ArticlePDF Available

Climate and Dispersal: Black-Winged Stilts Disperse Further in Dry Springs


Abstract and Figures

Climate affects the abundance and distribution of many species of wildlife. Nevertheless, the potential effects of climate on dispersive behaviour remain unstudied. Here, I combine data from (i) a long-term Black-winged Stilt (Himantopus himantopus) monitoring program, (ii) a capture-recapture marking program in Doñana, and (iii) reports from the Rare Birds Committee in the United Kingdom to analyse at different geographical scales the relationship between climate, survival, philopatry, and dispersive behaviour. Black-winged Stilt populations varied in size in consonance with changes in both the North Atlantic Oscillation (NAO) and local rainfall during the breeding season. Changes in population size are related to changes in philopatry and increases in dispersal beyond the traditional range of the species. The results indicate that climatic conditions influence the dispersive behaviour of individual birds, explaining rapid changes in the local population of this species breeding in unstable Mediterranean wetlands.
Content may be subject to copyright.
Climate and Dispersal: Black-Winged Stilts Disperse
Further in Dry Springs
Jordi Figuerola*
Department of Wetland Ecology, Estacio
n Biolo
gica de Don
ana, Consejo Superior de Investigaciones Cientı
ficas (CSIC), Seville, Spain
Climate affects the abundance and distribution of many species of wildlife. Nevertheless, the potential effects of climate on
dispersive behaviour remain unstudied. Here, I combine data from (i) a long-term Black-winged Stilt (Himantopus himantopus)
monitoring program, (ii) a capture-recapture marking program in Don
ana, and (iii) reports from the Rare Birds Committee in
the United Kingdom to analyse at different geographical scales the relationship between climate, survival, philopatry, and
dispersive behaviour. Black-winged Stilt populations varied in size in consonance with changes in both the North Atlantic
Oscillation (NAO) and local rainfall during the breeding season. Changes in population size are related to changes in philopatry
and increases in dispersal beyond the traditional range of the species. The results indicate that climatic conditions influence
the dispersive behaviour of individual birds, explaining rapid changes in the local population of this species breeding in
unstable Mediterranean wetlands.
Citation: Figuerola J (2007) Climate and Dispersal: Black-Winged Stilts Disperse Further in Dry Springs. PLoS ONE 2(6): e539. doi:10.1371/
Climate affect the abundance and distribution of many species of
wildlife. Impacts of last decades changes in climate include
reduction in population size, survival, and/or productivity, and
a northward shift in the distribution of a variety of different
organisms [1]. North Atlantic Oscillation (NAO) index is one of
the main cyclical climatic forces. During positive phases of the
NAO, westerly winds increase temperature and rainfall over
Northern Europe, and drought in the Mediterranean region [2].
Both ecological processes in the Sea (i.e. fish growth and survival)
and the continent (i.e. competition between sympatric species,
survival and productivity) seem affected by NAO phases [2].
Nevertheless, the potential effects of NAO and climate in general
on dispersive behaviour remain unstudied. Theoretical studies
predict major changes in the distribution of animals and plants in
response to climate, although the validity of these models has yet
to be established [3]. How do highly mobile organisms such as
birds respond to changes in climate? I investigated the case of the
Black-winged Stilt Himantopus himantopus, a common breeding
wader in European and, in particular, in southern European
wetlands [4]. The breeding population in Don˜ana (southwest
Spain) is very variable, ranging from 50 pairs in dry years to over
14,000 pairs in wet years. Given that the total European
population is estimated at 33,500–49,800 pairs, up to 28–42%
of European Black-winged Stilts breed in some years in Don˜ana.
Since 1988 the breeding population of Black-winged Stilts has
been monitored by means of censuses of breeding pairs, the
ringing of chicks with PVC rings, and the resighting of marked
I used capture-mark-resighting data spanning the years 1988–
2003 to estimate Black-winged Stilt survival and resighting rates.
Survival estimates are affected by mortality and permanent
emigration, while resighting rates are affected by mark observation
effort and temporal dispersal to other areas [5]. Survival is low
during the first year of life (1
year: 28.11%612.75; 1+ year:
69.65%64.78), although it was constant from one year to another.
