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1 July 2014 Female-Biased Sex Ratio in Moulting Black-Necked Grebes Podiceps nigricollis in Southern Spain
Juan A. Amat, Nico Varo, Marta I. Sánchez, Andy J. Green, Cristina Ramo
Author Affiliations +
Abstract

We tested if Black-necked Grebe, a species in which both sexes undertake moult-migration, have an unbiased sex ratio at a moulting site in Europe, as previously found in North America and as was expected for a species with biparental care. For this we used a unique long-term dataset of 5821 grebes captured for ringing throughout the moulting seasons of 2006–2012 in the Odiel salt-marshes (SW Spain). The grebes were sexed and classified as adults (74%) or juveniles (26%). Birds ringed at Odiel were recovered over a wide area up to central Russia and south to the Canary Islands and Morocco. We report on a unique case of a strongly biased sex ratio in a moult-migrating bird species with biparental care, in which adult females were significantly more abundant than adult males in all 7 years (1.6–4.2 females per male). Biased sex ratios were not found among juveniles. Differences between North America and Europe in the sex ratios of adult Black-necked Grebes at moulting sites may be explained by the much larger American moulting sites, which would facilitate an unbiased sex ratio in North America, but not in Europe. Moulting sites in Europe may reach carrying capacity because of their smaller size, forcing the late migrating individuals (adult females and juveniles) to move longer distances to sites farther from breeding areas, such us the Odiel salt-marshes.

Because breeding and moulting are energetically expensive processes they are usually separated in time (Payne 1972), and the sex with a smaller participation in breeding activities moults earlier than the sex contributing more to breeding activities (e.g. Siimaki et al. 1994, Svensson & Nilsson 1997). After breeding, many waterbird species (mainly Podicipedidae, Phoenicopteridae, Anatidae, Rallidae, Gruidaea and Alcidae) move to specific sites for moulting, where all flight feathers are shed simultaneously. This type of displacement is known as moult migration (Salomonsen 1968, Jehl 1990, Kjellén 1994). Age and sex differences in moult migration have been reported in several species. In general, the sex that does not provide parental care is the one that performs moult migration, whereas the sex that undertakes parental care moults at the breeding site. For instance, male ducks are more numerous than females at moult-migration sites (Salomonsen 1968, Hohman et al. 1992), and when female ducks undertake moult migrations, they are usually failed breeders (Salomonsen 1968, Amat et al. 1987, Hohman et al. 1992). In Wilson's Phalaropes Phalaropus tricolor, in which males remain in breeding areas attending broods, it is the females that undertake moult migration (Jehl 1988).

One of the main ecological conditions that allows the undertaking of moult migration by both sexes in biparental species is probably abundant food, whose availability extends well into the autumn, thus giving both parents the time necessary to complete moult in sites far from breeding areas (Jehl 1988, Cooper et al. 1984, Varo et al. 2011). Because in grebes both parents attend the chicks (Fjeldså 2004), an unbiased sex ratio should be expected in the moulting localities. Indeed, this has been reported for the Black-necked Grebe Podiceps nigricollis in North America (Jehl 1988, Cuéllar Brito 2007, Jehl & Henry 2010). Similarly, no biased sex ratio has been found in moult-migrant Little Terns Sternula albifrons, another species with biparental care, at a moulting site in Italy (Cherubini et al. 1996).

Perhaps the Black-necked Grebe is the avian species that forms the largest concentrations during moult migration. Up to one million birds may congregate to moult in a single lake in North America (Storer & Jehl 1985, Jehl 1988). The moulting concentrations of this grebe in Europe are much smaller than in North America: up to 10,700 individuals at our study site in the Odiel salt-marshes in SW Spain (Varo et al. 2011), 5700 in SE Romania (Van Impe 1969), 3900 in the Balearic Islands (Mayol 1984), and 3000 in both SE Spain (García-Jiménez & Calvo-Sendín 1987) and SE France (Iborra et al. 1991). Although up to 186,000 Black-necked Grebes were recorded in 1970 in Burdur Lake in Turkey (Cramp & Simmons 1977), nowadays the lake does not support so many grebes due to severe hydrological changes that may have affected food supplies (Green et al. 1996, Gülle et al. 2010). Indeed, a census in September 2006 reported 10,300 birds ( www.birdforum.net/archive/index.php?t-237529.html).

