This species underwent rapid declines in western Europe, equivalent to c.46% in each decade since 1950, on its wintering grounds in South Africa, equivalent to c.25% in each decade since 1971, and possibly in parts of its Asian range; however, recent evidence indicates a stable or slightly positive population trend overall during the last three generations. Consequently it has been downlisted from Vulnerable and now qualifies as Least Concern because it no longer approaches any of the thresholds for Vulnerable under the IUCN criteria.
AERC TAC. 2003. AERC TAC Checklist of bird taxa occurring in Western Palearctic region, 15th Draft. Available at: http://www.aerc.eu/DOCS/Bird_taxa_of _the_WP15.xls.
Cramp, S.; Perrins, C. M. 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
Dowsett, R. J.; Forbes-Watson, A. D. 1993. Checklist of birds of the Afrotropical and Malagasy regions. Tauraco Press, Li
Sibley, C. G.; Monroe, B. L. 1990. Distribution and taxonomy of birds of the world. Yale University Press, New Haven, USA.
Distribution and populationFalco naumanni
29-32 cm. Small falcon. Male has grey head, uniform rusty upperparts, buff underparts with black spots. Grey band from carpal to tertials and black flight feathers. Grey tail with black subterminal band. Female and immature rusty with black barring and streaking and paler underparts. Similar spp. Common Kestrel F. tinnunculus is larger. Male lacks grey band on wing and has black spotting on upperparts and moustachial stripe. Voice Kye-kye but weaker and hoarser than F. tinnunculus.
breeds in Spain
(to UK), France
, FYRO Macedonia
, Palestinian Authority Territories
, Turkmenistan, Uzbekistan
. Birds winter in southern Spain, southern Turkey, Malta
and across much of Africa, particularly South Africa
. The European population is estimated at 25,000-42,000 pairs, with half of these in Spain. Several thousand pairs breed outside this range, principally in central Asia. Western Palearctic populations have undergone serious declines, although a few have begun to increase again. The western European population has declined by c.95% since 1950, and the species has disappeared from the Ural region of Russia and from northern Kazakhstan, as well as from the western and central parts of the Balkan Peninsula (Davygora 1998, B. Barov in litt.
2007). However, some populations in south-western and central Europe are stable or increasing (Iñigo and Barov 2010) and eastern breeding populations are also reported to be stable (Galushin 2009). Italy has seen a marked population increase and range expansion since 2000 (N. Baccetti in litt.
2010), and the population in Andalucía, Spain, has increased from c.2,100 pairs in 1988 to c.4,800 in 2009 (J. R. Garrido in litt.
2011). In Kazakhstan, the species appears to be stable or increasing slightly, perhaps in association with the abandonment of villages and livestock stations in the 1990s (J. Kamp in litt.
2010). Coordinated counts of the South African wintering population recorded 117,000 birds in 2005/2006 (van Zyl 2007, A. van Zyl in litt.
2007) and 98,000 birds in 2006/2007 (A. van Zyl in litt.
2007), but it is not clear whether this represents a genuine reduction in numbers or whether the missing birds were wintering elsewhere, most likely in East Africa (A. van Zyl in litt.
2007). An enormous roost discovered in January 2007 in Senegal
contained over 28,600 individuals (most likely European/North African breeders). Population justification
The European population is estimated at 25,000-42,000 pairs, with half of these in Spain. Several thousand pairs breed outside this range, principally in central Asia. Wintering population estimates include a roost in Senegal of over 28,600 individuals in January 2007, and 98,000 in south Africa based on roost counts in 2006/2007. The population in China has been estimated at c.100-10,000 breeding pairs and c.50-1,000 individuals on migration (Brazil 2009).Trend justification
Although severe declines were recorded during the second half of the 20th century, the species appears to be stable or increasing slightly in many parts of its range (e.g. Iñigo and Barov 2010), and its overall population trend is considered to have been stable during the last three generations (estimated to be 17 years).Ecology
It is usually a colonial breeder, often in the vicinity of human settlements. It forages in steppe-like habitats, natural and managed grasslands, and non-intensive cultivation. It is mainly migratory, with most breeders overwintering in sub-Saharan Africa, although some travel to parts of north-west Africa, southern Europe and southern Asia. Migrants leave their breeding grounds in September and return between February and April (del Hoyo et al.
