Identity
Unique IDELEMENT_GLOBAL.2.1215996
Element CodeABNKD02030
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
CITESAppendix II
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderFalconiformes
FamilyFalconidae
GenusCaracara
USESAPS:LT
SynonymsCaracara cheriway(Jacquin, 1784)Caracara cheriway audubonii(Cassin, 1865)Falco plancusJ. F. Miller, 1777Polyborus cheriway(Jacquin, 1784)Polyborus plancus auduboniiCassin, 1865
Other Common NamesCaracará (PT) Caracara-Comun, Carancho (PT) Caracara du Nord (FR) Caracara Quebrantahuesos (ES) Carancho, Traro, Kara Kara (ES) crested caracara (EN)
Concept ReferenceAmerican Ornithological Society (AOS). Chesser, R. T., S. M. Billerman, K. J. Burns, C. Cicero, J. L. Dunn, B. E. Hernández-Baños, A. W. Kratter, I. J. Lovette, N. A. Mason, P. C. Rasmussen, J. V. Remsen, Jr., D. F. Stotz, and K. Winker. 2021. Sixty-second Supplement to the American Ornithological Society’s Check-list of North American Birds. Ornithology 138:1-18.
Taxonomic CommentsGroups: C. cheriway (Jacquin, 1784) [Crested Caracara] and C. plancus [Southern Caracara]. Formerly considered a single species (e.g., AOU 1983, 1998), the groups were separated in AOU (2000). Again treated as conspecific, following Remsen et al. (2021), based on extensive hybridization in the contact zone in Amazonia, clinal variation in phenotype, and an apparent lack of barriers to gene flow (Hellmayr and Conover 1949, Dove and Banks 1999, Fuchs et al. 2012) (AOS 2021).
Formerly included in the genus Polyborus, but that name has no standing because it is based on a type species that is not identifiable (AOU 1993, Banks and Browning 1995).
The Florida population was listed by USFWS as part of subspecies Polyborus plancus audubonii, but this taxon evidently is no longer accepted; audubonii was not mentioned as a distinctive "group" or subspecies by AOU (1983, 1998, 2000) nor by Sibley and Monroe (1990). Johnsgard (1990) included audubonii in subspecies cheriway, and Sibley and Monroe and AOU (1998) included it (unnamed) in the cheriway group. Palmer (1988) recognized audubonii as a valid subspecies. Extinct form on Guadalupe Island now recognized as a distinct species C. lutosa (AOU 2000, Dove and Banks 1999, Sibley and Monroe 1990).
Conservation Status
Review Date2000-09-08
Change Date2000-09-08
Edition Date2000-09-08
Edition AuthorsHammerson, G.; revised by S. Cannings
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences81 to >300
Rank ReasonsCommon in many areas of the very extensive range (southern U.S. to South America); population trend varies regionally; probably increasing with deforestation in some areas, declining with agricultural and other development elsewhere.
Range Extent CommentsResident [cheriway group] in central and southern Florida (north to Manatee, Osceola, and Brevard counties, formerly to St. Johns County), Cuba, and the Isle of Pines, and from northern Baja California, southern Arizona, Sonora, Sinaloa, Zacatecas, Nuevo León, central and southern Texas, and southwestern Louisiana south locally through Middle America (including the Tres Marías Islands off Nayarit), and in South America (including islands off Venezuela from Aruba east to Trinidad) south to northern Peru and northern Brazil; [plancus group] from central Peru and southern Amazonian Brazil south to Tierra del Fuego and the Falkland Islands (AOS 2021).
Casual [cheriway group] north to central New Mexico, southwestern Mississippi, and to islands off Panama (Taboga and Pearl) and Jamaica. Accidental west to Washington, Oregon, and California, and north throughout the United States to Canada (British Columbia, Alberta, Ontario, Quebec, New Brunswick, and Nova Scotia) (AOS 2021).
Threat Impact CommentsIn the U.S., declines have been associated with conversion of habitat to agriculture, residential development, and illegal shooting and trapping; increase in roads and traffic has resulted in increased mortality as the birds feed on road kills. Range has expanded in tropical America concurrent with deforestation; invasion of woody species with overgrazing tends to degrade habitat and result in declines (Ellis et al. 1988). In Texas, Dickinson (1995, Wilson Bull. 107:761-762) observed two instances of red imported fire ant predation on caracara hatchlings.