The sex ratio of Black-necked Grebes during moulting has not been previously investigated in any European locality. In this paper we report a biased adult sex ratio among grebes moulting in SW Spain, and advance a hypothesis aimed at explaining the observed difference between the sex ratios of moulting grebes at sites in North America and the present study site in southern Spain. In particular, we will propose that continental differences in the size of wetlands where the grebes moult may determine that the carrying capacity of sites in Europe is reached after the arrival of a given number of birds, leading late moulting individuals to migrate to more distant sites from breeding areas. This would not occur in North America because of the larger size of wetlands where the grebes moult.

METHODS

The study was conducted during 2006–2012 at the Odiel salt-marshes in south-western Spain (7185 ha; 37°14′N, 6°57′W; see description in Sánchez et al. 2006), in which 1174 ha were transformed into a saltpan complex. The evaporation ponds of the saltpan are used as moulting sites by Black-necked Grebes, mainly during late July to early December (Varo et al. 2011, Fox et al. 2013). Water levels in the ponds used by grebes are usually <1 m. A team of 15–30 persons drew moulting flocks of grebes into corrals, in which they were captured for ringing 9–19 times each season. The birds were sexed visually by an experienced ringer, without recording any body measurement. Sex was determined by head-bill length, males being larger than females (Jehl et al. 1998). The grebes were aged according to eye coloration (Storer & Jehl 1985), juveniles having a paler iris than adults.

To test the robustness of the sexing procedure we collected blood samples from a tarsus vein of 309 grebes, for which sex was determined using molecular methods (Griffiths et al. 1998). Using a 2 × 2 contingency table we then compared sexes visually assigned by the ringer with sexes determined using the molecular method.

During our study we captured 5821 individual grebes, of which 78.1–96.2% were sexed in a given year (see Table 2). Depending on the state of the remiges, birds were assigned to one of three categories: unmoulted, moulting and moulted. For the analysis of sex ratios, adults and juveniles were separated. Many birds were recaptured on several occasions throughout the season (n = 12,107, including recaptures), but when considering yearly variation only one captured individual per year was used. Data were analysed using χ2-tests assuming an expected 1:1 sex ratio. Because we used multiple tests (one for each year), we adjusted probability values by using the Bonferroni correction (Rice 1989, Beal & Khamis 1991), which set significant values at P<0.007.

Table 1.

Comparison of differences between sexes assigned visually (based on head-bill length) and sex determined using the molecular method. Comparisons were made for 309 birds.

t01_207.gif

Skewed sex ratios at Odiel could potentially be due to one sex staying for shorter periods at the moulting site than the other. To test this, we compared the number of days elapsed between the first and the last capture of individual adult grebes between sexes, for birds captured multiple times within a season. Sexual differences in this estimate of staying times were analysed using Mann—Whitney U-tests.

RESULTS

There were no statistically significant differences between sex ratios established visually and when sex was determined using the molecular method (Table 1). The ringer sexed 85% of the birds correctly. There were significant deviations from a 1:1 sex ratio in adults, females being significantly more abundant in all seven years (Table 2). The sex ratios of adults also remained female-biased in the three established categories: unmoulted (1.28 females/male, n = 468), moulting (2.03 females/male, n = 747), and moulted (1.68 females/male, n = 2608). However, there was no deviation from a 1:1 sex ratio in juveniles (Table 2).

There were no differences between adult males and females in the estimated staying time, i.e. mean number of days elapsed between first and last capture in a given season (Table 3), indicating that both sexes used the Odiel saltpan for similar periods.

Table 2.

Number of adult and juvenile male and female Black-necked Grebes captured at Odiel salt-marshes during 2006–2012. Differences in the abundance of males and females were tested using χ2-tests. Because of multiple testing, probability-values were adjusted with a Bonferroni correction.

t02_207.gif

Black-necked Grebes ringed during moult in the Odiel salt-marshes have been recovered across a large geographical area, spanning from south-central Russia to Morocco and the Canary Islands (Figure 1).

