Long-distance migrants in difficulty

bild

Common Redstart © Beat Rüegger

Overall, numbers of long-distance migrants are gradually declining, while those of short-distance migrants and residents appear to be increasing. This trend is not confined to Switzerland. Compared to short-distance migrants and residents, long-distance migrants are more specialised, more severely affected by habitat changes in breeding and wintering grounds, and thus more vulnerable.

Our native breeding birds can be divided into two groups based on their migration behaviour. Residents and short-distance migrants spend the winter in their breeding grounds or relocate to the Mediterranean region. In many species, only part of the population migrates, while the rest winters in the breeding grounds. The European Robin is an example of such a partial migrant. The second group includes species that mostly winter in sub-Saharan Africa. Only few of our native birds migrate to Asia (mainly India), like the Common Rosefinch.

The overall population trend of long-distance migrants in Switzerland has been negative since 1990, while residents and short-distance migrants are increasing in number. Other European countries report similar findings. Long-term declines are especially evident among long-distance migrants that winter in open habitats and breed in similarly open country in Europe.

Distribution change since 1993–1996 of residents and short-distance migrants (85 species, above) and long-distance migrants (30 species, below). The map combines the distribution change maps of the relevant species. For residents and short-distance migrants, the resulting picture is far from uniform, but reflects a positive overall development. In contrast, the trend for long-distance migrants is almost entirely negative at lower and medium altitudes.

Long-distance migrants are particularly vulnerable

It became apparent around 1960 that long-distance migrants were in difficulty. A first wave of decline occurred between then and 1970, in some cases continuing into the early 1980s. The decline concerned species wintering in the Sahel zone, which was affected by drought at the time. A second phase began in the 1980s and involved species that winter in the tropics and the forest zone of Guinea in West Africa, such as Willow Warbler and Wood Warbler. But still today, the declines predominantly affect species that winter in dry, open habitats in Africa.

Long-distance migrants tend to be specialists. They have evolved to spend short periods of time in the breeding grounds, occupying habitats and searching for food that is available only briefly (mostly insects in dense vegetation or in open terrain that is uninhabitable in winter). Residents and short-distance migrants, in contrast, need to be generalists (e.g. corvids, finches or sparrows) that can cope with the constant seasonal change of food sources and habitats. Moreover, long-distance migrants travel between several completely different locations, spending 4–5 months in the breeding grounds, two months on spring and autumn migration, and 5–6 months in the wintering sites. Certain species move considerable distances within the wintering range, while others stay in one location, returning to the same site year after year. Long-distance migrants are thus vulnerable in several respects: As specialists, habitat changes at one of the sites frequented in the course of the year can quickly put them under pressure. Moreover, they need to be in certain places at certain times, in keeping with their tight annual schedule. Finally, many species face a high risk of mortality during migration.

Swiss Bird Index SBI® for residents and short-distance migrants (green) and long-distance migrants (blue). While the first group has done well (with some exceptions), long-distance migrants have declined overall.

Changes in breeding grounds play a decisive role in the decline

Compared to residents and short-distance migrants, the group of long-distance migrants includes more species that occupy open habitats such as farmland, but also wetlands. There have been significant changes in these types of habitat both in the breeding and in the wintering grounds, so it is not possible to attribute the decline to either one or the other.

In the breeding grounds, open habitats in particular have deteriorated: farming practices have intensified, causing the decline of farmland breeding birds; wetlands have decreased in size and often suffer from a lack of water, causing the local extinction of species. The fact that long-distance migrants have above all disappeared from the Swiss lowlands, where the impact of human activity is especially strong, is an indication that the decline is largely «home-made».

For each altitude level, the graph shows the average number of species of long-distance migrants per kilometre square in 1993–1996 (light blue) and 2013–2016 (dark blue). Species richness declined in areas below 1500 m while staying constant above that altitude, suggesting that many causes of decline can be found in the breeding grounds.

Changes in the wintering grounds are also detrimental

Migrating birds face huge problems if stopover sites are unavailable. In particular, stopover sites at the edge of the Sahara are essential for migrants that replenish their fat reserves there (in northern Africa during autumn migration, in the Sahel during spring migration).

In the 1970s, the Sahel zone suffered from massive drought, leading to the decline of several species that winter in this region (e.g. Common Redstart, European Pied Flycatcher, Collared Sand Martin and commonr Whitethroat). Rainfall has increased again in the Sahel since the 1990s, without however reaching the amounts of earlier years. The area also suffers from deforestation. Landscapes are changing rapidly in the more southern latitudes of Africa as well, as forests are cleared, trees in the savannah are thinned out, and water use increases. Other negative factors include hunting of birds in the Mediterranean region and North Africa as well as climate change, which tends to cause droughts and irregular rainfall along the migration routes and in Africa.

