VU
Sooty Falcon Falco concolor



Taxonomy

Taxonomic source(s)
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. and Simmons, K.E.L. (eds). 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.

IUCN Red list criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - C2a(ii)

Red List history
Year Category Criteria
2021 Vulnerable C2a(ii)
2017 Vulnerable C2a(ii)
2016 Near Threatened C1+2a(ii)
2013 Near Threatened C1+2a(ii)
2012 Near Threatened C1+2a(ii)
2008 Near Threatened C1; C2a(ii)
2004 Least Concern
2000 Lower Risk/Least Concern
1994 Lower Risk/Least Concern
1988 Lower Risk/Least Concern
Species attributes

Migratory status full migrant Forest dependency Low
Land mass type Average mass -
Distribution

Estimate Data quality
Extent of Occurrence breeding/resident (km2) 6,140,000 medium
Extent of Occurrence non-breeding (km2) 2,370,000 medium
Number of locations -
Severely Fragmented -
Population and trend
Value Data quality Derivation Year of estimate
No. of mature individuals 2800-4000 poor estimated 2014
Population trend Decreasing poor inferred -
Decline (3 years/1 generation past) - - -
Decline (5 years/1 generation past) - - -
Decline (10 years/1 generation past) - - -
Decline (10 years/3 generation future) - - -
Decline (10 years/3 generation past and future) - - -
Number of subpopulations 1 - - -
Percentage in largest subpopulation 100 - - -
Generation length (yrs) 4.1 - - -

Population justification: Estimating the total population has proved notoriously difficult, partly due to lack of data, and the population may have been overestimated in the past (Kavanaugh and King 2008). Estimates of the total populations have ranged from 1,000-40,000 pairs, roughly equivalent to 2,000-80,000 mature individuals, and 3,000-120,000 individuals in total (Nicoll et al. 2008). However, there are now thought to be no more than a few thousand wintering in Madagascar and a review of all Arabian census data found that the total Arabian population is probably just below 500 breeding pairs (Jennings and Sadler 2006; F. Hawkins in litt. 2007). Given that the Arabian population is generally regarded as the largest within its range (perhaps half of the world population), the estimate from Madagascar may indeed prove to be accurate (Jennings and Sadler 2006). Knowledge gaps about the population exist for inland areas of Egypt, Sudan, and Libya, and from the islands of the Dhalak Archipelago, Eritrea, and some Egyptian islands in the Red Sea. More recently, the draft International Single Species Action Plan for the species has provided clearer population estimates, with the breeding population estimated at 1,400-2,000 pairs (Gallo-Orsi et al. 2014), equating to 2,800-4,000 mature individuals.

This species is migratory and based on its wintering grounds and passage route it is assumed that all individuals have an opportunity to mix. Therefore it is tentatively assumed to function as one subpopulation.

Trend justification: There have been declines in the breeding population in many countries, with no population known to be increasing (Kavanaugh and King 2008; Gallo-Orsi et al. 2014; McGrady et al. 2017). Anecdotal evidence from Madagascar indicates a decline, and this is mirrored by data from breeding colonies in the Middle East (Kavanagh and King 2003; F. Hawkins in litt. 2007; M. McGrady et al. 2017, 2018, 2019); each of the latter when surveyed has shown a decline relative to previous survey results (McGrady and Nicoll 2008; Shah et al. 2008; McGrady et al. 2018, 2019). The small population in the UAE declined from 14-25 pairs in 1996 to five pairs in 2007 (Shah et al. 2008). The draft ISSAP also reports that there have been declines in the breeding population in many countries, including up to a 50% decline in Saudia Arabia, which holds c.15% of the population, with no population known to be increasing (Gallo-Orsi et al. 2014). Therefore a slow or moderate and ongoing population decline is inferred to be taking place, the overall rate of which has not been quantified, but is not currently thought to be >20% over three generations.