In Central Europe (Belgium, Switzerland, Germany, Czech Republic, Poland, Hungary, Rumania, Belarus and Ukraine) and Russia, most of the grebes (77% of 35) were recovered during the breeding season (March–July). However, in Mediterranean countries (France, Italy, Portugal, Spain and Morocco), more grebes (64% of 53) were recovered outside the breeding season (χ21 = 14.4, P<0.001). This indicates that Black-necked Grebes breeding in Central Europe and Russia use the Odiel salt-marshes as a moulting site, whereas those recovered around the western Mediterranean were mainly moulting/wintering birds.

Table 3.

Dates at which Black-necked Grebes were captured and average number of days elapsed between the first and the last captures of individual male or female adult grebes in a given year. Differences between sexes were tested with Mann—Whitney U-tests.

t03_207.gif

Figure 1.

Geographical distribution of recoveries (dots) of Black-necked Grebes ringed during the moulting period at Odiel saltmarshes in SW Spain (star). Only sites located at >50 km from the ringing site are shown.

f01_207.jpg

DISCUSSION

Our study shows that the sex ratio of adult Blacknecked Grebes at a moulting locality in southern Europe is female-biased, and that this is not due to shorter staying periods of males than females. To our knowledge, this is the first time such a strongly biased sex ratio has been reported in any bird species with biparental care performing moult-migration. Furthermore, sex ratios also remained female-biased in grebes caught before starting wing moult and during and after completing wing moult. Our results suggest that adult males are likely to be more numerous than females at some other Palearctic localities during moulting, but to our knowledge ours is the only study on sex ratios of moulting Black-necked Grebes in Europe. This contrasts with what has been found in North America, where no biased sex ratios have been reported at several moulting sites (Jehl 1988, Cuéllar Brito 2007, Jehl & Henry 2010).

A sexual spatial segregation is common in many duck species during winter, with males wintering further north than females and juveniles (Bellrose et al. 1961, Campredon 1983). It has been suggested that male behavioural dominance is the mechanism behind this latitudinal segregation (Hepp & Hair 1984). However, no intraspecific agonistic interactions are observed among grebes in the moulting sites (Jehl 1988, Varo et al. 2011), hence sexual spatial segregation in the Black-necked Grebe in Europe is not likely to be related to behavioural dominance of males. In the case of the Black-necked Grebe in particular, we propose that the spatial distribution of moulting birds would conform to the ideal free distribution model (Fretwell & Lucas 1970), according to which individuals occur in direct proportion to the availability of resources among habitats. This has been shown for another grebe species during breeding (Sebastián-González et al. 2010).

In the Black-necked Grebe, males finish parental care earlier than females (Cullen et al. 1999). This may allow males to reach the moulting sites in advance of females and juveniles. Depending on the size of wetlands, the carrying capacity of sites could be reached after the arrival of thousands of moult migrating birds. Because the wetlands where the Black-necked Grebes moult in North America are very large, it is unlikely that they reach their carrying capacity. However, this may not be the case in Europe, where the size of wetlands used by Black-necked Grebes to moult is much smaller, which may lead to late moultmigrating adult females and juveniles in Europe having to travel longer distances to moulting sites in which the carrying capacity has not yet been reached.

Perhaps in Europe the distance between the Odiel salt-marshes in SW Spain, one of the most important moulting sites for the Black-necked Grebe in southern Europe, and the main breeding localities of the species is longer than between other moulting and breeding sites of the species on this continent. Black-necked Grebes moulting at Odiel originated from breeding areas all over Europe (Figure 1). Given that the more important breeding populations of Black-necked Grebes in the Palearctic are in south-central Russia and Kazakhstan (Fjeldså 2004), and many moulting sites are in south and south-western Europe (see Introduction), birds moving from Russia/Kazakhstan to moult would first reach the eastern sites, and birds initiating the moult-migration later (i.e. females and juveniles) should have to move to localities located further southwest, such as the Odiel saltpans. Therefore, in Europe there may be an inverse relationship between the proportion of males in moulting sites and the distance between the main breeding areas and moulting sites.

In conclusion, differences in the size and carrying capacity of moulting sites may account for continental differences in the sexual distribution of moulting Blacknecked Grebes between North America and Europe. To test our hypothesis it would be necessary to collect data on sex ratios at moulting sites of grebes across the south-western Palearctic, especially in Eastern Europe.