Resighting varied greatly with time and did not depend on age
(Table 1). Time-dependent variation in resighting rates was better
explained by local rainfall (45.1% variance explained) than by the
NAO (33.5% variance explained, Figure 1a). The simultaneous
combination of NAO and rainfall did not improve the fit on
models including only rainfall. Breeding population size increased
with resighting rates (r = 0.56, F = 5.95, df = 1, 13, p = 0.03) and
rainfall during the breeding season (r = 0.64, F = 10.82, df = 1, 16,
p = 0.005), but decreased with NAO (Figure 1b). Combining
simultaneously NAO and rainfall increased the fit of the model
(r = 0.86, F = 20.47, df = 2, 15, p,0.0001) and both factors
remained significantly related to population size in Don˜ana
(NAO, F = 18.37, df = 1, 15, p = 0.0006; rainfall, F = 10.01,
df = 1, 15, p = 0.006). NAO (but not local rainfall in Don˜ ana,
r = 20.12, F = 0.22, df = 1, 14, p = 0.65) tended to be positively
related, and Don˜ ana population size negatively related to the
frequency of observations of dispersing Black-winged Stilts in the
United Kingdom, a country outside the range of the species
(Figures. 1c and 2).
Considerable attention has been focused on the incidence of
climatic factors on survival, reproduction, and/or phenology [6,7].
However, the impact of climate on philopatry and dispersal has
received much less attention [8,9]. The results of this study suggest
that climatic conditions have important effects on birds’
philopatry, which is in turn related to changes in breeding
populations. Ultimately these changes lead to an increase in
Academic Editor: Peter Jones, University of Edinburgh, United Kingdom
Received February 21, 2007; Accepted May 22, 2007; Published June 20, 2007
Copyright: ß 2007 Jordi Figuerola. This is an open-access article distributed
under the terms of the Creative Commons Attribution License, which permits
unrestricted use, distribution, and reproduction in any medium, provided the
original author and source are credited.
Funding: The Junta de Andalucı
a funded this study via the project contract ‘Las
aves acua
ticas de Don
ana y el cultivo del arroz: la interaccio
n entre la agricultura y
la conservacio
n de las zonas hu
medas’. The Spanish Ministry of Science and
Technology provides support for my research with a Ramo
n y Cajal contract for
young researchers.
Competing Interests: The author has declared that no competing interests exist.
* To whom correspond ence should be addressed. E-mail:
PLoS ONE | 1 June 2007 | Issue 6 | e539
dispersive behaviour and an improved capacity for colonizing new
breeding localities. NAO, one of the Earth’s main large-scale
cyclical climatic patterns, is negatively associated to rainfall in
Spain and North Africa [10]. Both local rainfall and NAO have
been related by multivariate analyses to breeding population size
in Don˜ana: the former is a better estimator of habitat availability
for birds migrating into Don˜ana, while the latter may affect the
probability that birds wintering in Africa will breed closer to their
wintering grounds. Unfortunately, no information is available on
numbers of Black-winged Stilts breeding in North African
countries to directly test this relation between NAO and African
breeding distribution. The resighting rate is not only affected by
philopatry, but also by other factors such as research effort and
consequently analyses of this factor should be considered
conservative (and may explain the moderate amount of variance
explained by the models). Despite this, the resighting rate is clearly
associated with population changes in the study area and in
a region more than 1500 kilometres from Don˜ana, a fact that
increases confidence in the soundness of results.
Temperature increases leading to rising sea-levels [11] and
changes in rainfall patterns [12] will harm coastal wetlands. In
addition to cyclical fluctuations, a long term trend towards more
positive NAO is occurring [2]. While rain will probably increase in
northern Europe, the Mediterranean region will become drier [12]
and under this scenario information on how weather influences the
demographic parameters of organisms is urgently needed. In terms
of survival I found no direct costs of dispersal, although the effects
on individuals fitness cannot be excluded given that other studies
have found a relationship between dispersal and delayed breeding
Understanding how species’ ranges are modified in light of
climate change is an important issue in ecology. Travis & Dytham
[14] have recently produced a model that suggests that during
range expansion selection may favour individuals with a higher
propensity for dispersal. A paradoxical result of my study is that
climate itself can modify the propensity of individuals to disperse,
thereby increasing the probability of range expansion in species
that live, for example, in unstable environments such as
Mediterranean wetlands.
The data
Since 1988 the number of breeding pairs of Black-winged Stilts has
been counted every year in the Don˜ana National Park and the
resulting figures have been found to be closely correlated to the
numbers counted in the whole of Don˜ ana (r = 0.93, F = 69.03,
df = 1, 10, p,0.0001), which are available for far fewer years.
The observation of rare birds outside their normal ranges has
long been a common hobby in many countries and the British
Birds Rarities Committee revised and evaluated all observations of
rare birds in Great Britain since 1959. This task provides valuable
information regarding the frequency of the rare bird species that
wander to Great Britain and can be consulted on the Internet
( Observations from all
years between 1988 and 2004 were included in the analyses.
The number of observations in any given year or territory will
clearly depend on the number of ornithologists living or visiting
that area. To control for differences in observer effort, the number
of any other rare species of waders (Infraorder Charadriides,
excluding the family Laridae; 15) observed in the UK was included
as a covariate in the analyses. Both the numbers of Black-winged
Stilts and waders observed in UK were log transformed.
