NATIVE FISH SOCIETY P.O. Box 19570 Portland, Oregon 97280 503/ 977-0287 May 22, 1997 Mr. Steve Phelps Washington Department of Fish and Wildlife 600 Capitol Way North Olympia, WA 98501-1091 RE: Issues related to the Draft Wild Salmonid Policy Dear Mr. Phelps: In reviewing the draft Wild Salmonid Policy of April 1997, the Native Fish Society has identified the following issues in that document that we believe should be specifically addressed in the final plan. We are submitting these comments to you for the record. Sincerely, Bill M. Bakke Director ISSUES IDENTIFIED IN THE WILD SALMONID POLICY APPENDIX A ISSUES Resolving Stock Conflicts Issue: The WSP ought to mandate a stock by stock management program rather than aggregate collections of stocks into management units. Aggregation increases risk, especially to small less productive populations. These small populations should be the bellwether of the WSP. If the small, less productive populations cannot be maintained through this policy then it will fail to maintain biological diversity, evolutionary potential and genetic variation of adapted stocks within each species. APPENDIX C ISSUES Issue: Are water quality and sediment standards adequate in the state law? Appealing to state laws that are not adequate or not enforced do nothing for the fish. How effective is this kind of language in making the WSP work on the ground? The WSP should state the standards it must rely on to sustain native, wild populations of salmonids in the state. If the standards presently adopted as state policy are not adequate to protect native species they should be identified. The WDFW should recommend in the WSP those standards that should replace inadequate standards adopted by the state, or standards the state should adopt where none now exist. APPENDIX D ISSUES Issue: WDFW argues MSY rather than MSE can be used to rebuild wild stocks, protect local adaptations and genetic diversity, but does not explain this assumption. Certainly it has not been used to accomplish these good goals in the past. The discussion should explain how it has been used to cause the decline in stocks and how it can be used to protect the stocks according to the policy. In addition, the MSY or MSE standard must address ecological functions. The numerical value of these standards should be based on delivering specific ecological values. The two I am thinking of are: achieving the nutrient capital standard for each watershed from fish carcasses, and maximizing natural selection by having enough spawning adults to maintain locally adapted and genetically diverse stocks. The effective breeding population is about 1/4 of the census population. In other words, if the biological goal for adult spawners is 1000, then 4000 actual adults must be in the spawning escapement. Issue: WDFW assumes the management unit at the stock level will provide benefits of fine scale (sub-stock structure management) at less cost and allow more harvest. Yes, maybe this is so, but at what risk. A risk analysis of this "assumption" must be done. This assumption places small less productive stocks, or sub- stocks at risk. Page D7 Issue: Fails to describe value of small less productive populations and fails to include standards to provide conservation management of these populations. Issue: 500 spawners (effective breeding population) is adequate for maintaining genetic diversity over short term, a few generations according to the literature I looked at. But this must be the Nb population not the N population. If the adult escapement (N) is 500 then the effective breeding population (Nb) is 125. An effective breeding population of 125 is not adequate to maintain the genetic integrity of the wild population. The WSP must state whether the 500 number is Nb or N. Issue: MSY is a harvest/commodity production model that assumes salmon produce a harvestable surplus and it is predicated upon a non-fluctuating environment. This model has not been successful in protecting native, locally adapted stocks especially small, less productive ones. It ignores ecological values such as stock fitness to cope successfully with a fluctuating environment, and natural selection and nutrient capital by stock and watershed. Saying MSY can be used to protect stocks and maintain biological functions is a critical uncertainty that must be evaluated and treated as an experiment. It is loaded with risk and must be treated as such. MSY is harvest friendly not conservation biology friendly. As we have found out, if WDFW is not conservation biology friendly the harvesters lose opportunity and the resource loses capacity. APPENDIX E ISSUES Issue: The 500 spawners issue here again. To get 500 Nb (effective breeders) the spawner escapement must be 500 X 4 = 2,000. I hope the WSP is treating the 500 spawners as Nb rather than N or it will not prevent the loss of genetic diversity and locally adapted stocks will continue to be lost. The first to go will be the multitude of small, less productive stocks. APPENDIX F ISSUES Issue: There is no discussion on ecological interactions regarding disease and transfer of disease to wild stocks. And there is no discussion of disease treatment of hatchery fish and the potential for developing resistant strains of pathogens that outrun the capacity of wild stocks to resist them. This is a major issue in the document. The hatchery folks are scared of disease issues and have shown an aversion to discussing them publicly. Disease treatment in the form of chemicals such as formalin is potentially a very serious EPA water quality issue since this chemical is a carcinogen, and released into public waters. APPENDIX H ISSUES Issues: RASP: This definition would control the use of supplementation but the discussion is limited to this section (the appendices) and should be stated in the policy alternatives. Gene conservation protocols: This is not mentioned. Protocols must be identified and implemented to maintain genetic diversity and local adaptation of hatchery stocks