ACKNOWLEDGEMENTS

Many volunteers from Estación Biológica de Doñana (EBD) and SEO/BirdLife, led by Luis García, trapped grebes over the years. Thanks also to Luis García for his skilfulness in sexing so many birds, and to Equipo de Seguimiento de Procesos Naturales-EBD for the database. The Oficina de Especies Migratorias from Dirección General de Medio Natural y Política Forestal, Ministerio de Medio Ambiente, Medio Rural y Marino, granted access to the database of ringing recoveries. Enrique Martínez, Director of Paraje Natural Marismas del Odiel, and Consejería de Medio Ambiente, Junta de Andalucía, authorised the field work. David Aragonés, from LAST-EBD, drew the map, and Mónica Gutiérrez, from LEM-EBD, did the molecular sexing. Our thanks also to Peter Korsten and Popko Wiersma for comments that greatly improved earlier versions. Financial support was received from Consejería de Innovación, Ciencia y Empresa, Junta de Andalucía/EU-ERDF (project P07-CVI-02700).

REFERENCES

1.

J.A. Amat , J. Lucientes & X. Ferrer 1987. La migración de muda del Pato Colorado (Netta rufina) en España. Ardeola 34: 79–88. Google Scholar

2.

K.G. Beal & H.J. Khamis 1991. A problem in statistical analysis: simultaneous inference. Condor 93: 1023–1025. Google Scholar

3.

F.C. Bellrose , T.G. Scout , A.S. Hawkins & J.B. Low 1961. Sex ratios and age ratios in North American ducks. Illinois Nat. Hist. Survey Bull. 27: 391–474. Google Scholar

4.

P. Campredon 1983. Sexe et âge ratios chez le canard siffleur Anas penelope L. en période hivernale en Europe de l'Ouest. Rev Ecol. 37: 117–128. Google Scholar

5.

G. Cherubini , L. Serra & N. Baccetti 1996. Primary moult, body mass and moult migration of Little Tern Sterna albifrons in NE Italy. Ardea 84: 99–114. Google Scholar

6.

S.D. Cooper , D.W. Winkler & P.H. Lenz 1984. The effect of grebe predation on a brine population. J. Anim. Ecol. 53: 51–64. Google Scholar

7.

S. Cramp & K.E.L. Simmons (eds) 1977. The birds of the western Palearctic, Vol. 1. Oxford University Press, Oxford. Google Scholar

8.

A. Cuéllar Brito 2007. Migración e invernación del Zambullidor Orejón (Podiceps nigricollis), en la salina de Guerrero Negro, B.C.S. M.Sc. Thesis, Instituto Politécnico Nacional, La Paz, Mexico. Google Scholar

9.

S.A. Cullen , J.R. Jehl Jr & G.L. Nuechterlein 1999. Eared Grebe (Podiceps nigricollis). In: A. Poole & F. Gill (eds) The birds of North America, Vol. 433. The Birds of North America, Inc., Philadelphia. Google Scholar

10.

J. Fjeldså 2004. Grebes. Oxford University Press, Oxford. Google Scholar

11.

A.D. Fox , C. Ramo , N. Varo , M.I. Sánchez , J.A. Amat & A.J. Green 2013. Late-moulting Black-necked Grebes Podiceps nigricollis show greater body mass in the face of failing food supply. Ibis 155: 814–822. Google Scholar

12.

S.D. Fretwell & H.L. Lucas 1970. On territorial behaviour and other factors influencing habitat distribution in birds. I. Theoretical development. Acta Biotheor. 19: 16–36. Google Scholar

13.

F.J. García-Jiménez & J.F. Calvo-Sendín 1987. El Zampullín Cuellinegro, Podiceps nigricollis, en la laguna de la Mata (Alicante). Ardeola 34: 102–105. Google Scholar

14.

A.J. Green , A.D. Fox , G. Hilton , B. Hughes , M. Yarar & T. Salathé 1996. Threats to Burdur Lake ecosystem, Turkey and its waterbirds, particularly the White-headed Duck Oxyura leucocephala. Biol. Conserv. 76: 241–252. Google Scholar

15.