Two different indicators of environmental conditions were used
in the analyses: rainfall in Don˜ana from March to August (the
Black-winged Stilt breeding season) (available at http://www-rbd.
em05.htm), and the mean winter NAO-index (available at http:// NAO is a major
source of interannual variability in atmospheric circulation and the
NAO index is estimated on the basis of differences in pressure at
sea-level between Lisbon and Reykjavik from December to
Modelling survival and resighting rates
Chicks have been ringed in Don˜ ana since 1988 with metal rings
and white plastic DARVIC rings marked with a black, three-digit
code. These rings can be read from a distance with the aid of
a telescope. I conducted a capture-resighting analysis to estimate
survival and resighting rate using the program MARK and
information pertaining to 2964 individuals ringed and observed in
Table 1. Modelling the survival and resighting rates of Black-
winged Stilts during the period 1988–2003 using capture-
resighting data gathered in Don
ana (southwest Spain).
a) Testing for age and time variation in survival and recapture parameters
Model QAICc Parameters QDeviance
Ø(age) p(time) 949.370 17 75.323
Ø(constant) p(time) 950.148 16 78.124
Ø(age) p(constant) 953.888 3 108.038
Ø(constant) p(constant) 954.072 2 110.226
Ø(age) p(age) 955.872 4 108.017
Ø(constant) p(age) 956.042 3 110.192
Ø(time) p(constant) 956.700 16 84.676
Ø(time) p(age) 958.550 17 84.503
Ø(age) p(age*time) 963.328 31 60.818
Ø(time) p(time) 968.177 29 69.750
Ø(age*time) p(constant) 968.765 30 68.297
Ø(age*time) p(age) 970.756 31 68.247
Ø(time) p(age*time) 983.817 44 54.637
Ø(age*time) p(time) 985.683 44 56.503
Ø(age*time) p(age*time) 1000.515 58 42.349
Ø(constant) p(age*time) 1036.888 30 136.421
b) Testing for the effects of weather on model parameters in the model Ø(age)
Ø(age) p(rain March–August) 941.131 4 93.275
Ø(age) p(NAO+rain March–August) 941.183 5 91.321
Ø(age) p(NAO) 944.958 4 97.103
Ø(age) p(time) 949.370 17 75.323
c) Testing for effects of weather on model parameters in the model Ø(constant)
Ø(constant) p(rain March–August) 941.497 3 95.647
Øconstant) p(NAO+rain March–August) 941.472 4 93.617
Ø(constant) p(NAO) 944.997 3 99.147
Ø(constant) p(time) 950.148 16 78.124
Models are defined in terms of survival (Ø) and recapture rates (p) that vary
between first-year and adult birds (age) and between years (time). AIC was
adjusted for a c-hat value of 1.12. The models supported by the AIC criterion
during the model selection process are marked in bold.
Climate, Survival & Dispersal
PLoS ONE | 2 June 2007 | Issue 6 | e539
Don˜ ana during the period 1988–2003. Only captures and
observations occurring between March and August were included
in the analyses so as to estimate the probability of a bird alive in
one breeding season being still alive during the next breeding
Survival analysis was based on the Cormack-Jolly-Seber models
(CJS). Survival rates are affected both by mortality and by
permanent emigration from the study area and resighting rates
reflect both variation in observation/capture effort and the
temporary emigration of individuals from the study area [16].
The relationship between climatic variables and survival and/or
recapture parameters was tested using a capture-recapture model
selection and simplification approach [5]. Model selection was
based upon a fully parameterized model in which both survival
and recapture probabilities varied with age and time. Models
incorporating age-dependent effects only allowed parameters to be
different from adults during the year after capture as chicks. The
adjustment of the CJS model to the data was assessed with the
RELEASE programme’s goodness-of-fit test [17] and with a para-
metric bootstrap approach. The parameteric estimates from the
Figure 1. North Atlantic Oscillation and Black-winged Stilt population dynamics. a, Philopatry to breeding grounds estimated as resighting rates
from the model Ø(age) p(time), r = 0.58, F = 6.49, df = 1, 13, p = 0.02, 1989–2003. b, Number of pairs breeding in Don
ana National Park, r = 0.74,
F = 19.78, df = 1, 16, p = 0.0004, 1988–2005. c, Frequency of Black-winged Stilt observations in the United Kingdom after controlling for the number of
rare waders observed in the UK, a country outside the actual range of this species, r = 0.48, F = 4.15, df = 1, 14, p = 0.06, 1977–2004.
