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Testimony of Edward C. Bowles 9/14/00 - Delivered before the Committee on Environment and Public
Recovery requires a three-fold improvement in overall life cycle survival
Mr. Chairman and members of the Subcommittee, thank you for the opportunity to testify on the National MarineFisheries Service (NMFS) Draft Biological Opinion (2000 BiOp) for operation of the Federal Columbia RiverPower System (FCRPS) and the Federal Caucus Draft Basinwide Salmon Recovery Strategy (RecoveryStrategy). These documents will shape the region's focus for recovery efforts and thus profoundly effect the veryexistence and future of wild salmon and steelhead in the Snake River Basin.
Your leadership on this issue, Mr. Chairman, is both refreshing and vital. I had the pleasure of testifying a coupletimes to your subcommittee in the House of Representatives, and found your approach thoughtful, open-mindedand solution oriented. Your knowledge and first hand experience with the fish are unprecedented in Congressand reflect highly on your commitment to solve this decades-old tragedy. I think you would agree that there issomething about personally watching wild salmon spawn or wrestling with a hatchery salmon on the end of yourfishing line that helps make salmon recovery real and tangible.
The intent of this testimony is not to advocate specific management actions, but to help ensure the bestpossible science provides the analytical basis of the draft 2000 BiOp and Recovery Strategy. The selection ofrecovery actions is a policy decision made in the context of biological and non-biological considerations. Therole of the Idaho Department of Fish and Game (IDFG) is to help strengthen the scientific foundation from whichvarious management alternatives are considered, and assess these alternatives from a biological and scientificbasis. A strong scientific foundation for conservation decisions is a goal common to both the State of Idaho andthe Federal Caucus.
My professional judgement is that the draft 2000 BiOp and Recovery Strategy are doomed for failure on severalfronts. For ecological, political and economic reasons, it is imperative that the 2000 BiOp and RecoveryStrategy are set up for success, not failure. If the desire is to address all significant sources of "discretionary"mortality (short of using breach and additional Idaho water) to see if fish recovery can be secured withoutbreach, then the 2000 BiOp and Recovery Strategy should focus on:
NMFS' estimates of expected improvement provided by Reasonable and Prudent Actions (RPA) identified inthe draft 2000 BiOp accentuate my concern that the 2000 BiOp is set up for failure. The draft 2000 BiOpconcludes current FCRPS operations constitute jeopardy, and then identifies a RPA to avoid jeopardy.Surprisingly, the RPA measures associated with juvenile spring/summer chinook migration through thehydrosystem are only expected to improve survival by 1-2% over current operations (2000 BiOp, pages 6-76and 9-161, Tables 6.3-2 and 9.7-6). NMFS then speculates on hoped for benefits in adult migration, habitat andhatcheries to make up the difference to get to no jeopardy. It is disappointing and perplexing that NMFSconcentrates so little effort to improve survival associated with juvenile migration, when all other salmonmanagers in the Basin, and regional societies of professional fisheries scientists, are in agreement that this isthe primary factor limiting the survival and recovery of listed Snake River salmon and steelhead. It is alsodisappointing and perplexing that NMFS stakes such high hopes on improvements in adult migration, habitatand hatcheries, when available data indicates these benefits are unlikely to be biologically feasible. NMFS hasnot assessed feasibility, and all other salmon managers in the Basin are in agreement that these areas ofdiscretionary mortality are less significant than hydrosystem impacts on juveniles, and cannot add up torecovery.
If the decision to breach lower Snake River dams is deferred, I believe the Four Governors' Plan does a betterjob of keeping the primary sources of discretionary mortality in focus and embracing a conceptual approach toattempt to address these problems prior to breaching dams. Although there is no scientific basis for concludingSnake River salmon and steelhead are likely to recover with non-breach alternatives, interim actions focused onthe primary sources of discretionary mortality can certainly benefit the fish. Available scientific analyses indicatethese actions will help moderate extinction risk, will increase the frequency of rebuilding opportunities, and willincrease the frequency of harvestable hatchery surpluses compared to current operations, even though they areunlikely to provide the magnitude of survival benefits required to secure recovery.
In general, the structure of the draft 2000 BiOp and Recovery Strategy is adequate to frame the scientificinformation. The problem is that the underlying scientific information used in the documents has severalfundamental errors and omissions. These errors and omissions alter the conclusions, accentuate uncertaintybeyond the limits of scientific objectivity, and result in a misleading depiction of the fundamental choices thatface the region if salmon recovery is to succeed. The technical information currently available is adequate toproduce a biologically sound and scientifically defensible 2000 BiOp and Recovery Strategy. If the errors andomissions are corrected, we believe the documents can accurately represent the biological component ofrecovery options, which policy makers can consider along with important social and economic information indetermining recovery actions.
The remainder of my comments will identify the procedural and technical aspects of the draft 2000 BiOp andRecovery Strategy that heighten the risk of failure and identify changes necessary to promote success.
