Anas rubripes

Brewster, 1902

American Black Duck

G5Secure Found in 3 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
Identity
Unique IDELEMENT_GLOBAL.2.102967
Element CodeABNJB10040
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassAves
OrderAnseriformes
FamilyAnatidae
GenusAnas
Other Common Names
American black duck (EN) Canard noir (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
Appears to constitute a superspecies with A. platyrhynchos and A fulvigula (AOU 1998). Commonly interbreeds with and sometimes considered conspecific with A. platyrhynchos and/or other species (AOU 1983). Some authors suggest that it might be taxonomically appropriate to recognize the black duck as a dark morph (not subspecies) of the mallard, based on genetic and behavioral similarity and frequent hybridization (Ankney et al. 1986) in this species (AOU 1983). Mitochondrial DNA data indicate an extremely close evolutionary relationship between mallards and black ducks, and, in conjunction with geographic distribnutions, suggest that the black duck is a recent evolutionary derivative of a more broadly distributed mallard-black duck ancestor (Avise et al. 1991). See Livezey (1991) for a phylogenetic analysis and classification (supergenera, subgenera, infragenera, etc.) of dabbling ducks based on comparative morphology.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-06
Change Date1996-11-21
Edition Date2014-03-03
Edition AuthorsJennings, R.
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences81 to >300
Rank Reasons
High population numbers, but declining due to overhunting and increasing hybridization.
Range Extent Comments
BREEDING: northern Saskatchewan to Labrador and Newfoundland, south to northern South Dakota, southern Wisconsin, central Indiana, central West Virginia, and North Carolina on Atlantic coast. NON-BREEDING: southeastern Minnesota to southern Ontario and Nova Scotia, south to Texas, Gulf Coast, and Florida. The highest winter densities occur along the Maumee River in Ohio, along the Kankakee River in Illinois, along the Mississippi River bordering Tennessee and extending along the Ohio River to southwestern Indiana, in southwestern Tennessee and northern Alabama, and along the U.S. Atlantic coast from eastern North Carolina to Maine (Root 1988).
Occurrences Comments
This is an estimate. With a breeding range that encompasses the northeastern U.S. states and much of eastern Canada up to Hudson Bay (Longcore, et. al. 2000) and an estimated 900,000 individuals (National Audubon Society, 2014) , there are undoubtedly more than 81 element occurrences.
Threat Impact Comments
Recent decline attributed to habitat change and loss, hybridization and/or competition with Mallard (Ankney et al. 1987; see also Conroy et al. 1989, Ankney et al. 1989, and Merendino and Ankney 1994), and possibly over-hunting (Krementz et al. 1988), and the effects of acid precipitation and aerial spraying for spruce budworm (Ehrlich et al. 1992). Rusch et al. (1990) reviewed status and concluded that hunting and loss of breeding habitat apparently are not major factors in the decline; loss of winter habitat in some areas was noted. Chesapeake Bay breeding populations have declined since the 1950s; the decline is not related to changes in laying date, clutch size, or nest success (Krementz et al. 1991). There is some evidence that this species is much more intolerant of human disturbances than other duck species, including abandonment of nests due to flushing (Longcore, et.a l., 2000).
Ecology & Habitat

Habitat

Shallow margins of lakes, streams, bays mud flats, and open waters. Nests in both dry and wet woodlands. Wide variety of wetland habitats in both freshwater and marine situations, in and around marshes, swamps, ponds, lakes, bays, estuaries, and tidal flats. As a result of a study of postfledging habitat use, Frazer et al. (1990) recommended maintaining large (30-50 ha) marshes containing dense emergent vegetation near a complex of diverse wetland types. BREEDING: Breeding habitat and nest sites very diverse; favors wooded swamps and marshes, brackish or freshwater. In central Ontario, preferred small fertile wetlands with a moderate amount of open water and an irregular shoreline (Merendino and Ankney 1994). Usually nests on ground in concealing vegetation, rarely in abandoned tree nest of other bird species. Significant numbers may return to the natal home range to breed.

Ecology

In fall in eastern Maine and southwestern New Brunswick, maximum distance moved from roost to marsh averaged 10 km (range 1-43 km) (Frazer et al. 1990).

Reproduction

Clutch size 5-17 (usually 9-10). Incubation 23-33 days, by female. Young tended by female, first fly at about 60 days. Can breed as yearling but many males not mated until about 2 or more years old.
Palustrine Habitats
TEMPORARY POOLHERBACEOUS WETLANDFORESTED WETLANDBog/fenRiparian
Other Nations (2)
United StatesN5B,N5N
ProvinceRankNative
New JerseyS4Yes
South CarolinaS3NYes
New HampshireS4Yes
LouisianaS3NYes
District of ColumbiaS3NYes
WisconsinS2BYes
Rhode IslandS4B,S4NYes
MissouriSNRNYes
North CarolinaS3B,S4NYes
IndianaS1Yes
ConnecticutS3B,S4NYes
IowaSNAYes
VirginiaS4Yes
KentuckyS4NYes
South DakotaSNAYes
KansasSNAYes
MichiganS4Yes
DelawareS4B,S4NYes
MarylandS4B,S5NYes
New YorkS3B,SNRNYes
VermontS3B,S5NYes
ArkansasS2NYes
GeorgiaS3Yes
West VirginiaS2B,S2NYes
AlabamaS2B,S5NYes
FloridaS3NYes
TennesseeS3NYes
NebraskaSNRNYes
MinnesotaSNRB,SNRNYes
North DakotaSUYes
MaineS5B,S5NYes
TexasSHYes
PennsylvaniaS3B,S4N,S3MYes
MassachusettsS4B,S5NYes
ColoradoSNAYes
WashingtonSNANo
OhioS2Yes
OklahomaS2NYes
MississippiS2NYes
CanadaN5B,N5N
ProvinceRankNative
British ColumbiaSNANo
ManitobaS2BYes
LabradorS5BYes
QuebecS4BYes
SaskatchewanS4BYes
Island of NewfoundlandS4B,S4NYes
OntarioS4Yes
Prince Edward IslandS5B,S4NYes
Nova ScotiaS5B,S5NYes
AlbertaSUBYes
New BrunswickS5B,S4NYes
NunavutSUBYes
Roadless Areas (3)
New Hampshire (1)
AreaForestAcres
Wild RiverWhite Mountain National Forest46,878
West Virginia (2)
AreaForestAcres
Mcgowan MountainMonongahela National Forest10,504
Middle MountainMonongahela National Forest19,020
References (35)
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  2. 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 <i>The Auk</i>]. Also available online: http://www.aou.org/.
  3. Ankney, C. D., D. G. Dennis, and R. C. Bailey. 1987. Increasing mallards, decreasing American black ducks: coincidence or cause and effect? J. Wildl. Manage. 51:
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  5. Ankney, C. D., et al. 1986. Low genetic variation between black ducks and mallards. Auk 103:701-709.
  6. Avise, J. C., C. D. Ankney, and W. S. Nelson. 1991. Mitochondrial gene trees and the evolutionary relationship of mallard and black ducks. Evolution 44:1109-1119.
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