Climate, Survival & Dispersal
PLoS ONE | 3 June 2007 | Issue 6 | e539
model were used to simulate data in line with the assumptions
contained in the CJS models (individuals were independent and no
overdispersion of data occurred). This process was repeated 1000
times and the deviance of each model was calculated to determine
whether the deviance of the observed model exceeded that of the
simulated data. The overdispersion parameter (c-hat) was
calculated as the ratio between the mean deviance of simulated
models and the deviance of the observed model [18]. We found no
evidence of significant overdispersion (c-hat = 1.12) and thus no
evidence for the assumption that fates of individual birds were
independent of each other [19]. We adjusted results to a c-hat of
1.12 (ideally c-hat should be 1.00), although this adjustment had
no qualitative effect on the results.
Model simplification was based on an analysis of the factors
affecting survival and resighting probabilities and constructed
models with variation between age and time, and the age*time
interaction. Finally, using the simplified capture and survival
model, we tested the possible relationships between resighting
rates, which were found to vary annually, local rainfall and NAO.
I used a small sample size adjusted by Akaike’s information
criterion (AICc) for model selection. AICc is considered to be
a simple, effective, and objective means for model selection [20].
Models with lower AICc values are assumed to best fit the data
with the least possible number of parameters. Models with AICc
values differing by less than 2 were considered to be equivalent.
The amount of variance explained by climatic variables was
calculated as Deviance(model constant) - Deviance(model with
covariate) / Deviace(model constant) - Deviance(model with time
dependent parameter), as per [21].
Statistical analyses
A Pearson regression was used to analyse the relationship between
NAO and rainfall in Don˜ana, and breeding population size and
frequency of observations in the UK.
Manolo Man˜ ez supplied information on the breeding populations in
Don˜ ana National Park. The Equipo de Seguimiento de Procesos Naturales
and many volunteer ringers and observers in Don˜ ana and the United
Kingdom have contributed to the databases analysed and have made
possible this paper. Tama´s Sze´kely provided useful comments on a first
draft of the manuscript.
Author Contributions
Conceived and designed the experiments: JF. Analyzed the data: JF. Wrote
the paper: JF.
1. Walther G-R, Post E, Convey P, Menzel A, Parmesan C, et al. (2002) Ecological
responses to recent climate change. Nature 416: 389–395.
2. Stenseth NC, Mysterud A, Ottersen G, Hurrell JW, Chan K-S, et al. (2002)
Ecological effects of climate fluctuations. Science 297: 1292–1296.
3. Araujo MB, New M (2007) Ensemble forecasting of species distributions. Trends
Ecol Evol 22: 42–47.
4. Thorup O (2006) Breeding waders in Europe 2000 International Wader Study
5. Lebreton JD, Burnham KP, Clobert J, Anderson DR (1992) Modeling survival
and testing biological hypotheses using marked animals: a unified approach with
case studies. Ecol Monogr 62: 67–118.
6. Saether BE, Sutherland WJ, Engen S (2004) Climate influences on avian
population dynamics. Adv Ecol Res 35: 185–209.
7. Weatherhead PJ (2005) Effects of climate variation on timing of nesting,
rep roductive success, and offspring sex ratios of red-winged blackbird s.
Oecologia 144: 168–175.
8. Blums P, Nichols JD, Hines JE, Mednis A (2002) Sources of variation in survival
and breeding site fidelity in three species of European ducks. J Anim Ecol 71:
9. Mwller AP, Flensted-Jensen E, Mardal W (2006) Dispersal and climate change:
a case study of the Arctic tern Sterna paradisaea. Global Change Biol 12:
10. Hurrell JW (1995) Decadal trends in the North-Atlantic Oscillation: Regional
temperatures and precipitation. Science 269: 676–679.
11. IPCC (2002) Climate Change and Biodiversity. IPCC Technical Paper V,
WMO-UNEP. Available at:
12. IPCC (2001) Climate change 2001: the scientific basis. Third Assesment Report
of Working Group I. Cambridge: Cambridge University Press.
13. Danchin E, Cam E (2002) Can non-breeding be a cost of breeding dispersal?
Behav Ecol Sociobiol 51: 153–163.
14. Travis JMJ, Dytham C (2002) Dispersal evolution during invasions. Evol Ecol
Res 4: 1119–1129.
15. Sibley CG, Monroe BL Jr (1990) Distribution and taxonomy of birds of the
world Yale University Press.
16. Kendall WL, Nichols JD, Hines JE (1997) Estimating temporary emigration
using capture-recapture data with Pollock’s robust design. Ecology 78: 563–578.
17. Burnham KP, Anderson DR, White GC, Brownie C, Pollock KH (1987) Design
and analysis methods for fish survival experiments based on release-recapture.
Am Fish Soc Monogr 5.
18. Cooch E, White G (2004) Program Mark: A gentle introduction. 3
Available at.
19. Anderson DR, Burnham KP, Wh ite GC (1994) AIC model selection in
overdispersed capture-recapture data. Ecology 75: 1780–1793.
