e01544. 10.1002/ecs2.1544
Abstract. Sex-related divergences in many phenotypic traits, such as morphology, physiology, and be-
havior, have widely been described in animals. These asymmetries may adapt the sexes to different subniches, but also may produce sex-specific optima for life-history traits, as well as different costs. In birds,
long movements in search of food and intraspecific competition may entail important metabolic costs that
can be predicted to be unequal if both sexes perform somehow differently. However, the extent to which
sex-specific individual movements, foraging strategies and social dominance relationships are correlated
with physiological costs has rarely been evaluated. The effects of prolonged exposure to stressors can be
mirrored in accelerated cellular damage and aging as well as in the by-products resulting from the activation of the stress response machinery. Both indicators, measured as telomere length and the concentration
of feather corticosterone (CORTf ), respectively, would reflect physiological costs at different time frames.
Here, on the basis of information provided by GPS-tagged Andean condors, a sexually dimorphic scavenger with a highly despotic social system, we determined whether sex-specific movement patterns correlated to variation in telomere length and CORTf levels. We found a striking pattern of spatial structure of
telomere length that was, in addition, sex-specific; males breeding farther from feeding grounds exhibited
longer telomeres, while the opposite pattern was found in females. Nevertheless, telomere length was not
related to the range of movements performed by condors. We also found that females displayed higher
CORTf values than males, regardless of the location of their nests, which is likely related to social dominance hierarchy and sexual size dimorphism. Sex-specific optima for trade-offs associated with ecological
factors might underlie the fact that populations are spatially structured from a telomere-length perspective, which has never been described before.
Key words: feather corticosterone; long-lived birds; movement patterns; social environment; telomere length.
Received 1 September 2016; accepted 7 September 2016. Corresponding Editor: W. Alice Boyle.
Copyright: © 2016 Gangoso et al. This is an open access article under the terms of the Creative Commons Attribution
License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.
† E-mail: laurag@ebd.csic.es
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GANGOSO ET AL.
strategies, and dominance relationships are correlated with physiological costs remains virtually unexplored.
The Andean condor (Vultur gryphus) is a top
scavenger living in the Andean range, from
Colombia to Tierra del Fuego, Argentina, and
Chile. Andean condors are unique among birds
of prey because they show a strong direct sexual size dimorphism, with males being 30–40%
heavier than females (del Hoyo et al. 1994). The
species is highly despotic with adult males being
at the top of the hierarchy and clearly dominant
in conspecific interactions, particularly at feeding
places (Donázar et al. 1999). Andean condors are
specialized for highly efficient gliding flight, but
their huge body size and mass (wingspan about
3 m and body mass up to 16 kg) represent a major
challenge when weather conditions are adverse
(Shepard and Lambertucci 2013). Here, we took
advantage of the data obtained by GPS-tracked
Andean condors in the Argentinean Patagonia.
In this region, most individuals share common
feeding grounds in the Andean piedmont steppes
(Fig. 1), but whereas some pairs breed close to the
steppe, others do so in the Cordillera and along
the Pacific slope and are thus forced to make long
daily trips and crosses over the mountain range
to access feeding grounds (Lambertucci et al.
2014). Previous research showed that although
both sexes forage in similar areas (Lambertucci
et al. 2014), intersexual competition determines
that sexes segregate at a mesohabitat scale, so
that larger males are more prone to exploit carcasses in rugged slopes, whereas females are
more frequently observed on food resources
found in more humanized plains (Donázar et al.
1999, Lambertucci et al. 2012).
On the basis of this scenario, we hypothesize
that physiological cost will be related to foraging
movement patterns, yet unequally for males and
females if they perform somehow differently. To
test this hypothesis, we used two different evaluators providing long- and medium-term perspectives on individual physiology, that is, telomere
length and feather corticosterone (CORTf ) levels,
respectively, and related them to the movement
patterns of GPS-tagged condors.
Telomeres are evolutionarily conserved caps
consisting of repeated DNA sequences that protect eukaryotic linear chromosome ends (Zakian
1995). Telomere attrition is thought to play a key
INTRODUCTION
Within-species sex-related differences in
morphology, behavior, and longevity are widespread in the animal kingdom (Promislow 2003,
Fairbairn et al. 2007). In birds, sexes usually
differ in size and coloration, which has largely
been thought to be driven by sexual selection
and distinct parental roles (Andersson 1994).
Likewise, differences in foraging strategies have
been observed in a number of both sexually
size-dimorphic and size-monomorphic species,
which have been related to reduction in intersexual competition for food and foraging niches
(Newton 1979, Lewis et al. 2002, Weimerskirch
et al. 2006). Besides morphological asymmetries
that may confer one sex competitive advantages
over the other while feeding, sexual differences
in energy or nutritional requirements could also
explain the observed differences in foraging
behavior (Stauss et al. 2012). Sexual divergence
may have ecological significance in adapting the
sexes to different subniches, but also may produce sex-specific optima for life-history traits,
including investment in longevity and somatic
maintenance (Bonduriansky et al. 2008).
One of the most distinctive features of birds is
the ability to fly, which represents a clear advantage that also entails important metabolic costs
(Norberg 1990). Long-lived avian species, such
as seabirds and scavengers that exploit spatially
unpredictable food sources, often cover enormous ranges to forage (Fritz et al. 2003, Ruxton
and Houston 2004). The flying performance of
these large-sized species strongly relies on the
dynamic of local climatic conditions, like the
availability of winds and thermals (Weimerskirch
et al. 2000, Duriez et al. 2014), so that movements
under adverse weather conditions may became
extremely difficult and even impossible (Shepard
and Lambertucci 2013). Moreover, sexual size
dimorphism may result in differences in flight
efficiency and competitive abilities between
sexes (Wearmouth and Sims 2008). During the
breeding season, both longer movements and
increased habitat exploitation intensify energy
demands, and thus, resource allocation tradeoffs and physiological costs potentially affecting
lifetime fitness are expected to occur (Amélineau
et al. 2014). However, the extent to which
sex-specific individual movements, foraging
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GANGOSO ET AL.
Fig. 1. Map of the study site showing the location of the study area (in a square top left) and the distribution
of nesting sites and telomere length associated with each female (circles) and male (squares) breeding condors.
The area represented by a reticulated texture delimits the steppe feeding grounds.
role in organismal senescence given that, in the
absence of telomerase-driven restoration, they
gradually shorten during each cellular division
to a critical threshold that triggers chromosome instability and cell death (Armanios and
Blackburn 2012). In general, telomeres shorten
predictably with age, particularly in short-lived
birds (Haussmann et al. 2003, but see Hall et al.
2004), although it has been recognized that the
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amount of shortening greatly depends on accumulated oxidative damage affecting both the
telomere sequence and the restorative ability
of the enzyme telomerase (von Zglinicki 2002).
Additionally, we evaluate physiological response
to the cost of movement and foraging strategies
by means of the glucocorticoid corticosterone
(CORT) in feathers. Recent evidence suggests
that glucocorticoids modulate oxidative stress
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GANGOSO ET AL.
balance and telomere dynamics (Haussmann
and Marchetto 2010, Costantini et al. 2011). Birds
release CORT into the bloodstream as a mediator
of allostasis (maintaining homeostasis through
change), combining the energetic costs related
to sudden life-threatening challenges with daily
life-history stages (McEwen and Wingfield 2003).
