Catharus bicknelli

(Ridgway, 1882)

Bicknell's Thrush

G4Apparently Secure Found in 46 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
VulnerableIUCN
Bicknell's Thrush (Catharus bicknelli). © Matt Felperin; Cornell Lab of Ornithology | Macaulay Library.
© Matt Felperin; Cornell Lab of Ornithology | Macaulay Library
Bicknell's Thrush (Catharus bicknelli). © Kaleb Anderson; Cornell Lab of Ornithology | Macaulay Library.
© Kaleb Anderson; Cornell Lab of Ornithology | Macaulay Library
Bicknell's Thrush (Catharus bicknelli). © Sacha Balavoine; Cornell Lab of Ornithology | Macaulay Library.
© Sacha Balavoine; Cornell Lab of Ornithology | Macaulay Library
Bicknell's Thrush (Catharus bicknelli). © Frédérick Lelièvre; Cornell Lab of Ornithology | Macaulay Library.
© Frédérick Lelièvre; Cornell Lab of Ornithology | Macaulay Library
Bicknell's Thrush (Catharus bicknelli). © Ryan Sanderson; Cornell Lab of Ornithology | Macaulay Library.
© Ryan Sanderson; Cornell Lab of Ornithology | Macaulay Library
Bicknell's Thrush (Catharus bicknelli). © Darren Clark; Cornell Lab of Ornithology | Macaulay Library.
© Darren Clark; Cornell Lab of Ornithology | Macaulay Library
Bicknell's thrush (Catharus bicknelli). 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.2.106330
Element CodeABPBJ18120
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNVulnerable
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderPasseriformes
FamilyTurdidae
GenusCatharus
Other Common Names
Grive de Bicknell (FR) Tordo (ES)
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 included as a subspecies of C. minimus; elevated to full species status by Ouellet (1993) (see also McLaren 1995); not known to intergrade/hybridize with C. minimus. AOU (1995) accepted full species status for C. bicknelli Formerly placed in genus Hylocichla (AOU 1983).
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-07
Change Date1996-12-03
Edition Date2014-10-07
Edition AuthorsJue, Dean K.
Range Extent250-20,000 square km (about 100-8000 square miles)
Number of Occurrences81 to >300
Rank Reasons
Breeds in the northeastern U.S. and southeastern Canada, winter records are from the West Indies; apparently stable in New York/New England, but overall conservation status is not well known.
Range Extent Comments
BREEDING: eastern New York (south to the Catskill Mountains), Massachusetts (formerly, on Mount Greylock), central and northern Vermont, northern New Hampshire, Maine, southern Nova Scotia (has disappeared from Seal Island), Magdalen Islands (at least formerly), Gaspe Peninsula, interior highlands of New Brunswick, and (formerly) along the north shore of the Gulf of St. Lawrence from Natashquan, Quebec, east to Cape Saint Charles, southern Labrador (AOU 1957, Rimmer et al. 1993). In the U.S., mainly at elevations above 3000 ft; in 1992, found on 4 peaks lower than 3000 ft. In Quebec, elevations of 175-1160 (Ouellet 1993). NON-BREEDING: poorly documented; known from Hispaniola, Cuba, Puerto Rico, and St. Croix; winter stronghold almost certainly is the Dominican Republic (Rimmer 1996); not known from Central or South America (Ouellet 1993). Migration records encompass eastern coastal states of U.S. and Bahamas (Ouellet 1993).
Occurrences Comments
In 1992-1993 surveys, found on 230 peaks of 332 surveyed in New York and New England found at 61 of 71 historical breeding sites surveyed (Rimmer 1996).
Threat Impact Comments
Threatened by the damaging effects of acid precipitation and airborne pollution, habitat loss from ski area development and transmission tower construction, and overuse by hikers; global climate change is a potential threat (Rimmer et al. 1993). Wind power development is an increasing threat in parts of the breeding range (Rimmer 1996). Deforestation in the winter range probably has eliminated much of its habitat and human settlements are expected to double over the next few years (Rimmer 1996; National Audubon Society, 2014).
Ecology & Habitat

Diagnostic Characteristics

Smaller and typically richer brown dorsally than the gray-cheeked thrush; tail color (with various amounts of chestnut) contrasts with the back color in Bicknell's whereas there is little contrast in gray-cheeked thrush; pale area at base of bill is yellowish in Bicknell's, fleshy-pink in gray-cheeked; white of ventral region is duller than in gray-cheeked thrush; songs differ as well, with those of Bicknell's ending on an even or ascending pitch whereas the gray-cheeked's descends (Rimmer et al. 1993, Ouellet 1993). However, Bicknell's thrush from the Gaspe Peninsula lacks bright yellow on the mandible, and some Newfoundland gray-cheeked thrushes have more extensively pale mandibles, "warm" plumage tones, and appear to have a chestnut tail (McLaren 1995). In migration, Bicknell's thrush and gray-cheeked thrush probably cannot be reliably separated without specimens in hand.

Habitat

In New England and New York, inhabits montane forests, primarily areas dominated by stunted balsam fir and red spruce at elevations above 3000 ft (Rimmer et al. 1993). Habitats in Canada include mountaintop and dense coastal coniferous forests as well as mixed second-growth regenerating stands (Rimmer 1996). In southern Quebec, occurs mainly in second growth stands characterized by relatively young conifers of small size (balsam fir, white spruce) intermixed with a variety of deciduous species typical of second-growth regeneration (PRUNUS sp., BETULA sp., AMELANCHIER sp., ACER SPICATUM, POPULUS sp.) following forest fires or clear cutting; trees seldom exceed 10 m in height (Ouellet 1993). Nests generally are situated close to the trunk in the upper half of a small-to-medium-sized fir or spruce, typically in conifer thickets, often on steep slopes (Rimmer 1996). In migration and winter also in deciduous forest, forest borders, open woodland, second growth, and scrub. Winter habitat may be restricted to primary tropical forest (Rimmer et al. 1993). Occurred at fairly high densities in moist, broad-leafed montane forest in the Dominican Republic (Rimmer 1996).

