Vireo griseus

(Boddaert, 1783)

White-eyed Vireo

G5Secure Found in 20 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Identity
Unique IDELEMENT_GLOBAL.2.103052
Element CodeABPBW01020
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyVireonidae
GenusVireo
Other Common Names
Viréo aux yeux blancs (FR) Vireo Ojo Blanco (ES) white-eyed vireo (EN)
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
Puebla and Veracruz populations often have been recognized as a distinct species, V. PERQUISITOR (Veracruz Vireo) (AOU 1983). Species boundaries in the white-eyed vireo complex (GRISEUS, CRASSIROSTRIS, PALLENS, BAIRDI, CARIBAEUS, MODESTUS, GUNDLACHII, LATIMERI, and NANUS) are poorly understood (AOU 1998). See Johnson et al. (1988) and Murray et al. (1994) for analyses of the phylogenetic relationships among vireos.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-10
Change Date1996-12-03
Edition AuthorsPALIS, J.
Range Extent Comments
BREEDING: central Iowa, southeastern Minnesota (rarely), southern Wisconsin, southern Michigan, extreme southern Ontario, southern New York, and southern Massachusetts, south to southern Mexico (San Luis Potosi, Hidalgo), southern Texas, Gulf Coast, southern Florida and west to eastern Nebraska (formerly), eastern Kansas, central Oklahoma, west-central Texas, and Coahuila (AOU 1998). NON-BREEDING: central Texas, the Gulf states, and extreme southeastern Virginia (Dismal Swamp) south to Guatemala, Belize, and northwestern Honduras (casually to western Panama); also in Bermuda, Bahamas, Jamaica, Cuba, Cayman Islands, Puerto Rico, and St. John (Hopp et al. 1995, AOU 1998). RESIDENT: Bermuda (subspecies BERMUDIANUS) (Hopp et al. 1995). Casual north to North Dakota, southern Manitoba, southern Minnesota, northern Michigan, southern Quebec, Maine, and Nova Scotia, west to California, Utah, Arizona, Colorado, southern New Mexico, Chihuahua, and south to Costa Rica, Panama, Puerto Rico (including Mona Island) and the Virgin Islands (St. John); sight report for Socorro (Revillagigedo Islands) (AOU 1998).
Threat Impact Comments
PREDATION: Potential predators of nests and fledglings include snakes (e.g. Rat Snakes, ELAPHE OBSOLETA), Blue Jays (CYANOCITTA CRISTATA), mice (PEROMYSCUS sp.), Eastern Chipmunks (TAMIAS STRIATUS), Raccoons (PROCYON LOTOR), Virginia Opossums (DIDELPHIS MARSUPIALIS), and Striped Skunks (MEPHITIS MEPHITIS). Short-tailed Hawks (BUTEO BRACHYURUS) are confirmed predators (Ogden 1974). In Bermuda, fledglings sometimes get entangled in golden-silk spider webs (NEPHILA CLAVIPES; Forbush and May 1939 cited in Hopp et al. 1995). NEST PARASITISM: Observed rates of Brown-headed Cowbird nest parasitism vary from 40% in Louisiana (Goertz 1977), to 48.9% in Virginia (Hopp et al. 1995), to 83% in Illinois (Graber et al. 1985). Parasitized host nests typically fledge only cowbird young (Hopp et al. 1995). OTHER: During migration, large numbers are sometimes killed during severe weather. An estimated 1800 individuals were killed by thunderstorms and a tornado in Louisiana during spring migration (Weidenfeld and Weidenfeld 1995). Migrating individuals are killed by colliding with towers (Crawford 1978, Taylor and Anderson 1973, Taylor and Kershner 1986).
Ecology & Habitat

Habitat

BREEDING: Inhabits early-late successional, shrubby habitats such as deciduous scrub, old fields, abandoned pastures, regenerating clearcuts or other heavily logged areas, drainage and streamside thickets, forest edges, reclaimed strip mines, and mangrove swamps (Bent 1950, Bradley 1980, Graber et al. 1985, Hopp et al. 1995, Mumford and Keller 1984, Palmer-Ball 1996). In east Texas, positively associated with high shrub density and species diversity, and foliage density (Conner et al. 1983). In Virginia, prefers habitats with extensive undergrowth, shrubs, and tree saplings interspersed with widely spaced taller trees (Hopp et al. 1995). Birds inhabiting the Atlantic coastal region of Georgia and the Carolinas prefer scrub lacking an overstory, whereas birds ranging from Alabama to Louisiana appear to prefer edge habitat (S. L. Hopp, pers. comm.). Nest is typically placed in a Y-shaped horizontal branch of a deciduous tree or shrub, 0.3-2.11 m above the ground (Hopp et al. 1995).

NON-BREEDING: Considered a habitat generalist on the wintering grounds. Observed in all habitat types surveyed on the Yucatan Peninsula, including field, pasture, acahual (shrubby, early successional habitat), semi-deciduous forest, semi-evergreen forest, moist tropical forest, mangrove forest and coastal scrub (Lynch 1989). In a habitat-use study of three habitat types on the Yucatan Peninsula (pasture, acahual and subtropical dry forest), observed most frequently in the latter (Greenberg 1992). Captured most frequently in pine savanna and early successional scrub in Belize (Petit et al. 1992). In Veracruz, Mexico, occupied young (1-10 m tall) and old (10-20 m tall) second-growth forest, as well as undisturbed evergreen tropical forest (Rappole and Warner 1980).

