Identity
Unique IDELEMENT_GLOBAL.2.106553
Element CodeABNSB10010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
CITESAppendix II
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderStrigiformes
FamilyStrigidae
GenusAthene
SynonymsSpeotyto cunicularia
Other Common Namesburrowing owl (EN) Chevêche des terriers (FR) Coruja-Buraqueira (PT) Tecolote Llanero, Lechucita de las Viscacheras (ES)
Concept ReferenceAmerican Ornithologists' Union (AOU). 1998. Check-list of North American birds. Seventh edition. American Ornithologists' Union, Washington, D.C. [as modified by subsequent supplements and corrections published in The Auk]. Also available online: http://www.aou.org/.
Taxonomic CommentsPlaced in genus Athene by AOU (1997). Karyotypic studies suggest separate generic status as Speotyto (AOU 1991). Sibley and Monroe (1990) cited DNA-DNA hybridization evidence in asserting that Speotyto cunicularia is not closely related to owls of the genus Athene.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2024-04-12
Change Date1996-11-27
Edition Date2024-04-12
Edition AuthorsGundy, R. L. (2024)
Threat ImpactHigh
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Rank ReasonsThis species is widespread throughout the Western Hemisphere, although populations are localized. Populations in the United States and Canada have been in decline for decades. Threats include habitat loss due to development and agriculture, habitat becoming less suitable as burrow-digging mammals are lost and as disturbance by humans and domestic animals increases, pesticide exposure, invasive predators, and collisions with man-made objects.
Range Extent CommentsThe range includes much of the Western Hemisphere. The range extends from southwestern Canada southward through North America, Central America, and South America as far south as Santa Cruz Province, Argentina and includes parts of the Caribbean (COSEWIC 2017, Poulin et al. 2020, Saggese and Montero 2021, Fink et al. 2023). A migratory population occupies the portion of the range from southwestern Canada to the southwestern United States from April to September, and that population occupies the portion of the range from central México to El Salvador from September through March (COSEWIC 2017, Poulin et al. 2020, Fink et al. 2023). Other populations are year-round residents. Using Global Biodiversity Information Facility (GBIF 2024) records since 2004 (i.e., the past 20 years), range extent was calculated to be approximately 40 million km² (GeoCat 2024).
Throughout the range, occurrences are very localized and unevenly distributed with large portions of the range unoccupied (Tipton et al. 2009, Wilkerson and Siegel 2011, Ruiz Ayma et al. 2016, COSEWIC 2017, Fink et al. 2023). In the Caribbean, it is found in The Bahamas, Cuba, and on the island of Hispaniola in the countries of Haiti and the Dominican Republic (Thorstrom and Gallardo 2017, Gallardo and Thorstrom 2019). It is absent east of the Mississippi River in the United States except for parts of Florida (Bowen 2001). It is generally absent in much of Central America, the northern Andes, and the Amazon Basin (Poulin et al. 2020).
Occurrences CommentsThe number of distinct breeding occurrences has not been determined using standardized criteria. There are likely many hundreds to a few thousand occurrences throughout the range, but more information is needed in Central America and South America to accurately assess the number of occurrences.
Threat Impact CommentsHabitat loss due to conversion to agriculture and urban development continues to occur throughout the range (Villarreal et al. 2005, Panella 2013, Baladrón et al. 2016, Valencia-Maldonado et al. 2016, COSEWIC 2017). The hunting and persecution of fossorial mammals that initially dig burrows used by burrowing owls causes a reduction in habitat quality and suitability over time (Evans 1982, Conway and Pardieck 2006, Panella 2013, COSEWIC 2017, Conway et al. 2018, Sheffield 2021). Disturbance by humans and unleashed dogs causes the abandonment of otherwise suitable sites (Panella 2013, COSEWIC 2017). Industry, utility, and wind energy developments in North America cause fatal collisions as well as habitat fragmentation (Panella 2013, COSEWIC 2017, Linger et al. 2018). Exposure to insecticides, rodenticides, herbicides, and other contaminants can have negative impacts that are direct (e.g. illness, mortality) and indirect (e.g. prey species reduction) (Engelman et al. 2012, Panella 2013, COSEWIC 2017, Justice-Allen and Loyd 2017). See COSEWIC (2017) for a summary of pesticide usage in the breeding range. In the Caribbean, mongoose (Herpestes auropunctatus), black rat (Rattus rattus), and brown rat (R. norvegicus) are suspected of extirpating several island populations (Gallardo and Thorstrom 2019). Storms during the migration and the non-breeding season are thought to have negative impacts on adult survival in the migratory population (Wellicome et al. 2014).
Partners in Flight considered threats to be high in the breeding range and moderate in the non-breeding range, although exact threats were not detailed (Rosenberg et al. 2016).