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Survival Estimates For Migrant Juvenile Salmonids
Passing Through The Bonneville Dam Using
Radio-telemetry

The Problem

As anadromous juvenile salmonids migrate from freshwater rearing habitats to the ocean, they are vulnerable to a host of factors that affect their survival. Direct effects associated with dam passage (e.g., instantaneous mortality, injury, loss of equilibrium, etc.) and indirect effects (e.g., predation, disease, and physiological stress) contribute to the total mortality of seaward migrating salmonids. Many studies have been conducted to determine the effects of hydroelectric dams on the survival of salmonid migrants. Based on this research and studies examining migrant salmonid behavior at dams in the Columbia River Basin, management actions are currently being implemented to improve the survival of juvenile salmonid migrants.

Bonneville Dam, Columbia River.
Bonneville Dam, Columbia River.

Radio telemetry has been used extensively to evaluate the survival of fish and wildlife populations and to monitor the behavior and passage routes of yearling and sub-yearling chinook salmon Oncorhynchus tshawytscha and juvenile steelhead O. mykiss through hydroelectric projects in the Columbia River Basin. Detection rates of marked fish affect the sample size required for a given level of precision and thus, the reliability of survival estimates. Similar to the advantages provided by Passive Integrated Transponder (PIT) tags over other marking techniques, the high detection rates observed in radio-telemetry studies of migrant salmonids in the lower Columbia River suggest that the numbers of fish necessary to generate survival estimates with similar or greater precision could be reduced using radio-tagged fish. Recent technological advancements in radio-telemetry equipment have decreased the size and increased the life of transmitters, eliminating many of the past problems associated with using this technique. Further, in areas where PIT-tag survival estimates continue to be generated, the use of radio telemetry would provide a means of validating these estimates using a different technique.

Objectives

The objective of this study during 2003 is to evaluate the survival of juvenile yearling and sub-yearling chinook salmon and steelhead trout through various passage routes at Bonneville Dam.

Methodology

The I-205 Bridge near Portland, OR.
The I-205 Bridge near Portland, OR.
Radio-telemetry antenna.
Radio-telemetry antenna.

Radio-telemetry systems are installed at hydroelectric projects and at various locations along the Columbia River. For the Bonneville Dam evaluations, the lowermost radio-telemetry array is the I-205 Bridge which spans the breadth of the Columbia River near Portland, OR. Juvenile salmonids are then tagged and released at pre-determined locations based on the research questions posed by fish and water managers. As the radio-tagged fish migrate downstream they are interrogated with the radio-telemetry systems. Data collected with these systems are processed and subjected to QA/QC protocols before being analyzed. Survival estimates are then generated using the statistical methods described in the following publications:

Burnham, K.P., D.R Anderson, G.C. White, C. Brownie, and K.H. Pollock. 1987. Design and analysis methods for fish survival estimates based on release-recapture. American Fisheries Society Monograph No. 5.

Cormak, R. M. 1964. Estimates of survival from the sighting of marked animals. Biometrika 51:429-438.

Jolly, G. M. 1965. Explicit estimates from capture-recapture data with both death and immigration-stochastic model. Biometrika 52:225-247.

Leberton, J.D., K.P. Burnham, J. Clobert, and D. R. Anderson. 1992. Modeling survival and testing biological hypotheses: using marked animals: A unified approach. Ecological Monographs 62:67-118.

Seber, G. A. F. 1965. A note on the multiple recapture census. Biometrika 52: 249-252.

Skalski, J.R., R.L. Townsend, and A.E. Giorgi. 1998. The design and analysis of salmonid tagging studies in the Columbia River Basin, Volume XI, Recommendations on the design and analysis of radio-telemetry studies of salmonid smolts to estimate survival and passage efficiencies. Report prepared for the U.S. Department of Energy, Bonneville Power Administration. Division of Fish and Wildlife, Contract DE-B179-90BP02341.

Highlights and Key Findings

Release mechanism used during the 2002 Minimum Gap Runner turbine unit evaluation.
Release mechanism used during the 2002 Minimum Gap Runner turbine unit evaluation.

Past studies at Bonneville Dam have been designed to evalaute the effects of passing under differeing dam operation conditions and through various routes at this hydroelectric project. The information from these studies is routinely evaluated by federal, state, and tribal management agencies and used to formulate strategies that will improve the survival of juvenile salmon and thus, aid in the recovery of endangered salmon populations in the Columbia River Basin. Studies during 2002 included evaluations of an experimental turbine unit (Minimum Gap Runner). Results from this evaluation indicated that survival through this experimental turbine unit was high. Based on this result, evaluations of the Minimum Gap Runner Turbine Unit will continue during 2003.

Where Are We Headed In 2003

During 2003, the survival of juvenile salmonids passing through the ice and trash sluiceway, downstream migration channel at Bonneville Dam's first powerhouse, and through a minimum gap runner turbine unit will be evaluated. The experimental design of this study will be formaulated to provide information to fish and water managers that can be used to assess the effectiveness of proposed mitgation strategies during 2003.

Project Contact

Tim Counihan
U.S. Geological Survey
Western Fisheries Research Center
Columbia River Research Laboratory
5501-A Cook-Underwood Rd.
Cook, WA 98605-9717

Email: tim_counihan@usgs.gov
Phone: 509-538-2299
Fax: 509-538-2843

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