Appendix B. Monthly depth distributions of kokanee in front of Dworshak Dam during the day and at night, depth of water withdrawal (cross hatched area), possible depth of water withdrawal (shaded box), amount of discharge at the time of the survey, and temperature
Dworshak Reservoir pool recommendations contained herein are independent of conditions for upstream or downstream anadromous fish migration and of any other purposes not specifically stated. Nothing in this report shall limit or restrict future water rights claims or flow recommendations made by the Nez perce Tribe for any purposes. The authors also recognize that the needs of the resident fish studied may conflict with the needs of downstream anadromous fish. This report makes no attempt to resolve the conflicts or recommend priorities among alternative uses of Dworshak Reservoir water. The kokanee fishery declined during our study from a harvest of 206,000 kokanee and a catch rate of 1.5 fish/hour in 1988 to 95,000 kokanee at a catch rate of 0.8 fish/hour in 1990. Limited surveys in 1991 indicated a further decline in catch rates to 0.5 fish/hour.
The Nez Perce Tribe (NPT) and the Idaho Department of Fish andChanges in the kokanee fishery reflected population changes in the reservoir.Mid-water trawling in 1989 indicated the reservoir contained 13 kokanee of harvestable size per acre but that dropped to 2 kokanee per acre in 1991. Angler satisfaction also declined throughout the study from 37% rating the fishing as poor in 1988, to 55% giving it this rating in 1990.Nearly all anglers cited low numbers of fish caught as the reason for the rating.Management goals should therefore be towards more numerous but slightly smaller kokanee to maximize angler satisfaction.Dworshak kokanee have exceedingly low annual survival rates; much lower than other kokanee populations.Over 80% of yearling kokanee die before recruiting to the fishery the following year.Losses of kokanee through Dworshak Dam appear responsible for the high mortality rates. As many as 83,000 to 235,000 kokanee of a single age group were estimated to be lost annually.The resulting low densities reduced catch rates from 1.5 to 0.5 fish/hour and likely reduced fishing effort by 66%. Low kokanee density has, however, triggered good growth rates. Kokanee averaged 11 inches by July of their third summer in the reservoir. This compares to 7.5 inches in Coeur d'Alene Lake, and 8.3 inches in Lake Pend Oreille. Kokanee in these other lakes live to be 1 to 3 years older than Dworshak Reservoir kokanee and so ultimately make up some of the difference in length.During our study, Dworshak Reservoir was much more nutrient poor than when it was first filled in 1971. We would have expected nutrient input from inundated vegetation and soils to have stabilized, however, our results indicated the reservoir may still be declining in nutrient status.Near-shore habitat has also been altered since initial inundation. Vegetation along the shoreline has been eliminated due to fluctuating water levels and wave action. Cover and food production for littoral fish species have been adversely affected by this change. Abundance of redside shiners, an important forage species, peaked only a few years following initial impoundment. This species was in decline prior to the reservoirwide...
CHAPl-92 16 LITERATURE CITED Anonymous. 1983. A proposal for compensation of kokanee fishery losses at Pend Oreille Lake, Idaho. Idaho Department of Fish and Game. Boise. Bowler, B. 1975. Lake Pend Oreille kokanee life history studies. Idaho Department of Fish and Game.
We used split-beam hydroacoustics to monitor kokanee Oncorhynchus nerka kennerlyi abundance in Dworshak Reservoir from 1995 to 1996 in order to quantify the impacts of water releases from Dworshak Dam. The kokanee population was at a record high level of 1.9 million age-I and age9 fish (350 fishlha) during June 1995. Large discharges of water during July and August of 1995 did not result in major losses of kokanee. Midwinter flooding in February. March, and April of 1996: however, caused entrainment losses of 90% of all kokanee in the reservoir. The population declined to 140,000 kokanee. High flows during spring ~n-o f f caused another 50% of the kokanee to be lost, further reducing the population to 71,000 fish (13 fishlha). Entrainment losses were partially explainable by the distribution of kokanee in the reservoir. During winter, all age-classes of kokanee congregated near the dam making them susceptible to high releases of water. Kokanee appeared to be less susceptible to entrainment during summer and early fall because most kokanee were in other parts of the reservoir: adults were in the upper reservoir staging to spawn, fry were in the upper reservoir having emerged from tributary streams, and juvenile kokanee were spread throughout the reservoir.
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