20. Burnham KP, Anderson DR (1998) Model selection and inference: a practical
information-theoretic approach. New York: Springer.
21. Skalski JR, Hoffmann A, Smith SG (1993) Testing the significance of individual-
and cohort-level covariates in animal survival studies. In: Lebreton J-D,
North PM, eds. Marked individuals in the study of bird populations. Basel:
Birkha¨user-Verlag. pp 9–28.
Figure 2. Population size in Don
ana and Bla ck-winged Sti lt
population dynamics. Frequency of Black-winged Stilt observations
after controlling for the number of rare waders observed in the United
Kingdom (r = 0.52, F = 5.00, df = 1, 14, p = 0.04).
Climate, Survival & Dispersal
PLoS ONE | 4 June 2007 | Issue 6 | e539
... However, not much work ever proved it empirically, and highlighted the responsibility of an increase in dispersal costs on dispersal patterns, especially in animals (but see Cheptou et al. 2008 for an example on a weed species and Duriez et al. 2009 for an example on oystercatchers). For now, many empirical and theoretical studies have shown that dispersal propensity or distance may decrease with global changes, especially if those are targeting the habitat experienced during transience, but they have not directly linked these changes in dispersal patterns to increases in dispersal costs (Bonte et al. 2003, 2008a, Figuerola et al. 2007, Ahlroth et al. 2010, Baines and McCauley 2018. Moreover, these studies have not highlighted which or how life history traits may be modified when environmental conditions change, and may in turn lead to the observed changes in dispersal propensity or distance. ...
... A study from Hansson et al. (2004) highlighted that short and long-distance dispersers may not incur the same dispersal costs, and that in consequence, gene flow is decreased for long-distance dispersers which incur more costs. Lastly, global changes have been shown to decrease individual propensity to disperse in this study but also in other study systems in the literature (Bonte et al. 2003, 2008a, Figuerola et al. 2007, Ahlroth et al. 2010, Baines and McCauley 2018, which also means decreased gene flow. This may have strongly detrimental effects on populations as decreases in gene flow elevate extinction risks (Spielman et al. 2004). ...
Full-text available
Natal dispersal is a process by which individuals move from their natal to reproductive ranges which is fundamental for population dynamics and persistence. Through for example the limitation of inbreeding or the capacity it provides to reach and colonize new habitats containing resources or mates, it can be highly beneficial to dispersing individuals. However, dispersal can also be costly for the individuals, through increased mortality or attrition, energy expenditure, or lost habitat opportunities and time. Its expression at the population level thus depends on the balance between costs and benefits, and theory states that dispersal may become counter-selected if costs outweigh benefits. In the current context of global change, we may expect (1) dispersal costs to increase with the degradation of environments and (2) increased dispersal costs to decrease dispersal success and geographical reach through evolutionary mechanisms. Moreover, because dispersal costs may vary with actual dispersal movement, we may wonder what are the discrete alternative tactics roe deer may use in contrasting environments (3). In this PhD, I aimed to address these three perspectives using two roe deer datasets from two geographically distinct populations (GPS data in Haute-Garonne and Capture-Mark-Recapture data in Deux-Sèvres, France), as well as a modelling approach. First, I show that, despite having a good body condition, dispersers incur costs in terms of mortality, reproduction and growth, and that climate change may increase mortality costs. Concomitant to these variations in costs, I also found that realised dispersal has diminished over the past 30 years by more than 30% in both sexes. Second, I identified at least six alternative dispersal tactics in roe deer, characterised by different movement timing, amplitude and duration, which may imply different outcomes in terms of costs and population dynamics. Lastly, my analyses suggest that dispersal might evolve towards tortuous and short distance movements when mortality costs increase, limiting the geographical reach of dispersal. Overall, these results highlight the concerning effects global changes may have on dispersal costs and dispersal evolution. Because dispersal is a species and context dependent process, more studies addressing the impacts of global changes on dispersal costs, ideally incorporating alternative dispersal tactics, will provide valuable information to better predict how species may cope with environmental changes.
... Twenty-three bird species showed a significant association with NAO − (Table 2), in studies from Canada, the USA, the UK, Norway, Sweden, Denmark, Romania, and Spain (Jonzen et al., 2002;Almaraz & Amat, 2004;Olsen & Schmidt 2004;Grosbois & Thompson, 2005;Votier et al., 2005;Weatherhead, 2005;Anders & Post, 2006;Zydelis et al., 2006;Figuerola, 2007;Balbontin et al., 2009;Goodenough, Elliot & Hart, 2009;Lewis et al., 2009;Pearce-Higgins et al., 2009;Gaston & Robertson, 2010;Bustnes et al., 2013;Jensen et al., 2014;Veit & Manne, 2015;Guery et al., 2017;Schimpf et al., 2020;Baltag, Kovacs & Sfica, 2021;Saunders et al., 2021; Table S1). They spanned diverse taxa from loons, cormorants, and eiders to New World blackbirds and Old World finches. ...
