FY 2002 Columbia Plateau proposal 199506325

Section 1. Administrative

Proposal titleYakima/Klickitat Fisheries Project Monitoring And Evaluation
Proposal ID199506325
OrganizationYakama Nation (YN)
Proposal contact person or principal investigator
NameMelvin Sampson
Mailing addressP.O. Box 151 Toppenish, WA 98948
Phone / email5098656262 / [email protected]
Manager authorizing this projectMelvin Sampson
Review cycleColumbia Plateau
Province / SubbasinColumbia Plateau / Yakima
Short descriptionMonitors YKFP in terms of natural production, harvest , ecological and genetic impacts, guides adaptive management within the project and provides detailed information on supplementation to the region.
Target speciesspring chinook, fall chinook, coho, and steelhead
Project location
LatitudeLongitudeDescription
Aspects of this project take place throughout the entire Yakima Subbasin.
46.73 -120.67 Yakima subbasin
Reasonable and Prudent Alternatives (RPAs)

Sponsor-reported:

RPA

Relevant RPAs based on NMFS/BPA review:

Reviewing agencyAction #BiOp AgencyDescription
NMFS Action 184 NMFS The Action Agencies and NMFS shall work within regional prioritization and congressional appropriation processes to establish and provide the appropriate level of FCRPS funding for a hatchery research, monitoring, and evaluation program consisting of studies to determine whether hatchery reforms reduce the risk of extinction for Columbia River basin salmonids and whether conservation hatcheries contribute to recovery.

Section 2. Past accomplishments

YearAccomplishment
2000 First hatchery spring chinook return to Yakima Subbasin as three year old fish (jacks).
2000 Artificial spawning channel contructed at Cle Elum Supplementation and Research Facility to be used to evaluate potential differences in reproductive ecology of hatchery versus wild origin returns.
2000 Continued refinement of the Ecosystem, Diagnosis and Treatment Model (EDT) for spring chinook and steelhead in the Yakima Subbasin to be used to guide enhancement (production, supplementation and habitat) activities.
2000 Successfully marked all hatchery coho smolts released in Yakima Subbasin, in order to estimate total natural coho production at CJMF, and naturally produced adults in the fall of 2001.
1999 Release of first experimental optimal conventional and semi-naturally reared spring chinook.
1999 Completed Ecosytem Diagnosis and Treatment models for spring chinook, fall chinook, coho, and steelhead in the Yakima and Klickitat Subbasins.
1999 Developed a new method of estimating smolt survival indices from Prosser to McNary Dam, and refined existing smolt passage estimator at the Chandler Juvenile Monitoring Facility.
1999 Demonstrated a relative hatchery-wild spring chinook smolt survival of 80% (Roza to McNary Dam). Demonstrated relatively high survival (>50%) for experimental hatchery spring chinook releases (acclimation pond to McNary Dam).
1999 Continued development of a localized broodstock adapted to the Yakima basin. Demonstrated relatively high survival (~50%) for locally collected, experimental hatchery coho releases (acclimation pond to McNary Dam).
1999 Developed a repeatable predation index for piscivorous birds and fish in the Yakima basin.
1999 Completed genetic modeling demonstrating an increase in the effective population size for hatchery fish produced by factorial matings.
1999 Identified the spawning distribution of returning coho in the Yakima River.
1999 Demonstrated the ability to accelerate smoltification in experimental fall chinook to circumvent late spring temperature problems in the lower Yakima River.
1998 Monitoring prescriptions for 16 non-target taxa of concern have been developed and are being implemented to meet conservation objectives.
1998 A practical approach for assessing ecological risks associated with stocking anadromous salmonids was developed to facilitate decision making and direct monitoring efforts.
1998 Preliminary results of indirect predation experiments suggest that hatchery fish may increase survival of commingled smolts.
1998 Produced manuscript titled "A Production Function Based Model of Supplementation Dynamics" submitted to Trans. Am. Fish Soc.
1998 Produced multi-year power analysis of OCT/SNT survival comparison
1998 Modelled genetic effects of broodstock collection and usage rules
1998 Recorded detailed behavioral observations on wild spawning spring chinook (first ethological description of these behaviors on Columbia River spring chinook)
1998 Characterised detailed reproductive traits of Yakima wild spring chinook
1998 Developed DNA microsatellite profiles of Yakima spring chinook populations.
1998 Refined species-specific outmigration estimators for Chandler smolt trap.
1998 The adult broodstock collection and monitoring facility at Roza Dam was shown to have no adverse effects on passage timing or spawning distribution of wild Yakima spring chinook.
1998 Refined and augmented in-basin Yakima harvest monitoring methods.
1998 Strobe lights and infrasound were shown to be ineffective fish guidance methods at the juvenile trap at Roza Dam.
1998 Preliminary results indicate low competitive impacts of outplanted hatchery coho parr on trout.
1998 Developed 4 supplementation dynamics computer models
1997 Produced Yakima Fisheries Project Spring Chinook Supplementation Monitoring Plan (DOE/BP-64878-1)
1997 Studies indicated that smolts marked with VI-jet tags were not reliably identifiable as adults; therefore, CWTs implanted at multiple body locations were used in 1998 to mark YKFP hatchery spring chinook parr for smolt-to-adult monitoring.
1997 A preliminary ecosystem diagnosis and treatment modeling analysis of Yakima fall chinook indicated that the major factor limiting natural production was a combination of excessive temperature in the lower river and late emergence timing.
1997 Began development of locally-adapted coho and fall chinook broodstocks by collecting returning adults in the Yakima subbasin.
1997 Survival studies showed benefits from the following rearing treatments: raceway color pattern, overhead cover and mid-water structure. 1997 SNT treatment includes these elements plus mid-water feed delivery.
1997 Began broodstock collection of upper Yakima spring chinook at Roza Dam in 1997 and continued in 1998 using outlined genetic selection guidelines (Busack et al. 1997).
1996 Developed "Pedigree" computer model for investigation of monitoring power using DNA markers.
1994 Produced report "Experimental designs for testing differences in survival among salmonid populations" (DOE/BP-00029-3)

