NATIVE FISH SOCIETY P.O. Box 19570 Portland, Oregon 97280 (503) 977-0287 March 17, 1997 Mr. Brian Cunninghame Relicensing Coordinator Warm Springs Power Enterprises P.O. Box 960 Warm Springs, Oregon 97761 RE: Comments on First Stage Consultation Document for license of Pelton-Round Butte Hydro Project Dear Mr. Cunninghame: These comments are specific to the effect of the Pelton-Round Butte Hydro Project on native, wild salmonids with particular emphasis on populations downstream form the hydro dam complex. These comments are primarily in response to the section in your document on genetics at page 96. The fundamental productive capacity of native fish populations within the Deschutes Basin resides within the genetic structure of native fish populations. A framework for management of native fish populations in the Deschutes River is needed to evaluate the effect of the dam on native fish fauna of the river, and this framework would protect and rebuild the genetic variation, life history attributes, and the evolutionary potential for each population affected by dam construction and operation. The existing answer to this framework has been the operation of two fish hatcheries in the Deschutes Basin. The purpose of the Round Butte Fish Hatchery is to mitigate for lost salmon and steelhead production and the Warm Springs Hatchery is to augment spring chinook production in the basin. The management objective of these two hatcheries has been to maintain the wild runs and the wild run characteristics. This decision probably contributed to the maintenance of the productive capacity of native Deschutes salmon and steelhead. Evaluation of these hatcheries to determine whether the hatchery fish have diverged from the wild seed stock and the wild fish still using the river, is necessary. Evaluation of the Warm Springs Hatchery spring chinook program shows that some divergence has taken place. It may be impossible to keep this from happening, but measures can be taken to control it. Each hatchery ought to have a gene conservation program as part of its operational structure and each hatchery should be evaluated on maintaining native genetic resources in the fish populations they affect. This must be a part of the Hydro license. The hydro dams and other dams within the basin once available to anadromous salmonids have not only fragmented the habitat for native fish species, they have also fragmented the native gene pool for salmonids and other fishes. It is this latter situation that the Native Fish Society would like the Warm Springs Tribes to address in its competitive bid for the license to operate the hydro dam complex. It is possible that the portion of the anadromous salmonid gene pool historically found above these dams is lost. For example, the Round Butte Hatchery used Metolius River spring chinook as its egg source, but longterm hatchery failures forced the importation of spring chinook eggs from the Warm Springs River Hatchery. The Metolius River spring chinook is extinct. The same point could be made for Squaw Creek steelhead. It can be assumed that the native gene pool for anadromous salmonids above the Pelton-Round Butte Hydro Dams no longer exists. Therefore, the effect of these dams has been to eliminate a portion of the historic gene complex of the Deschutes Basin. Where there were at least three native, wild populations of spring chinook in the basin, there are now only two. There were many more native wild steelhead populations in the basin, but now the only ones are found below the dams. It is our opinion, then, that because the hydro dams have fragmented the original gene pool for native fish, mitigation should be focused on maintaining the productive capacity and evolutionary potential of native anadromous salmonid populations below the dams. In addition, other native fishes should also be included. For example, bull trout below the dams should be included. Our view of mitigation is not more hatchery fish, but making investments into rebuilding and protection of native fish populations and their spawning and rearing habitats below the dams. By taking this approach what remains of the wild, native gene pool can be maintained, contributing to maintenance of the biological diversity of the basin that had been fragmented by the hydro dams. It is our concern that if mitigation remains primarily one of hatchery releases, the wild portion of the gene pool will be lost eventually and the hatchery stock cannot be maintained. Your list of references does not include the large and growing literature on gene conservation and the problems associated with hatchery programs. For example, in 1978, Reginald Reisenbichler published a study that showed hatchery and wild steelhead crosses did not survive in nature as well as wild - wild crosses. This reduced survival, they theorized would result in fewer smolts produced from matings of hatchery and wild steelhead and fewer returning adults. In short, the hatchery has a significant effect upon the productive capacity of native, wild steelhead in the basin. This study has since been repeated in a 18 year study evaluating hatchery and wild steelhead interactions on the Kalama River by the Washington Department of Fish and Wildlife. In their work, the hatchery steelhead produced 55% of the juveniles in the stream through natural spawning but the adult progeny survival back to the stream was zero. So the hatchery system can also be part of the hydro effect on the natural ecosystem below the dam, because it is producing fish that are less fit for survival in nature, and when they interbreed with wild fish of the same species, the progeny are less fit. Since the hatchery is an artifact of the hydro dam, the hatchery is a hydro dam effect upon the natural system. How does one mitigate the effect of the hatchery program? Several options are possible: First, the hatchery can be operated better so that divergence is controlled better, but probably will never be eliminated; second, the hatchery is eliminated; or third, the mitigation program is focused on maintaining the biological diversity of native fishes below the projects in the mainstem and accessible tributaries. The Native Fish Society recommends the following to assist in the development of a framework for the protection and rebuilding of native fish in the Deschutes Basin: 1. Is a framework concept for native wild, salmonids needed for the Deschutes Basin? If so, then state the reasoning and the short and long-term objectives. 2. Identify how this framework fits into tribal values and traditions and how the framework would advance those values and traditions into the future. 3. Identify in what ways the construction of dams in the basin have increased risk to native fish populations and what corrective actions are needed. 4. Develop studies that provide biological information that help resolve risks 5. Determine how biological risks and solutions affect tribal cultural values and economic expectations. Specific biological study recommendations: 1. Inventory existing genetic structure and life history attributes of native, wild anadromous salmonids. 2. Compare this information on native fish to existing hatchery reared anadromous salmonids. 3. Based on this information evaluate risk and the means to control risk to native salmonids and to maintain a high degree of fitness in hatchery salmonids. Determine whether hatchery programs should be reduced or eliminated. Determine native salmonid conservation strategies to mitigate for the operation of the hatchery and hydro system. The EDT methodology is designed to address the creation of a native fish productivity framework for the Deschutes Basin. I would recommend that this be a product of that work. The Native Fish Society may be submitting additional comments, but if you have any questions regarding the above, please give me a call. Sincerely, Bill M. Bakke, Director