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Northern Parula
Distribution and Abundance
- BBS Map
- Breeding range eastern United States and eastern southern Canada; although
absent in a gap ranging from southern Minnesota and northern Iowa eastward to
portions of New England.
- Largely extirpated or reduced in numbers in southern Michigan (Brewer et al.
1991), southern Wisconsin (Robbins 1991), and the Mississippi lowlands of Missouri
(Robbins and Easterla 1992) and in several northeast states including
Massachusetts (Forbush 1929), Connecticut (Zeranski and Baptist 1990), New
Jersey (Sibley 1993), New York (Peterson 1988), Rhode Island (Enser 1992), and
Vermont (Kibbe 1985).
- Disappeared from several northeastern counties in Ohio, but by 1958 had
expanded into southwest Ohio where it nested for the first time in the
Cincinnati area (Peterjohn and Rice 1991). Prior to 1952, no records in
California; since then, this species has nested several times along coastal areas (Yee et al.
1993).
- Densities range widely with habitat and geographic location. BBS data
indicate that in the western part of this species' range, populations declined
significantly from 1966 to 1988; eastern populations declined from 1978-1988. No
significant increases over the long term (Sauer and Droege 1992), although
increases have occurred in the Mississippi alluvial plain and lower coastal
plain (James et al. 1992). From 1986-1992, in Wisconsin, mean number of
individuals increased, whereas in the Upper Peninsula of Michigan, there was a
slight decrease (Blake et al. 1994).
- Winters in the Caribbean, Bermuda, parts of southern Mexico and parts of
Central America.
Habitat
- Primarily a riparian species; usually associated with mature forest with
epiphytic growth. In northern part of range, prefers tall, mature coniferous forests with
spruce, hemlock, and fir in moist bog and swamp habitat where beard moss is
abundant.
- In Wisconsin, 37.5% of 232 observations from 1995-2000 were in upland mixed forest, 21% in lowland
conifer forest, and 13% in lowland
mixed forest (WSO 2002). In Michigan, this species
predominately breeds in northern coniferous forests, although will also use
northern hardwood forest, mesic mixed forest, and wet
coniferous areas (Brewer et al. 1991). Along the northern shore of Lake
Huron in Michigan's Upper Peninsula, this species occurs exclusively right
along the shoreline where it nests in beard lichens (Hamas, personal
communication).
- In Illinois,
population densities consistently higher in bottomland forest than in upland
forest (Graber et al. 1983). In north-central Minnesota, inhabits primarily mature, undisturbed mixed
forest of predominately deciduous trees with moderate ground and shrub cover and
greater than 75% canopy cover (Collins et al. 1982).
- In Nova Scotia, prefers hardwood stands of sugar maple, red maple, paper
birch, and yellow birch; most abundant in 40-yr-old stands of trees, less
numerous in younger and older-aged stands; density
positively correlated with tree density, basal area, percent of canopy cover,
and canopy height (Morgan and Freedman 1986).
- During breeding season in areas where there is a mixture of coniferous and
deciduous trees, this species prefers to forage in coniferous rather than
deciduous trees; foraging areas expand after young hatch to include nearby
deciduous growth (Morse 1967).
- Nest usually hidden in hanging tendrils of epiphytic growth, either beard
moss or lace lichen in the north (Spanish moss in the south). Preferred
nesting sites are usually near water; e.g., river bottoms, sloughs, swamps.
Nests tend to be located at the end of a branch, anywhere from 2-30 m above
ground. Less common non-epiphytic nests reported in areas where epiphytic
growth is rare or absent (Hall 1983).
- During spring migration, habitat selection similar to that of breeding
season (Bairlien 1992), although during fall migration in Wisconsin, found in
any tree or shrub (Robbins 1991).
- This species is a habitat generalist on winter grounds, occurring with
nearly equal frequencies in most common habitat types available (Arendt et al.
1992, Robbins et al. 1992).
Behavior
- Diet mostly insects and spiders; in suboptimal habitat in winter will also feed on berries, seeds and
nectar.
- Generally monogomous. Males defend established territories with singing and
chasing during the breeding season. Relatively nonsocial on breeding grounds.
Intraspecific physical interactions more common than interspecific
interactions, although interactions with other warblers reported (Morse 1967,
Wunderle 1978, Burtt 1986, Stacier 1992).
- Territory sizes range from 0.30-0.51 ha in Maine (Morse 1977); 0.08-0.65 ha
in Nova Scotia.
- Forms mixed flocks with other paruline species on wintering grounds and
during migration (Post 1978, Ewert and Askins 1991, Stacier 1992).
Parasitism and Predation
- Few but widespread records of Brown-headed Cowbird parasitism. Owing to
the closed structure of its nest, Northern Parula is probably an uncommon
cowbird host. Reported to build over nests containing cowbird eggs (Schwilling
1951), although adults feeding cowbird fledglings have been observed. In
Wisconsin, of 477 confirmed Brown-headed Cowbird observations from 1995-2000,
Northern Parula was not indicated as a host species (WSO 2002).
- No specific predators reported, but red squirrels and Blue Jays are probable
nest predators. Snakes may feed on eggs, young, and adults (Stevenson and
Anderson 1994). Adults likely preyed on by small hawks and owls. Injury
feigning (Graber and Graber 1951) and distraction displays (Peterjohn and Rice
1991) observed.
Conservation and Management
- Has been extirpated as a nesting species in several northeast states where
increasing air pollution has adversely affected the growth of the epiphytes the
birds use for nesting.