Section 3. Relationships to other projects

Project IDTitleDescription
8812001 Yakima/Klickitat Fisheries Project Mgmt. Core Management/Admin. Support Services for all YKFP Tasks
9506404 Policy/Tech. involvement/planning YKFP Supports the required co-manager process for the YKFP
199701725 YKFP Operation and Maintenance for the Yakima River Subbasin, submitted April 2001 This management proposal (198812025) supports O & M of YKFP fish production facilities in the Yakima Subbasin..
198811525 YKFP Design and Construction for the Yakima River Subbasin, submitted April 2001. This management proposal (198812025) supports YKFP design and construction projects/activities in the Yakima Subbasin.
199506404 YKFP Policy/Technical Involvement and Planning for WDFW 199506404 provides for WDFW participation in YKFP planning and management activities. WDFW is the project sponsor.
9705000 Little Naches Riparian and In-Channel Habitat Enhancement Enhance and restore degraded riparian and habitat conditions in the Little Naches River by re-vegetating eroding banks and unstable channels, restricting vehicular traffic in the floodplain and enhancing habitat by placement of trees and boulders.
199705100 Yakima Side Channel Protect, restore, and re-establish access to productive off-channel rearing habitats, protected and reconnected floodplains associated with the mainstem Yakima and Naches Rivers.
9803300 Upper Toppenish Watershed assessment suggests that land use in the forest and rangelands of the Toppenish Creek watershed has alterd the flow regime of the creek. Project activites are designed to moderate runoff patterns in Toppenish Creek by increasing the
199803400 Reestablish Safe Access into Tributaries of the Yakima Subbasin. Restore access to productive tributary habitat through consolidation of irrigation diversions, construction of fishways and installation of screens. Protect and restore a limited amount of habitat through fencing and re-vegetation.
199901300 Ahtanum Creek Watershed Assessment Habitat restoration and monitoring in the irrigated reach of Ahtanum Creek of the Yakima Subbasin, with emphasis upon the restoration of steelhead populations

Section 4. Budget for Planning and Design phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2002 costSubcontractor
1. Natural Production: Develop and implement methods of detecting indices of increasing natural production, as well as methods of detecting a realized increase in natural production, with specified statistical power. a1. Ecosystem Diagnosis and Treatment (EDT) Modeling: To design supplementation/habitat enhancement programs for coho, spring & fall chinook & steelhead in both Subbasins, and to investiagte popuation dynamics of supplemented populations 20 $257,790
a2. Technical assistance with application, interpretation and modification of EDT model 2 $175,000 Yes
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
1. Natural Production: Develop and implement methods of detecting indices of increasing natural production, as well as methods of detecting a realized increase in natural production, with specified statistical power. 2003 2006 $1,266,070
Outyear budgets for Planning and Design phase
FY 2003FY 2004FY 2005FY 2006
$432,790$277,760$277,760$277,760