The draft 2000 BiOp and Recovery Strategy are federal products developed without true collaboration withstate and tribal fisheries scientists. Many of the state and tribal technical concerns could have been addressedduring development of these documents if NMFS would have allowed collaboration on its Cumulative RiskInitiative (CRI). The CRI analyses provide much of the scientific basis for the draft 2000 BiOp and RecoveryStrategy. The CRI analyses are also the primary source of the scientific errors and omissions in these federaldocuments, which result in misleading conclusions. Although the ramifications of these errors and omissionsare significant, they can be easily corrected for the final federal documents if scientific collaboration is allowed.
Collaboration means working jointly on scientific issues to develop methodologies and analyses that embracethe full expertise of appropriate state, tribal, federal and independent scientists. True collaboration promotesdefensible science through peer review, promotes broader acceptance and ownership of methodologies andresults through active participation, and reduces the risk of institutional bias. Collaboration does not underminethe statutory authorities and responsibilities each participant brings to the process. Science developedcollaboratively can provide a common foundation from which differing authorities and responsibilities canproceed accordingly.
Recovery decisions facing the region are important and controversial. Sound science must lay the foundationfor these decisions. Broad ownership of this science through collaboration is a vital step in developing recoveryactions that will withstand judicial challenge and garner regional support. NMFS embraced true collaboration inPATH, and has set up collaborative teams to develop recovery standards and plans for other listed salmon andsteelhead ESUs in the Basin. It is disappointing and perplexing that NMFS chose to take a unilateral,non-collaborative approach in the Snake River Basin after PATH was discontinued. Inadequate time forcollaboration is not a worthy excuse. PATH was a five-year collaborative effort. Time was short only after PATHwas abandoned.
Regrettably, NMFS' track record for embracing collaboration with their state and tribal peers is dismal forSnake River science issues once PATH was discontinued. The current process is coordination, notcollaboration. NMFS develops their methodologies and conducts their analyses unilaterally, then posts theirinformation on a web page for comment, or holds a "workshop" to discuss their information. The states andtribes have spent considerable time and resources trying to insert their concerns and analyses into thisprocess, but have little to show for their efforts. When corrections have been made, it often seems adjustmentsare made in other standards or analyses to compensate so general conclusions remain the same. Forexample, NMFS made some necessary corrections to the rate of population growth that accelerated projecteddeclines, but then NMFS arbitrarily lowered the survival standard, resulting in little change to extinction risk andthe amount of improvement needed to avoid jeopardy. We have been encouraged by attempts of some NMFSscientists to establish more collaboration with our scientists, but opportunities remain sparse. Withoutcollaboration on the draft 2000 BiOp or Recovery Strategy, the states and tribes are forced to try to correcterrors and omissions through the formal and brief comment period. To add to this difficulty, new analyses byNMFS relating to the 2000 BiOp have come out in the middle of this comment period (Toole 2000).
Scientific collaboration with state and tribal fisheries scientists was a key element of Judge Marsh's decision inIDFG v. NMFS , and a key provision in the 1995 and 1998 biological opinions for FCRPS operations (NMFS1995; NMFS 1998). To NMFS' credit, PATH was created to meet these mandates and represents a trulycollaborative scientific approach to sorting out the science associated with the long-term recovery decision forSnake River salmon and steelhead specified in the 1995 and 1998 FCRPS BiOps. NMFS and other FederalCaucus members were key participants in PATH.
As PATH conclusions began to clarify the science, NMFS suddenly and unilaterally began an alternativescientific process called CRI. Although the CRI analyses are non-collaborative, preliminary, and not fullyanalyzed or peer reviewed, CRI results became equal, if not greater, partners with PATH in defining the sciencein the Anadromous Fish Appendix of the Corps' Draft Environmental Impact Statement and the Federal Caucus'All-H Paper. This pattern continues in the latest draft 2000 BiOp and Recovery Strategy, which marginalizePATH results even further.
Although the PATH and CRI analyses reach similar conclusions on several key points, there are also severalkey differences. These differences accentuate the need for continuing a truly collaborative process to helpidentify and frame the differences and help promote a convergence of the science where possible.Accentuating the differences, without an honest attempt to resolve the differences through scientificcollaboration, is a disservice to the decision process established in the 1995 and 1998 FCRPS BiOps.
I do not want to leave the impression that CRI is not constructive toward resolving conservation and recoveryissues. The intent and general framework of CRI is to estimate extinction risks and identify and allocateopportunities for conservation. This is necessary for recovery discussions and decisions. Some of the CRIfocus is in areas PATH did not focus, and thus brings new information for consideration. Other areas overlap,and provide an opportunity to corroborate results from the different scientific approaches. But for this effort tobe constructive, the CRI analyses must be based on the best available information and incorporate state, tribaland independent expertise in helping resolve scientific disputes and uncertainties. We are confident that ifNMFS and the Federal Caucus embrace this approach, PATH and CRI can be complementary rather thanadversarial. If NMFS maintains an autonomous approach to CRI, the opportunity to clarify the science forrecovery decisions will be lost and regional "ownership" diminished.