1994). It migrates in flocks of varying sizes, usually tens to low hundreds, often with other falcons such as F. tinnunculus
, F. vespertinus
and F. amurensis
(Ferguson-Lees and Christie 2001). Large numbers, sometimes up to thousands, gather at roosts on migration (del Hoyo et al.
1994). They cross water bodies readily on a broad front, flying high enough to be barely detectable; they fly lower over land (often c.20-30 m), particularly on northward migration (Brown et al.
1982, Ferguson-Lees and Christie 2001).Threats
The main cause of its decline was habitat loss and degradation in its Western Palearctic breeding grounds, primarily a result of agricultural intensification, but also afforestation and urbanisation. In South Africa, key grasslands have been lost to agricultural intensification, afforestation and intensive pasture management (Pepler 2000). The use of pesticides may cause direct mortality, but is probably more important in reducing prey populations. The neglect or restoration of old buildings has resulted in the loss of nest-sites (Davygora 1998, J.-P. Biber in litt.
1999). At La Crau in southern France, where such nest sites are rare, a population increase in the 1990s may be linked to the progressive selection of ground nests in stone piles, reducing interspecific and intraspecific competition (Prugnolle et al.
2003).Conservation Actions Underway
CITES Appendix II, CMS Appendix I and II. Research and management of the species, its sites and habitats have been carried out in France, Spain, Portugal, Gibraltar, Italy, Greece, Bulgaria, Turkey, Israel, Jordan and South Africa. A European action plan has been published. Conservation Actions Proposed
Encourage surveys and monitoring. Research limiting factors and habitat management. Promote national action plans. Promote appropriate agricultural policies, control of pesticides and zoned forestry. Construct artificial nests. Protect colonies. Encourage legal protection.
Related state of the world's birds case studies
Biber, J.-P. 1996. International action plan for the Lesser Kestrel Falco naumanni. In: Heredia, B.; Rose, L.; Painter, M. (ed.), Globally threatened birds in Europe: action plans, pp. 191-203. Council of Europe, and BirdLife International, Strasbourg.
Brazil, M. 2009. Birds of East Asia: eastern China, Taiwan, Korea, Japan, eastern Russia. Christopher Helm, London.
Brown, L. H.; Urban, E. K.; Newman, K. 1982. The birds of Africa vol I. Academic Press, London.
Davygora, A.V. 1998. Factors limiting area and numbers of lesser kestrel Falco naumanni in the South Ural steppes. 5th World Conference on Birds of Prey and Owls, Johannesburg, South Africa.
del Hoyo, J.; Elliott, A.; Sargatal, J. 1994. Handbook of the Birds of the World, vol. 2: New World Vultures to Guineafowl. Lynx Edicions, Barcelona, Spain.
Ferguson-Lees, J.; Christie, D. A. 2001. Raptors of the world. Christopher Helm, London.
Pepler, D. 1996. Management of Lesser Kestrels Falco naumanni overwintering in Africa. Thesis. MPhil, University of Cambridge, U.K..
Prugnolle, F.; Pilard, P.; Brun, L. U. C.; Tavecchia, G. 2003. First-year and adult survival of the endangered Lesser Kestrel Falco naumanni in southern France. Bird Study 50: 68-72.
Further web sources of information
Detailed species account from Birds in Europe: population estimates, trends and conservation status (BirdLife International 2004)
Detailed species accounts from the Threatened birds of Asia: the BirdLife International Red Data Book (BirdLife International 2001).
International Action Plan
Text account compilers
Benstead, P., Capper, D., Harding, M., Khwaja, N., Peet, N., Pilgrim, J., Starkey, M., Symes, A., Taylor, J.
Baccetti, N., Biber, J., Garrido, J., Kamp, J., van Zyl, A.
BirdLife International (2014) Species factsheet: Falco naumanni. Downloaded from
http://www.birdlife.org on 16/04/2014.
Recommended citation for factsheets for more than one species: BirdLife International (2014) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 16/04/2014.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.
Additional resources for this species