Section 5. Budget for Construction and Implementation phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2002 costSubcontractor
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Outyear budgets for Construction and Implementation phase

Section 6. Budget for Operations and Maintenance phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2002 costSubcontractor
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Outyear budgets for Operations and Maintenance phase

Section 7. Budget for Monitoring and Evaluation phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2002 costSubcontractor
1. Natural Production: Develop and implement methods of detecting indices of increasing natural production, as well as methods of detecting a realized increase in natural production, with specified statistical power. a. EDT modeling and enhancement planning. See section 4 continual $0
1 b. Yakima River fall chinook fry survival study: determine optimal target areas for supplementation by estimating fry-to-smolt survival of marked hatchery fry used as surrogates for wild fry. 3-4 $75,000
1 c. Juvenile spring chinook micro-habitat utilization: Estimate baseline microhabitat utilization of juvenile 4-7 $23,000 Yes
1 d1. Yakima Hatchery spring chinook juvenile PIT-tagging: Estimate hatchery spring chinook smolt survival to Chandler & mainstem dams using PIT-tags, and smolt-to-adult survival (release to Yakima mouth) using CWTs. continual $212,685
1 d2. Yakima Hatchery spring chinook juvenile CWT-tagging: Estimate hatchery spring chinook smolt survival to Chandler & mainstem dams using PIT-tags, and smolt-to-adult survival (release to Yakima mouth) using CWTs. continual $250,000
1 e. Roza juvenile wild/hatchery smolt PIT tagging: To capture, PIT-tag and release wild and hatchery spring chinook to estimate relative wild/hatchery smolt survival to Chandler and the McNary Dam. continual $65,666
1 f. Wild/hatchery smolt survival and enumeration (Chandler Juvenile Monitoring Facility):To estimate hatchery and wild smolt passage at Chandler smolt trap. continual $430,676
1 g1. Fall chinook optimal rearing treatment: Develop an accelerated rearing treatment for fall chinook to enable early outmigration and increase overall smolt survival. 5-7 $52,890
1 g2. Fall chinook optimal rearing treatment: Subcontract with USFWS for fish marking. 5-7 $22,515 Yes
1 h1. Yakima coho stock and release study: Determine optimal location, date, and stock of release for Yakima coho re-introduction efforts. 5-7 $203,279
1 h2. Yakima coho stock and release study: Subcontract with USFWS to CWT fish.. 5-7 $155,921 Yes
1 i. Yakima spring chinook juvenile behavior: Determine differences in hatchery & wild spring chinook smolt behavior closely related to survival ? $52,084
1 j. Yakima hatchery spring chinook juvenile morphometric and coloration studies: Determine whether significant difference in body shape and coloration exist between OCT and SNT hatchery spring chinook before and during the time of release. continual $6,719
1 k. Yakima hatchery/wild spring chinook smolt physiology studies: Determine whether significant physiological differences exist among wild, OCT and SNT Yakima spring chinook smolts during rearing, at release, at Chandler and at McNary Dam. 2 $0
1 l. Adult salmonid enumeration at Prosser Dam: Estimate the total number of adult salmonids returning to the Yakima Basin by species (spring and fall chinook, coho and steelhead), including return of externally marked fish. continual $104,602
1 m. Adult salmonid enumeration and broodstock collection at Roza and Cowiche dams: Estimate the total number of adult salmonids returning to the upper Yakima (Roza), and the total number of adult coho returning to the Naches (Cowiche). continual $212,433
1 n. Spawning ground surveys (redd counts): Monitor spatiotemporal redd distribution in theYakima (spring chinook, Marion Drain fall chinook, coho, Satus/Toppenish steelhead). continual $85,995
1 o. Natural Spawning Observations: Characterize wild spring chinook reproductive behavior (adults & precocials) to analyze behavior of hatchery fish relative to wild fish. deferred $0
1 p. Yakima spring chinook residuals/precocials studies: Estimate baseline abundance of residual and precocial spring chinook salmon and determine the necessary sampling effort for long term monitoring following supplementation. continual $23,000 Yes
1 q1. Relative hatchery/wild reproductive success: Determine if spawning behavioral & reproductive success of wild and hatchery spring chinook are comparable, & estimate reproductive success of hatchery coho in a natural stream: Field work & data analysis. continual $128,088
1 q1. Relative hatchery/wild reproductive success: Determine if spawning behavioral & reproductive success of wild and hatchery spring chinook are comparable, & estimate reproductive success of hatchery coho in a natural stream: Study design. continual $30,000
1 r. Yakima spring chinook gamete quality monitoring: Estimate sex-specific fertility, in-hatchery mortality, incidence of monstrosities and fry emergence timing for upper Yakima spring chinook from a subsample of eggs. continual $28,970