Long-distance migrants have evolved remarkable adaptations and accomplish extraordinary feats of flight. Barn Swallow, Common Nightingale and Eurasian Golden Oriole manage to take advantage of peak insect abundance during summer in Europe while spending the rest of the year thousands of kilometres away. We must make every effort to offer them the best possible conditions in our country.

keine Übersetzung benötigt: Lukas Jenni & Hans Schmid


Recommended citation of the Atlas online:
Knaus, P., S. Antoniazza, S. Wechsler, J. Guélat, M. Kéry, N. Strebel & T. Sattler (2018): Swiss Breeding Bird Atlas 2013–2016. Distribution and population trends of birds in Switzerland and Liechtenstein. Swiss Ornithological Institute, Sempach.

References

BAFU & BLW (2008): Umweltziele Landwirtschaft. Hergeleitet aus bestehenden rechtlichen Grundlagen. Umwelt-Wissen Nr. 0820. Bundesamt für Umwelt (BAFU) und Bundesamt für Landwirtschaft (BLW), Bern.

Birrer, S., P. Mosimann-Kampe, M. Nuber, S. Strebel & N. Zbinden (2013): Ökologischer Ausgleich und Brutvögel - das Beispiel Grosses Moos 1997-2009. Ornithol. Beob. 110: 475–494.

Birrer, S., P. Mosimann-Kampe & S. Strebel (2018): Brutvogelmonitoring Grosses Moos. Bericht 2017. Schweizerische Vogelwarte, Sempach.

BLW (2017): Agrarbericht 2017. Bundesamt für Landwirtschaft (BLW), Bern.

Bundesamt für Statistik (2015): Die Bodennutzung in der Schweiz. Auswertungen und Analysen. Statistik der Schweiz, Fachbereich 2, Raum und Umwelt 002-0905. Bundesamt für Statistik (BFS), Neuchâtel.

Chevillat, V., S. Stöckli, S. Birrer, M. Jenny, R. Graf, L. Pfiffner & J. Zellweger-Fischer (2017a): Mehr und qualitativ wertvollere Biodiversitätsförderflächen dank Beratung. Agrarforsch. Schweiz 8: 232–239.

Chevillat, V., S. Stöckli, S. Birrer, M. Jenny, R. Graf, L. Pfiffner & J. Zellweger-Fischer (2017b): Surfaces de promotion de la biodiversité: amélioration quantitative et qualitative par le conseil. Rech. Agron. Suisse 8: 232–239.

Christen, W. (2017): Bestandsentwicklung von zehn Brutvogelarten in der Aareebene bei Solothurn von 1982 bis 2016. Ornithol. Beob. 114: 25–40.

de Baan, L., S. Spycher & O. Daniel (2015a): Einsatz von Pflanzenschutzmitteln in der Schweiz von 2009 bis 2012. Agrarforsch. Schweiz 6: 48–55.

de Baan, L., S. Spycher & O. Daniel (2015b): Utilisation des produits phytosanitaires en Suisse de 2009 à 2012. Rech. Agron. Suisse 6: 48–55.

Guntern, J., T. Lachat, D. Pauli & M. Fischer (2013a): Flächenbedarf für die Erhaltung der Biodiversität und der Ökosystemleistungen in der Schweiz. Kurzfassung. Forum Biodiversität Schweiz der Akademie der Naturwissenschaften SCNAT, Bern.

Guntern, J., T. Lachat, D. Pauli & M. Fischer (2013b): Surface requise pour la sauvegarde de la biodiversité en Suisse. Version courte. Forum Biodiversité Suisse, Académie suisse des sciences naturelles (SCNAT), Berne.

Jenny, M., O. Holzgang & N. Zbinden (2005a): Das Rebhuhn - Symbol für eine artenreiche Kulturlandschaft. Avifauna Report Sempach 4. Schweizerische Vogelwarte, Sempach.

Jenny, M., O. Holzgang & N. Zbinden (2005b): La Perdrix grise - symbole d'un paysage agricole diversifié. Avifauna Report Sempach 4. Station ornithologique suisse, Sempach.

Jenny, M., B. Josephy & B. Lugrin (2003): Ökologische Aufwertungsmassnahmen in Ackerbaugebieten und ihre Auswirkungen auf ausgewählte Brutvogelarten. S. 151–155 in: R. Oppermann & H. U. Gujer (Hrsg.): Artenreiches Grünland, bewerten und fördern: MEKA und ÖQV in der Praxis. Ulmer, Stuttgart.

Jenny, M., J. Zellweger-Fischer, L. Pfiffner, S. Birrer & R. Graf (2011a): Leitfaden für die Anwendung des Punktesystems. Biodiversität auf Landwirtschaftsbetrieben im Projekt "Mit Vielfalt punkten - Bauern beleben die Natur". Schweizerische Vogelwarte, Sempach, und Forschungsinstitut für biologischen Landbau, Frick.

