| Characterization
of the Beaufort Sea Flyway:
Common Eiders and Long-tailed Ducks
Populations
of common eiders (Somateria mollissima) and long-tailed
ducks (Clangula hyemalis) have been listed as species-at-risk
by Region 7, U.S. Fish and Wildlife Service (USFWS) because both
species are declining (Goudie et al. 1994, Suydam et al. 1997,
Wilbor 1999, Suydam et al. 2000). Current and proposed development
activity throughout the Beaufort Sea raises concern for these
species. Historically, large numbers of both of these species
were found on coastal barrier islands and lagoons of the Beaufort
Sea. Coastal Beaufort Sea is exposed to increasing disturbance
and habitat change as a result of expanding oil and gas development.
Information on how sea ducks use the Beaufort Sea is limited primarily
to anecdotal data or site specific studies (Johnson and Herter
1989, Wilbor 1999).
In
the fall and spring, western arctic populations of common eiders
and long-tailed ducks migrate along the coast of the Beaufort
Sea to and from breeding areas in Canada and Alaska (Johnston
and Herter 1989). Currently (1990’s) about 72,600 common
eiders migrate past Point Barrow in spring (May and June) and
autumn (August - October) (Suydam et al. 2000). Data on how common
eiders use Beaufort Sea waters is fragmentary except during the
brood rearing period when successfully nesting hens and ducklings
are found near barrier islands. How much eiders use the Beaufort
Sea in summer and autumn is unknown. In spring, eiders are known
to migrate past points in the Beaufort Sea; however, staging locations,
if they occur, are unknown for eiders nesting on barrier islands
in the coastal waters of the Beaufort Sea in Alaska. Identification
of spring staging areas, key foraging areas and habitats used
in summer, and fall staging areas throughout the Beaufort Sea
is poorly described for common eiders and long-tailed ducks.
The primary objectives of this study are to locate
and describe staging areas and habitats used by common eiders
and long-tailed ducks in the Beaufort Sea. These objectives include:
- Locate migratory flocks during spring and autumn,
- Determine the timing and duration of migration,
- Define migration pathways and corridors in relation to
sea ice and other climate factors,
- Delineate and describe habitat characteristics of marine
staging and feeding areas.
Marking - Satellite
telemetry is a useful tool to determine movement patterns
and locate staging areas for species that are difficult to survey
because of frequent inclement weather, unknown distribution, and
remote locations (Petersen et al. 1995, Clausen and Bustnes 1998,
Petersen et al. 1999). Individual adult female common eiders and
long-tailed ducks were marked with implanted satellite transmitters
using the surgical technique
first described by Korschgen et al. (1996) and subsequently modified
for eiders and other sea ducks (D. Mulcahy personal communication).
Transmitters were programmed to maximize the
frequency of locations per individual while still adequately covering
the period birds may be in the Beaufort Sea. To document post-nesting
staging areas, foraging sites, and autumn migration pathways,
12 transmitters per year were programmed to provide location information
for 6 hours during a 25 hour period and provide locations for
about 4 months. To characterize spring migration corridors and
staging areas, 18 birds received transmitters that are programmed
to deliver location data every 8 days until 1 May of the following
year, when the radios switched to deliver signals for 6 hours
every 25 hours. These transmitters were expected to last approximately
1 year. Thus, there are two sets of transmitters; one will provide
locations in autumn and the other the following spring. By the
end of the project we hope to have data from two years of autumn
and two years of spring migration from each species (maps).
Long-tailed
ducks were captured at molting areas at Point Thompson in 2002
and common eiders from nests near Egg Island in 2001. The number
of individuals for each sample is the minimum number necessary
to obtain sufficient locations to meet statistical requirements
(Alldredge and Ratti 1986, Otis and White 1999, Seaman et al.
1999), and derived by taking into consideration transmitter performance
and battery life. Sampling is expected to be completed in 2003.
Eider and long-tailed duck locations are plotted
on maps using ArcView software. Maps which are posted here will
be updated weekly during migration or until batteries fail to
allow anyone interested to track the birds movements.