1 s. Scale analysis: Determine age and stock composition of juvenile and adult salmonid stocks in the Yakima basin. continual $31,417
1 t. Fish health monitoring: Monitor the disease status of Yakima Basin hatchery juveniles and broodstock, and determine pre-supplementation incidence of pathogens in wild Yakima spring chinook continual $0
1 u. Habitat inventory aerial videos and ground truthing: Measure critical environmental variables by analyzing data extracted from aerial videos and verified by ground examinations. 4-9 $5,019
1 v. Out-of-basin environmental monitoring: Obtain and utilize information regarding mainstem and marine environmental and harvest-related impacts on all Yakima anadromous salmonids. defered $0
1 w. Sediment impacts on habitat: Monitor stream sediment loads associated with the operation of dams and other anthropogenic factors (e.g., logging, agriculture and road building) affecting streams in the Yakima subbasin. continual $42,835
1 x. Yakima hatchery spring chinook predator avoidance training: Determine efficacy of exposing Yakima hatchery spring chinook to avian predation prior to release in terms of increasing survival to Chandler. 4 $25,095
1 y. Biometrical Support: Provide the services of a half-time PH.D. level biometrician for the project. continual $50,000 Yes
2. Harvest: Develop methods to detect increases in harvest of YKFP targeted stocks. a. Out-of-basin harvest monitoring: Estimate group- and stock-specific harvest of hatchery and wild anadromous salmonids outside of the Yakima subbasin. continual $0
2 b. In-basin harvest: Estimate group- and stock-specific harvest of hatchery and wild anadromous salmonids within theYakima subbasin. continual $53,543
3. Genetics: Develop methods of detecting significant Pre- & post-supplementation (PAPS) genetic changes in targeted stocks as reflected by changes in extinction risk, within-stock genetic variability, between-stock genetic variability, and domesticat3 a.Allozyme/DNA data collection and analysis: Augment allozyme and DNA microsatellite baselines of all Yakima chinook stocks for monitoring within- and between population genetic variability. continual $200,000
3 b. Stray recovery on Naches and American spawning grounds: Determine the extent of gene flow from the supplemented Upper Yakima stock into the Naches and American River stocks. continual $31,800
3 c. Yakima spring chinook domestication: develop a domestication selection study for Upper Yakima spring chinook involving HxH and WxW matings that is sufficeitnly powerful to detect effects but also does not violate broodstock compositon rules. continual $10,000
4. Ecological Interactions: Determine if impacts to non-target taxa can be kept within specified biological limits, and determine if biotic interactions limit ability of supplementation to increase natural production. a1. Avian predation index: Develop methods to index impact of avian predation on annual smolt production of Yakima salmon and steelhead. continual $110,000 Yes
4 a2. Avian predation index: Develop methods to index impact of avian predation on annual smolt production of Yakima salmon and steelhead. continual $35,788
4 b. Fish predation index: Develop methods to index impact of piscivorous fish on annual smolt production of Yakima salmon and steelhead. continual $274,757
4 c. Indirect predation: Determine the impact of the abundance of outmigrating hatchery smolts on the survival of commingled smolts (wild and hatchery) via alterations in predator behavior. 2-4 $23,797
4 d.Yakima River spring chinook competition/prey index: Determine whether prey abundance limits the production of upper Yakima spring chinook smolts.. continual $23,000 Yes
4 e.Upper Yakima Non-Target Taxa of Concern (NTTOC) monitoring: Determine the impact of spring chinook supplementation on the abundance, distribution or size structure of 16 NTTOC in the Yakima Subbasin. continual $359,968
4 f. Pathogen sampling: Determine supplementation impacts on the incidence of pathogens in wild Yakima spring chinook smolts. continual $10,000
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
1. Natural Production: Develop and implement methods of detecting indices of increasing natural production, as well as methods of detecting a realized increase in natural production, with specified statistical power. 2003 2006 $9,748,200
2. Harvest: Develop methods to detect increases in harvest of YKFP targeted stocks. 2003 2006 $225,182
3. Genetics: Develop methods of detecting significant Pre- & post-supplementation (PAPS) genetic changes in targeted stocks as reflected by changes in extinction risk, within-stock genetic variability, between-stock genetic variability, and domesticat3 2003 2006 $1,000,349
4. Ecological Interactions: Determine if impacts to non-target taxa can be kept within specified biological limits, and determine if biotic interactions limit ability of supplementation to increase natural production. 2003 2006 $3,521,422
Outyear budgets for Monitoring and Evaluation phase
FY 2004FY 2003FY 2005FY 2006
$3,649,365$3,547,058$3,649,365$3,649,365