CORT is an important metabolic regulator, and
its baseline level can increase during energetically demanding situations (Landys et al. 2006,
Angelier et al. 2008). The concentration of CORT
in blood denotes the bird’s physiological status at
a particular moment, while the amount of CORT
deposited in feathers (CORTf ) represents an integrated measure of the hypothalamus–pituitary–
adrenal axis activity during the feather growth
period (Bortolotti et al. 2008). CORTf levels have
been positively correlated with both baseline
and acute CORT levels in blood (Bortolotti et al.
2008, Fairhurst et al. 2013, Jenni-Eiermann et al.
2015). Taking into account these evaluators, we
specifically predict that condors breeding farther from the foraging area and thus performing
longer-distance foraging movements will have
shorter telomeres and higher CORTf levels than
those breeding close to the feeding grounds. In
addition, females will have even shorter telomeres and higher CORTf levels than males as a
consequence of their pervasive subordinate status. Finally, we predict that trade-offs will occur
between self-maintenance and longevity and
that the specific optima will differ between sexes.
concentrated in the steppe where most of the
condors forage (Lambertucci et al. 2014).
Between 2010 and 2011, 20 adult breeding condors (11 females and nine males) were captured
using cannon-net traps baited with ungulate
carcasses. The breeding status of condors was
verified when handled at the time of capture,
by confirming the presence of a brood patch in
all individuals. All birds were weighed using a
Pesola scale, and wing length was measured to
the nearest millimeter.
We tagged condors with GPS devices (2010:
10 patagial PTT-100 50 g Solar Argos/GPS tags
(Microwave Telemetry Inc., Columbia, Maryland,
USA); 2011: 10 backpack 100 g Solar GPS–GSM
CTT-1070-1100 tags (CellTrack Tech, LLC,
Somerset, Pennsylvania, USA). These devices
were cycled to transmit as much as possible,
which resulted in different device performance.
Thus, Microwave PTT-tags were able to record
one GPS location every one hour, while CellTrack
CTT-1070-1100 tags recorded one location every
15 min. Additionally, a greater covert feather, that
is, those on the outer wing, which overlay the
primary flight feathers, was collected from every
individual for hormone analyses. We chose this
particular feather because it is easily identifiable,
which guarantees that the same feather was taken
from all individuals, and has a sufficiently large
size, despite not being an essential flight feather.
Finally, 5 mL of blood from the brachial or medial
metatarsal vein was collected from every individual and preserved in ethanol 96% until molecular
analyses were performed, that is, telomere length
determined (see details in Determination of telomere length below).
MATERIALS AND METHODS
Study area, bird tagging, and sampling
Our study was conducted on the northwestern
Patagonia of Argentina and Chile (Fig. 1). The
western part includes the Andes mountains where
terrain is steep and dominated by the Valdivian
Forest. Toward the east, there is a transitional area
(ecotone) followed by the Patagonian steppe
where a less steep relief and vegetation dominated
by grasses and shrub predominates. Weather is
characterized by a mean annual precipitation that
declines from ca. 4000 mm on the west to ca.
500 mm on the east and is largely concentrated
during autumn and winter (March to August).
In this area, Andean condors eat introduced
herbivores, mainly livestock (Lambertucci et al.
2009). Larger abundances of those herbivores are
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Spatial analyses
Our analyses included individual movement
data from a six-month period (spring–autumn
seasons from the Southern Hemisphere). From a
total of 49,022 GPS locations, we computed fixed
kernel density estimators for each individual and
defined the home-range sizes as the areas encompassed within 95% isopleths using ABODE (beta
v5) tool (Laver 2005) for ArcGIS 9.3 (ESRI Inc.,
Redlands, California, USA; see Lambertucci et al.
2014). We used a least-squares cross-validation
method (Seaman and Powell 1996) to select the
smoothing parameter (h). We estimated the daily
distance (km) flown by a condor by first summing
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the straight-line distance between consecutive
locations along a day. Then, for each bird, we estimated the mean value of daily distance as the
average of the sum of the straight-line distance
between each pair of sequential fixes along a day,
for all monitoring days. We used the steppe,
which concentrates the highest livestock and other
large herbivores density that currently represents
the main food source for condors in Patagonia to
delimit the foraging area (see Lambertucci et al.
2009). In addition, we delineated breeding areas
as places with the highest concentration of locations (coordinates) in an area of 2 km radius, with
most later corroborated in the field.
target samples when compared with a reference
sample. qPCR assay measures both terminal and
interstitial telomeric repeats (ITSs) (Nakagawa
et al. 2004). Although ITSs do not vary with age
(Delany et al. 2003), substantial variation between
species as well as between individuals of the same
species has been reported (Foote et al. 2013). The
inclusion of ITSs in telomere-length estimations
always underestimates telomere length because
most ITSs are shorter than most telomeres (Foote
et al. 2013). However, it is so far unclear whether
or not this variation is problematic, since it
depends on the extent of ITSs in the study species. Unfortunately, the extent to which ITSs are
present and vary among individual condors, as
for most bird species, is completely unknown.
Nonetheless, within-species estimates of telomere length obtained through different methods that avoid or include ITSs in calculations are
positively and significantly correlated (Criscuolo
et al. 2009, Foote et al. 2013). Consistent relationships between telomere length measured
through different methods and fitness components have been reported (Pauliny et al. 2006,
Bize et al. 2009, Salomons et al. 2009, Foote et al.
2011, Barrett et al. 2013) which suggest that the
potential negative effects of both intra- and interspecific variations in ITSs on telomere-length
estimation do not necessarily confound those
connections found between telomere dynamics
and life-history traits. Consequently, although
our approach presents some drawbacks, such
as the generalized underestimation of telomere
length (Foote et al. 2013) and the likelihood to
not detecting slight differences that may exist
between groups (see Young et al. 2013), qPCR
assay is an appropriate method for studies aimed
at investigating intraspecific variation in relative
telomere length and erosion rate (Cawthon 2002,
Criscuolo et al. 2009, Reichert et al. 2014, Badás
et al. 2015).
We used glyceraldehyde-3-phosphate dehydrogenase (GAPDH) as a control single copy
gene, which was amplified using the forward
and reverse primers GAPDH-F (5′-AACCAG
CCAAGTACGATGACAT-3′) and GAPDH-R
(5′-CCATCAGCAGCAGCCTTCA-3′). We used
the telomere forward and reverse primers: Tel1b
(5′- CGGTTTGTTTGGGTTTGGGTTTGGGTTT
GGGTTTGGGTT-3′) and Tel2b (5′-GGCTTGCC
TTACCCTTACCCTTACCCTTACCCTTACCCT
Determination of telomere length
We used DNA extracted from erythrocytes to
evaluate telomere length. In birds, nucleated
erythrocytes have a high turnover rate, leading
to the expectation of telomere-length loss in these
blood cells over time (Nussey et al. 2014). Due to
their high turnover rate, blood cell telomere
lengths may shorten at a greater rate than telomere lengths in other tissues (e.g., leukocytes,
skin), which may give rise to significant withinindividual differences in telomere length among
tissues (Friedrich et al. 2000). In long-lived birds,
as the Andean condor, a large telomere loss with
chronological age seems not to be the rule
(Haussmann et al. 2003, Hall et al. 2004, Foote
et al. 2011). Indeed, telomere loss occurs more
rapidly in the early stages of life, and once an
individual reaches the adult status, the shortening rate is much slower (Barrett and Richardson
2011). Therefore, although the biological age of
each free-ranging condor was unknown, the fact
that all samples came from the same tissue
(whole blood) and all sampled birds were adult
breeders facilitated the comparison of telomere
length among them (Nussey et al. 2014).
