Setophaga americana

(Linnaeus, 1758)

Northern Parula

G5Secure Found in 43 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Identity
Unique IDELEMENT_GLOBAL.2.102108
Element CodeABPBX02010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyParulidae
GenusSetophaga
Synonyms
Parula americana(Linnaeus, 1758)
Other Common Names
northern parula (EN) Parula Norteña (ES) Paruline à collier (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
Formerly placed in the genus Parula. Phylogenetic analyses of sequences of mitochondrial and nuclear DNA (Lovette et al. 2010) indicate that all species formerly placed in Dendroica, one species formerly placed in Wilsonia (citrina), and two species formerly placed in Parula (americana and pitiayumi) form a clade with the single species traditionally placed in Setophaga (ruticilla). The generic name Setophaga has priority for this clade (AOU 2011).

Constitutes a superspecies with P. pitiayumi (AOU 1998). A mitochondrial DNA study by Lovette and Bermingham (2001) suggests that the two taxa are conspecific and, in addition, do not form a monophyletic group with P. superciliosa and P. gutteralis of Central America; P. americana and P. pitiayumi group with dendroica whereas P. superciliosa and P. gutteralis group with vermivora. Moldenhauer (1992) documented the existence of two song populations and recommended that the eastern population be recognized as subspecies americana and the western population as subspecies ludoviciana.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-09
Change Date1996-12-03
Edition Date2001-04-09
Edition AuthorsRobertson, B.
Range Extent Comments
BREEDING: southeastern Manitoba across southern Canada to Nova Scotia, south to east Texas, Gulf Coast, and southern Florida; absent or rarely breeds in southern Michigan, northwestern Ohio, northern Indiana, northern Illinois, southern Wisconsin, southern Minnesota, and most of Iowa (Moldenhauer and Regelski 1996). NON-BREEDING: primarily in West Indies, from central Bahamas to Lesser Antilles; also west to western Caribbean and Gulf slopes of mainland, in Mexico from Veracruz through Yucatan peninsula; also in Belize and rarely as far south as Nicaragua and Costa Rica. This is the most common wintering warbler throughout the West Indies (Raffaele 1983, Pashley 1988, Pashley 1988, Pashley and Hamilton 1990).
Threat Impact Comments
HABITAT LOSS: In the southeastern U.S. large tracts of bottomland hardwood forest are becoming increasingly rare. Habitat loss is the primary factor adversely impacting migrant bird populations throughout the Caribbean region. Population and land use trends suggest this trend is likely to continue. Few natural areas and reserves have been set aside throughout the region, but where land conservation has been coupled with subsequent natural and artificial reforestation migrant landbirds have made recoveries (Arendt 1992). In southern Michigan, southern Wisconsin, and the Mississippi lowlands of Missouri, eradicated due to habitat destruction (Robbins 1990, Brewer et al. 1991, Robbins and Easterla 1992 in Moldenhauer and Regelski 1996). Currently, acid precipitation may pose a more important threat to this habitat component (Dunn and Garrett 1997). Logging, agricultural conversion and coastal development continue to threaten resident and migrant landbirds throughout the Yucatan (Lynch 1992), where Northern Parula winters. While Northern Parula tends to shun disturbance, it may do well in second-growth tropical forest edges, or woodlots. However, deforestation in the tropics only rarely results in such habitats, but more often results in vast expanses of overgrazed pastures, canefields and other inhospitable habitats (Ehrlich et al.1988). POLLUTION: Has disappeared from many parts of the Northeast and Great Lakes region where increasing levels of air pollution has limited growth of moss and lichens that are a key component of nesting habitat. Affected areas include: Massachusetts (Veit and Petersen 1993), Connecticut (Zeranski and Baptist 1990), New Jersey (Sibley 1993), New York (Bull 1974), Rhode Island (Enser 1992), and Vermont (Kibbe 1985). PESTICIDES AND CONTAMINANTS: Earlier use of DDT to combat outbreaks of spruce budworm (CHORISTONEURA FUMIFERANA) caused population declines in the Maritime Provinces (Erskine 1992). COLLISIONS: Significant deaths attributed to collisions with human-made structures such as TV towers throughout range (Graber et al. 1983, Robbins and Easterla 1992, Ralph 1981 Robbins 1990). From 1955-1985 a total of 1,469 Northern Parulas hit one tower in Leon Co., FL (Stevenson and Anderson 1994). HURRICANES: Hurricanes may reduce local wintering populations of neotropical migrants in the West Indies. Abundance of Northern Parula in coastal Louisiana decreased following Hurricane Andrew, possibly due to decreased abundance of Spanish moss or defoliation of forest canopy (Torres and Leberg 1996). PARASITISM: Some instances of nest parasitism, but owing to the closed structure of its nest, probably an uncommon cowbird host (Dunn and Garrett 1997).
Ecology & Habitat