Section 8. Estimated budget summary

Itemized budget
ItemNoteFY 2002 cost
Personnel FTE: 42.5 $1,608,598
Fringe $309,604
Supplies $507,066
Travel $63,888
Indirect $605,640
Capital $0
NEPA $0
PIT tags # of tags: 91,600 $206,100
Subcontractor USF&W $178,436
Subcontractor University of Washington $110,000
Subcontractor Mobrand Biometrics $75,000
Subcontractor International Statistical Training and Technical Services $50,000
Subcontractor Cascade Aquatics $69,000
Subcontractor Central Washington University $100,000
$3,883,332
Total estimated budget
Total FY 2002 cost$3,883,332
Amount anticipated from previously committed BPA funds$0
Total FY 2002 budget request$3,883,332
FY 2002 forecast from 2001$4,111,696
% change from forecast-5.6%
Reason for change in estimated budget

Certain projects were dropped as unfeasible, PIT-tag costs declined and the need for new M&E efforts anticipated earlier failed to materialize.

Reason for change in scope

See above

Cost sharing
OrganizationItem or service providedAmountCash or in-kind

Reviews and recommendations

This information was not provided on the original proposals, but was generated during the review process.

Recommendation:
Fundable only if response is adequate
Date:
Jun 15, 2001

Comment:

Fundable; with clarification required for tasks identified in the table below.

This is a very large proposal that provides the information heart of the YKFP supplementation experiment. Programs related to this have been conducted since 1995 (documented in this text) and this proposal includes 36 objective/tasks combinations conducted annually in the YFP. Given the scope of these activities and the historical background to some tasks, this proposal is well prepared and informative. The scope/size of the proposal does, however, limit the information provided for any particular task. The authors have used table formats to summarize past work and tasks proposed, and we have adopted a similar format in providing comments. If a task is not included in the table below, then the ISRP agreed with the task description and did not comment. Given the importance of this proposal and the budget requested, a brief description of the proposal is included (copy of the Abstract as presented by YN). In total, the FY02 funding request is for $3,833,332 (reduced slightly from forecast); and the projected budgets through FY06 remain the same.

One concern in the presentation, however, is the limited number of publications and citations to work completed under these projects. Several references to publications are made in Part 1 of the proposal but few publications are cited. These citations would strengthen our sense of past accomplishments.

The ISRP also wishes to note that the sites visited during our tour were very well maintained and staff well organized. Each site indicated a well-organized program.

Proposal Abstract (section 9a): The YKFP is an effort to increase natural production and harvest opportunity of salmon and steelhead in the Yakima and Klickitat Subbasins using supplementation and habitat improvements. The project includes all stocks historically present in both basins. Currently, stock-specific plans are at widely differing levels of development: Yakima coho and fall chinook programs are in feasibility stages, while Yakima steelhead and all Klickitat programs involve only habitat/life history inventory, passage improvements and stock-status monitoring. The most complete program is the upper Yakima spring chinook supplementation program (Busack et al. 1997). We will monitor each program in terms of natural production, harvest, genetics and ecological interactions. Studies of defined statistical power in these areas will guide project adaptive management and provide critical information for regional enhancement efforts. Expected outcomes include evaluations of:

Project success is defined as a significant increase in natural production with limited adverse impacts on non-target stocks. Natural production is monitored in terms of natural origin recruits and its components (adult reproductive performance and survival from egg to fry, fry to smolt, and smolt to adult). Genetic impacts will be monitored in terms of domestication and within- and between-population variability. Ecological impacts on nontarget stocks will be monitored by comparing abundance, size structure, geographic distribution and interaction indices before and after supplementation. Impacts of nontarget species on project fish will be assessed by indices of predation, competition, prey abundance, mutualism and disease.

