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Justification Justification of Red List Category This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence 30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern. Population justification The global population size is estimated at 700,000-704,000 individuals (Wetlands International 2015). The European population is estimated at 224,000-247,000 pairs, which equates to 447,000-495,000 mature individuals (BirdLife International 2015). Trend justification The overall population trend is increasing, although some populations are decreasing or stable (Wetlands International 2015).

The population in Europe is estimated to have undergone a moderate increase between 1980 and 2013 (EBCC 2015). Ecology Behaviour This species is a Palearctic migrant (del Hoyo et al. 1992) that travels with the assistance of thermal updrafts, the occurrence of which restricts the migratory routes the species can take (Hancock et al. For example the species must avoid long stretches of open water such as the Mediterranean Sea and must therefore bypass it on narrow fronts to the west or east (Snow and Perrins 1998, Van den Bossche 2002), after which it crosses the Sahara on a broad front (Brown et al. Once within Africa the species becomes considerably nomadic in response to changing abundances of food (e.g.

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Locust swarms) (Hancock et al. It breeds from February to April in the Palearctic, whilst the tiny breeding population in South Africa breeds from September to November (del Hoyo et al. It nests in loose colonies of up to 30 pairs (Hancock et al. 1992, del Hoyo et al. 1992) or solitarily (del Hoyo et al. The main departure from the European breeding grounds occurs in August (Hancock et al. 1992) with the species travelling in large flocks (Brown et al.

1982, Hancock et al. 1992) of many thousands of individuals (Snow and Perrins 1998), generally arriving in Africa by early-October (Brown et al. It forages singly, in small groups of 10-50 individuals (Hockey et al. 2005), or in large flocks if prey is abundant and on its wintering grounds it may gather in large numbers (hundreds or thousands of individuals) at abundant food sources (e.g. Locust swarms or grass fires) (Hancock et al. The species feeds diurnally (Hancock et al. 1992) and roosts communally at night in trees (Brown et al.

Habitat The species inhabits open areas, generally avoiding regions with persistent cold, wet weather or large tracts of tall, dense vegetation such as reedbeds or forests (Hancock et al. 1992, del Hoyo et al. 1992, del Hoyo et al.

1992), shallow marshes, lakesides (Hancock et al. 1992, del Hoyo et al.

1992), lagoons (del Hoyo et al. 1992), flood-plains, rice-fields and arable land (Snow and Perrins 1998) especially where there are scattered trees for roosting (del Hoyo et al. Non-breeding During the winter the species shows a preference for drier habitats (Hancock et al. 1992) such as grasslands, steppe, savanna and cultivated fields (del Hoyo et al.

1992), often gathering near lakes, ponds (Hancock et al. 1992), pools, slow-flowing streams, ditches (del Hoyo et al.

1992) or rivers (Hancock et al. Diet The species is carnivorous and has a varied and opportunistic diet (del Hoyo et al.

Cesmm3 explained pdf free download. It takes small mammals (del Hoyo et al. Voles, water voles, mice, shrews, young rats (Hancock et al. 1992)), large insects (e.g. Beetles, grasshoppers, crickets and locusts), adult and juvenile amphibians, snakes, lizards, earthworms, fish (del Hoyo et al. 1992), eggs and nestlings of ground-nesting birds, molluscs and crustaceans (Hancock et al. Breeding site The nest is constructed of sticks (del Hoyo et al.

1992) and is commonly positioned up to 30 m above the ground (Brown et al. 1982) in trees or on the roofs of buildings, as well as on pylons, telegraph poles, stacks of straw and other anthropogenic sites (including specially erected nesting structures), cliffs and occasionally among rushes on the ground (del Hoyo et al. The species nests solitarily or in loose colonies, often using traditional nesting sites (there are records of individual nests being used every year for 100 years) (Hancock et al. 1992, del Hoyo et al.

Nesting sites are usually situated near foraging areas, but may be up to 2-3 km away (Snow and Perrins 1998). Management information Intensively grazed (> 1 cow per hectare) unfertilised grassland was found to attract a higher abundance of this species in Hungary (Baldi et al. 2005), and traditional livestock-farming practices such as creating herb-rich meadows for stock grazing and hay production are thought to be beneficial (Goriup and Schulz 1990).