Description

ADULT MALE: Head and upperparts mostly grayish blue; patch on center of back greenish yellow; wings and tail grayish blue, the wings showing two prominent white bars and the tail having white spots on the outer feathers near its end; throat and breast mostly yellow, the breast crossed by a band of bluish black bordered with chestnut; belly white; flanks slightly washed with rufous. ADULT FEMALE: Similar, but patch on back duller and underparts light yellow with breast band generally lacking.

Habitat

BREEDING: Breeding habitat varies considerably throughout range, but primarily a riparian species associated with epiphytic growth. Found in open deciduous, coniferous, or mixed forest, woodland, floodplain and swamp forest. Prefers mature forest but also occurs in young deciduous woods (Bushman and Therres 1988). Favors woods with a very dense understory of saplings and shrubs near slow or non-flowing water; canopy may range from poorly developed to mainly closed (see Bushman and Therres 1988).

Southern populations occupy the canopy or subcanopy of riparian bottomland forest, especially where Spanish moss (TILLANDSIA) is found.. In eastern Texas, prefers floodplain hardwood forest dominated by water oak (QUERCUS NIGRA), willow oak (Q. PHELLOS), swamp chestnut oak (Q. MICHAUXII), and black gum (NYSSA SYLVANTICA) with an understory of dwarf palmetto (SABAL MINOR). Found less abundantly in mixed pine-hardwood forests. In the coastal plain of Georgia, breeds in mature hardwood bottomlands with Spanish moss, but in northern Georgia where Spanish moss is absent, breeds in moist wooded ravines of eastern hemlock (TSUGA CANADENSIS, Moldenhauer and Regelski 1996).

In northern part of range, prefers tall, mature, coniferous forest with spruce (PICEA), hemlock (TSUGA), true fir (ABIES), White Cedar, and Tamarack in moist bogs and swamps where Old Man's Beard lichen (USNEA spp.) or lace lichen (RAMALINA RETICULATA) is abundant. In Nova Scotia, found in stands of Sugar Maple (ACER SACCHARUM), Red Maple (A. RUBRUM), Paper Birch (BETULA PAPYRIFERA), and Yellow Birch (B. ALLEGHANIENSIS) and most abundantly in 40-yr-old stands of trees. Less abundant in both older and younger stands (Morgan and Freedman 1986). Density positively correlated with tree density, basal area, percent canopy cover, and canopy height (Morgan 1984). In northern-central Minnesota, inhabits primarily mature undisturbed mixed forest of predominantly deciduous trees with moderate ground and shrub cover and greater than 75 per cent canopy cover (Collins et al. 1982). In Illinois, numbers positively correlated with the presence of sycamore (PLATANUS OCCIDENTALIS, Graber et al. 1983). Appalachian populations favor wet ravines dominated by hemlocks. Found at edges of spruce forests, spruce-covered islands off the Maine coast (Dunn and Garrett 1997).