It is important that recovery decisions are not delayed unnecessarily while the science is sorted out once again.We believe most of our concerns regarding possible errors and omissions in the CRI analyses can beaddressed quite easily and quickly through collaboration. We are committed to working collectively with NMFSscientists to move this process forward.
In IDFG v. NMFS, Judge Marsh was critical of "arbitrary and capricious" decision-making by NMFS in the 1993FCRPS BiOp. Given this litigation history, it is perplexing why NMFS tended to select the most optimistic (i.e.,least conservative) assumptions regarding extinction risk, lack of hydrosystem impacts, and the benefits ofimproving habitat and hatcheries in the draft 2000 BiOp and Recovery Strategy. At best, this approach appearsinconsistent with the ESA requirement to be risk-averse in the face of scientific uncertainty when protectinglisted species. At worst, this approach is poor stewardship when non-conservative assumptions areaccentuated and conservative assumptions ignored, in spite of scientific evidence to the contrary.
For example, NMFS usually selected non-conservative assumptions for factors affecting the amount of survivalimprovements needed to avoid jeopardy. NMFS selected the optimistic assumption that small, threatenedpopulations face no threat of an extinction vortex, in spite of theoretical and empirical evidence to the contrary(Dennis 1991; BRWG 1994; Botsford 1997). NMFS also selected optimistic assumptions for their extinctionand survival standard, recovery standard, FCRPS hydrosystem performance standard, definition of high risk,hatchery effectiveness, years for time series, and effect of fish density on population growth rates (Table 1).
NMFS also typically selected optimistic assumptions for factors affecting the amount of survival improvementsattributed to existing and proposed measures in the 2000 BiOp. For example, NMFS selected the mostoptimistic assumptions to attribute hydrosystem improvements for any survival improvements of juvenilemigrants since the 1995 BiOp, rather than balance this assumption with the possibility that model differences orhigh natural flow and spill from good water years could also account for these increases. In contrast, NMFSselected pessimistic assumptions regarding the effectiveness of breach on fish survival. NMFS assumed thereis no delayed mortality associated with juveniles migrating inriver through the FCRPS, in spite of a wealth ofinformation to the contrary (Marmorek et al. 1996; IDFG 1998, 1999, 2000a, 2000b; Marmorek and Peters1998; SRP 1998; Bouwes et al. 1999; Congleton et al. 1999; Schaller et al. 1999; NMFS 2000a) and no NMFSdata or analyses confirming their assumption.
The effect of NMFS accentuating non-conservative assumptions, regardless of scientific information questioning these assumptions, results in several fundamental errors in the Draft 2000 BiOp and Recovery Strategy:
The 2000 BiOp and Recovery Strategy should present a more objective characterization of PATH results anduncertainty as a decision-analysis tool, across the full range of scientific debate and uncertainty, without biastoward assumptions promoted by NMFS scientists. There is much evidence in PATH, the draft AnadromousFish Appendix and the ESA record as a whole that the hydrosystem is a source of both direct and delayedmortality of transported and in-river juvenile migrants. NMFS presents an unbalanced view of sources of extramortality, emphasizing uncertainty for one of the listed populations (spring/summer chinook). All Snake Riveranadromous salmonids are threatened or endangered or extinct (coho), and have hydropower impacts incommon. Alternative, non-hydro explanations of extra mortality posited by NMFS in the federal documentsshould explain recruitment patterns for the entire suite of Snake River anadromous salmonids, but they do not.
IDFG disagrees with NMFS decision to disregard the PATH Weight of Evidence process and the ScientificReview Panel weighted analysis. Full disclosure of the weight of scientific evidence for key alternativehypotheses, across species lines, should be presented in the final 2000 BiOp and Recovery Strategy.
Objective Risk Assessment
Risk assessment is critical to ESA decision-making processes. There will always be ecological and scientificuncertainty. The key to objective risk assessment is determining how to best meet the biological needs of thefish in the face of these uncertainties. There should be a clear recognition that lack of a decision, or delay, isactually a conscious decision that the uncertainties are too great to act on, and that the listed populations cansurvive the delay and still retain enough inherent productivity and diversity to remain poised for recovery. Tomoderate the risk, this approach should be coupled with aggressive actions in all possible areas that can beagreed on, recognizing the greatest uncertainty may actually be whether there will be any fish left to save onceall the questions are answered.
In my professional opinion, the amount of time available for decision makers to continue trying to sort outrecovery options is largely dependent on the weather and the ocean. Available data indicate Snake Riverspring/summer chinook salmon can maintain current population levels, or even rebuild somewhat, when thereare above average runoff conditions (e.g., high natural flow and uncontrolled spill) coupled with average orbetter ocean conditions (e.g., cool temperature and strong coastal upwelling) (Figures 1, 2 and 3). The samedata indicate Snake River salmon can decline precipitously when runoff or ocean conditions are poor. Theoverall trend for salmon across the range of environmental conditions is downward. These environmentalfactors appear to influence adult returns and survival rates far more than any suite of management actions takenin recent years.