R. Griffiths , M.C. Double , K. Orr & R.J.G. Dawson 1998. A DNA test to sex most birds. Mol. Ecol. 7: 1071–1075. Google Scholar

16.

I. Gülle , I.I. Turna , S.S. Güçlü , P. Gülle & Z. Güçlü 2010. Zooplankton seasonal abundance and vertical distribution of highly alkaline Lake Burdur, Turkey. Turk. J. Fish. Aquat. Sc. 10: 245–254. Google Scholar

17.

G.R. Hepp & J.D. Hair 1984. Dominance in wintering waterfowl (Anatini): effects on distribution of sexes. Condor 86: 251–257. Google Scholar

18.

W.L. Hohman , C.D Ankney & D.H. Gordon 1992. Ecology and management of postbreeding waterfowl. In: B.D.J. Batt , A.D. Afton , M.G. Anderson , C.D. Ankney , D.H. Johnson , J.A. Kadlec & G.L. Krapu (eds) Ecology and management of breeding waterfowl. University of Minnesota Press, Minneapolis, pp. 129–189. Google Scholar

19.

O. Iborra , F. Dhermain & P. Vidal 1991. L'hivernage du Grèbe à cou noir sur l'Étang de Berre (Bouches-du-Rhône). Alauda 59: 195–205. Google Scholar

20.

J.R. Jehl Jr. 1988. Biology of the Eared Grebe and Wilson's Phalarope in the nonbreeding season: a study of adaptations to saline lakes. Stud. Avian Biol. 25: 1–74. Google Scholar

21.

J.R. Jehl Jr 1990. Aspects of the molt migration. In: E. Gwinner (ed.) Bird migration: physiology and ecophysiology. Springer, Berlin, pp. 102–113. Google Scholar

22.

J.R. Jehl Jr & A.E. Henry 2010. The postbreeding migration of Eared Grebes. Wilson J. Ornithol. 122: 217–227. Google Scholar

23.

J.R. Jehl Jr. , A.E. Henry & S.I. Bond 1998. Sexing Eared Grebes by bill measurements. Col. Waterbirds 21: 98–100. Google Scholar

24.

N. Kjellén 1994. Moult in relation to migration in birds - a review. Ornis Svecica 4: 1–24. Google Scholar

25.

J. Mayol 1984. Concentración invernal de Zampullín Cuellinegro Podiceps nigricollis C. L. Brehm 1831, en Formentera. Bol. Est. Centr. Ecol. 13: 63–65. Google Scholar

26.

R.B. Payne 1972. Mechanism and control of molt. In: D.S. Farner , J.R. King & K.C. Parkes (eds) Avian biology. Vol. II. Academic Press, New York, pp. 103–155. Google Scholar

27.

W.R. Rice 1989. Analyzing tables of statistical tests. Evolution 43: 223–224. Google Scholar

28.

F. Salomonsen 1968. The moult migration. Wildfowl 19: 5–24. Google Scholar

29.

M.I. Sánchez , A.J. Green & E.M. Castellanos 2006. Temporal and spatial variation of an aquatic invertebrate community subjected to avian predation at the Odiel salt pans (SW Spain). Archiv Hydrobiol. 166: 199–223. Google Scholar

30.

E. Sebastián-González , F. Botella , R.A. Sempere & J.A. Sánchez-Zapata 2010. An empirical demonstration of the ideal free distribution: Little Grebes Tachybaptus ruficollis breeding in intensive agricultural landscapes. Ibis 152: 643–650. Google Scholar

31.

P. Siimaki , M. Hovi & O. Rätti 1994. A trade-off between current reproduction and moult in the Pied Flycatcher - an experiment. Funct. Ecol. 8: 587–593. Google Scholar

32.

R.W. Storer & J.R. Jr. Jehl 1985. Moult patterns and moult migration in the Black-necked Grebe Podiceps nigricollis. Ornis Scand. 16: 253–260. Google Scholar

33.

E. Svensson & J.-fi01_207.gif. Nilsson 1997. The trade-off between molt and parental care: a sexual conflict in the Blue Tit? Behav. Ecol. 8: 92–98. Google Scholar

34.

J. Van Impe 1969. Concentration énorme de Podiceps nigricollis Brehm, en Dobroudja - Roumanie. Alauda 37: 77–79. Google Scholar

35.