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Justification Justification of Red List Category This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence 30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern. Population justification The global population size is estimated at 700,000-704,000 individuals (Wetlands International 2015). The European population is estimated at 224,000-247,000 pairs, which equates to 447,000-495,000 mature individuals (BirdLife International 2015). Trend justification The overall population trend is increasing, although some populations are decreasing or stable (Wetlands International 2015).

The population in Europe is estimated to have undergone a moderate increase between 1980 and 2013 (EBCC 2015). Ecology Behaviour This species is a Palearctic migrant (del Hoyo et al. 1992) that travels with the assistance of thermal updrafts, the occurrence of which restricts the migratory routes the species can take (Hancock et al. For example the species must avoid long stretches of open water such as the Mediterranean Sea and must therefore bypass it on narrow fronts to the west or east (Snow and Perrins 1998, Van den Bossche 2002), after which it crosses the Sahara on a broad front (Brown et al. Once within Africa the species becomes considerably nomadic in response to changing abundances of food (e.g.

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Locust swarms) (Hancock et al. It breeds from February to April in the Palearctic, whilst the tiny breeding population in South Africa breeds from September to November (del Hoyo et al. It nests in loose colonies of up to 30 pairs (Hancock et al. 1992, del Hoyo et al. 1992) or solitarily (del Hoyo et al. The main departure from the European breeding grounds occurs in August (Hancock et al. 1992) with the species travelling in large flocks (Brown et al.

1982, Hancock et al. 1992) of many thousands of individuals (Snow and Perrins 1998), generally arriving in Africa by early-October (Brown et al. It forages singly, in small groups of 10-50 individuals (Hockey et al. 2005), or in large flocks if prey is abundant and on its wintering grounds it may gather in large numbers (hundreds or thousands of individuals) at abundant food sources (e.g. Locust swarms or grass fires) (Hancock et al. The species feeds diurnally (Hancock et al. 1992) and roosts communally at night in trees (Brown et al.

Habitat The species inhabits open areas, generally avoiding regions with persistent cold, wet weather or large tracts of tall, dense vegetation such as reedbeds or forests (Hancock et al. 1992, del Hoyo et al. 1992, del Hoyo et al.

1992), shallow marshes, lakesides (Hancock et al. 1992, del Hoyo et al.

1992), lagoons (del Hoyo et al. 1992), flood-plains, rice-fields and arable land (Snow and Perrins 1998) especially where there are scattered trees for roosting (del Hoyo et al. Non-breeding During the winter the species shows a preference for drier habitats (Hancock et al. 1992) such as grasslands, steppe, savanna and cultivated fields (del Hoyo et al.

1992), often gathering near lakes, ponds (Hancock et al. 1992), pools, slow-flowing streams, ditches (del Hoyo et al.

1992) or rivers (Hancock et al. Diet The species is carnivorous and has a varied and opportunistic diet (del Hoyo et al.

Cesmm3 explained pdf free download. It takes small mammals (del Hoyo et al. Voles, water voles, mice, shrews, young rats (Hancock et al. 1992)), large insects (e.g. Beetles, grasshoppers, crickets and locusts), adult and juvenile amphibians, snakes, lizards, earthworms, fish (del Hoyo et al. 1992), eggs and nestlings of ground-nesting birds, molluscs and crustaceans (Hancock et al. Breeding site The nest is constructed of sticks (del Hoyo et al.

1992) and is commonly positioned up to 30 m above the ground (Brown et al. 1982) in trees or on the roofs of buildings, as well as on pylons, telegraph poles, stacks of straw and other anthropogenic sites (including specially erected nesting structures), cliffs and occasionally among rushes on the ground (del Hoyo et al. The species nests solitarily or in loose colonies, often using traditional nesting sites (there are records of individual nests being used every year for 100 years) (Hancock et al. 1992, del Hoyo et al.

Nesting sites are usually situated near foraging areas, but may be up to 2-3 km away (Snow and Perrins 1998). Management information Intensively grazed (> 1 cow per hectare) unfertilised grassland was found to attract a higher abundance of this species in Hungary (Baldi et al. 2005), and traditional livestock-farming practices such as creating herb-rich meadows for stock grazing and hay production are thought to be beneficial (Goriup and Schulz 1990).

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