Passerina ciris

(Linnaeus, 1758)

Painted Bunting

G5Secure Found in 11 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Painted Bunting (Passerina ciris). © Suzie McCann; Cornell Lab of Ornithology | Macaulay Library.
© Suzie McCann; Cornell Lab of Ornithology | Macaulay Library
Painted Bunting (Passerina ciris). © Beau Cotter; Cornell Lab of Ornithology | Macaulay Library.
© Beau Cotter; Cornell Lab of Ornithology | Macaulay Library
Painted Bunting (Passerina ciris). © Brian Genge; Cornell Lab of Ornithology | Macaulay Library.
© Brian Genge; Cornell Lab of Ornithology | Macaulay Library
Painted Bunting (Passerina ciris). © Laura Keene; Cornell Lab of Ornithology | Macaulay Library.
© Laura Keene; Cornell Lab of Ornithology | Macaulay Library
Painted Bunting (Passerina ciris). © Ian Davies; Cornell Lab of Ornithology | Macaulay Library.
© Ian Davies; Cornell Lab of Ornithology | Macaulay Library
Painted Bunting (Passerina ciris). © Brandon Nidiffer; Cornell Lab of Ornithology | Macaulay Library.
© Brandon Nidiffer; Cornell Lab of Ornithology | Macaulay Library
Painted Bunting (Passerina ciris). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.100705
Element CodeABPBX64060
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyCardinalidae
GenusPasserina
Other Common Names
Colorín Sietecolores (ES) Passerin nonpareil (FR)
Concept Reference
American 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 Comments
An examination of morphological variation by Thompson (1991b) indicated that recognition of the two nominal subspecies, pallidior and ciris, as currently defined, is not warranted. However, Thompson (1991b) suggested that the eastern population (breeds from North Carolina south to Florida) and the western population (breeds from Arizona, Kansas, and Missouri south to northern Mexico, southern Texas, southern Louisiana, southern Mississippi, southern Alabama, and extreme western Florida) may be two distinct species. A phylogenetic, mitochondrial cytochrome-b study by Klicka et al. (2001) did not examine this relationship, but placed P. ciris and P. versicolor as sister species. Linaria is an invalid generic name for North America buntings (Banks and Browning 1995).
Conservation Status
Review Date1996-12-04
Change Date1996-12-04
Range Extent Comments
BREEDING: southeastern New Mexico, northern Texas, central Oklahoma, west-central Kansas, southern Missouri, and southwestern Tennessee south to southern Chihuahua, northern Coahuila, southern Texas, southern Louisiana, and along Gulf Coast to southern Alabama, locally to western Florida, and, disjunctly, North Carolina to central Florida (AOU 1998, Lowther et al. 1999).

NON-BREEDING: northwestern Bahamas, Florida, southern Tamaulipas, and Sinaloa south to West Indies and Panama (AOU 1998); also locally in the U.S. along the Gulf Coast (Thompson 1991). Eastern population winters mainly in southern Florida, the Bahamas, Cuba, Jamaica, and Haiti; western population winters mainly in southern Texas, Mexico, and Central America (Thompson 1991).
Threat Impact Comments
HABITAT: Breeding habitat loss is generally considered to be the greatest threat (Muehter 1998, Lowther et al. 1999); this is especially well documented along the Atlantic coast (Meyers, pers. comm.).

PET TRADE: Capture of individual birds for sale in the pet trade is apparently a significant concern on the wintering grounds in Central America (Muehter 1998).

PARASITISM: Brown-headed cowbird (MOLOTHRUS ATER) parasitism is known from both western and eastern populations. Thirteen 13 of 45 nests parasitized in Oklahoma (Parmalee 1959), 4 of 60 nests parasitized in Texas in an area where extensive cowbird removal had been carried out (Barber and Martin 1997), and 8 percent of an unspecified number of nests on barrier islands in Georgia (Meyers et al. 1999). Whether or not brood parasitism is a significant factor in population declines is not known.

PREDATION: Predators are likely similar to those of other small passerines and do not seem to be an unusual threat (Lowther et al. 1999).
Ecology & Habitat

Description

See Thompson (1992) for a key for determining age and sex.

Habitat

In general, few data exist on habitat requirements and they are not well quantified (Lowther et al. 1999). Partly open situations with scattered brush and trees, riparian thickets and brush, weedy and shrubby areas, woodland edges, yards and gardens in the southern U.S. Nests in bush or vine tangle, usually 1-2 meters up; sometimes in tree in thick Spanish moss at greater height (Harrison 1978). Western breeding populations use semi-open country with scattered trees and shrubs, riparian areas, abandoned farmland and other early successional stages (Parmalee 1959, AOU 1998).