References
Alldredge, J. R. and J. T. Ratti. 1986. Comparison
of some statistical techniques for analysis of resource selection.
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Clausen, P. and J. O. Bustnes. 1998. Flyways
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hrota reassessed by satellite telemetry. Pp. 235-249 in Mehlum,
F., Black, J. M., and Madsen, J. (eds.): Research on Arctic Geese.
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Report. US Geological Survey, Alaska Biological Science Center,
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M. R. Petersen, B. Conant, and K. Vermeer. 1994. The status of
sea ducks in the North Pacific Rim: Toward their conservation
and management. Trans. N. Am. Wildl. and Nat. Res. Conf. 59:27-49.
Goudie, R. I., G. J. Robertson and A. Reed.
2000. Common Eider (Somateria mollissima). In A. Poole
and F. Gill, (eds.): The Birds of North America, No. 546. The
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Johnson, L. L. 1971. The migration, harvest
and importance of waterfowl at Barrow, Alaska. M.Sc. Thesis. Univ.
Alaska, Fairbanks, AK.
Johnson, S. R. 1984. Prey selection by oldsquaws
in a Beaufort Sea lagoon, Alaska. Pp. 12-19, in D. HN. Nettleship,
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of the Beaufort Sea. BP Exploration (Alaska) Inc., Anchorage,
Alaska.
Johnson, S. R., D. R. Herter and M. S. W. Bradstreet.
1987. Habitat use and reproductive success of Pacific eiders Somateria
mollissima v-nigra during a period of industrial activity.
Biol. Conserv. 41:77-89.
Korschgen, C. E., K. P. Kenow, A. Gendron-Fitzpatrick,
W. L. Green and F. J. Dein. 1996. Implanting intra-abdominal radiotransmitters
with external whip antennas in ducks. J. Wildl. Manage. 60:132-137.
Otis, D. L. and G. C. White. 1999. Autocorrelation
of location estimates and the analysis of radiotracking data.
J. Wildl. Manage. 63:1039-1044.
Petersen, M. R., D. C. Douglas and D. M. Mulcahy.
1995. Use of implanted satellite transmitters to locate spectacled
eiders at-sea. Condor 97:276-278.
Petersen, M. R., W. W. Larned and D. C. Douglas.
1999. At-sea distribution of spectacled eiders: A 120-year-old
mystery resolved. Auk 116:1009-1020.
Schamel, D. 1977. Breeding of the common eider
(Somateria mollissima) on the Beaufort Sea coast of Alaska.
Condor 79:478-485.
Seaman, D. E., J. J. Millspauch, B. J. Kernohan,
G. C. Brundige, K. J. Raedeke, and R. A. Gitzen. 1999. Effects
of sample size on kernel home range estimates. J. Wildl. Manage.
63:739-747.
Suydam, R. S., D. L. Dickson, J. B. Fadely and
L. T. Quakenbush. 2000. Population declines of king and common
eiders of the Beaufort Sea. Condor 102:219-222.
Thompson, D. Q. and R. A. Person. 1963. The
eider pass at Point Barrow, Alaska. J. Wildl. Manage. 27:348-356.
Wilbor, S. L. 1999. Status Report on the Bering/Pacific
Oldsquaw (Clangula hyemalis) Population. Unpublished
Report. Alaska Natural Heritage Program, Environment and Natural
Resources Institute, University of Alaska Anchorage.
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migration of eiders and other waterbirds at Point Barrow, Alaska.
Arctic 35:403-410.
This
study was funded by:
US Geological Survey, USFWS Science Support funds
US Geological Survey, Alaska
Science Center
Sea Duck Joint Venture
with in-kind support from:
BP Exploration, Inc. (AK)
USFWS,
Arctic National Wildlife Refuge
For more information
about this study please contact:
Margaret Petersen
US Geological Survey
Alaska Science Center
1011 E. Tudor Road, MS 701
Anchorage, AK 99503
Common
eider maps
Autumn migration
Wintering locations
Spring migration
Long-tailed
duck maps
Autumn migration
Wintering locations
Spring migration
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