We estimated telomere length by a quantitative PCR assay (qPCR) (Cawthon 2002) adapted
to measure relative telomere length in birds
(Criscuolo et al. 2009). qPCR provides an estimate of the amount of telomere sequence present
in the sample relative to the amount of a specified
non-telomeric reference sequence that is autosomal and non-variable in copy number (Cawthon
2002). We measured relative telomere length by
determining the ratio of telomere repeat copy
number to single control gene copy number in
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GANGOSO ET AL.
-3′). We carried out telomere and GAPDH realtime amplifications on two different plates. Each
reaction for the telomere (or GAPDH) plates
was performed using 20 ng/μL of DNA per well
with sets of primers Tel1b/Tel2b (or GAPDH-F/
GAPDH-R), each used at a concentration of
200 nM/200 nM, in a final volume of 20 μL containing 10 μL of Fast Start Universal SYBR Green
Brilliant Master (Roche, Diagnostics GmbH,
Mannheim, Germany). PCR conditions for the
telomere portion of the assay were 10 min at 95°C
followed by 30 cycles of 1 min at 56°C and 1 min
at 95°C, while conditions for the GAPDH portion
of the assay were 10 min at 95°C followed by 40
cycles of 1 min at 60°C and 1 min at 95°C.
We performed PCRs in a Light Cycler 480 RTPCR System (Roche). To test the efficiency of each
PCR, a standard curve was produced in every plate
by serially diluting one sample (160, 40, 10, 2.5, and
0.66 ng/μL of DNA per well) and by running it in
triplicate. The slopes of the standard curves ranged
from −3.01 to −3.67 with a R2 value between 0.98
and 1.00; efficiencies ranged from 87% and 114%
(mean efficiencytelomere = 95.5%; mean efficiencyGAPDH = 106.5%), thus falling within the acceptable range of efficiencies for qPCR assays (see
review in Horn et al. 2010). The coefficients of variation (CV) of the quantification cycle (Cq) values
for the GAPDH and telomere amplifications were
<5% in all samples following Criscuolo et al. (2009).
Sample level repeatability within and across plates
was ≥97.9% for telomere and GAPDH RT-PCR. To
be able to compare measurements among plates,
one individual was used as a reference and run in
triplicate on every plate. We then calculated the
threshold Ct of this reference sample for each plate;
the Ct of a DNA sample is the fractional number of
PCR cycles to which the sample must be subjected
in order to accumulate enough products to cross
a set threshold of magnitude of fluorescent signal.
All other samples were run in duplicate on the
plates, and mean values per plate were used to calculate relative ratios of target individual relative to
the reference individual. qPCRs were performed
a minimum of two times (i.e., two telomere and
two GAPDH plates) for each sample. Mean intraand interplate CV were 0.71% and 2.32%, respectively, for the Ct values of GAPDH assays, while
intra- and interplate CV were 0.41% and 0.97%,
respectively, for the Ct values of telomere assays.
To take into account the variation of efficiencies
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between telomere and GAPDH amplifications, we
calculated relative telomere length by transforming quantification cycle values (Ct) into normalized
relative quantities (NRQs) following Hellemans
et al. (2007).
Determination of CORTf concentration
We extracted CORT from each covert feather
using a methanol-based extraction technique following the protocol described in Bortolotti et al.
(2008) with some modifications. We used half of
the feather (cutting the feather longitudinally and
including the rachis) for hormone analyses. The
length of each feather was first weighed and measured excluding the calamus, which was discarded. We then cut each feather into pieces of
less than 5 mm2 and placed in a glass vial with
10 mL of methanol (HPLC grade; VWR
International, Mississauga, Ontario, Canada). The
capped vials were sonicated in a water bath at
room temperature for 30 min, followed by incubation at 50°C overnight in a shaking water bath.
The methanol containing the hormones was separated from the feather bits using vacuum filtration, washing the vial and feather remains with
an additional 10 mL of methanol, and adding it to
the original methanol extract. When the evaporation of the samples was completed in the fume
hood, the extract residues were reconstituted
with 1200 μL of phosphate buffer (PBS; 0.05 M,
pH 7.6) and frozen at −20°C until CORT was measured by radioimmunoassay (RIA). Since it is not
possible to incorporate tritium into the growing
feathers, we evaluated what percentage of CORT
extracted from the feather and contained in the
methanol is recovered by spiking the feathers
with a known amount of H3-CORT. Antiserum
and purified CORT for standards were purchased
from Sigma Chemicals, Oakville, Canada (AntiCorticosterone product no. C8784, lot no.
090M4752; purified CORT product no. C-2505, lot
no. 22K1439). All samples were extracted in one
single batch and assessed the recovery efficiency
of the methanol extraction by including feather
samples spiked with approximately 5000 DPM of
3H-CORT (Amersham Bioscience, Baie d'Urfe,
Quebec). Ninety-one percentage of the radioactivity was recoverable in the reconstituted samples. CORTf concentration (pg/mm) was
determined using RIA as in previous studies
(Bortolotti et al. 2008). Antiserum and purified
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GANGOSO ET AL.
CORT for standards were purchased from Sigma
Chemicals. Samples were duplicated and randomly measured in the RIA. A parallel relationship was found between serial dilutions of
reconstituted feather extracts and the standard
curve. Assay variability was determined as the
percentage of CV resulting from six samples of
internal standard. Samples were measured in one
single RIA with CV of 6% and limit of detection
(ED 80) of 24.55 pg/assay tube. We corrected data
by length because CORT deposition in growing
feathers is hypothesized to be time dependent
(see Bortolotti et al. 2008, 2009, Bortolotti 2010,
Jenni-Eiermann et al. 2015).
(2004), we computed the Akaike weights (AICcω)
to assess the mass of evidence in favor of each
candidate model.
RESULTS
Andean condor breeding sites were located from
the west side of the Andean mountains (Chile) to
the east part (Argentina), and even occurred inside
the steppe in some cases, thus ranging from zero to
83 km (linear distances) from feeding areas (Fig. 1).
The number of days we monitored individuals
with a GPS device ranged from 65 to 174, with
variation due to the device type (see Materials and
methods), the performance of the device, as well as
the date of deployment. Likewise, the number of
fixes per individual varied from 899 to 6394. Birds
moved between the breeding and feeding areas an
average of 83 km/d (range 46–152 km, skewness = 0.99, kurtosis = 3.45, median = 54.54), covering an average home-range size of 7368 km2 (kernel
95%, range 745–26,264 km2).
Movement patterns differed between sexes.
Thus, home ranges and maximum daily distances (but not mean distances) were significantly larger in males than in females (Table 1).
A detailed inspection of the data indicated that,
in general, males performed larger mean daily
distances than females, yet with highly variable
values that also included very short distances,
which overlapped with those of females in some
cases. These patterns might explain the lack of
statistical differences in mean distances travelled between sexes. Within each sex, the values
of these three variables were independent of the
longitude position of the nest site (Spearman correlations, P > 0.20 in all cases).