and to minimize genetic problems when hatchery fish interbreed with wild fish. Even if one takes the hatchery brood from wild fish, the hatchery environment will select for traits that favor survival in the hatchery and select against traits that favor survival in nature. Consequently, hatchery fish will always diverge from their wild ancestors. Genetic protocols are needed to control and slow this divergence, but it cannot be stopped. One must also ask, do we want the hatchery fish to be like wild fish. Maybe the only reason we have wild runs left is that hatchery fish have been like drones and have not been effective breeders. Taking this route and trying to make them more effective at breeding in the wild may be the single most important item causing the extinction of our remaining wild runs. Yes, this whole issue is a critical uncertainty and should be tested. Uncertainties must be monitored. A monitoring plan must be developed and all uncertainties must be identified. I do not see this in the WSP Low similarity and high similarity of hatchery stocks to wild stocks must be defined by specific criteria to guide the implementation of the WSP. It is needed so decisions can be made. They are game rules so one can successfully play the game. Ignores the fact that hatchery fish diverge from their wild source stocks through domestication selection. A hatchery stock that has high similarity to the parent wild stock in generation one may have low similarity in generation three. The test for hatchery fish is to evaluate the survival of the F3 generation in producing adult progeny. So far the record is rather poor. Yet the hatchery fish spawn, interbreed with wild fish and compete for food and space. They are, as Jim Karr said, biological pollution. We purposely release drones to control insect pests now we are doing it to salmon. OTHER ISSUES Issue: No discussion of WDFW institutional structure changes needed to implement the WSP. a. Need specific staff expertise (genetics, T&E specialist, biometrician, habitat, program director, staff to write WSP annual report on status of native, wild populations. b. b. Need program structure and staff to implement the WSP internally as well as externally. The program director should report directly to the agency director. c. c. This staff will in effect, be the ones responsible for ensuring the WSP is implemented by the agency and will be the home for conservation management in the agency. The dual mission of WDFW to provide harvest and conserve the resource then will have the organizational structure to do the job. The WSP must add a discussion of the institutional structure it will use to implement the policy. Issue: No discussion regarding how other agencies will be organized to assist WDFW in implementation standards of the WSP especially for habitat. These would include state and federal land and water management agencies. The governor's office should be organized to get the habitat agencies to respond to fish conservation issues. Issue: Need to address monitoring and evaluation in a separate appendix and incorporate in a discussion of monitoring and evaluation among the alternatives. The M&E program must address adaptive management and how the WSP proposes to use it to inform policy and management of salmonids. Issue: Need time series data base on population/habitat by ecological region in state to measure the effect of WSP as a management policy. Need to develop reference populations by ESU, GCMUs and/or Ecological Regions in state. Time series data base grows in value the longer it is in place. This is a long - term commitment to data collection. Issue: Need reference wild, locally adapted native populations and habitat throughout the state. Issue: Columbia River reservoir drawdown or dam breaching is not discussed in the WSP, but for Washington native salmonids in the Snake basin, this may be the only way they will be recovered. GENERAL LIST OF STANDARDS OF THE WSP: 1. Hatchery supplementation will be based on RASP 2. Harvest based on MSY not MSE 3. Management Units are "Stocks in major basin that empties into saltwater" 4. Assumption that Management Units as defined work for substock protection. 5. Spawner counts - should be all wild stocks including wild strays. 6. Spawner escapement = 500 (Is this the effective breeding population?) 7. Habitat management and protection to address all life history stages. 8. Habitat standards for LWD, O2, pH,etc.(state standards). 9. Management priority = TES stocks (the ones in trouble). 10. State template to guide local restoration efforts promised. ARE ALTERNATIVES COMPARABLE The main difference among all alternatives is in fish management since the habitat criteria has the same potential among all alternatives except alternative no. 1 (p.21) Issue: It is difficult to compare alternatives because the categories are not consistent among them. For example, Alternative 2 has 14 categories from spawner abundance to gene banking. However, Alternative 3 has only 5 of these 14 categories listed, stating standards and criteria. Recommend developing a spread sheet by alternative, listing categories and standards and criteria for each category. The spread sheet should include at least the following categories: Spawner abundance, What counts as a spawner, M&E, Gene conservation, Base spawner number, Ecological interactions, Gene flow, Fishing selectivity, Hatchery, Habitat fragmentation, Harvest, Supplementation, Gene banking. I did a spread sheet and found Alternative 2 did a fairly complete job of listing categories and standards per each, but alternatives 3,4,5 did not. Issue: In the final WSP the agency should identify the priority each measure will have for implementation and the funding required to do the work. Also, the agency should put wild salmonids as a cost category in its budget so the public can identify the amount of money that is being invested for protection of native wild salmonids in the state. Bill M. Bakke Native Fish Society May 22, 1997