The scope and complexity of this, and the other YKFP projects, involves much data generation but the data management and analysis capabilities appear inadequate due to limited description of these activities. Resources should be devoted to ensuring complete, timely, useful archiving of data and data analyses including measures of variability and uncertainty to accompany quantitative results. To assess this will required more comprehensive description of procedures and resources.

Comments on Individual Objectives/Tasks:

A common concern with the proposal tasks and methods is the inappropriate phrasing or statement of the hypotheses. Frequently, hypotheses are stated as a statement of belief or assumption but not as a testable expression for study. Each monitoring task may not need a hypothesis statement and, in the future, the authors may wish to group activities under fewer tasks and hypotheses.

OBJECTIVEISRP COMMENT
1. Natural Production
1a. Natural Production & Modelling: It is not evident why indices are required when the real measure of success will be an increase in the natural population size and fish production. We also presume that this task includes EDT models and statistical models for experimental design work. Given the profile of EDT in the Yakima basin and the budget requested for this task (Section 4); the description of methods is far too vague. YKFP managers should clarify why EDT data collection and modelling is not described in more detail and/or included under a separate proposal.
1b. Yakima Fall chinook survival study The description in Section 9f (PIT of wild juveniles) does not seem consistent with statements in Section 7, task 1b. If wild fall chinooks are large enough to use PIT tags, is their survival actually indicative of reach productivity and suitability for fall chinook? Can sufficient numbers of fry be PIT tagged to compare survivals between tag groups? Do these investigations study the use of reaches by tagged fry? This task is not adequately described, particularly if feasibility work has been conducted.
1c. Spring chinook micro-habitat use These investigations are logically associated with supplementation but dispersion should be expected as populations increase (as noted). However, how would the program address emigration (downstream dispersion or use of tributaries) as opposed to local sub-optimal habitats? We would also not expect "carrying capacity" to be constant annually. This task is likely to be largely descriptive but may also be useful in EDT assessments... proceed given the modest cost.
1d. Spring chinook PIT tagging & CWT application This task combines costs for Section 7.1.d1. & 7.1.d2. The initial results of the PIT tagging presented in the Basin Summary were instructive and demonstrate adequate numbers of recoveries. Recommend continuation

Concerning CWT application, we understood that all hatchery production would be CWT ... but the task only refers to tagging 400,000 chinook? Is this a value left over from a previous proposal? Further, authors must also clarify the basis of the tagging cost projected. With a production of 800K juveniles, the projected tag cost per individual is much higher than in other tagging programs.

