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Wiesenvögel zählen zu den in Mitteleuropa am stärksten gefährdeten Vogelgilden. Monitoring-Daten der im Grünland brütenden Watvogelarten Austernfischer, Kiebitze, Alpenstrandläufer, Kampfläufer, Bekassine, Großer Brachvogel, Uferschnepfe und Rotschenkel zeigen erhebliche Bestandsveränderungen in den letzten Jahrzehnten. Sowohl in den Niederlanden, dem wichtigsten „Wiesenvogelland“ Europas, als auch in Deutschland und in anderen Ländern gehen die Bestände fast aller Arten zurück. Lediglich Rotschenkel weisen keine negativen Trends ihrer Gesamtpopulation auf. Die Brutpopulationen von Kampfläufern und Alpenstrandläufern in Mitteleuropa stehen offensichtlich kurz vor ihrem Erlöschen. In den Niederlanden hat sich der Rückgang fast aller Arten in den vergangenen Jahren noch einmal beschleunigt. Auch in Deutschland gibt es keine Hinweise auf eine Verbesserung der Situation in jüngerer Zeit. Die Bestandsveränderungen weisen in beiden Ländern große regionale Unterschiede auf. In Deutschland ist das Binnenland am stärksten vom Rückgang betroffen, während der Nordsee-Küstenbereich vergleichsweise stabile Bestände aufweist. Die Verbreitung etlicher früher häufiger Arten wird lückenhaft.
Meadowbird populations in The Netherlands are under great pressure. Recently, predation is named increasingly
often as one of the key factors in contributing to the declines. A four-year research project (2001-2005) aimed to
collect (as yet mostly nonexisting) data to provide a factual basis for this discussion. A country-wide inventory based
on data for wader nests found by volunteers who mark nests for their protection from grazing/mowing indicated that
above-average predation losses are found predominantly in the half-open landscapes of northern and eastern Netherlands,
but also locally in the low-lying open grasslands which are the key areas for meadowbirds. Nest predation has increased in recent years, but the same is true for agricultural losses, at least in areas where no nest-protection takes
place. At a local scale, predation losses vary greatly from area to area and from year to year. Temperature loggers in nest showed that diurnal and nocturnal predators contribute equally in total predation losses up to 50%, but higher predation losses are mainly caused by nocturnal predators. As many as 10 animal species were identified as nest predators
on nests under surveillance with video cameras. Chick survival, investigated using radiotelemetry, was very low. About 60-80% were lost by predation, 5-15% by agricultural activities and 10-15% to all kind of other losses. At least 15
predator species were implied, with an apparently larger share taken by birds (notably Buzzard (16%) and Grey Heron
(7-18%)) than mammals, with one exception: stoat (16%). Of the most-discussed predator species, Carrion Crows were
W. Teunissen et al. Osnabrücker Naturwiss. Mitt. 32 2006
138 remarkably rarely involved in both nest and chick predation, while Red Foxes take a large toll of clutches in some areas, but not in others. Of all losses during the reproductive cycle about 75% and 60% was due to predation in Lapwing and Black-tailed Godwit respectively. Predation on chicks by birds had the largest effect on total breeding success, but at the same time elimination of this loss factor (if at all possible) alone would not be sufficient to establish a self-sustaining population. Predation seems to have become a factor of importance in some areas, in combination with already existing other losses. Our findings suggest that solutions to predation problems probably have to be found in locally/regionally targeted, specific action on multiple fronts rather than countrywide measures.
Black-tailed Godwits (Limosa limosa) have been declining for decades in The Netherlands and so far this has not been slowed by conservation measures. A new form of agri-environment scheme was tried out in 2003-2005 at 6 sites where a ‘grassland mosaic’ (200-300 ha) was created by collectives of farmers through a diverse use of fields including postponed and staggered mowing, (early) grazing, creating ‘refuge strips’ during mowing, and active nest protection. We measured breeding success of godwits in each of the experimental sites and nearby, paired controls. Breeding success was higher (0.28 chicks fledged / pair) in mosaics than in controls, but due to lower agricultural nest losses only. Chick survival was 11 % in both mosaics and controls. The amount of late-mown and other grassland suitable for chicks hardly differed between treatments during the fledging period, mainly due to rainfall delaying postponed mowing in all sites. Chick survival was however positively correlated with site variation in the amount of high grass (>18 cm). Breeding success was high enough to compensate for adult mortality (ca. 0.6) in only one mosaic site. Chick survival was lower than in previous Godwit studies, indicating that additional loss factors have increased. Predation (50-80 % of chicks, mostly by birds) is a candidate, but changes in the suitability of late-mown grassland (insect abundance and sward density in grass monocultures) may also play a role. Consequently a higher management investment is needed to achieve a self-sustaining population.
