Ecology and Vulnerability
Blue-winged Teal
Photo credit: US Fish and Wildlife Service
Profile: Blue-Winged Teal ▾▸
Background
Massachusetts is at the eastern edge of the blue-winged teal's distribution. The historical status of blue-winged teal in Massachusetts is unclear, but the current breeding population is...
Background
Massachusetts is at the eastern edge of the blue-winged teal's distribution. The historical status of blue-winged teal in Massachusetts is unclear, but the current breeding population is relatively small and dispersed1. The species is, however, common during spring and fall migrations between wintering and breeding grounds2. Blue-winged teal breed from coast to coast, but their distributional center is in the Prairie Pothole Region of the Northern Great Plains. This is an area characterized by a high density of shallow wetlands that produces 50-80% of the continent’s ducks3. The blue-winged teal appears to be more sensitive to cold than most duck species and winters from the Gulf coast south through Mexico, the Carribean, Central America, and South America1,4.
Climate Impacts
Because the Prairie Pothole Region produces a large proportion of the continent’s ducks, events in this region can greatly impact entire populations. Duck production has been shown to vary greatly from year to year due to changes in the amount of wetlands in this region linked to variable weather patterns5. Climate models project increased drought conditions for the region, resulting in northward shifts in the ducks' breeding distribution, with the potential for dramatic reductions in overall duck populations3. In addition, loss of pothole wetlands through drying can concentrate predators, which would have a greater impact on nesting ducks in the remaining pothole wetlands. Dramatically reduced duck populations in the Prairie Pothole Region could also potentially reduce the number of blue-winged teal that migrate through the state of Massachusetts.
Climate change also has the potential to impact the small local breeding population of blue-winged teal in many ways. Climate models generally predict increased short term drought conditions, reduced summer stream flows, and increased duration of low summer flows in the northeastern US6. Typical responses to drought conditions in ducks include less breeding, decreased clutch sizes (number of eggs laid by nesting pair), shortened breeding season, decreased frequency of renesting, and other responses that reduce reproduction3,7,8,9. Changes in migration timing are likely, and have already been documented for blue-winged teal in Massachusetts and New York10. Modeling by the US Forest Service predicts the loss of breeding populations from the state of Massachusetts, along with a range-wide decrease in both distribution and abundance11.
1. Massachusetts Audubon. 2015. Blue-winged Teal Anas discors. Breeding Bird Atlas 2 Species Accounts. <http://www.massaudubon.org/our-conservation-work/wildlife-research-conservation/statewide-bird-monitoring/breeding-bird-atlases/bba2/find-a-bird/(id)/188 > (Accessed 23 April 2015).
2. DeGraaf, R.M., and M. Yamasaki. 2001. Blue-winged Teal (Anas discors). Page 100 in: New England Wildlife: Habitat, Natural History, and Distribution. University Press of New England, Hanover, NH.
3. Sorenson, L.G., R. Goldberg, T.L. Root, and M.G. Anderson. 1998. Potential effects of global warming on waterfowl populations breeding in the Northern Great Plains. Climatic Change 40:343-369.
4. Johnsgard, P.A. 1975. Blue-winged Teal Anas discors Linnaeus 1766. Pages 270-279 in: Waterfowl of North America. Indiana University Press, Bloomington, IN.
5. Klett, A.T., T.L. Shaffer, and D.H. Johnson. 1988. Duck nest success in the Prairie Pothole Region. The Journal of Wildlife Management 52:431-440.
6. Huntington, T.G., A.D. Richardson, K.J. McGuire, and K. Hayhoe. 2009. The disproportionate effect of global warming on the arrival dates of short-distance migratory birds in North America. Canadian Journal of Forest Research 39:199-212.
7. Davies, J.T., and F. Cooke. 1983. Annual nesting productivity in snow geese: prairie droughts and arctic springs. The Journal of Wildlife Management 47:291-296.
8. Krapu, G., A. Klett, and D. Jorde. 1983. The effect of variable spring water conditions on mallard reproduction. The Auk 100:689-698.
9. Cowardin, L.M., D.S. Gilmer, and C.W. Shaiffer. 1985. Mallard recruitment in the agricultural environment of North Dakota. Wildlife Monographs 92:3-37.
10. Butler, C.J. 2003. The disproportionate effect of global warming on the arrival dates of short-distance migratory birds in North America. Ibis 145:484-495.
11. Matthews, S.N., R.J. O’Connor, L.R. Iverson, and A.M. Prasad. 2004. Atlas of climate change effects in 150 bird species of the eastern United States. General Technical Report NE-318. USDA Forest Service, Washington, D.C.