Climate is a major extrinsic factor affecting the population dynamics of many organisms. The Broad-Scale Climate Hypothesis (BSCH) was proposed by Elton to explain the large-scale synchronous population cycles of animals, but the extent of support and whether it differs among taxa and geographical regions is unclear. We reviewed publications examining the relationship between the population dynamics of multiple taxa worldwide and the two most commonly used broad-scale climate indices, El Niño-Southern Oscillation (ENSO) and North Atlantic Oscillation (NAO). Our review and synthesis (based on 561 species from 221 papers) reveals that population changes of mammals , birds and insects are strongly affected by major oceanic shifts or irregular oceanic changes, particularly in ENSO-and NAO-influenced regions (Pacific and Atlantic, respectively), providing clear evidence supporting Elton's BSCH. Mammal and insect populations tended to increase during positive ENSO phases. Bird populations tended to increase in positive NAO phases. Some species showed dual associations with both positive and negative phases of the same climate index (ENSO or NAO). These findings indicate that some taxa or regions are more or less vulnerable to climate fluctuations and that some geographical areas show multiple weather effects related to ENSO or NAO phases. Beyond confirming that animal populations are influenced by broad-scale climate variation, we document extensive patterns of variation among taxa and observe that the direct biotic and abiotic mechanisms for these broad-scale climate factors affecting animal populations are very poorly understood. A practical implication of our research is that changes in ENSO or NAO can be used as early signals for pest management and wildlife conservation. We advocate integrative studies at both broad and local scales to unravel the omnipresent effects of climate on animal populations to help address the challenge of conserving biodiversity in this era of accelerated climate change.
... The size of the breeding population in Doñana (south-west of Spain) widely varies, ranging from 50 pairs in dry years to more than 14,000 in wet years. Given that the total European population is estimated at 33,500-49,800 pairs, up to 28-42% of European black-winged stilts reproduce in Doñana in some years (Figuerola, 2007;Toral & Figuerola, 2012). ...
Full-text available
A stable group of birds has been formed at water treatment facilities. Sewage treatment sites are a well-known nesting place for long-legged waders. Black-winged stilts are included in the Bonn (Appendix II) and Berne (Appendix II) conventions, the AEWA agreement. Listed in the Red Book of Ukraine (1994, 2009) (status – vulnerable). In Ukraine, it is under protection on the territory of the natural reserve fund. The arrival of black-winged stilts waders at the nesting sites was recorded in the second-third decade of April (April 23, 2020; April 17, 2021). Immediately after returning to the nesting areas, the birds begin to build nests and lay eggs. The first eggs in this population were seen on 01.05.2020, 07.05.2021. The process of laying eggs lasted until the end of the first decade of July (08.07.2020). The average clutch size in the nests of Himantopus himantopus decreased from 3.8 ± 0.1 (2020) to 3.5 ± 0.1 (2021). The average egg sizes and their limits have been determined for long-legged waders. The chicks hatched from late May (30.05.2020), throughout June to the first decade of July (02.07.2020). The chicks were able to fly in a month – 29.06.2020. The muddy site of the wastewater treatment ponds of Kharkiv supported Black-winged Stilts until early August. Later, the birds started post-breeding movements. The last adults with juvenile birds were observed on 13.08.2020. Stilts in some years may stay until early October. The reproductive success of the black-winged stilt increased from 35.6% (2020) to 38.8% (2021). On average, 1.3 ± 0.2 (2020) and 1.4 ± 0.3 (2021) chicks fledged from the nests. In 2021, the number of nesting stilts increased, which is apparently due to rainy weather at the beginning of the reproductive period. For the purpose of more effective protection, the nesting settlements of the stilt should be protected and the appearance of people in the nesting places should be prohibited.
... It can also provide suitable climatic conditions in habitats beyond the native range. These two changes could lead to range expansion or shift if species cannot adapt to novel conditions (Figuerola, 2007). Moreover, global changes can also facilitate the invasion of introduced species (Stachowicz, Terwin, Whitlatch, & Osman, 2002). ...
... Dispersal of birds can be used as important data for studies on the population structure and dynamics of the species, behavioral ecology research, and the development of conservation strategies (Clobert et al. 2012). It is typically determined by a variety of internal factors, including age, gender, and body condition, and can be distinguished by external factors, such as social status, climate, and habitat environment change (Figuerola 2007;Clobert et al. 2012). P. falcinellus has the greatest dispersal capability of any bird species (Patten and Lasley 2000). ...