Average telomere length (NRQ) of males
(mean = 0.98 ± 0.18 standard error (SE) was longer than that of females (mean = 0.63 ± 0.19 SE),
yet not significantly (Mann–Wilcoxon χ2 = 2.19,
df = 1, P = 0.15). With regard to the variation in
telomere length (log-NRQ), our informationtheoretic approach yielded only one model with
ΔAICc < 2 (see Table 2). This model showed that
variation in telomere length was only explained
by the longitude coordinate of the nest site, which
represents the distance of the nest to the feeding
areas (longitude: estimate [est]: 0.74 ± 0.33 SE), the
sex (est: −101.12 ± 32.84 SE), plus the interaction
between the two variables (est: −1.41 ± 0.46 SE).
Statistical procedure
We analyzed variation in the response variables NRQ and CORTf by means of linear models. The response variables were log-normalized,
and multicollinearity between explanatory variables was assessed (VIF values <2 in all cases)
prior to performing models in R software v 3.1.0
(R Development Core Team 2014). In each case,
we included year, sex, home-range size (km2),
position (longitude coordinate) of each nest site,
and a body condition index (residuals from the
regression of body mass against wing length) as
explanatory variables. Because the longitude
coordinate was strongly correlated to the distance from the nest to the steppe (r = −0.981,
P < 0.001), it was clear that this variable, but not
the latitude, represents a good surrogate of distance from breeding to feeding areas. We
included the longitude coordinate instead of the
distance of the nest site to the feeding grounds in
our models because some nests are located inside
the steppe and, although they are located at variable distances from the feeding grounds, the distance values approach zero in all cases. We fitted
alternative models by including single variables
and also the two- and three-term additive combinations plus two-term interactions between the
different explanatory variables.
Model selection was made on the basis of the
Akaike’s information criterion (AICc) corrected
for small sample sizes to find the most parsimonious model (lowest AICc) and rank the remaining models (Burnham and Anderson 2002). Delta
AICc (ΔAICc) was calculated as the difference
in AICc between each model and the best model
in the set. Following Burnham and Anderson
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Table 1. Summary statistics and comparison between sexes of the explanatory variables defining movement
patterns of GPS-tagged individual Andean condors.
Variable
Home range km2
Maximum distance km
Mean distance km
Males
Females
Sample size
9
11
Mann–Whitney U test
Z
P-value
Maximum
Minimum
Mean
SD
Maximum
Minimum
Mean
SD
Maximum
Minimum
Mean
SD
53,254
10,580
25,230
16,371.87
349.5
238.3
292.3
29.5
152.3
46.6
90.9
32.2
27,231.8
2670.7
8964.3
6852.9
310.8
197.2
248.3
36.1
117.8
53.1
76.7
21.3
−2.925
0.002
−2.469
0.012
−0.912
0.370
Note: Home ranges were computed as fixed kernel density estimators, with sizes defined as the areas encompassed within
95% isopleths.
None of the 95% confidence intervals (CI) for the
parameter estimates included zero (sex: −170.73,
−31.51; distance to the feeding areas: 0.03, 1.44;
sex × distance: −2.39, −0.44), indicating that all
these predictors significantly influenced variation in telomere length. As predicted, results for
this model indicate that females showed shorter
telomeres than males. In addition, variation in
telomere length was strongly related to the location of the nest site (longitude), but in opposite
directions for both sexes and with a stronger
effect (steeper slope) in the case of males (Fig. 2).
Thus, males breeding toward the Pacific coastal
areas of Andean mountains showed longer telomeres than those breeding close to the steppe,
while females breeding near to the coast showed
shorter telomeres than those breeding in the
steppe.
Levels of CORTf were negatively correlated
with NRQ values (Spearman ρ = −0.48, P = 0.03),
with those individuals showing higher CORTf
levels having shorter telomeres. When analyzing
sexes separately, this pattern was only statistically
significant for females (r = −0.69, P = 0.02), but not
for males (r = −0.45, P = 0.22). Again, we predicted
a negative association between CORTf and distance from the nest site to the feeding grounds
and foraging movement patterns. However, variation in log-CORTf levels was mainly explained
by sex. We obtained three models with ΔAICc < 2
(Table 2). The first model included only sex (est:
−0.31 ± 0.10 SE) with females showing higher
v www.esajournals.org
CORTf levels than males (Fig. 3). This model
received much higher support (double Akaike
weight) than the other two (see Table 2). Also,
the 95% CI for the parameter estimates of this
model did not include zero (−0.53, −0.09). The
second model included sex (est: −0.30 ± 0.10
SE) and year (est: −0.13 ± 0.10 SE) with females
exhibiting higher levels than males and slightly,
yet not significant, higher CORTf values in 2010
than in 2011. In fact, the 95% CI did not include
zero for sex (−0.51, −0.08), but they did for year
(−0.34, 0.09) indicating a very low influence of
this latter variable. The third model included
sex (est: −0.32 ± 0.98 SE) and body condition
(est: −8.27 × 10−05 ± 7.38 × 10−05 SE). Likewise,
the 95% CI did not include zero for sex (−0.53,
−9.50 × 10−02), but they did for body condition
(−0.00, 7.30 × 10−05). Therefore, the most important variable explaining variation in feather corticosterone was the sex and thus the model with
only this variable the best.
DISCUSSION
To our knowledge, this is the first study reporting a spatial structure of telomere length in a
wild long-lived vertebrate population. This pattern was, in addition, sex-specific; male condors
breeding within the Andean mountain range and
far from steppe feeding areas had longer telomeres, while females showed the opposite pattern. Although our cross-sectional approach only
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October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
Table 2. AICc-based model selection to assess the
effect of individual and environmental variables on
telomere length (logNRQ) and feather corticosterone (logCORTf) values.
Model
Telomere length
Sex × long
Sex
Intercept
Year
HR
Sex + year
Sex × BCI
Long
Sex + BCI
Sex + HR
Sex + long
BCI
Sex × HR
Sex × year
Sex + year + long
Sex + year + BCI
Sex + year + HR
Year × long
Year × HR
Year + HR + long
Year × BCI
Year + HR + BCI
HR × long
HR + long + BCI
HR × BCI
Long × BCI
Feather corticosterone
Sex
Sex + year
Sex + BCI
Sex + HR
Sex + long
Sex + year + HR
Sex × BCI
Sex + year + BCI
Sex × long
Sex + year + long
Sex × year
Intercept
Sex × HR
Year
BC
HR
Long
Year × long
Year + HR + BCI
Year + HR + long
HR × BCI
Year × BCI
Year × HR
AICc
ΔAICc
AICcω
R2 adj
20.47
23.04
23.53
25.03
25.06
25.11
25.32
25.92
26.17
26.18
26.20
26.30
27.85
28.16
28.56
28.70
28.73
29.05
29.73
30.26
30.55
30.94
31.37
31.47
31.51
32.59
0
2.57
3.06
4.56
4.59
4.64
4.85
5.45
5.70
5.71
5.73
5.83
7.38
7.69
8.09
8.23
8.26
8.58
9.26
9.79
10.08
10.47
10.90
11.00
11.04
12.12
1.00
0.28
0.22
0.10
0.10
0.10
0.09
0.07
0.06
0.06
0.06
0.05
0.02
0.02
0.02
0.02
0.02
0.01
0.01
0.01
0.01
0.01
0.00
0.00
0.00
0.00
0.37
0.10
3.11
4.49
4.85
5.33
5.67
6.41
6.62
7.41
7.78
7.98
8.05
8.51
8.63
9.49
10.37
10.57
11.20
15.20
15.29
15.48
15.52
15.70
15.88
0
1.38
1.74
2.22
2.56
3.30
3.51
4.30
4.67
4.87
4.94
5.40
5.52
6.38
7.26
7.46
8.09
12.09
12.18
12.37
12.41
12.59
12.77
1.00
0.50
0.42
0.33
0.28
0.19
0.17
0.12
0.10
0.09
0.08
0.07
0.06
0.04
0.03
0.02
0.02
0.00
0.00
0.00
0.00
0.00
0.00
v www.esajournals.org
Table 2.
