|
Feasibility of Using 3-D Acoustic Telemetry to Assess the Response of Resident Salmonids to Strobe Lights in Lake Roosevelt, Washington
The Problem
 |
| Third
Powerhouse area of Grand Coulee Dam where high entrainment of
kokanee has been documented. |
The Chief Joseph Kokanee Enhancement Project was initiated in 1995 by
the Colville Confederated Tribes to determine the stock status of kokanee
above Chief Joseph and Grand Coulee dams. Subsequently, an entrainment
study at Grand Coulee Dam indicated that 200,000 - 600,000 kokanee were
entrained, primarily at the 3rd powerhouse, during a 40-month time period.
Therefore, the entrainment of resident salmonids at Grand Coulee Dam was
identified as a management problem to be solved in the coming years. Following
the recommendations of the Independent Scientific Review Panel, research
was initiated to investigate a strategy to reduce entrainment by using
strobe lights to repel salmonids away from the 3rd powerhouse at Grand
Coulee Dam. The research conducted under this study corresponds to reimbursable
agreement number 00004767.
Objectives
Our objective is to evaluate the behavioral response of kokanee salmon and rainbow trout to strobe lights.
Methodology
 |
| A
kokanee from Lake Roosevelt, the impoundment above Grand Coulee
Dam. |
The Columbia River Research Laboratory is evaluating the effectiveness
of strobe lights using fish telemetry techniques to locate and track the
movements of acoustic-tagged Kokanee. The method provides precise information
about fish position. The telemetry data will provide species-specific
time series information on an individual fishs movement behavior. The
3-D position of acoustic-tagged fish will be monitored over time to study
the Kokanee movement response to strobe light operation.
Highlights and Key Findings
Within our fixed hydrophone array located in the cul-de-sac of the third powerhouse, we detected 15 kokanee salmon and 34 rainbow trout during 3 of the 8 treatment blocks for which we collected data. Kokanee had a median residence time within the array of 0.36 h and rainbow had a median residence time of 2.1 h. There were approximately equal numbers of fish and number of detections during the day and night, and during the strobe on and off treatments. We observed differences in the spatial distribution of kokanee detections among strobe light treatments and diel periods. When the strobe lights were on, the mean depth of kokanee was deeper than when the strobe lights were off for both day and night periods. We observed one potential example of entrainment where a kokanee salmon entered the array at a shallow depth and descended to a potential entrainment depth near a turbine intake. Between treatments and day/night, we detected nearly equal numbers of rainbow within 25 m of the strobe light, although no kokanee were detected within 25 m of the strobe lights when they were on. Mean depth distributions above and below the strobe lights showed that a high proportion of the tagged rainbow trout were at the depth of the strobe light (10 m). The directional vectors, number of detections, residence time, and swimming velocities within 25 m of the strobe light suggest that rainbow were attracted to the strobe lights.
Where Are We Headed In 2003
Data analysis and report writing will take place in 2003.
Project Contact
Dennis Rondorf
U.S. Geological Survey
Western Fisheries Research Center
Columbia River Research Laboratory
5501-A Cook-Underwood Rd.
Cook, WA 98605-9717
Email: dennis_rondorf@usgs.gov
Phone: 509-538-2299
Fax: 509-538-2843
Publications
|