Improved adult returns this year and projected for next year are largely the result of good runoff and oceanconditions. As long as these environmental conditions remain above average, Snake River salmon populationswill likely persist or even rebuild slightly; allowing society some additional time to debate and experiment withmanagement options. Conversely, if these environmental conditions do not remain above average (orpotentially good runoff conditions are dampened by FCRPS operations), then Snake River salmon populationswill likely decline; making any additional delay risky for conservation and recovery of these fish. Dr. Petrosky,the lead fisheries scientist from IDFG on this issue, characterized NMFS' approach to salmon recovery thus: "Ifwe can always average above average, things should average out okay." Regrettably, that is not the way natureworks, therefore this is not a risk-averse approach to species conservation.
If additional aggressive actions to address the mainstem FCRPS are delayed, I recommend linking thisdecision to prevailing environmental conditions, particularly snowpack, runoff, mainstem water temperature andocean temperature and upwelling. If these conditions deteriorate from what was observed for juvenilesmigrating during 1997-1999, then the FCRPS configuration decision should be revisited immediately andadditional emergency actions taken in other sectors until FCRPS reconfiguration is authorized andimplemented. These emergency actions should focus on actions with immediate and direct benefits to the fish,such as removing avian piscivores from the estuary, reducing pinniped predation, altering flood controloperations to help maintain high springtime flows, increased mainstem spill, and additional harvest constraints.
It will be both regrettable and scientifically unprofessional if recent and future changes in fish survival andabundance are credited to management actions without first factoring out the influence of natural runoff andocean conditions. For example, if new management actions are implemented which are actually beneficial, butenvironmental conditions deteriorate relative to the baseline, then it may appear these factors are not beneficialwhen in fact they may have eased the impact of these deteriorated environmental conditions. Conversely, ifmanagement actions are credited for an upswing in survival and abundance, which are actually the result ofimproved environmental conditions, then a false sense of security can result in further delay and elevated riskwhen environmental conditions deteriorate.
The history of debate on Snake River salmon recovery actually demonstrates this risk. Snake River salmon andsteelhead declined precipitously in the late 1970s and ESA listing was avoided in 1980 when the NorthwestPower Planning Act ushered in a new period of management planning and action. Good outmigrationconditions in 1982-84 from high natural flow and spill at mainstem dams apparently resulted in an upturn insalmon survival and adult returns in the mid 1980s (Figure 1). At the time, this upturn was often equated withmanagement actions (e.g, Raymond 1988). Environmental conditions shifted in the late 1980s and early 1990s,demonstrating that Snake River salmon and steelhead had not actually turned the corner toward recovery fromthe management actions. We are at risk of repeating this error again. Environmental conditions were onceagain above average during the late 1990s, resulting in an upturn in fish survival and abundance at the turn ofthe century. The draft 2000 BiOp credits much of this upturn to actions implemented with the 1995 and 1998BiOps (Draft 2000 BiOp, pages 6-75 and 6-76, Tables 6.3-1 and 6.3-2). Fish survival during the next five, eightand ten years will be used to determine if the 2000 BiOp is successful, or if the breach alternative needs to beimplemented to meet minimum needs of the fish. It is vital that the relative influence of environmental factors,such as above or below average natural runoff and ocean conditions, are factored out in the decision process. Ifdecisions whether or not to breach are simply made based on annual population growth rates over a setnumber of years, then decision makers are basically playing breach roulette with the weather.
Another important aspect of risk assessment is determining the biological consequences of being wrong. Thisassessment requires determining which actions are likely to have the most positive biological response even ifdecisions are made based on false assumptions. This assessment helps determine the most risk-aversealternatives.
IDFG believes objective risk assessment in the final 2000 BiOp and Recovery Strategy will demonstrate:
Scientific Approach for Assessing Jeopardy and Conservation Actions
There are several important scientific steps that must be taken to determine biologically defensible recoverystrategies:
As mentioned earlier, the general structure of the draft 2000 BiOp and Recovery Strategy is adequate to framethe necessary scientific information. The problem is that the scientific information used in these steps hasseveral fundamental errors and omissions, and some steps, such as determination of discretionary mortalityand ability of management actions to address this mortality (i.e., biological feasibility), were not included in theNMFS analysis.
IDFG is currently preparing formal comments on the draft 2000 BiOp and Recovery Strategy, which willhopefully be submitted as part of the official State of Idaho comments. These comments are due September25, 2000. IDFG has commented extensively in the past on the federal scientific analyses used in the draft 2000BiOp and Recovery Strategy (IDFG 1999, 2000a, 2000b). We only provide a brief synopsis of these concernsin this document and request the Subcommittee refer to our prior documents, as well as the comments we willbe completing this month, for more detailed discussion.
Step 1: Determine extinction risk and survival and recovery standards for jeopardy.
NMFS used optimistic assumptions to evaluate extinction risk and lowered the standards used for jeopardyrelative to the 1995 and 1998 FCRPS BiOps. The effect of these errors is underestimation of actual extinctionrisk and reduction in the amount of survival improvements necessary to avoid jeopardy. To correct these errors,NMFS must include a more objective range of assumptions regarding extinction threshold, depensation,definition of high risk, hatchery effectiveness and density dependence.
