Shooting and
Entanglement and the decline of Steller sea lions
Andrew Trites and Peter Larkin(UBC) worked on a mathematical
model to evaluate the role that pup harvests, native kills, and incidental
and intentional killing by commercial fisheries may have played in the
population decline in Alaska. Their model estimate how many sea lions
would have been alive since 1956 if no unusual deaths occurred, and how
many additional sea lions would have had to die to cause the pattern of
population change that was observed in the wild.
The model indicated that the historic harvesting of 45,000 sea lion
pups between 1963 and 1972 was substantial and contributed to stabilizing
the numbers of sea lions breeding in Alaska through the 1960s and 1970s.
The number of sea lions 'missing' from the model were consistent with
estimates of intentional and incidental kills during this time period.
However these sources of mortality cannot account for the dramatic population
declines through the 1980s. From 1980 to 1990, the model suggests the
number of Steller sea lions disappearing each year rose from 5% to 24%
of the population. Whether these losses were caused by the removal of
prey by fisheries is a circumstantial possibility, but comparisons of
catch data and sea lion numbers have not shown a direct linkage.
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Last updated 26 June 2006
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The status of Steller sea lion populations and the development of fisheries in the Gulf of Alaska and Aleutian Islands.
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Trites, A.W. and P.A. Larkin. 1992.
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In A report of the Pacific States Marine Fisheries Commission pursuant to National Oceanic and Atmospheric award no. NA17FD0177. University of British Columbia, Fisheries Centre, 2204 Main Mall, Vancouver, B.C. V6T 1Z4. pp. 134
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abstract
The goal of our study was to assess the status of Steller sea lions in Alaska, review their
population biology, and develop a simulation model to explore the role that harvesting and
incidental kills by fisheries may have played in the sea lion decline. We also attempted to relate
the population declines to the amount of fish caught in the Gulf of Alaska and Aleutian Islands,
and to the number of vessels fishing from 1950 to 1990.
Using life tables to estimate population size, the numbers of Steller sea lions were estimated
for all rookeries for which information was available in each of six areas in the Gulf of Alaska
and Aleutian Islands. The total population appears to have risen from 150,000 to 210,000 from
the mid 1950s to 1967. The population was then stable for roughly ten years, then increased to
225,000 by 1979. Since then it has decreased to about 85,000. Most of the decline took place
in Area 3 (Kodiak region) but there were also significant declines in Areas 4 to 6 (westward of
Kodiak). Increases have occurred in the smaller populations of Areas 1 and 2 (southeast Alaska
and Prince William Sound).
A major growth in domestic fisheries occurred after the declaration of 200 mile zones. The
traditional fisheries for salmon, herring and halibut were augmented by major groundfish
fisheries. The decline in the numbers of Steller sea lions has been coincidental with the growth
in the numbers and size of vessels and the increase in catch.
The stabilization in the numbers of Steller sea lions in the Gulf of Alaska from 1956 to 1980
can be attributed to the direct effect of incidental capture in fishing gear, the shooting of sea lions
and the harvesting of adults and pups. However, these factors explain but a small portion of the
recent population decline, from 1980 to the present. Some sea lions are missing in the arithmetic
of population dynamics which cannot be accounted for by movements of animals from one area
to another. Whether these losses are caused by the removal of food resources is a circumstantial
possibility, but evidence of local abundance of food resources at particular times of the year for
particular segments of the population is needed to build a convincing case. Other causes, such
as diseases and parasites must also be kept in mind as possible contributing factors.
Research on Steller sea lions should focus on the decline in abundance since 1980, changes
in body size, the diet at various seasons of the year, bioenergetics and nutritional requirements,
and assessment of local abundance of various food items. Long term research on the ecosystem
dynamics of the region will be necessary for long term management of all living resources but
how best to focus that research is a matter of current scientific debate that will not be resolved
quickly.
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