1e. Roza PIT tagging of W & H spring chinook Re-state and clarify the hypothesis ... as stated it is not clear how this hypothesis relates to the task. Recommend continuation
1f. Chandler monitoring Re-state and clarify the hypothesis ... as stated it is not clear how this hypothesis relates to the task. Chandler fish sampling site is essential to the YFP, recommend continuation and refinement of smolt estimation procedures.
1g. Accelerated rearing of Fall chinook Hypothesis is a statement of belief ... re-state as a testable hypothesis. The task statement does not adequately provide an indication of the problem. Based on our briefings, the ISRP understands the need for this program but it is not evident in this task statement. However, it is not evident how this strategy would aid the restoration of naturally spawning chinook in the Yakima River. Task combines budget items Section 7.1.g1 & 7.1.g2 (PIT tagging of juveniles).
1h. Coho stock and date of release study This task combines budget items Section 7.1.h1 & 7.1.h2 and is a costly project. The hypothesis suggests the study will assess "a suitable stock" of hatchery coho salmon but the rationale and methods do not address the variable stock. Clarify the present intent of this study.
1i. Spring chinook juvenile behavior Behavioral comparison of chinook reared under OCT and SNT in the Cle Elum facility. We strongly doubt that this hypothesis is testable or that such simply correlation exists. For example, the migratory behavior of a smolt may differ substantially from the behavior studied in the hatchery juveniles. We place a lower priority on this work compared to other tasks.
1j. Spring chinook morphometric and coloration Comparison of body morphology and coloration in wild fish and hatchery fish reared under OCT and SNT. As in task 1i. we place a lower priority on this work compared to other tasks (but these costs are substantially less than for task 1i.).
1k. Smolt physiology Not considered in this proposal
1l. Adult monitoring at Prosser Dam This is clearly an annual monitoring program that does not need a hypothesis statement. Recommend continuation.
1m. Adult monitoring at Roza and Cowiche dams This is clearly an annual monitoring program that does not need a hypothesis statement. Recommend continuation.
1n. Spawning ground surveys The hypothesis stated is actually an assumption of this task ... is there an issue that you are testing? While the ISRP strongly supports this task, we question whether sufficient resources are assigned to this task. For example, is it adequate to only have an index of spawning activity in a stream reach when our objective is to assess supplementation and productivity of the naturally-spawning populations?
1o. Natural spawning observations This task has no budget assigned and indicates that the task has been deferred. Since hatchery produced adults will be returning in 2001, does this mean the project has been completed or has it been cancelled? This loss of this work could be a significant limitation to interpreting the behaviors observed in the artificial spawning channels at Cle Elum.
1p. Spring chinook residuals & precocial study The high incidence of precocial development in hatchery male chinook supports undertaking this task. Recommend completing this investigation.
1q. Hatchery / Wild reproductive success The development of an artificial spawning channel at Cle Elum provides an opportunity for reproductive behavioral studies, but we must be patient before concluding similarity or difference between the hatchery and wild spring chinook. As discussed above, hatchery production in Cle Elum is not representative of production in older hatchery programs. Recommend proceeding with research on spring chinook.

Part 2 of this task involves coho salmon. The hypothesis stated for coho salmon is another assumption, how would this statement be tested and related to reproductive success? The coho work is not compatible with the statement of the task. The coho work is more related to habitat suitability for spawning and egg survival. The committee is doubtful of the merit of constructing stream reaches in the artificial channel. In natural environments, site selection may involve many more variables than substrate composition. Further, how would the effect of hatchery ancestry be isolated from the substrate effect ... where is the related information on "wild" coho spawning success in these substrates? We also are doubtful that substrates of known composition can be artificially constructed and stable through the spawning period. We not support of this coho task as presently described.