NMFS should also adhere to the survival and recovery standards developed collaboratively as a result of IDFGv. NMFS (BRWG 1994; Marmorek et al. 1998) and the jeopardy standards established in the 1995 and 1998FCRPS BiOps (NMFS 1995, 1998). NMFS apparently has shifted from a focus on recovery, to simply trying toavoid absolute extinction. The 2000 BiOp should develop a clear "crosswalk" linking the earlier jeopardystandard developed collaboratively to the standard currently proposed by NMFS. IDFG believed the standarddeveloped for the 1995 BiOp was not conservative enough to protect Idaho's wild salmon populations, andobjects to any attempts to "lower the bar" even farther.
For example, NMFS defined a "moderate to high probability of recovery" as only a 50:50 chance that thestandard would be achieved within 48 years (NMFS 1995; 2000b). The IDFG v. NMFS collaborative processrecommended 24 and 48 year recovery standards (BRWG 1994), but NMFS selected a standard for only the48-year period (NMFS 1995). NMFS now states: "It may be unrealistic to expect populations to return torecovery abundance levels within this time period [48 years]," and therefore introduced a 100 year standard(draft 2000 BiOp, page 1-12).
Step 2: Determine the amount of survival improvements needed to avoid extinction and meet survival and recovery standards.
The problems identified in Step 1 carry over into Step 2. NMFS' use of optimistic assumptions regardingextinction risk, lowering of the jeopardy standard, and assumption that populations can grow exponentially resultin the perception of less difference between the current productivity of the fish and the productivity necessary toavoid extinction and provide recovery. This narrowing of the gap by NMFS is not scientifically supportable.
Thus the draft 2000 BiOp concludes that approximately a 30% improvement in lifecycle survival of Snake Riverspring/summer chinook is necessary to meet the 24-year jeopardy standard. Because the CRI approachincludes such optimistic assumptions (Table 1), it is not surprising that this estimate is far lower than estimatesfor recovery that include less optimistic assumptions (IDFG 2000a, 2000b; Peters and Marmorek 2000). Theseassessments indicate a 170% or more improvement in lifecycle survival is needed for recovery of Snake Riverspring/summer chinook.
Step 3: Determine fish mortality and allocate among life stages.
The CRI analysis used in the draft 2000 BiOp and Recovery Strategy does address one concern expressed byother Salmon Managers regarding allocation of overall lifecycle mortality of Snake River spring/summerchinook salmon (IDFG 2000a, 2000b; STUFA 2000). CRI now uses empirically derived estimates ofsmolt-to-adult survival to solve for egg-to-smolt survival, similar to the approach recommended by the SalmonManagers. Mortality allocation issues related to delayed hydrosystem mortality (smolt-to-adult) were notresolved in the CRI analysis.
Step 4: Determine the amount of discretionary mortality above the natural baseline.
NMFS failed to determine the amount of discretionary mortality for each life stage above the natural baseline.This step is crucial to developing recovery strategies because it allows decision makers to focus actions on theprimary limiting factors that can be managed. The majority of mortality in the lifecycle of salmon and steelheadis natural mortality that has little chance of being improved by man. Effective recovery strategies will focus onthe discretionary mortality beyond this natural baseline, which is usually the result of anthropogenic factors.
Available data indicate relatively little discretionary mortality of Snake River salmon and steelhead during theegg-to-smolt stage, and relatively large discretionary mortality during the smolt-to-adult stage. Potential survivalimprovements from addressing the discretionary mortality in the egg-to-smolt stage (i.e., spawning and rearinghabitat) range from 0-34% for seven indicator populations (median 6%) (Marmorek et al. 1998; IDFG 2000a).Estimated potential survival improvements from addressing discretionary mortality during the smolt-to-adultstage is over 200%, based on survival trends of comparable upriver and downriver stocks (Figures 3 and 4)(Marmorek and Peters 1998; IDFG 2000a, 2000b; STUFA 2000).
The draft 2000 BiOp and Recovery Strategy imply much of this mortality in the smolt-to-adult life stage is notdiscretionary because smolt transportation has largely fixed the dams and NMFS assumes no delayed mortalityof fish migrating inriver. NMFS assumes the extra mortality must be associated with non-discretionary oceanconditions, discretionary estuary conditions (e.g., estuary habitat and predators), and delayed effects ofdiscretionary conditions during the egg-to-smolt stage (e.g., hatcheries and spawning and rearing habitat).Although the potential sources of discretionary mortality in the estuary (e.g., avian and pinniped predators)should be addressed, NMFS' assessment is not based on the weight of scientific evidence.
NMFS concurs that the level of delayed or "extra" mortality associated with the fishes' hydrosystem experienceis pivotal to survival and recovery decisions for the Snake River ESUs (NMFS 1995, 1998, 1999, 2000b).Given the importance of this issue, NMFS should have devoted much of the draft 2000 BiOp and RecoveryStrategy to an objective and thorough assessment of the weight of scientific evidence supporting or notsupporting this source of mortality. Regrettably, NMFS failed to take this approach and instead accentuateduncertainty and recommended more study.