- Clearcutting of forest habitat has negatively affected the species in
southern Michigan (Brewer et al. 1991), southern Wisconsin (Robbins 1991), and
the Mississippi lowlands of Missouri (Robbins and Easterla 1992).
- Northern Parula may be an area-sensitive species as it is uncommon in small
forests (Freemark and Collins 1991). In middle Atlantic states, forest area was
a significant predictor of relative abundance; rarely encountered in forests of
less than 100 ha (Robbins et al. 1989).
- Draining of bogs and other moist habitats has been implicated in population
declines in southern Wisconsin (Robbins 1991) and New York (Bull 1974).
- Population decline in the Maritime Provinces prior to 1966 attributed to
widespread use of DDT in New Brunswick from 1952-1967 to combat spruce budworm
outbreaks (Erskine 1992).
- Hundreds of birds killed annually during migration after collisions with TV
towers and other tall human-made structures (Bull 1974, Ralph 1981, Graber et
al. 1983, Robbins 1991, Robbins and Easterla 1992, Stevenson and Anderson 1994).
- BBS trend results from 1966-2000 (Sauer et al. 2001) in the Northern Spruce-Hardwoods region indicate a significant population
increase of
the Northern Parula in this region (2.1, p=0.00 Trend
Graph S28); in the Great Lakes Transition region, this species may be
experiencing an increase, but more data are needed (1.9, p=0.71 Trend
Graph S20). Survey-wide (US and Canada), this species has overall shown a slight but
significant increase (0.9, p=0.02 Trend
Graph SUR).
For more information about the conservation and management of the
Black-and-white Warbler, please
see the Species
Management Abstract, from the Conserve
Online public library, maintained by The Nature Conservancy.
This species account is based on: Moldenhauer, R.R. and D.J. Regelski. 1996. Northern
Parula. In The Birds of North America, No. 215 (A. Poole and F. Gill, eds.). The
Academy of Natural Sciences, Philadelphia, PA, and The American Ornithologists'
Union, Washington, DC.
References
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landbirds in the Caribbean region: a summary. Pp. 143-171 in Ecology and
conservation of neotropical migrant landbirds (J.M Hagen III and D.W.
Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
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D.W.
Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
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variation in bird populations of mixed conifer-northern hardwood forests. Condor
96:381-399.
- Brewer, R., G.A. McPeek and R.J. Adams. 1991. The breeding birds of
Michigan. Michigan State University Press, East Lansing.
- Bull, J. 1974. Birds of New York State. Cornell University Press, Ithaca,
NY.
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aspects of avian coloration with emphasis on wood-warblers. Ornithol. Monogr.
38.
- Collins, S.L., F.C. James and P.G. Risser. 1982. Habitat relationships of
wood warblers in northern central Minnesota. Oikos 39:50-58.
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Dept. Environ. Manage.
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in winter in the Virgin Islands. Condor 93:864-868.
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3. Commonwealth of Massachusetts.
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temperate forest fragments. Pp. 443-454 in Ecology and conservation of neotropical migrant landbirds
(J.M Hagen III and D.W.
Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
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Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
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birds of Vermont (S.B. Laughlin and D.P. Kibbe, eds.). University Press of New
England, Hanover, NH.
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forest succession in Nova Scotia. Can. Field-Nat. 100:506-519.
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other species during the breeding season. Auk 84:490-502.
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79:399-412.
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birds in New York state (R.F. Andrle and J.R. Carroll, eds.). Cornell Univ.
Press, Ithaca, NY.
- Post, W. 1978. Social and foraging behavior of warblers wintering in Puerto
Rican coastal scrub. Wilson Bull. 90:197-214.
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routes of passerine migrants. Wilson Bull. 93:164-188.
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of breeding forest birds of the middle Atlantic states. Wildl. Monogr.
103:1-34.
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R. Estrada, A. Sutton, R. Sutton and D. Weyer. 1992. Comparison of neotropical
migrant landbird populations wintering in tropical forest, isolated fragments,
and agricultural habitats. Pp. 207-210 in Ecology and
conservation of neotropical migrant landbirds (J.M Hagen III and D.W.
Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
- Robbins, M.B. and D.A. Easterla. 1992. Birds of Missouri. University of
Missouri Press, Columbia.
- Robbins, S.D., Jr. 1991. Wisconsin birdlife. University of Wisconsin Press,
Madison.
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of neotropical migrants in North America. Pp. 26-42 in Ecology and
conservation of neotropical migrant landbirds (J.M Hagen III and D.W.
Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
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Bird Survey, Results and Analysis 1966-2000. Version 2001.2, USGS
Patuxent Wildlife Research Center, Laurel, MD.
- Schwilling, M.D. 1951. Parula Warbler nesting in Kansas. Condor
53:100-101.
- Sibley, D. 1993. The birds of Cape May. Cape May Bird Observ., Cape May, NJ.
- Stacier, C.A. 1992. Social behavior of the Northern Parula, Cape May
Warbler, and Prairie Warbler wintering in second-growth forest in southwestern
Puerto Rico. Pp. 308-328 in Ecology and
conservation of neotropical migrant landbirds (J.M Hagen III and D.W.
Johnston, eds.). Smithson. Inst. Press, Washington, D.C.
- Stevenson, H.M. and B.H. Anderson. 1994. The birdlife of Florida. University
Press of Florida, Gainseville.
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Warbler. Wilson Bull. 90:297-299.
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