In the Ouachitas of southwestern Arkansas, common in areas with a patchy mixture of open pasture and well-developed fencerows where farms are still small and family-run (J. Neal, pers. comm.). In southwest Missouri, 18 of 19 measured territories included predominantly old field vegetation (82 percent), with the remainder woodland (18 percent). Vegetative characteristics, however, varied widely between territories suggesting that a broad range of conditions are tolerated (Norris 1982, Norris and Elder 1982).

The southeastern coastal population uses a variety of habitats for breeding (Lanyon and Thompson 1986, Cox 1996, Meyers et al. 1999). While Meyers et al. (1999) found nesting success to be similar in beach shrub-scrub, managed pine-oak forest, and old growth oak forest, some forest-nesting individuals traveled up to 800 meters to feed in grassy or marshy openings, while shrub-scrub birds remained in core areas. Lanyon and Thompson (1986) determined that salt marsh/forest edge territories were preferred over interior forest, and concluded they were of higher quality.

Territory sizes measured include 1.13 hectares for one in Oklahoma (Parmalee 1959) and an average of 3.15 hectares on the edge of the range in Missouri (range 0.64-6.66 hectares, n = 19; Norris 1982, Norris and Elder 1982). Territories tend to be larger when there are no other territories adjoining (Norris 1982, Norris and Elder 1982), and smaller in high-quality habitat where territories are contiguous (Finke 1979, Lanyon and Thompson 1986). Males tend to return to nesting sites used in previous year (Lanyon and Thompson 1986).

Ecology

In winter in Mexico, occurs singly or in small groups; individuals may return to the same wintering site in successive years (Rappole and Warner 1980). Mean territory size 3.15 hectares (range 0.64-6.66, n=19) in Missouri (Norris 1982, Norris and Elder 1982).

Reproduction

Eggs are laid March-July (mostly May-June). Usually produces two broods per year, sometimes up to four. Clutch size usually is three to four. Incubation, by female, lasts 11-12 days. Young are probably tended by female alone; leave nest at 8-14 days.
Terrestrial Habitats
Woodland - HardwoodShrubland/chaparralSavannaOld fieldSuburban/orchard
Palustrine Habitats
Riparian
Other Nations (1)
United StatesN5B
ProvinceRankNative
South CarolinaS3BYes
OklahomaSNRBYes
AlabamaS2BYes
New MexicoS4B,S4NYes
MississippiS3BYes
TennesseeS2Yes
LouisianaS5BYes
KansasS4BYes
ArkansasS4BYes
GeorgiaS3Yes
ArizonaS2MYes
FloridaS2Yes
TexasS4BYes
MissouriS3Yes
North CarolinaS2BYes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
1.1 - Housing & urban areasPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
4 - Transportation & service corridorsSmall (1-10%)Moderate or 11-30% pop. declineHigh (continuing)
4.1 - Roads & railroadsSmall (1-10%)Moderate or 11-30% pop. declineHigh (continuing)
5 - Biological resource usePervasive - largeModerate or 11-30% pop. declineHigh (continuing)
5.1 - Hunting & collecting terrestrial animalsPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesPervasive - largeSlight or 1-10% pop. declineHigh (continuing)
8.2 - Problematic native species/diseasesPervasive - largeSlight or 1-10% pop. declineHigh (continuing)

Roadless Areas (11)
Arizona (3)
AreaForestAcres
Catalina St. Pk. Roadless AreaCoronado National Forest951
ChiricahuaCoronado National Forest76,876
TumacacoriCoronado National Forest44,594
New Mexico (2)
AreaForestAcres
Last Chance CanyonLincoln National Forest8,934
South Guadalupe MountainsLincoln National Forest20,930
North Carolina (2)
AreaForestAcres
Pocosin AdditionCroatan National Forest286
Pocosin AdditionCroatan National Forest286
Oregon (1)
AreaForestAcres
TenmileSiuslaw National Forest10,818
South Carolina (2)
AreaForestAcres
Wambaw ExtFrancis Marion National Forest527
Wambaw ExtFrancis Marion National Forest527
Utah (1)
AreaForestAcres
Boulder Mtn. / Boulder Top / Deer LakeDixie National Forest110,690
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