The final 2000 BiOp and Recovery Strategy should include full disclosure of compelling scientific evidence forsubstantial delayed effects of the hydrosystem experience. This evidence includes:
The above points are discussed in more detail in prior IDFG comments (IDFG 2000a, 2000b). The final 2000 BiOp and Recovery Strategy should also explicitly incorporate previous assessments of the weight of scientific evidence associated with various models and assumptions relating to FCRPS and non-FCRPS sources of mortality (IDFG 1998, 1999, 2000; Marmorek and Peters 1998; SRP 1998). NMFS' disregard for the PATH weight of evidence analyses (Marmorek and Peters 1998; SRP 1998) is particularly discouraging.
The draft 2000 BiOp and Recovery Strategy also fail to provide a thorough and objective assessment of theweight of scientific evidence indicating other factors, not related to the hydrosystem, are primarily responsiblefor masking benefits of smolt transportation and other FCRPS measures, particularly within the context of theevidence described above. This line of reasoning and weight of evidence must be able to rationally address thefull biological picture observed in the region.
The draft 2000 BiOp and Recovery Strategy should clearly describe the assumptions that must be true in orderto conclude that current operations (e.g., smolt transportation, flow augmentation, spill, etc.) have successfullycompensated for the adverse effects of the FCRPS. NMFS should then describe the weight of scientificevidence and theory for and against these assumptions.
For smolt transportation to provide survival benefits to offset the FCRPS related direct and delayed mortality,the following assumptions must be true:
The weight of scientific evidence supporting this narrow set of assumptions is low (IDFG 1998, 1999, 2000;Marmorek and Peters 1998; SRP 1998). If NMFS chooses to accentuate this narrow set of assumptions, itmust explain in detail why other assumptions were treated with less weight. NMFS must also convey theconsequences of falsely accepting this narrow set of assumptions in alternative management options.
It is important to reiterate that the non-hydrosystem "masking" hypothesis requires two things to be true:
The draft 2000 BiOp and Recovery Strategy should also clearly describe the management implications if 'D' isnot high or "extra" mortality is hydrosystem related, and the management implications if 'D' and "extra" mortalityare moderate. These assessments are critical to an objective risk analysis.
Step 5: Assess management opportunities to address this discretionary mortality.
If the 2000 BiOp and Recovery Strategy correct the errors and omissions outlined in steps 1 through 4, thedocuments will focus management actions on addressing the direct and delayed effects of the mainstemFCRPS, complemented with appropriate actions addressing freshwater and estuary habitat, predators, harvestand hatcheries.
It is apparent in the draft 2000 BiOp and Recovery Strategy that NMFS is trying to shift the focus off the hydrosystem as a major source of mortality (i.e., it has been fixed) and putting the focus on tributary and estuary habitat. This approach is not scientifically defensible and is unlikely to secure the survival and recovery of Snake River salmon and steelhead.
In an attempt to rationalize this approach, the 2000 BiOp and Recovery Strategy overestimates, or in some measures does not estimate, survival improvements expected from the Reasonable and Prudent Alternative (RPA).
Because NMFS inappropriately shifts the conservation burden away from the FCRPS, the draft 2000 BiOpRPA for hydrosystem actions does not significantly change from current operations. The RPA basically has thesame spill, flow and transportation actions identified in the 1995 and 1998 FCRPS BiOps. As a representativeof the Technical Management Team for the State of Idaho, I can attest that there were numerous times duringthe past five years that even these provisions were not met.
Step 6: Select a suite of management actions that are likely to provide the necessary survival improvements.
Selection of management actions to address discretionary mortality is a policy decision based on biologicaland non-biological factors. However, these actions must be based on sound science and address enough ofthe primary sources of mortality to meet survival and recovery standards. The draft 2000 BiOp and RecoveryStrategy fail to identify specific management actions or thoroughly assess the expected contribution of theseactions toward necessary survival improvements.
The draft 2000 BiOp concludes that a 30% increase in survival estimated from FCRPS improvements of theRPA result in no-jeopardy to Snake River spring/summer chinook, even though not all stocks meet the standardwithout additional survival improvements. It is not surprising that the CRI analysis indicates some stocks meetthe standards because of the numerous optimistic assumptions incorporated into the analysis (Table 1). Incontrast, PATH estimated recovery would require approximately a 170% increase in survival rates for SnakeRiver spring/summer chinook (Peters and Marmorek 2000).
Our analyses indicate it is highly unlikely for non-breach alternatives alone to provide the necessary survivalimprovements required for survival and recovery of Snake River salmon and steelhead. Regrettably, thenumbers just do not add up. Given the current unacceptablity of the natural river option, it is important toimplement an aggressive suite of alternative management actions across the lifecycle of the fish, but focusedon the mainstem FCRPS. This is important to not only test whether there are viable alternatives to breach, butalso to protect and enhance salmon and steelhead as much as possible during the interim. Without thesefocused and aggressive actions, the 2000 BiOp and Recovery Strategy are more likely to fail because theconservation burden has been shifted to Hs that are incapable of providing the necessary survivalimprovements.