Jenny, M., J. Zellweger-Fischer, L. Pfiffner, S. Birrer & R. Graf (2011b): Manuel d'utilisation du système de points. La biodiversité dans les domaines agricoles, avec le projet "Les paysans marquent des points - la nature gagne en diversité". Station ornithologique suisse, Sempach, et Institut de recherche pour l’agriculture biologique (FiBL), Frick.

Knaus, P., R. Graf, J. Guélat, V. Keller, H. Schmid & N. Zbinden (2011): Historischer Brutvogelatlas. Die Verbreitung der Schweizer Brutvögel seit 1950/Atlas historique des oiseaux nicheurs. La répartition des oiseaux nicheurs de Suisse depuis 1950. Schweizerische Vogelwarte/Station ornithologique suisse, Sempach.

Martinez, N. & S. Birrer (2017): Entwicklung ausgewählter Vogelarten im Landwirtschaftsgebiet des Kantons Basel-Landschaft. Ornithol. Beob. 114: 161–178.

Meichtry-Stier, K. S., J. Duplain, M. Lanz, B. Lugrin & S. Birrer (in Vorb.): The importance of size, location and vegetation composition of perennial fallows for farmland birds.

Meichtry-Stier, K. S., M. Jenny, J. Zellweger-Fischer & S. Birrer (2014): Impact of landscape improvement by agri-environment scheme options on densities of characteristic farmland bird species and brown hare (Lepus europaeus). Agric. Ecosyst. Environ. 189: 101–109.

Meichtry-Stier, K. S., F. Korner-Nievergelt, U. Kormann, M. Spiess, P. Mosimann-Kampe, S. Strebel, J.-L. Zollinger & R. Spaar (2013): Habitatwahl der Dorngrasmücke Sylvia communis in der Westschweiz: Folgerungen für die Artenförderung. Ornithol. Beob. 110: 1–15.

OFAG (2017): Rapport agricole 2017. Office fédéral de l’agriculture (OFAG), Berne.

OFEV & OFAG (2008): Objectifs environnementaux pour l’agriculture. A partir de bases légales existantes. Connaissance de l'environnement n° 0820. Office fédéral de l’environnement (OFEV) et Office fédéral de l’agriculture (OFAG), Berne.

Office fédéral de la statistique (2015): L’utilisation du sol en Suisse. Exploitation et analyse. Statistique de la Suisse, domaine 2, Espace et environnement 002-0906. Office fédéral de la statistique (OFS), Neuchâtel.

Rudin, M., P. Horch, I. Hugentobler, U. Weber & S. Birrer (2010): Bestandsentwicklung von Brutvögeln im ökologisch aufgewerteten St. Galler Rheintal. Ornithol.Beob. 107: 81–100.

UFAG (2017): Rapporto agricolo 2017. Ufficio federale dell'agricoltura (UFAG), Berna.

Walter, T., S. Eggenberg, Y. Gonseth, F. Fivaz, C. Hedinger, G. Hofer, A. Klieber-Kühne, N. Richner, K. Schneider, E. Szerencsits & S. Wolf (2013a): Operationalisierung der Umweltziele Landwirtschaft. Bereich Ziel- und Leitarten, Lebensräume (OPAL). ART-Schriftenreihe 18. Forschungsanstalt Agroscope Reckenholz-Tänikon ART, Tänikon.

Walter, T., S. Eggenberg, Y. Gonseth, F. Fivaz, C. Hedinger, G. Hofer, A. Klieber-Kühne, N. Richner, K. Schneider, E. Szerencsits & S. Wolf (2013b): Opérationnalisation des objectifs environnementaux pour l’agriculture. Domaine espèces cibles et caractéristiques, milieux naturels (OPAL). ART-Schriftenreihe 18. Agroscope, Tänikon.

Weggler, M. & Y. Schwarzenbach (2011): Zusammenhänge zwischen der Bestandsentwicklung der Brutvögel 1988-2008 und der Quantität und Qualität der Ökoflächen im Landwirtschaftsgebiet im Kanton Zürich. Ornithol. Beob. 108: 323–344.

Zollinger, J.-L. (2012): Oiseaux nicheurs de jachères florales. Nos Oiseaux 59: 123–142.

Zollinger, J.-L., S. Birrer, N. Zbinden & F. Korner-Nievergelt (2013): The optimal age of sown field margins for breeding farmland birds. Ibis 155: 779–791.

 

Species concerned
Subject
Mountains & Alpine habitats
Waters and wetlands
Farming area
Climate change & weather
Species in decline
Atlas bestellen