NON-BREEDING: A habitat generalist in winter. Occurs in nearly equal frequencies in most common habitat types available. Tropical lowland evergreen forest, pine-oak forest, gallery forest, and secondary forest up to a maximum elevation of 1500 m (Stotz et al. 1996). In scrub and brushy areas (AOU 1998), woodland edge, and mangroves but also arboreal agriculture, sun coffee, citrus plantations, croplands (Arendt et al. 1992, Robbins et al. 1992) and tall second growth, usually from middle heights to high in the canopy (Lynch et al. 1985). Has exhibited sexual segregation in Quintana Roo, Yucatan, Mexico with more males in taller forest and more females in scrub habitats (Morton et al. 1987)

In Mexico occupies humid to semiarid forest and edge, plantations, and mangroves. Found singly at mid- to upper-levels (Howell and Webb 1995). In Costa Rica found at woodland edges, in semi-open and tall second growth, usually from middle amid foliage to high in canopy (Stiles and Skutch 1989). In Cuba, occupies forest, where it usually forages in higher branches (Garrido and Kirkconnell 2000). In Jamaica, most common in damper woods; trees with broad, thin leaves (Lack 1976).

MIGRATION: Uses all kinds of wooded areas on migration including humid lowland forest, second growth, scrub and brushy areas (AOU 1998), but shows a preference for deciduous woods; occasionally found in overgrown fields and hedgerows. (Dunn and Garrett 1997).

Ecology

BREEDING: Relatively nonsocial on breeding grounds. Males arrive early to establish territories and defend them with singing and chasing. Potential competitors affect territory size and density. Territories in mainland spruce forests of Maine were 0.4 hectares, but on offshore islands were only 0.16 hectares in size (Moldenhauer and Regelski 1996).

NON-BREEDING: Social behavior is quite variable during the non-breeding season sometimes showing site-fidelity with restricted home ranges (Ewert and Askins 1991). Forms mixed flocks or "temporary social aggregations" with other paruline species and residents (Post 1978, Stacier 1992, Stiles and Skutch 1989). Found singly, but most often associated with a mixed flock; a "nucleus species" (Eaton 1953). In southwestern Puerto Rico, ranged from territorial to gregarious to wandering (Hagan and Johnston 1992). Breeding and winter-site fidelity is suggested by banding results (Stacier 1992).

Reproduction

Nest built in hanging bunches of mosses or lichens (Spanish moss, beard moss or lace lichen), usually at the end of the branch, 2 to 30 m from the ground. Usually near water (Baicich and Harrison 1997, Moldenhauer and Regelski 1996). Inside of nest lined with moss or lichen fibers, hair, fine grass, pine needles or plant down (Bent 1953). A hole leading through the moss is usually located at the level of the nest bowl. Occasionally two holes are used. Where epiphytes are absent, other materials are used (Petrides 1942, Hall 1983).