Through their annual migration plans and involvement in the Regional Forum, NPPC program, and FourGovernors Plan, IDFG and the State of Idaho have identified several actions that would more aggressivelyaddress significant sources of direct and delayed discretionary mortality than the existing RPA.
Step 7: Develop an aggressive monitoring and evaluation plan to assess effectiveness within the context ofenvironmental variability.
The draft 2000 BiOp and Recovery Strategy do not identify an adequate monitoring and evaluation program toassess the effectiveness of management actions within five, eight and ten years. It is not scientifically feasibleto implement new actions, particularly focused on habitat improvement, and expect to evaluate the effect ofthese actions on population growth rates within one decade. Thus, many of the performance standards andmeasures in the 2000 BiOp and Recovery Strategy are relatively meaningless in the context of the breachdecision.
Instead, the primary factors that will likely determine whether or not population growth rates are adequate duringthe next few years are the weather and ocean conditions. If snowpack and ocean conditions are favorableduring the evaluation period, population growth rates may meet the standard. If these environmental conditionsdeteriorate, then it is unlikely population growth rates will meet the standard. Thus, it is very important thatperformance standards and measures capture the relative influence of these environmental variables.
IDFG is concerned that the draft 2000 BiOp and Recovery Strategy represents a fundamental shift away froman emphasis on recovery to an emphasis on simply avoiding extinction. Recovery standards and performancemeasures must all point toward the goal of sustainable and naturally diverse fish runs with inherentproductivities adequate to meet the biological needs of the fish and provide societal benefits. Performancemeasures are the means of tracking progress toward recovery standards, and should be nested within ahierarchy to ensure a clear delineation toward recovery. For example,
Botsford, L.W. 1997. Depensation, performance standards and probabilities of extinction for Columbia Riverspring/summer chinook salmon. Draft in D.R. Marmorek and C.N. Peters (eds. 1998. Plan for Analyzing andTesting Hypotheses (PATH): Retrospective and prospective analyses of spring/summer chinook reviewed inF?Y97. Compiled and edited by ESSA Technologies, Vancouver, B.C.
Bouwes, N., H. Schaller, P. Budy, C. Petrosky, R. Kiefer, P. Wilson, O. Langness, E. Weber, E. Tinus. 1999. Ananalysis of differential delayed mortality experienced by stream-type chinook salmon of the Snake River. Aresponse by state, tribal, and USFWS technical staff to the 'D' analyses and discussion in the Anadromous FishAppendix to the U.S. Army Corps of Engineer' Lower Snake River Juvenile Salmonid Migration FeasibilityStudy. October 4, 1999. Submitted to NMFS for ESA record.
BRWG (Biological Requirements Work Group). 1989. Analytical Methods for Determining Requirements ofListed Snake River Salmon Relative to Survival and Recovery. Progress Report of the Biological RequirementsWork Group, October 13, 1994. IDFG et al. v. NMFS et al.
Congleton, J.L., T. Welker and L. Haley. 1999. Evaluation of the effects of multiple dam passage onphysiological condition of migrating juvenile salmon. In Idaho Cooperative Fish and Wildlife Research UnitAnnual Report, October 1, 1998 September 30, 1999. University of Idaho, Moscow, Idaho.
Dennis, B. 1989. Allee effects: population growth, critical density, and the chance of extinction. NaturalResource Modeling 3:481-538.
IDFG 1998. Idaho's anadromous fish stocks: their status and recovery options. Report to the Director, May 1,1998. Idaho Department of Fish and Game, Boise, Idaho.
IDFG 1999. Comments on the National Marine Fisheries Service's "An Assessment of Lower Snake RiverHydrosystem Alternatives on Survival and Recovery of Snake River Salmonids" (Draft Anadromous FishAppendix). August 30, 1999. Idaho Department of Fish and Game, Boise, Idaho.
IDFG 2000a. Technical Comments on the Scientific Analyses Used for the Federal Caucus Draft All-H Paper.March 17, 2000. Idaho Department of Fish and Game, Boise, Idaho.
IDFG 2000b. Technical Comments on NMFS' Draft Anadromous Fish Appendix. April 29, 2000. IdahoDepartment of Fish and Game, Boise, Idaho.
Marmorek, D.R. and Peters, C. (eds.). 1998. Plan for Analyzing and Testing Hypotheses (PATH): Weight ofEvidence Report. ESSA Technologies, Ltd. 1765 West 8th Avenue, Suite 300. Vancouver BC, V6J 5C6. 116pp. + Appendices.
Marmorek, D.R., C.N. Peters and I. Parnell. 1998. Plan for Analyzing and Testing Hypotheses (PATH): FinalReport for Fiscal Year 1998. ESSA Technologies, Ltd. 1765 West 8th Avenue, Suite 300. Vancouver BC, V6J5C6. 263 pp.