Ecology

At Mount Mansfield, Vermont, density was estimated at about 50-60 pairs/40 ha in optimal habitat (Rimmer 1996).

Reproduction

Eggs are laid in June (mostly) and July. Clutch size is 3-6 (average 3-4). Incubation, by female, lasts 12-14 days. Young are tended by both parents, leave nest at 11-13 days. Pairs with failed nests early in the season may renest. Causes of nest failure include predation by red squirrel and blue jay and desertion (Rimmer 1996).
Terrestrial Habitats
Forest - HardwoodForest - ConiferForest - MixedWoodland - HardwoodWoodland - ConiferWoodland - MixedShrubland/chaparral
Palustrine Habitats
Riparian
Other Nations (2)
CanadaN2B
ProvinceRankNative
Prince Edward IslandSHBYes
New BrunswickS2BYes
Nova ScotiaS1BYes
QuebecS2BYes
OntarioSNAYes
United StatesN4B
ProvinceRankNative
MarylandSNAYes
VirginiaSNAYes
MaineS2BYes
PennsylvaniaSNAYes
New HampshireS2BYes
South CarolinaSNAYes
ConnecticutSNAYes
New YorkS2BYes
MassachusettsSXBYes
DelawareSNAYes
GeorgiaS3MYes
New JerseyS3NYes
North CarolinaSNAYes
VermontS2BYes
Rhode IslandSNAYes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentSmall (1-10%)Slight or 1-10% pop. declineModerate (short-term)
1.3 - Tourism & recreation areasSmall (1-10%)Slight or 1-10% pop. declineModerate (short-term)
2 - Agriculture & aquaculturePervasive - largeModerate or 11-30% pop. declineHigh (continuing)
2.1 - Annual & perennial non-timber cropsPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
5 - Biological resource usePervasive - largeModerate or 11-30% pop. declineHigh (continuing)
5.3 - Logging & wood harvestingPervasive - largeModerate or 11-30% pop. declineHigh (continuing)
6 - Human intrusions & disturbanceUnknownUnknownModerate (short-term)
6.1 - Recreational activitiesUnknownUnknownModerate (short-term)
9 - PollutionPervasive (71-100%)Moderate or 11-30% pop. declineLow (long-term)
9.5 - Air-borne pollutantsPervasive (71-100%)Moderate or 11-30% pop. declineLow (long-term)
11 - Climate change & severe weatherPervasive (71-100%)UnknownLow (long-term)
11.1 - Habitat shifting & alterationPervasive (71-100%)UnknownLow (long-term)

Roadless Areas (46)
New Hampshire (39)
AreaForestAcres
Carr MountainWhite Mountain National Forest17,110
Carr MountainWhite Mountain National Forest17,110
Carr MountainWhite Mountain National Forest17,110
Cherry MountainWhite Mountain National Forest8,766
Cherry MountainWhite Mountain National Forest8,766
Dartmouth RangeWhite Mountain National Forest9,233
Dartmouth RangeWhite Mountain National Forest9,233
Dartmouth RangeWhite Mountain National Forest9,233
Great Gulf Ext.White Mountain National Forest15,110
Great Gulf Ext.White Mountain National Forest15,110
Great Gulf Ext.White Mountain National Forest15,110
JobildunkWhite Mountain National Forest3,660
JobildunkWhite Mountain National Forest3,660
JobildunkWhite Mountain National Forest3,660
KilkennyWhite Mountain National Forest28,766
KilkennyWhite Mountain National Forest28,766
Kinsman MountainWhite Mountain National Forest8,999
Kinsman MountainWhite Mountain National Forest8,999
Kinsman MountainWhite Mountain National Forest8,999
Mt. Wolf - Gordon PondWhite Mountain National Forest11,846
Mt. Wolf - Gordon PondWhite Mountain National Forest11,846
Mt. Wolf - Gordon PondWhite Mountain National Forest11,846
PemigewassetWhite Mountain National Forest32,255
PemigewassetWhite Mountain National Forest32,255
PemigewassetWhite Mountain National Forest32,255
Pemigewasset ExtWhite Mountain National Forest15,840
Pemigewasset ExtWhite Mountain National Forest15,840
Pemigewasset ExtWhite Mountain National Forest15,840
Presidential - Dry River ExtWhite Mountain National Forest10,555
Presidential - Dry River ExtWhite Mountain National Forest10,555
Presidential - Dry River ExtWhite Mountain National Forest10,555
Sandwich RangeWhite Mountain National Forest16,797
Sandwich RangeWhite Mountain National Forest16,797
Sandwich RangeWhite Mountain National Forest16,797
WatervilleWhite Mountain National Forest4,312
WatervilleWhite Mountain National Forest4,312
Wild RiverWhite Mountain National Forest46,878
Wild RiverWhite Mountain National Forest46,878
Wild RiverWhite Mountain National Forest46,878
Vermont (7)
AreaForestAcres
Bread LoafGreen Mountain and Finger Lakes National Forests1,768
Bread LoafGreen Mountain and Finger Lakes National Forests1,768
Bread LoafGreen Mountain and Finger Lakes National Forests1,768
Griffith Lake 09084Green Mountain and Finger Lakes National Forests1,833
Griffith Lake 09084Green Mountain and Finger Lakes National Forests1,833
Lye Brook Addition 09085Green Mountain and Finger Lakes National Forests1,111
Lye Brook Addition 09085Green Mountain and Finger Lakes National Forests1,111
References (28)
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