Continued.
Model
AICc
ΔAICc
AICcω
R2 adj
HR + long + BCI
HR × long
Long × BCI
15.90
16.66
16.84
12.79
13.55
13.73
0.00
0.00
0.00
−0.06
−0.11
−0.12
Notes: Akaike’s second-order corrected information criterion (AICc) values, AICc differences (ΔAICc) with the highest
ranked model (i.e., the one with the lowest AICc), Akaike
weights (AICcω), and adjusted R2 are shown. Explanatory
variables: sex, year; long, longitude coordinate; HR, home
range; BCI, body condition index. The symbol “×” denotes the
independent effect of two variables plus their interaction.
0.01
0.01
0.10
0.20
−0.03
0.05
0.05
0.05
−0.05
0.09
0.07
0.05
0.05
0.05
0.03
−0.00
−0.03
−0.04
−0.07
−0.09
−0.09
−0.10
−0.16
shows a fixed picture, the negative relationship
between nest site longitude and telomere length
is extremely suggestive and leads to a suite of
alternative interpretations.
Telomeres have been usually related with the
biology of aging, and hence, they have been
shown to shorten with age in many vertebrate
species (Haussmann et al. 2003, Müezzinler
et al. 2013). Accordingly, our results may imply
that males breeding toward the Pacific coast are
younger (having longer telomere length) than
those breeding close to the steppe, while females
showed the opposite, yet less evident, pattern.
The trend found within males agrees with the
largely known evidence that high quality, often
older, raptors usually breed close to feeding
areas (e.g., Sergio et al. 2007). The fact that the
known highest breeding densities of Andean
0.30
0.32
0.31
0.29
0.28
0.34
0.33
0.30
0.29
0.28
0.28
0.26
0.04
−0.01
−0.02
−0.05
−0.03
−0.03
−0.04
−0.04
−0.05
−0.06
Fig. 2. Relationship between the telomere length
(normalized relative quantity [NRQ]) and the
longitude coordinate of the nest site for female (solid
line) and male (dashed line) Andean condors. Condor
drawings were modified from Sanchez et al. (1998).
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October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
the steppe showed patterns of north–south foraging movements that covered the same or even
larger areas than those covered in the east–west
axis by the condors breeding in the Pacific coast,
although the latter should necessarily face higher
physiological costs when crossing the cordillera.
Following this reasoning, the question arises as
to why female Andean condors do not follow a
similar spatial structure of telomere length to that
of males, but the opposite? This can be motivated
by intersexual foraging niche differentiation and
social dominance relationships, ultimately promoting human-induced female-biased mortality
near the foraging steppe areas. During the last few
decades, the Patagonian steppe has experienced
an increased anthropization and, consequently,
condors have been increasingly subject to direct
and indirect persecution through shooting and
poisoning, as well as casualties involving manmade structures (Lambertucci 2007, Lambertucci
et al. 2011). Donázar et al. (1999) found that, due
to intraspecific competition and social hierarchy,
condors segregate at mesohabitat scale within
the steppe, with adult females being relegated to
scavenge in flatter and more humanized areas,
while adult males forage mainly on the steep
and safer slopes. Therefore, the observed structure of telomere length might be the outcome of
asymmetric mortality events and higher turnover rates of those females breeding in this area,
where new (and young) females would recruit
into the breeding population. Indeed, sex-biased
mortality toward female condors determines a
skewed sex ratio in the adult fraction of the studied population with important consequences in
its long-term viability (Lambertucci et al. 2012).
Telomere length might alternatively be reflecting biological, but not chronological age (Aviv
2002, Bize et al. 2009). Telomere damage is associated with internal metabolic processes, as
well as external factors, causing oxidative stress
(Kotrschal et al. 2007, Houben et al. 2008). Thus,
the rate of telomere loss may be a useful biomarker of chronic oxidative stress (Houben et al.
2008, Young et al. 2015). Our results showed that
female Andean condors had shorter telomeres
than males (except at the eastern extreme distribution area), which would be reflecting that
females, in general, experience higher levels of
oxidative stress. Apart from potential genetic and
endocrine causes (Horn et al. 2011), sex-specific
Fig. 3. Feather corticosterone (CORTf) levels (pg/
mm) of male and female Andean condors. The line
within boxes indicates the median, the edges of the
boxes indicate the first (Q1) and third (Q3) quartiles,
and the whiskers extend 1.5 times the interquartile
range.
condors are located near the steppe, in the eastern slopes of the Cordillera (S. Lambertucci,
unpublished data), further supports that this area
is of high quality. It seems clear that breeding in
central or western slopes of the cordillera, and
far from the steppe main foraging area, should
impose important constraints linked to the necessity of crossing important topographical barriers
and facing inclement weather (annual rainfall is
up to 4000 mm), especially to a large-sized bird
with very limited capacity for flapping flight
(Pennycuick and Scholey 1984). These circumstances would decrease the quality of the mountainous areas for breeding, thus favoring their
occupation by young and subordinate individuals. Nonetheless, it is surprising that those variables describing the daily range of movements
performed by individual condors are unrelated
to the variability in telomere length. However, an
examination of the intrasexual variability of these
movement patterns revealed that they were independent from the position (longitude coordinate)
of the nest site relative to the foraging areas. In
other words, condors breeding in areas far from
the steppe foraging grounds do not perform longer daily movements than those breeding close.
Actually, some Andean condors breeding within
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October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
telomere loss rates have been proposed to be
driven by different environmental conditions,
physiological stress, and reproductive history
experienced by each sex and not by chronological age (Pauliny et al. 2006, Reed et al. 2008,
Young et al. 2013). The pattern of telomere length
found within females agrees with that predicted.
Therefore, females breeding farther from the
feeding grounds would experience higher physiological costs associated with longer movements
and adverse weather conditions than those
breeding near this area. Furthermore, the subordinate status that yields to frequent intraspecific
aggressions, the use of lower quality habitats,
and lower access to food resources would result
in increased loss of telomere lengths in females.
Accordingly, female condors had much higher
levels of CORTf than males, regardless of nest
location. Circulating CORT levels play a role in
the regulation of parental care and have been
positively correlated with foraging effort and
provisioning rate in birds (Angelier et al. 2008,
Bonier et al. 2011). However, in condors, both
sexes share parental care, although we found
they perform dissimilar foraging trips. Homerange sizes of male condors, as well as maximum daily distances, were larger than those of
females. Carrete et al. (2013) reported that the
Egyptian vulture (Neophron percnopterus), also a
scavenger, showed higher levels of CORTf and
larger home-range sizes when overwintering in
Africa as compared to levels and home-range
sizes measured during breeding in Europe. In
addition, females had the largest home ranges
at wintering quarters and higher CORTf than
males (Carrete et al. 2013). We found, however,
that female condors had comparatively smaller
home ranges and higher CORTf than males. In
a scenario of social conflict and competition for
resources, concentrations of CORT will vary
depending on how physiologically costly is to
acquire and maintain dominant and subordinate
status (see review in Goymann and Wingfield
2004). Subordinate females could elevate circulating CORT levels in response to physical and
physiological threats from more dominant males
(Abbott et al. 2003). Given that we measured the
integrated amount of CORTf, increased levels
in females could be due to higher baseline concentrations and/or higher frequency of stressors.
