Second North American Sea Duck Conference - Patuxent Wildlife ...
Second North American Sea Duck Conference - Patuxent Wildlife ...
Second North American Sea Duck Conference - Patuxent Wildlife ...
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Nora A. Rojek<br />
SECOND NORTH AMERICAN SEA DUCK CONFERENCE<br />
STATUS, BREEDING BIOLOGY, AND CONSERVATION<br />
OF STELLER’S EIDER NEAR BARROW, ALASKA, 1991-2005<br />
Fairbanks Fish and <strong>Wildlife</strong> Field Office, U.S. Fish and <strong>Wildlife</strong> Service, 101 12th Avenue, Room<br />
110, Fairbanks, Alaska 99701; nora_rojek@fws.gov<br />
The Alaska-breeding population of Steller’s eider (Polysticta stelleri) was listed as a U.S. Federally<br />
threatened species in 1997 due to concerns over apparent declines in numbers inferred from a reduction<br />
of nesting range in Alaska. Aerial survey and observational data indicate the region surrounding the<br />
village of Barrow is the core of Steller’s eiders breeding distribution in northern Alaska. In 1991, the<br />
U.S. Fish and <strong>Wildlife</strong> Service and the <strong>North</strong> Slope Borough, Department of <strong>Wildlife</strong> Management<br />
initiated breeding biology studies of Steller’s eider near Barrow. Between 1991 and 2005, breeding<br />
has occurred in 53% of the years. A total of 116 viable nests have been monitored, with low nest<br />
success averaging 15.7% (95% C.I.: 10.9-20.4%). Only four out of 17 hens monitored with VHF<br />
radio-transmitters successfully fledged at least one duckling. Standardized ground-based breeding<br />
pair surveys were initiated in 1999 to estimate abundance and distribution within 3 km of the road<br />
system (total standard survey area of 135 km²). In non-nesting years (2001-2004), density has ranged<br />
between 0 and 0.16 males/km², while in the last three nesting years (1999, 2000, and 2005) density<br />
has ranged between 0.43 and 0.98 males/km². Due to the periodic non-breeding and rarity of finding<br />
nests even in good nesting years, there is still much to learn about this species’ breeding biology in<br />
order to determine what management actions would be most effective in assisting recovery. While<br />
we now have an understanding that the abundance of lemmings and breeding status of lemming<br />
avian predators is positively correlated with Steller’s eider breeding activity, we have not been able to<br />
predict nesting frequency and lack an understanding of how Steller’s eider assess nesting conditions<br />
upon arrival. In 2005, the first nests were found since 2000 and several new management actions<br />
were implemented. These included deployment of video cameras to document causes of nest failure,<br />
localized fox control, and artificial incubation of eggs to reduce predation and egg removal to start a<br />
captive propagation program (implemented by the Alaska <strong>Sea</strong>Life Center).<br />
NOV. 7-11, 2005 ANNAPOLIS, MARYLAND, USA<br />
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