Eggs white to creamy white and speckled. Clutch size usually 3-5 eggs, range 2-7. One egg laid per day. Incubation period 12-14. Incubation 12-14 days, by female. Young tended by both parents. Brooding usually by female. Young fed mainly by female (Baicich and Harrison 1997, Moldenhauer and Regelski 1996).Young leave nest 10-11 days after hatching (Graber and Graber 1951, Moldenhauer and Regelski 1996) but are unable to fly. After fledging they remain near their parents, begging constantly. Female continues to do most of the feeding, while male sings. Time to independence from parents unknown (Baicich and Harrison 1997, Moldenhauer and Regelski 1996). Single brooded, but second broods reported (Potter et al. 1980).
Terrestrial Habitats
Forest - HardwoodForest - ConiferForest - MixedWoodland - HardwoodWoodland - ConiferWoodland - MixedShrubland/chaparralOld field
Palustrine Habitats
FORESTED WETLANDRiparian
Other Nations (2)
United StatesN5B
ProvinceRankNative
AlabamaS5BYes
New JerseyS4B,S4NYes
TennesseeS5Yes
VirginiaS5Yes
MarylandS4BYes
OhioS3Yes
New YorkS3BYes
ArkansasS4B,S4NYes
OklahomaS3BYes
MaineS5B,S5MYes
IowaS3B,S3NYes
IllinoisS5Yes
WisconsinS4BYes
PennsylvaniaS5B,S4MYes
LouisianaS5BYes
New MexicoS4NYes
KansasS4BYes
North CarolinaS5BYes
MassachusettsS1B,S4MYes
South DakotaSNAYes
ColoradoSNAYes
ConnecticutS1BYes
North DakotaSNAYes
MichiganS5Yes
District of ColumbiaS3B,S3NYes
MinnesotaSNRBYes
MissouriSNRBYes
South CarolinaS4Yes
GeorgiaS5Yes
TexasS4BYes
IndianaS4BYes
New HampshireS5BYes
Rhode IslandS1B,S1NYes
KentuckyS4BYes
DelawareS1BYes
VermontS4BYes
West VirginiaS5BYes
MississippiS5BYes
ArizonaS2NYes
FloridaSNRBYes
CanadaN5B
ProvinceRankNative
OntarioS5BYes
SaskatchewanSNAYes
Prince Edward IslandS5BYes
Nova ScotiaS5BYes
Island of NewfoundlandS1B,SUMYes
ManitobaS4BYes
New BrunswickS5BYes
QuebecS5BYes
Roadless Areas (43)
Arizona (2)
AreaForestAcres
Black CanyonPrescott National Forest10,683
GoldfieldTonto National Forest15,257
Arkansas (1)
AreaForestAcres
Gee CreekOzark-St. Francis National Forest7,957
California (3)
AreaForestAcres
Benton RangeInyo National Forest9,637
HortonInyo National Forest5,717
South SierraSequoia National Forest8,008
Florida (2)
AreaForestAcres
Alexander Springs CreekOcala National Forest2,954
Farles PrairieOcala National Forest1,901
Louisiana (1)
AreaForestAcres
Saline Bayou W & S River CorridorKisatchie National Forest5,355
Minnesota (1)
AreaForestAcres
Kawishiwi Lake To SawbillSuperior National Forest15,305
New Hampshire (2)
AreaForestAcres
Cherry MountainWhite Mountain National Forest8,766
PemigewassetWhite Mountain National Forest32,255
North Carolina (6)
AreaForestAcres
Bald MountainPisgah National Forest11,085
Barkers Creek (addition)Nantahala National Forest975
Middle Prong AdditionPisgah National Forest1,852
Overflow CreekNantahala National Forest3,379
South Mills RiverPisgah National Forest8,588
Tusquitee BaldNantahala National Forest13,670
Oklahoma (1)
AreaForestAcres
Beech CreekOuachita National Forest8,303
Puerto Rico (2)
AreaForestAcres
El Toro AreaCaribbean National Forest12,584
Mameyes AreaCaribbean National Forest11,150
Tennessee (5)
AreaForestAcres
Bald MountainCherokee National Forest11,743
Beaver Dam CreekCherokee National Forest5,070
London Bridge BranchCherokee National Forest3,387
Sampson Mountain AdditionCherokee National Forest3,064
Upper Bald RiverCherokee National Forest9,202
Texas (2)
AreaForestAcres
Little Lake CreekNational Forests in Texas596
Winters BayouNational Forests in Texas730
Vermont (1)
AreaForestAcres
Bread LoafGreen Mountain and Finger Lakes National Forests1,768
Virginia (11)
AreaForestAcres
Adams PeakGeorge Washington National Forest7,135
Beaver Dam CreekJefferson National Forest1,135
Brush MountainJefferson National Forest6,002
Crawford MountainGeorge Washington National Forest9,892
Gum RunGeorge Washington National Forest12,620
JerkemtightGeorge Washington National Forest16,687
Oak KnobGeorge Washington National Forest10,882
Peters Mountain Addition BJefferson National Forest2,909
Seng MountainJefferson National Forest6,428
SkidmoreGeorge Washington National Forest5,641
The PriestGeorge Washington National Forest5,737
West Virginia (3)
AreaForestAcres
Dry River (WV)George Washington National Forest7,331
Little MountainMonongahela National Forest8,172
Middle MountainMonongahela National Forest19,020
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