The high CORTf levels found in females may
v www.esajournals.org
thus be mirroring recurrent stressful episodes,
likely associated with social dominance hierarchy (Goymann and Wingfield 2004). In contrast, male condors would exploit larger areas in
search of food, and the increased physiological
costs of these long movements would be counterbalanced by a reduction in agonistic interactions
through avoidance of intraspecific encounters at
carcasses.
Alternatively, this pattern may be related to
sexually dimorphic constraints and resolutions
in trade-off associated with size differences
between the sexes. Comparatively small females
may have higher metabolic demands than males
(Glazier 2008), and thus, higher CORTf levels as
a by-product of increased mobilization of metabolic fuel during breeding and increased foraging
effort needed to maintain homeostatic balance
(McEwen and Wingfield 2003). Both chronic
stress and elevated CORT are associated with
increased oxidative stress and short telomeres
(Epel et al. 2004), a pattern that precisely matches
with the general trend of higher CORTf levels
and shorter telomere length we found in females
as compared to males. Interestingly, withinspecies negative associations between body size
and telomere length have been recently shown in
wild house sparrows (Passer domesticus) (Ringsby
et al. 2015) and proposed as a feasible mechanism
underlying the apparent trade-off between body
size and longevity often found within vertebrate
species (e.g., Kraus et al. 2013). Our results, however, seem to contradict this trend. Male Andean
condors are larger than females, while showing
longer telomeres. It is important to note that
selective pressures could act in a reversed manner in this species as compared to other raptors,
mainly due to the atypical direct sexual size
dimorphism. Although we do not know how
the long-term costs associated with larger size
are incurred, these could be linked to changes
in telomere dynamics. These changes either as
a correlated trait or a consequence of larger size
could reduce potential longevity of larger individuals (Ringsby et al. 2015). Thus, our results
would imply that older males, even if they are of
the same chronological age than females, could
have died already. Alternatively, the long-lasting
stressful conditions experienced by females
could mask the actual pattern of telomere length
attributable to their lower body size. Therefore,
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October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
females would invest more in traits that increase
immediate survival, such as circulating CORT,
even if they come at a cost to traits associated
with longevity, such as telomere length.
Studies aimed at exploring connections
between physiological stress and cellular aging
in non-human or model organisms are still
scarce. Haussmann et al. (2011) reported that
embryonic exposure to experimentally increased
CORT resulted in higher levels of reactive oxygen
metabolites and an overrepresentation of short
telomeres compared with control birds, thus hastening aging and ultimately increasing mortality.
Therefore, telomere length can be viewed as an
integrative measure of both telomere dynamics
and glucocorticoid-induced oxidative stress, and
all are thought to influence longevity (Haussmann
and Marchetto 2010, Haussmann et al. 2011).
Furthermore, recent evidence suggests that exposure to stressors experienced by the parental generation can have long-term, cross-generational
effects for offspring health, a relationship mediated in part by telomere dynamics (see review
in Haussmann and Heidinger 2015). The conserved nature of both the glucocorticoid stress
response and telomeres suggests that the links
found between exposure to stressors and telomere
dynamics in a few species, mostly humans and
model organisms, are likely to occur in all vertebrates (Haussmann and Heidinger 2015).
Our study highlights that parallel variations in
telomere length and concentrations of CORT may
appear in a sexually dimorphic species with a
highly despotic social system and divergent sexspecific foraging strategies. Sexual differences in
the optimal resolution of trade-offs associated
with food acquisition and the social environment
might underlie the fact that populations are spatially structured from a telomere-length perspective, which has never been described before. This
novel finding gives rise to stimulating questions
for evolutionary and ecological studies, such as
the potential links between environmental conditions, physiological-oxidative stress, and aging,
and how they impact performance and lifehistory trajectories of long-lived organisms.
molecular analysis at the Laboratory of Ecophysiology EBD-CSIC, Seville, Spain. This study was
supported by Projects FBBVA (BIOCON 08-126),
ANPCyT-PICT 0725 (2014), CONICET PIP 0095, and
CGL2012-40013-C02-01-02 and CGL2015-66966-C2-12-R MINECO/FEDER EU. During the writing of this
manuscript, LG was supported by the Excellence
Project from Junta de Andalucía (RNM-6400). The Dirección de Fauna Silvestre from Argentina provided
necessary permissions RN (No. 132.730-DF-2010-2012).
LITERATURE CITED
Abbott, D. H., et al. 2003. Are subordinates always
stressed? A comparative analysis of rank differences in cortisol levels among primates. Hormones
and Behavior 43:67–82.
Amélineau, F., C. Péron, A. Lescroël, M. Authier,
P. Provost, and D. Grémillet. 2014. Windscape and
tortuosity shape the flight costs of northern gannets. Journal of Experimental Biology 217:876–885.
Andersson, M. B. 1994. Sexual selection. Princeton
University Press, Princeton, New Jersey, USA.
Angelier, F., C. A. Bost, M. Giraudeau, G. Bouteloup,
S. Dano, and O. Chastel. 2008. Corticosterone and
foraging behavior in a diving seabird: the Adélie
penguin, Pygoscelis adeliae. General and Comparative Endocrinology 156:134–144.
Armanios, M., and E. H. Blackburn. 2012. The telomere
syndromes. Nature Reviews Genetics 13:693–704.
Aviv, A. 2002. Chronology versus biology: telomeres,
essential hypertension, and vascular aging. Hypertension 40:229–232.
Badás, E. P., J. Martínez, J. Rivero de Aguilar Cachafeiro, F. Miranda, J. Figuerola, and S. Merino. 2015.
Ageing and reproduction: Antioxidant supplementation alleviates telomere loss in wild birds.
Journal of Evolutionary Biology 28:896–905.
Barrett, E. L. B., T. A. Burke, M. Hammers, J. Komdeur,
and D. S. Richardson. 2013. Telomere length and
dynamics predict mortality in a wild longitudinal
study. Molecular Ecology 22:249–259.
Barrett, E. L. B., and D. S. Richardson. 2011. Sex differences in telomeres and lifespan. Aging Cell 10:913–921.
Bize, P., F. Criscuolo, N. B. Metcalfe, L. Nasir, and
P. Monaghan. 2009. Telomere dynamics rather than
age predict life expectancy in the wild. Proceedings
of the Royal Society of London B: Biological Sciences 276:1679–1683.
Bonduriansky, R., A. Maklakov, F. Zajitschek, and
R. Brooks. 2008. Sexual selection, sexual conflict
and the evolution of ageing and life span. Functional Ecology 22:443–453.
Bonier, F., I. T. Moore, and R. J. Robertson. 2011. The
stress of parenthood? Increased glucocorticoids in
ACKNOWLEDGMENTS
We thank J. Figuerola for discussions on early drafts
of the manuscript. F. Miranda performed the
v www.esajournals.org
12
October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
Epel, E. S., E. H. Blackburn, J. Lin, F. S. Dhabhar, N. E.
Adler, J. D. Morrow, and R. M. Cawthon. 2004.
Accelerated telomere shortening in response to
life stress. Proceedings of the National Academy of
Sciences USA 101:17312–17315.
Fairbairn, D. J., W. U. Blanckenhorn, and T. Székely.
2007. Sex, size, and gender roles: evolutionary
studies of sexual size dimorphism. Volume 266.
Oxford University Press, Oxford, UK.
