Barn Owl - Tyto alba
( Scopoli, 1769 )

 

 

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Subspecies: Unknown
Est. World Population: 1960000-3240000

CITES Status: NOT LISTED
IUCN Status: Least Concern
U.S. ESA Status: NOT LISTED

Body Length:
Tail Length:
Shoulder Height:
Weight:

Top Speed:
Jumping Ability: (Horizontal)

Life Span: in the Wild
Life Span: in Captivity

Sexual Maturity: (Females)
Sexual Maturity: (Males)
Litter Size:
Gestation Period:

Habitat:
This species is found in a great variety of habitats. It mainly occurs in open but not treeless, lowlands, with some trees, including farmland with hedges, ditches, ponds and banks, roadside verges and related rougher terrain, and young conifer plantations, it is also around towns, suburbs, villages or more isolated buildings suitable for daytime roosts and nest-sites and sometimes near refuse dumps. In lower latitudes it is also found in semi-arid and some arid regions with xerophytic vegetation, dwarf shrub and herb communities, deciduous or mixed eucalypt woodland, Acacia savanna, thornbush, heathland, open marshes, mudflats, oil palm (Elaeis guineensis) plantations, irrigation areas, rice paddies and cane fields, and cliffs and rocky coasts in some regions, notably on continental offshore islands. Some island races are found in forest and on small tropical islands the species is found in all available habitats (Bruce et al. 2014). The species is mostly sedentary, with post-breeding dispersal of juveniles (Bruce et al. 2014).

Conservation:

Conservation Actions Underway

Nest boxes are used as part of local conservation efforts in Europe. Conservation measures have also included protection and re-establishment of rough-grassland habitat mosaics, providing prey-rich foraging areas, and controls over use of second-generation anticoagulant rodenticides. Reintroduction schemes in some areas have had mixed success, as well as conflicting with wild populations (Bruce et al. 2014).


Conservation Actions Proposed

Work should continue on the protection and re-establishment of rough grasslands, particularly alongside watercourses, field margins and woodland edge in order to help reduce habitat fragmentation and provide a network of prey-rich foraging grounds. The provision of nest boxes around these habitats is also important. The use of rodenticides should be controlled. Reintroduction projects need to be implemented with care and awareness of the potential dangers of introducing poor and incorrect genetic stock (Tucker and Heath 1994).


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