N. Varo , A.J. Green , M.I. Sánchez , C. Ramo , J. Gómez & J.A. Amat 2011. Behavioural and population responses to changing availability of Artemia prey by moulting Black-necked Grebes, Podiceps nigricollis. Hydrobiologia 664: 163–171. Google Scholar

Appendices

SAMENVATTING

Het wetlandgebied rondom de monding van de Odielrivier in het zuidwesten van Spanje is een belangrijk ruigebied voor Geoorde Futen Podiceps nigricollis. Elk jaar, in de periode van eind juli tot begin december, verzamelen zich grote aantallen ruiende Geoorde Futen in de ondiepe zoutpannen in het gebied. Bij de Geoorde Fuut dragen beide ouders bij aan de broedzorg. Na afloop van de broedperiode vertonen beide geslachten een ruitrek. Daarom lijkt het aannemelijk dat mannetjes en vrouwtjes naar dezelfde ruigebieden trekken. Dit onderzoek toont aan dat de geslachtsverhouding van de ruiende Geoorde Futen in het Odielgebied sterk afwijkt van een 1:1 ratio. Er verblijven hier veel meer vrouwtjes dan mannetjes. Dit blijkt uit de vangstgegevens uit de jaren 2006–2012, waarin 5821 ruiende Geoorde Futen gevangen werden voor het ringonderzoek. Elk jaar werden het geslacht en de leeftijdsklasse (juveniel of adult) van een groot deel van de gevangen vogels op het oog vastgesteld (78,1–91,1% van de gevangen vogels in een gegeven jaar). Veel van deze vogels werden meermalen in het Odielgebied gevangen (aantal vangsten inclusief hervangsten, n = 12.107). Terugmeldingen van in het Odielgebied geringde Geoorde Futen kwamen uit een groot gebied, dat zich uitstrekt van Centraal-Rusland in het noordoosten tot aan Marokko en de Canarische Eilanden in het zuiden. Van 309 vogels werd een bloedmonster verzameld om het geslacht vast te kunnen stellen door middel van een DNA-analyse. Hieruit bleek dat de geslachtsbepaling op het oog in 85% van de gevallen correct was. Ook waren er geen significante verschillen tussen de berekende geslachtsverhouding op het oog en die gebaseerd op de DNA-analyses. In elk van de zeven onderzochte jaren bleken er significant meer adulte vrouwtjes dan adulte mannetjes te zijn (1,58–4,23 vrouwtjes per mannetje). Bij de juveniele vogels werd geen scheve verhouding tussen mannetjes en vrouwtjes gevonden. Een verschil in de verblijfstijd tussen mannetjes en vrouwtjes kan de afwijkende geslachtsverhouding bij de adulte vogels niet verklaren. Het tijdsinterval tussen de eerste en laatste vangst van individuele vogels in het gebied verschilde namelijk niet tussen beide geslachten. De afwijkende geslachtsverhouding van de ruiende Geoorde Futen in het Odielgebied staat in sterk contrast met de waargenomen geslachtsverhouding (1:1) in Noord-Amerikaanse ruigebieden. Een mogelijke verklaring voor dit verschil zou kunnen zijn dat de meren waarop de Amerikaanse vogels ruien, een veel grotere draagkracht hebben dan de Europese ruigebieden. Daardoor kan een groot deel van die populatie Geoorde Futen daar terecht, terwijl in Europa de kleinere ruigebieden eerder verzadigd raken. Individuen die wat later wegtrekken, vooral vrouwtjes en juveniele vogels, worden hierdoor mogelijk gedwongen om vanuit de broedgebieden verder zuidwaarts te reizen op zoek naar geschikte ruigebieden, bijvoorbeeld aan de monding van de Odielrivier. (PK)

Juan A. Amat, Nico Varo, Marta I. Sánchez, Andy J. Green, and Cristina Ramo "Female-Biased Sex Ratio in Moulting Black-Necked Grebes Podiceps nigricollis in Southern Spain," Ardea 102(2), 207-212, (1 July 2014). https://doi.org/10.5253/arde.v102i2.a10
Received: 8 November 2013; Accepted: 28 July 2014; Published: 1 July 2014
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