Fairhurst, G. D., T. A. Marchant, C. Soos, K. L. Machin,
and R. G. Clark. 2013. Experimental relationships
between levels of corticosterone in plasma and
feathers in a free-living bird. Journal of Experimental Biology 216:4071–4081.
Foote, C. G., F. Daunt, J. Gonzalez-Solis, L. Nasir, R. A.
Phillips, and P. Monaghan. 2011. Individual state
and survival prospects: age, sex, and telomere
length in a long-lived seabird. Behavioral Ecology
22:156–161.
Foote, C. G., D. Vleck, and C. M. Vleck. 2013. Extent
and variability of interstitial telomeric sequences
and their effects on estimates of telomere length.
Molecular Ecology Resources 13:417–428.
Friedrich, U., E. U. Griese, M. Schwab, P. Fritz, K. P.
Thon, and U. Klotz. 2000. Telomere length in different tissues of elderly patients. Mechanisms of
Ageing and Development 119:89–99.
Fritz, H., S. Said, and H. Weimerskirch. 2003. Scaledependent hierarchical adjustments of movement
patterns in a long-range foraging seabird. Proceedings of the Royal Society of London B: Biological
Sciences 270:1143–1148.
Glazier, D. S. 2008. Effects of metabolic level on the
body size scaling of metabolic rate in birds and
mammals. Proceedings of the Royal Society of London B: Biological Sciences 275:1405–1410.
Goymann, W., and J. C. Wingfield. 2004. Allostatic load, social status and stress hormones: the
costs of social status matter. Animal Behavior 67:
591–602.
Hall, M. E., L. Nasir, F. Daunt, E. A. Gault, J. P. Croxall, S. Wanless, and P. Monaghan. 2004. Telomere
loss in relation to age and early environment
in long-lived birds. Proceedings of the Royal
Society of London B: Biological Sciences 271:
1571–1576.
Haussmann, M. F., and B. J. Heidinger. 2015. Telomere
dynamics may link stress exposure and ageing
across generations. Biology Letters 11:20150396.
Haussmann, M. F., A. S. Longenecker, N. M. Marchetto, S. A. Juliano, and R. M. Bowden. 2011.
Embryonic exposure to corticosterone modifies the
juvenile stress response, oxidative stress and telomere length. Proceedings of the Royal Society of
London B: Biological Sciences 279:1447–1456.
birds with experimentally enlarged broods. Biology Letters 7:944–946.
Bortolotti, G. R. 2010. Flaws and pitfalls in the chemical analysis of feathers: bad news-good news for
avian chemoecology and toxicology. Ecological
Applications 20:1766–1774.
Bortolotti, G. R., T. A. Marchant, J. Blas, and S. Cabezas. 2009. Tracking stress: localisation, deposition
and stability of corticosterone in feathers. Journal
of Experimental Biology 212:1477–1482.
Bortolotti, G. R., T. A. Marchant, J. Blas, and T. German.
2008. Corticosterone in feathers is a long-term, integrated measure of avian stress physiology. Functional Ecology 22:494–500.
Burnham, K. P., and D. R. Anderson. 2002. Model
selection and multimodel inference: a practical
information-theoretic approach. Springer-Verlag
New York, Inc., New York, New York, USA.
Burnham, K. P., and D. R. Anderson. 2004. Multimodel
inference: understanding AIC and BIC in model selection. Sociological Methods & Research 33:261–304.
Carrete, M., G. R. Bortolotti, J. A. Sánchez-Zapata,
A. Delgado, A. Cortés-Avizanda, J. M. Grande, and
J. A. Donázar. 2013. Stressful conditions experienced by endangered Egyptian vultures on African
wintering areas. Animal Conservation 16:353–358.
Cawthon, R. M. 2002. Telomere measurement by quantitative PCR. Nucleic Acids Research 30:e47.
Costantini, D., V. Marasco, and A. P. Moller. 2011.
A meta-analysis of glucocorticoids as modulators
of oxidative stress in vertebrates. Journal of Comparative Physiology B 181:447–456.
Criscuolo, F., P. Bize, L. Nasir, N. B. Metcalfe, C. G.
Foote, K. Griffiths, E. A. Gault, and P. Monaghan.
2009. Real-time quantitative PCR assay for measurement of avian telomeres. Journal of Avian Biology 40:342–347.
Delany, M. E., L. M. Daniels, S. E. Swanberg, and H. A.
Taylor. 2003. Telomeres in the chicken: genome
stability and chromosome ends. Poultry Science
82:917–926.
del Hoyo, J., A. Elliott, and J. Sargatal. 1994. Handbook
of the birds of the world. Vol. 2: new world vultures
to guineafowl. Lynx Edicions, Barcelona, Spain.
Donázar, J. A., A. Travaini, O. Ceballos, A. Rodríguez,
M. Delibes, and F. Hiraldo. 1999. Effects of sexassociated competitive asymmetries on foraging
group structure and despotic distribution in Andean condors. Behavioral Ecology and Sociobiology
45:55–65.
Duriez, O., A. Kato, C. Tromp, G. Dell’Omo, A. L. Vyssotski, F. Sarrazin, and Y. Ropert-Coudert. 2014.
How cheap is soaring flight in raptors? A preliminary investigation in freely-flying vultures. PLoS
ONE 9:e84887.
v www.esajournals.org
13
October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
Andean condor: ecological replacement of native
fauna by exotic species. Animal Conservation
12:338–345.
Landys, M. M., M. Ramenofsky, and J. C. Wingfield.
2006. Actions of glucocorticoids at a seasonal baseline as compared to stress-related levels in the
regulation of periodic life processes. General and
Comparative Endocrinology 148:132–149.
Laver, P. N. 2005. Abode Home Range Tool for ArcGIS.
ABODE beta v.4.
Lewis, S., S. Benvenuti, L. Dall-Antonia, R. Griffiths,
L. Money, T. N. Sherratt, S. Wanless, and K. C.
Hamer. 2002. Sex-specific foraging behaviour in a
monomorphic seabird. Proceedings of the Royal
Society of London B: Biological Sciences 269:
1687–1693.
McEwen, B. S., and J. C. Wingfield. 2003. The concept
of allostasis in biology and biomedicine. Hormones
and Behavior 43:2–15.
Müezzinler, A., A. K. Zeineddine, and H. Brenner.
2013. A systematic review of leukocyte telomere
length and age in adults. Ageing Research Reviews
12:509–519.
Nakagawa, S., N. J. Gemmell, and T. Burke. 2004. Measuring vertebrate telomeres: applications and limitations. Molecular Ecology 13:2523–2533.
Newton, I. 1979. Population ecology of raptors. Poyser,
Berkhamsted, UK.
Norberg, U. M. 1990. Vertebrate flight: mechanics,
physiology, morphology, ecology and evolution.
Volume 27. Springer-Verlag Berlin, Heidelberg,
Germany.
Nussey, D. H., et al. 2014. Measuring telomere length
and telomere dynamics in evolutionary biology
and ecology. Methods in Ecology and Evolution
5:299–310.
Pauliny, A., R. H. Wagner, J. Augustin, T. Szép, and
D. Blomqvist. 2006. Age independent telomere
length predicts fitness in two bird species. Molecular Ecology 15:1681–1687.
Pennycuick, C. J., and K. D. Scholey. 1984. Flight
behavior of Andean condors Vultur gryphys and
turkey vultures Cathartes aura around the Paracas
Peninsula, Peru. Ibis 126:253–256.