NMFS 1995. Reinitiation of consultation on 1994-1998 operation of the federal Columbia River power systemand juvenile transportation program in 1995 and future years. Biological Opinion. National Marine FisheriesService. Seattle, Washington.
NMFS 1998. Operation of the federal Columbia River power system including smolt monitoring program andthe juvenile fish transportation program: a supplement to the biological opinion signed on March 2, 1995, for thesame projects. National Marine Fisheries Service, Seattle, Washington.
NMFS 1999. Draft lower Snake River juvenile salmon migration feasibility report/ environmental impactstatement, Appendix A, anadromous fish. Produced by National Marine Fisheries Service for US Army Corpsof Engineers, Walla Walla, Washington.
NMFS 2000a. NMFS White Papers: (1) salmonid travel time and survival related to flow in the Columbia Riverbasin; (2) summary of research related to transportation of juvenile anadromous salmonids around Snake andColumbia River dams; (3) passage of juvenile and adult salmonids past Columbia and Snake River dams; (4)predation on salmonids relative to the federal Columbia River power system. March 2000
NMFS 2000b. Draft Biological Opinion on Operation of the federal Columbia River power system including thejuvenile fish transportation program and the Bureau of Reclamation's 31 project, including the entire ColumbiaBasin Project. July 27, 2000 (draft). National Marine Fisheries Service, Seattle, Washington.
Peters, C.N., D.R. Marmorek.and I. Parnell. 1999. PATH Decision Analysis Report for Snake River FallChinook, September 1999. ESSA Technologies, Ltd. 1765 West 8th Avenue, Suite 300. Vancouver BC, V6J5C6. 332 pp.
Peters, C.N., and D.R. Marmorek. 2000. PATH Preliminary Evaluation of the Learning Opportunities andBiological Consequences of Monitoring and Experimental Management Actions. April 11, 2000. ESSATechnologies, Ltd. 1765 West 8th Avenue, Suite 300. Vancouver BC, V6J 5C6. 154 pp.
Raymond, H.A. 1988. Effects of hydroelectric development and fisheries enhancement on spring and summerchinook salmon and steelhead in the Columbia River Basin. N. Am. J. Fish. Manage. 8:1-24.
Schaller, H.A., C.E. Petrosky and O.P. Langness. 1999b. Contrasting patterns of productivity and survival ratesfor stream-type chinook salmon (Oncorynchus tshawytscha) populations of the Snake and Columbia rivers.Can. J. Fish. Aquat. Sci. 56:1031-1045.
SRP (Scientific Review Panel). 1998. Conclusions and Recommendations from the PATH Weight of EvidenceWorkshop. September 8-10, 1998. Vancouver, BC Canada. PATH Scientific Review Panel (S. Carpenter, J.Collie, S. Saila, C. Walters). Edited by C. Peters, D. Marmorek, R. Gregory, T. Eppel. ESSA Technologies, Ltd.1765 West 8th Avenue, Suite 300. Vancouver BC, V6J 5C6. 32 pp.
STUFA (State and Tribal and U.S. Fisheries Agencies). 2000. A technical review of the National MarineFisheries Service Leslie matrix model of Snake River spring and summer chinook populations. April 28, 2000.Submitted to NMFS for ESA Record.
Toole, C. 2000. Email memorandum to L. Krasnow and 9 others, September 5, 2000. Subject: [Fwd: NewAppB posted]
bluefish regrets that the following Tables and Figures are not included on this webpage.
Table 1 Assumptions considered by NMFS (grouped from optimistic to pessimistic) and used (shaded) in thedraft 2000 Biological Opinion for action agencies' responsibility to achieve survival and recovery of listedSnake River spring/summer chinook salmon. Recommended assumptions are presented in column on right.
Figure 1 Natural log of ratio of recruits to spawning grounds divided by parent spawners (ln(S:S)) for sevenindex stocks of Snake River spring/summer chinook used in PATH compared to average flow and spill atLower Granite Dam (kcfs at LGR) experienced during the springtime smolt migration, 1977-1996. Thepopulations increase when ln(S:S) > 0 and decrease when ln(S:S) < 0.
Figure 2 Average spawner to spawner ratio + 2 SE for seven index stocks of Snake River spring/summerchinook, smolt years 1977-1996, compared to average flow categories at Lower Granite Dam (LGR). 1995BiOp flow targets are 85-100 kcfs, which are associated with returns averaging less than replacement. Thepopulations increase when S:S > 1 and decrease when S:S < 1.
Figure 3 Survival rate index comparisons for Snake River spring/summer chinook and lower Columbia Riverspring chinook (stream-type), brood years 1959-1990. Survival index values of 0, -1, -2 and 3, representrelative survival of 100%, 37%, 14% and 5% that of the pre-1970 era. Source: Schaller et al. 1999.
Figure 4 Smolt-to-adult return rate (SAR) and smolts per spawner (log scale) for wild Snake Riverspring/summer chinook, 1964-1994 migration years. Estimates for 1984-1990 based on predicted wild smoltyield from PATH retrospective analyses. Source: STUFA 2000.
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