Country/territory distribution
Country/Territory Occurrence status Presence Resident Breeding Non-breeding Passage
Bahrain N Extant Yes
Cyprus V Extant
Djibouti N Extant Yes
Egypt N Extant Yes
Eritrea N Extant Yes
Iran, Islamic Republic of N Extant Yes
Israel N Extant Yes
Jordan N Extant Yes
Kenya N Extant Yes
Kuwait V Extant Yes Yes
Libya N Extant Yes
Madagascar N Extant Yes
Mali V Extant
Malta V Extant
Mauritius N Extant Yes
Mozambique N Extant Yes Yes
Oman N Extant Yes
Pakistan N Extant Yes
Palestine N Extant Yes
Qatar N Extant Yes
Réunion (to France) N Extant Yes
Saudi Arabia N Extant Yes
Seychelles V Extant Yes Yes
Somalia N Extant Yes
South Africa N Extant Yes
Sudan N Extant Yes
Syria V Extant Yes
Tanzania N Extant Yes
Turkey V Extant
United Arab Emirates N Extant Yes
Yemen N Extant Yes
Zimbabwe V Extant

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Djibouti Les Sept Frères
Egypt Hurghada archipelago
Egypt Wadi Gimal island
Egypt Qulân islands
Egypt Zabargad island
Egypt Nabq Protected Area
Egypt Gebel Elba
Egypt The Abraq area
Egypt St Katherine Protectorate
Egypt Gebel Maghara
Egypt Quseima
Egypt Wadi Gerafi
Eritrea Dehalak Archipelago and offshore islands
Eritrea Ghinda
Libya Zallaf
Libya Ghat oases
Niger NNR Aïr - Ténéré
Sudan Mukawwar island and Dunganab bay
Sudan Khor Arba'at
Chad Ouadi Rimé - Ouadi Achim
United Arab Emirates Dalma
Bahrain Hawar Islands
Israel Judean desert
Israel Northern Arava valley
Israel Cliffs of Zin and the Negev highlands
Israel Southern Arava valley and Elat mountains
Jordan Wadi Mujib
Jordan Dana
Jordan Petra
Jordan Aqaba coast and mountains
Oman Bandar Jussah
Oman Ra's Abu Da'ud
Oman Daymaniyat Islands
Oman Ra's as Sawadi - Juzor as Sawadi
Oman Fahl Island
Saudi Arabia Al-Wajh Bank
Saudi Arabia Qishran Bay
Saudi Arabia Kutambil island
Saudi Arabia Farasan Islands
Yemen Islands north of Al-Hudaydah
Jordan Hisma Basin - Rum
Oman Musandam islands
Yemen Bahr Ibn Abbas - Ra's Isa
Yemen Hawf deciduous cloud forest
Yemen Al-Mukha - Al-Khawkhah
Yemen Jaza'ir al-Hanish
Yemen Zubayr group of islands
Kenya Lolldaiga-Mugogodo-Ewaso N'yiro
United Arab Emirates Faziya
United Arab Emirates Ghagha Island

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Desert Hot major breeding
Forest Subtropical/Tropical Dry suitable non-breeding
Forest Subtropical/Tropical Moist Lowland suitable non-breeding
Marine Coastal/Supratidal Sea Cliffs and Rocky Offshore Islands major breeding
Rocky areas (eg. inland cliffs, mountain peaks) suitable breeding
Savanna Dry suitable non-breeding
Shrubland Subtropical/Tropical Dry suitable non-breeding
Shrubland Subtropical/Tropical Moist suitable non-breeding
Altitude 0 - 1500 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Scale Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Minority (<50%) Unknown Unknown
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Hunting & trapping terrestrial animals - Persecution/control Timing Scope Severity Impact
Ongoing Minority (<50%) Unknown Unknown
Stresses
Species mortality
Human intrusions & disturbance Recreational activities Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance
Human intrusions & disturbance Work & other activities Timing Scope Severity Impact
Ongoing Minority (<50%) Unknown Unknown
Stresses
Species disturbance
Pollution Agricultural & forestry effluents - Herbicides and pesticides Timing Scope Severity Impact
Ongoing Minority (<50%) Unknown Unknown
Stresses
Reduced reproductive success

Utilisation
Purpose Primary form used Life stage used Source Scale Level Timing
Pets/display animals, horticulture - - International Non-trivial Recent

Recommended citation
BirdLife International (2022) Species factsheet: Falco concolor. Downloaded from http://www.birdlife.org on 06/07/2022. Recommended citation for factsheets for more than one species: BirdLife International (2022) IUCN Red List for birds. Downloaded from http://www.birdlife.org on 06/07/2022.