Promislow, D. 2003. Mate choice, sexual conflict, and
evolution of senescence. Behavior Genetics 33:
191–201.
R Development Core Team. 2014. R: a language and
environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria.
http://www.R-project.org/
Reed, T. E., L. E. Kruuk, S. Wanless, M. Frederiksen,
E. J. Cunningham, and M. P. Harris. 2008. Reproductive senescence in a long-lived seabird: Rates of
decline in late-life performance are associated with
Haussmann, M. F., and N. M. Marchetto. 2010. Telomeres: linking stress and survival, ecology and
evolution. Current Zoology 56:714–727.
Haussmann, M. F., D. W. Winkler, K. M. O’Reilly, C. E.
Huntington, I. C. T. Nisbet, and C. M. Vleck. 2003.
Telomeres shorten more slowly in long-lived birds
and mammals than in short-lived ones. Proceedings of the Royal Society of London B: Biological
Sciences 270:1387–1392.
Hellemans, J., G. Mortier, A. De Paepe, F. Speleman,
and J. Vandesompele. 2007. qBase relative quantification framework and software for management
and automated analysis of real-time quantitative
PCR data. Genome Biology 8:R19.
Horn, T., B. C. Robertson, and N. J. Gemmell. 2010. The
use of telomere length in ecology and evolutionary
biology. Heredity 105:497–506.
Horn, T., B. C. Robertson, M. Will, D. K. Eason, G. P.
Elliott, and N. J. Gemmell. 2011. Inheritance of telomere length in a bird. PLoS ONE 6:e17199.
Houben, J. M. J., H. J. J. Moonen, F. J. van Schooten,
and G. J. Hageman. 2008. Telomere length assessment: Biomarker of chronic oxidative stress? Free
Radical Biology & Medicine 44:235–246.
Jenni-Eiermann, S., F. Helfenstein, A. Vallat, G. Glauser, and L. Jenni. 2015. Corticosterone: effects on
feather quality and deposition into feathers. Methods in Ecology and Evolution 6:237–246.
Kotrschal, A., P. Ilmonen, and D. J. Penn. 2007. Stress
impacts telomere dynamics. Biology Letters 3:128–
130.
Kraus, C., S. Pavard, and D. E. Promislow. 2013. The
size–life span trade-off decomposed: Why large
dogs die young. American Naturalist 181:492–505.
Lambertucci, S. A. 2007. Biología y conservación del
Cóndor Andino (Vultur gryphus) en Argentina. El
Hornero 22:149–158.
Lambertucci, S. A., P. A. E. Alarcón, J. A. Sanchez-Zapata, G. Blanco, F. Hiraldo, and J. A. Donázar. 2014.
Apex scavenger movements call for transboundary conservation policies. Biological Conservation
170:145–150.
Lambertucci, S. A., M. Carrete, J. A. Donázar, and
F. Hiraldo. 2012. Large-scale age-dependent
skewed sex ratio in a sexually dimorphic avian
scavenger. PLoS ONE 7:e46347.
Lambertucci, S. A., J. A. Donázar, A. D. Huertas,
B. Jiménez, M. Sáez, J. A. Sanchez-Zapata, and
F. Hiraldo. 2011. Widening the problem of lead
poisoning to a South-American top scavenger:
lead concentrations in feathers of wild Andean
condors. Biological Conservation 144:1464–1471.
Lambertucci, S. A., A. Trejo, S. Di Martino, J. A. Sánchez-Zapata, J. A. Donázar, and F. Hiraldo. 2009.
Spatial and temporal patterns in the diet of the
v www.esajournals.org
14
October 2016 v Volume 7(10) v Article e01544
GANGOSO ET AL.
Shepard, E. L. C., and S. A. Lambertucci. 2013. From daily
movements to population distributions: Weather
affects competitive ability in a guild of soaring birds.
Journal of the Royal Society Interface 10:20130612.
Stauss, C., et al. 2012. Sex-specific foraging behaviour
in northern gannets Morus bassanus: incidence
and implications. Marine Ecology Progress Series
457:151–162.
von Zglinicki, T. 2002. Oxidative stress shortens telomeres. Trends in Biochemical Sciences 27:339–344.
Wearmouth, V. J., and D. W. Sims. 2008. Sexual segregation in marine fish, reptiles, birds and mammals:
behaviour patterns, mechanisms and conservation implications. Advances in Marine Biology 54:
107–170.
Weimerskirch, H., T. Guionnet, J. Martin, S. A. Shaffer,
and D. P. Costa. 2000. Fast and fuel efficient? Optimal use of wind by flying albatrosses. Proceedings of the Royal Society of London B: Biological
Sciences 267:1869–1874.
Weimerskirch, H., M. Le Corre, Y. Ropert-Coudert,
A. Kato, and F. Marsac. 2006. Sex-specific foraging behaviour in a seabird with reversed sexual
dimorphism: the red-footed booby. Oecologia 146:
681–691.
Young, R. C., A. S. Kitaysky, C. P. Barger, I. Dorresteijn,
M. Ito, and Y. Watanuki. 2015. Telomere length is
a strong predictor of foraging behavior in a longlived seabird. Ecosphere 6:1–26.
Young, R. C., A. S. Kitaysky, M. F. Haussmann, S. Descamps, R. Orben, K. H. Elliott, and A. J. Gaston.
2013. Age, sex, and telomere dynamics in a longlived seabird with male-biased parental care. PLoS
ONE 8:e74931.
Zakian, V. A. 1995. Telomeres: beginning to understand the end. Science 270:1601–1607.
varying costs of early reproduction. American Naturalist 171:E89–E101.
Reichert, S., A. Stier, S. Zahn, M. Arrivé, P. Bize, S. Massemin, and F. Criscuolo. 2014. Increased brood size
leads to persistent eroded telomeres. Frontiers in
Ecology and Evolution 2:9.
Ringsby, T. H., et al. 2015. On being the right size:
Increased body size is associated with reduced telomere length under natural conditions. Proceedings
of the Royal Society of London B: Biological Sciences 282:20152331. http://dx.doi.org/10.1098/rspb.
2015.2331
Ruxton, G. D., and D. C. Houston. 2004. Obligate vertebrate scavengers must be large soaring fliers.
Journal of Theoretical Biology 228:431–436.
Salomons, H. M., G. A. Mulder, L. van de Zande,
M. F. Haussmann, M. H. K. Linskens, and S. Verhulst. 2009. Telomere shortening and survival
in free-living corvids. Proceedings of the Royal Society of London B: Biological Sciences 276:
3157–3165.
Sanchez, O., M. A. Pineda, H. Benitez, B. González,
and H. Berlanga. 1998. Guía de identificación para
las aves y mamíferos silvestres de mayor comercio
en México protegidos por la C.I.T.E.S. Secretaria
de Medio Ambiente, Recursos Naturales y Pesca
(SEMARNAP) – Comisión Nacional para el Conocimiento y Uso de la Biodiversidad (CONABIO),
México, D.F.
Seaman, D. E., and R. A. Powell. 1996. An evaluation of
the accuracy of kernel density estimators for home
range analysis. Ecology 77:2075–2085.
Sergio, F., J. Blas, M. G. Forero, J. A. Donázar, and
F. Hiraldo. 2007. Sequential settlement and site
dependence in a migratory raptor. Behavioral Ecology 18:811–821.
v www.esajournals.org
15
October 2016 v Volume 7(10) v Article e01544