Full-text available
Glossy Ibis (Plegadis falcinellus), which has never been recorded in South Korea, appeared on Jeju Island in 2018 and re-emerged in the inland area of Seocheon-gun (South Chungcheong Province) and in Goyang-si (Gyeonggi Province) in the following year. This study aims to report the progress in observing P. falcinellus in the inland areas of South Korea in 2019 and to predict its origin region and future propensity for habitats in the country through literature review. On 5 May 2019, an individual of P. falcinellus with breeding feathers was observed in a farmland in Wolsan-ri, Seocheon-gun. Twelve days later, another one was identified in a farmland in Janghang-dong, Goyang-si, about 173 km north of Wolsan-ri. The observed birds fed and rested in the area and stayed for only a day. The individual birds spotted in South Korea in 2019 are conjectured to have come from either Southeast Asia or Australia, among areas located in East Asian-Australasian Flyway (EAAF). This is because P. falcinellus, a species with excellent dispersal capacity, forms a population in new areas during extreme environmental changes in their current habitats, especially droughts. For 2 years, P. falcinellus was observed to be migrating in spring; however, in the future, they may exhibit the same propensity for breeding and habitats as that of birds migrating in autumn. As it is a conspicuous species, effective detection of their arrival requires a survey system that classifies the country by habitat type and involves periodic and multiple observations by experts and citizens.
... Por ejemplo, los individuos más pequeños a menudo tienen una capacidad de dispersión reducida, y el deterioro inducido por el clima en la calidad del hábitat o el rápido desarrollo a temperaturas más altas pueden reducir el tamaño corporal de las especies (McCauley y Mabry 2011). Por otro lado, condiciones desfavorables pueden llevar a otras especies a emigrar (Figuerola 2007). ...
Ecosystems worldwide are experiencing the consequences of global change, including those related to climatic warming and the destruction and fragmentation of natural habitats. These factors erode biodiversity and change biological communities and ecosystem processes that are ultimately responsible for the ecosystem services that nature provides to humans. To forecast and mitigate these effects is the environmental challenge of our age. Scientific research has advanced our knowledge of the impacts of global change on ecosystems. Comparatively, however, it remains unclear how ecosystem recover after perturbations, and we lack a general theory of the ecosystem recovery dynamics. In this article, I argue that the ecological interactions between species and the networks they form are essential components to understand the restoration and functioning of recovering ecosystems. Interaction networks allow us to understand the appropriate spatial and temporal scales for an efficient restoration of multifunctional ecosystems. Ecological restoration must also aim to recover stable ecosystems in a scenario where climate change and the fragmentation of natural habitats will be pervasive. Together, these factors will allow us to meet the international objectives on ecosystem restoration.
... areas (Wernham et al. 2002, Delany et al. 2009. The exception is the stilt, which has more potential as a circum-Mediterranean vector, but even this species often moves from southern Spain to the UK (Figuerola 2007). The godwit has a common flyway expanding from Iceland into the Iberian Peninsula and beyond into north-west Africa. ...
Full-text available
Shorebirds (Charadriiformes) undergo rapid migrations with potential for long‐distance dispersal (LDD) of plants. We studied the frequency of endozoochory by shorebirds in different parts of Europe covering a broad latitudinal range and different seasons. We assessed whether plants dispersed conformed to morphological dispersal syndromes. A total of 409 excreta samples (271 faeces and 138 pellets) were collected from redshank (Tringa totanus), black‐winged stilt (Himantopus himantopus), pied avocet (Recurvirostra avosetta), northern lapwing (Vanellus vanellus), Eurasian curlew (Numenius arquata) and black‐tailed godwit (Limosa limosa) in south‐west Spain, north‐west England, southern Ireland and Iceland in 2005 and 2016, and intact seeds were extracted and identified. Godwits were sampled just before or after migratory movements between England and Iceland. The germinability of seeds was tested. Intact diaspores were recovered from all bird species and study areas, and were present in 13% of samples overall. Thirteen plant families were represented, including Charophyceae and 26 angiosperm taxa. Only four species had an "endozoochory syndrome". Four alien species were recorded. Ellenberg values classified three species as aquatic and 20 as terrestrial. Overall, 89% of seeds were from terrestrial plants, and 11% from aquatic plants. Average seed length was higher in redshank pellets than in their faeces. Six species were germinated, none of which had an endozoochory syndrome. Seeds were recorded during spring and autumn migration. Plant species recorded have broad latitudinal ranges consistent with LDD via shorebirds. Crucially, morphological syndromes do not adequately predict LDD potential, and more empirical work is required to identify which plants are dispersed by shorebirds. Incorporating endozoochory by shorebirds and other migratory waterbirds into plant distribution models would allow us to better understand the natural processes that facilitated colonization of oceanic islands, or to improve predictions of how plants will respond to climate change, or how alien species spread. This article is protected by copyright. All rights reserved.
