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Annual Report: 1997 Sammamish River Sockeye Salmon Fry Production Evaluation PDF Format - [137KB]
Acknowledgements The success of this project relies on the hard work of a number of dedicated permanent and temporary WDFW personnel. WDFW Fish Biologist Steve Wolthausen, and Scientific Technician Chuck Ridley worked long hours at night operating and maintaining the trap, marking and releasing fry, and enumerating catches. WDFW Wild Salmon Production & Survival Evaluation Unit biologists Mike Ackley and Pete Topping provided valuable logistical support. |
Introduction
The numbers of adult sockeye salmon returning to the Lake Washington
system are estimated as they pass the Ballard Locks, and as spawners in
the Cedar River, primary tributaries to the Sammamish system, and on certain
beaches. The majority of the spawning has occurred in the Cedar River,
but in three recent years (1992, 1994, and 1996), biologists have estimated
that a quarter to a third of the Lake Washington Basin sockeye have spawned
in the Sammamish River Basin (Egan and Ames WDFW memo, 1997) .
Over the other twelve of the last fifteen years for which escapement estimates
are available for all areas, the Cedar River accounts for an average of
88% of the total spawners (range = 82% to 98%). This interannual variation
may result from differential survival as a function of spawning and emergence
timing relative to stream specific hydrology. In addition to run timing
differences, recent electrophoretic analysis indicates that the sockeye
which spawn in the Sammamish system are genetically distinct from the
larger Cedar River population.
In 1992, as part of a multi-agency effort to determine the cause(s) of the decline in the Lake
Washington sockeye run, we began enumerating sockeye fry production from the Cedar River.
Measuring the population at this lifestage and location separates freshwater survival into its two
major components; spawning which takes place in the river and rearing which occurs in the lake.
Over the past six broods, natural spawners in the Cedar River have produced fry populations to
the lake of 0.7 to 27.1 million. We have determined that the severity of peak flows is the primary
factor controlling survival from spawning to fry emigration in this system. Annual estimates of
the numbers of fry entering the lake are also needed to understand the complex ecological
relationships which regulate juvenile sockeye survival during their year in the lake. Because the
Sammamish system may account for a significant portion of the fry entering Lake Washington in
some years, an estimate of this production component is also needed to understand the dynamics
of the combined population.
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