Ecology

DENSITY/TERRITORIALITY: Territorial during the breeding season; size of breeding territories vary with habitat quality. Territory size varied from 0.13 hectares in a swamp thicket to 1.4 hectares in a forest edge in Illinois (Graber et al. 1985), and averaged 1.3 hectares in Florida (Bradley 1980). Also territorial on wintering grounds (Greenberg et al. 1993, Rappole and Warner 1980). Average size of winter territory on the Yucatan Peninsula is approximately 0.5 hectares (Greenberg et al. 1993). Density during the breeding season has been reported to be 1.2 pairs/10 hectares in Chestnut Oak (QUERCUS PRINUS) forest in the Smoky Mountains (Wilcove 1988), 18 birds/40.5 hectares in bottomland forests of Arkansas (James and Neal 1986), and to vary from <1-24 birds/40.5 hectares in Illinois, with lowest densities occurring in forested habitats and highest in shrub and forest edge habitats (Graber et al. 1985).

SITE FIDELITY: Exhibits strong breeding site fidelity. In Virginia, 97% of returning males re-occupied their previously held territories. Females returned to the study area, but not to the same territory; none paired with the same male as the previous year (Hopp et al. 1999). Also exhibits site fidelity to wintering sites. Banded individuals have returned to the same wintering site in consecutive years in Veracruz, Mexico (Rappole and Warner 1980).

POPULATION PARAMETERS: Lives to be at least 9 years old (Hopp et al. 1999).

PARASITES: Known ectoparasites include lice (PHILOPTERUS SUBFLAVESCENS and RICINUS sp.) and louse-flies (ORNITHOMYA ANCHINEURIA). Can also be infected with encephalitis (Hopp et al. 1995).

Reproduction

Three to five eggs are laid from early April through late May, although renesting can extend into late July (Bent 1950, Hopp et al. 1995). Known to produce two broods per season, and attempt to nest up to four times. The average clutch size of 103 sets of eggs collected from throughout the range was 3.74 eggs. One egg is laid per day until the clutch is complete; incubation begins after the penultimate or ultimate egg is laid. Both sexes incubate the eggs (13-15 days), and brood and feed the young. Young leave the nest 9-11 days after hatching at which time they are capable of short-distance flight. In Virginia, 29.8% of nests observed over a seven-year period fledged young. Successful nests produced 3.2 young per nest; whereas all nests (including unsuccessful) produced an average of 0.96 young/nest (Hopp et al. 1995).
Terrestrial Habitats
Forest - HardwoodWoodland - HardwoodShrubland/chaparralOld field
Palustrine Habitats
Riparian
Other Nations (2)
CanadaN1B
ProvinceRankNative
OntarioS1BYes
United StatesN5B,N5N
ProvinceRankNative
South CarolinaS5BYes
AlabamaS5B,S3NYes
North CarolinaS5B,S1NYes
FloridaS4Yes
IllinoisS5Yes
LouisianaS5BYes
MichiganS4Yes
OhioS5Yes
KentuckyS5BYes
TennesseeS4Yes
MissouriSNRBYes
VirginiaS5Yes
MassachusettsS2B,S4NYes
MarylandS5BYes
Rhode IslandS4BYes
DelawareS5BYes
ConnecticutS5BYes
District of ColumbiaS1B,S3NYes
MississippiS5B,S5NYes
IowaS2B,S3NYes
New YorkS4BYes
GeorgiaS5Yes
TexasS5BYes
IndianaS4BYes
West VirginiaS5BYes
PennsylvaniaS4BYes
OklahomaSNRBYes
New JerseyS4B,S4NYes
KansasS3BYes
WisconsinSNAYes
ArkansasS4B,S4NYes
ColoradoSNAYes
Roadless Areas (20)
Alabama (1)
AreaForestAcres
Reed BrakeTalladega National Forest621
Arkansas (1)
AreaForestAcres
East ForkOzark-St. Francis National Forest13,037
California (1)
AreaForestAcres
Dry LakesLos Padres National Forest17,043
Florida (3)
AreaForestAcres
Alexander Springs CreekOcala National Forest2,954
Farles PrairieOcala National Forest1,901
Impassable BayOsceola National Forest2,789
New Mexico (1)
AreaForestAcres
Candian RiverCibola National Forest7,149
North Carolina (2)
AreaForestAcres
Catfish Lake NorthCroatan National Forest11,299
Laurel MountainPisgah National Forest5,683
Oklahoma (1)
AreaForestAcres
Beech CreekOuachita National Forest8,303
Tennessee (2)
AreaForestAcres
Bald River Gorge AdditionCherokee National Forest1,728
Sycamore CreekCherokee National Forest6,984
Texas (1)
AreaForestAcres
Little Lake CreekNational Forests in Texas596
Virginia (7)
AreaForestAcres
Bear CreekJefferson National Forest18,274
Brush MountainJefferson National Forest6,002
Peters Mountain Addition BJefferson National Forest2,909
Raccoon BranchJefferson National Forest4,388
Seng MountainJefferson National Forest6,428
Shawvers Run AdditionJefferson National Forest1,927
Southern MassanuttenGeorge Washington National Forest11,985
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