Full-text available
El libro recoge las conferencias invitadas al V Congreso de la Asociación Española de Climatología, celebrado en Zaragoza entre el 18 y el 21 de septiembre de 2006
Full-text available
Animal dispersal patterns have important implications for many biological processes, but the measurement of dispersal is challenging and often requires the use of complementary approaches. In this study, we investigated the local-scale sex-biased dispersal pattern in a social bird, the black-throated tit (Aegithalos concinnus), in central China. Spatial genetic autocorrelation analyses suggested that significant fine-scale genetic structure existed in males but not in females. Mark–recapture analyses of ringed individuals also showed that female offspring were more dispersive than male offspring, supporting genetic evidence of local female-biased dispersal. These results were contrary to a previous finding of male-biased long-distance dispersal in this species that was based on analyses of gene flow across the species range in China. This implies that the species might potentially have a scale-dependent dispersal strategy, with females frequently dispersing further than males at the local level, but with a proportion of males occasionally dispersing over long distances and contributing more to gene flow at a larger geographical scale. Long-distance dispersal by male black-throated tits might be induced by competition for resources or by unfavourable environmental conditions, warranting further investigation, but our findings increase the evidence that geographical scale is an important factor to be considered when investigating animal dispersal patterns.
Full-text available
One of the most important issue in Population Ecology is understanding how demographic parameters change in response to environmental conditions. The relevance of this topic is increasing because of the current and future scenarios of global change. As a result, the scientific community is giving special interest to the study of ecological processes like dispersal, colonization and population growth and how they depend for demographic parameters of populations structured, for example, in age, sex and breeding status. Collating data suitable for the investigation of these processes is challenging as they typically require a long term monitoring of long-lived species, like the Glossy Ibis, which mean many years of patient field-work. Moreover, an extra difficulty for this kind of studies is the importance of starting the field-work from the very settlement of a new colony, something that allows addressing aspects of population ecology in a much more efficient way. The present work has been possible thanks to the dedication and effort of the research and technician staff (Monitoring team of natural processes) of the Estación Biológica de Doñana. Their farsightedness has made possible the monitoring of the Glossy Ibis Doñana population from the very starting point, in 1996, when seven breeding pairs settle in the National Park. The aim of this work has been describing and analyzing the population dynamic of this overlooked model species to infer the main factors which play a role in the processes of colonization, growth and expansion of a species.
Full-text available
Selection of a proper model as a basis for statistical inference from capture-recapture data is critical. This is especially so when using open models in the analysis of multiple, interrelated data sets (e.g., males and females, with 2-3 age classes, over 3-5 areas and 10-15 yr.) The most general model considered for such data sets might contain 1000 survival and recapture parameters. This paper presents numerical results on three information-theoretic methods for model selection when the data are overdispersed (i.e., a lack of independence so that extra-binomial variation occurs). Akaike's information criterion (AIC), a second-order adjustment to AIC for bias (AIC"c), and a dimension-consistent criterion (CAIC) were modified using an empirical estimate of the average overdispersion, based on quasi-likelihood theory. Quality of model selection was evaluated based on the Euclidian distance between standardized @? and @? (parameter @? is vector valued); this quantity (a type of residual sum of squares, hence donated as RSS) is a combination of squared bias and variance. Five results seem to be of general interest for these product-multinomial models. First, when there was overdispersion the most direct estimator of the variance inflation factor was positively biased and the relative bias increased with the amount of overdispersion. Second, AIC and AIC"c, unadjusted for overdispersion using quasi-likelihood theory, performed poorly in selecting a model with a small RSS value when the data were overdispersed (i.e., overfitted models were selected when compared to the model with the minimum RRS value). Third, the information-theoretic criteria, adjusted for overdispersion, performed well, selected parismonious models, and had a good balance between under- and overfitting the data. Fourth, generally, the dimension-consistent criterion selected models with fewer parameters than the other criteria, had smaller RSS values, but clearly was in error by underfitting when compared with the model with the minimum RSS value. Fifth, even if the true model structure (but not the actual parameter values in the model) is known, that true model, when fitted to the data (by parameter estimation) is a relatively poor basis for statistical inference when that true model includes several, let alone many, estimated parameters that are not significantly different from O.
Greenland ice-core data have revealed large decadal climate variations over the North Atlantic that can be related to a major source of low-frequency variability, the North Atlantic Oscillation. Over the past decade, the Oscillation has remained in one extreme phase during the winters, contributing significantly to the recent wintertime warmth across Europe and to cold conditions in the northwest Atlantic. An evaluation of the atmospheric moisture budget reveals coherent large-scale changes since 1980 that are linked to recent dry conditions over southern Europe and the Mediterranean, whereas northern Europe and parts of Scandinavia have generally experienced wetter than normal conditions.