1s. Scale analysis While monitoring age structure is essential to monitor the dynamics of a chinook salmon, the investigators must also be aware of the frequency of errors in scale aging. The presence of large numbers of CWT could provide a good estimation of aging error. Further, multiple aging structures should be used to verify ages and reduce errors. The committee was also uncertain why we must "ensure that the age structure does not change as the result of supplementation." If supplementation lead to a large, more diverse, natural population; then a shift to older larger adults may be beneficial to the stock.
1t. Fish Health Not included in the budget, work coordinated with samples already available from Chandler facility and analyzed by USFWS
1w. Sediment impacts on habitat This task is poor described. The hypothesis is simply a statement of fact and not testable. It is not clear what this task involves ... is it a monitoring program or just responsive to a problem? Authors must clarify before support is recommended.
2. Harvest
2a. Out-of-Basin monitoring While there are no costs associated with this task, are there information needed by investigators that they presently do not have?
2b. In-basin monitoring An in-river program is supported but the funds allocated seem limited. Further, is the monitoring for reported catch only or is there a plan to estimate total mortality associated with fishing? The latter is recommended.
3. Genetics
3a. DNA data collection & analysis Hypothesis is another assumption, not a hypothesis. The ISRP notes that this work activity may have to be expanded if the YKFP is adjusted to the recommends about (see notes for Box 2); i.e., sampling of pure hatchery strains and of isolated wild sub-population. We are unable to advise on changes to budget required since the basis for the $200,000 request is not provided ... what is the charge per sample and how many samples are provided for? This information should be provided. Further, the ISRP notes that this work is a major aspect of the supplementation assessment but no information has been provided about the accuracy of these analyses or the results from the initial sampling. We strongly recommend publishing the DNA information, methods to be used in estimating the genetically effective population size, and sensitivity testing of these analyses be conducted and reported. Recommend funding for analyses but reporting required before continued funding is provided ... however we would expect this monitoring to continue beyond the "first full cycle of adult returns" as suggested in the text.
3b. Stray recovery ... We understand that the American and Naches river spring chinook are genetically differentiated from the upper Yakima spring chinook ... but how different are they for the DNA markers to be applied. Again, it would be useful to know more about past sampling and comparisons between populations. Tagged hatchery fish can be counted in these spawning populations but is it likely that the true "gene flow" can be estimated using the DNA markers. The suggested budget is quite limited, how many samples are to be processed and what level of genetic difference maybe detected at this sample size? Recommend a preliminary investigation for the suggested budget.
3c. Domestication study The request is for planning and design work only ... unfortunately, the first generation of hatchery fish is returning in 2001. This aspect of the supplementation experiment needed to be decided upon before now. As the ISRP has commented above, we believe there is an immediate need to establish a pure hatchery stock within the Cle Elum facility in order study domestication and contrast with the supplementation groups currently being reared in the facility. Regrettably, the opportunity to monitor domestication from the first generation has been compromised by not initiating this program in 2001, but the Age-5 returns could be utilized next year.
4. Ecological Interactions Most of these tasks could be considered individual research studies and may be more thoroughly described in a separate project. Each of these requires understanding the methods of estimating predator population sizes, for estimating the predation rate, and extrapolating to the total mortality on the prey species. Future submissions should consider a more comprehensive description of these tasks ... 4c. and 4e., in particular, are very expensive projects.
4a. Avian predation index The hypothesis again includes two topic statements; separate testable hypotheses should be developed. This task includes budget items section 7.4.a1 and 7.4.a2 (sub-contractor and YN respectively). Recommend support for a few years, but the need for an on-going continual program is uncertain.
4b. Fish predation index The hypothesis again includes two topic statements; separate testable hypotheses should be developed. Summary comments (page 1335) based on projects 9506402 and 9506424 indicate that these investigation have been successful in providing an estimate of the predation losses but there are not sufficient details of these studies to provide other comment. The predation level from Northern Pike minnow was substantial in 2000 and an estimated 95% of the prey were yearling fish. When should attention be shifted from predation levels to controlling the predator populations? What is known about reproductive biology of Pike minnow and can this be used to control these populations?
4c. Indirect predation While this seems to be a tenable hypothesis, we are uncertain of the study to be conducted or the basis for the budget requested. The text states that "test groups will define themselves" ... which leads to the concern that how these are defined could determine the study outcome. Is the hypothesis being tested that predation on wild fish is proportional to the presence of hatchery fish in the migration period? This seems to be testable question without definition of groups. We place a lower priority on this work compared to other tasks.
4d. Competition / Prey index This is a reasonable task given the expected (hoped) response to supplementation. Habitat use and production in a year and/or stream, however, will also vary with environmental variation and the distribution of spawning adults. How will the effect of supplementation be assessed? For example, if the abundance of juveniles increase how can this be associated with the supplemented adults. Further, with increased populations of juvenile spring chinook, we may expect the distribution of size to change, but the total production of returning adults could still increase. While this type of study may be informative within stream reaches and about freshwater capacity ... supplementation should be assessed based on adult production from the natural spawning population. We would also suggest that the reaches monitored should be ones where the population size of spawners can be estimated.
4e. NTTOC The scale of this task and related project activities requires a separate project proposal to fully evaluate the activity (noted above). This task is consistent with considering ecosystem type impacts associated with large-scale supplementation. While the ISRP recognizes that this is the type of multi-species investigation called for in the NWPPC's new program, we do not have adequate information upon which to evaluate methods, impacts, etc.
4f. Pathogen sampling The proposal is for a minimum sampling (200) of wild spring chinook at the Chandler facility. Pathogen screening to be conducted by USFWS. Disease risk in a large supplementation program is a commonly expressed concern, but it seems to have very low profile in the YKFP proposals. Is there a reason for the minimal involvement of pathogen sampling/monitoring in the YKFP M&E proposal? This seems to be an obvious source of concern in an otherwise comprehensive set of tasks ... and should be clarified.

Recommendation:
High Priority
Date:
Aug 3, 2001

Comment:


Recommendation:
Fund
Date:
Aug 10, 2001

Comment:

Fundable in part. To briefly summarize the ISRP comments on the YKFP responses by tasks, the bolded comments were originally from the ISRP review, and the text following is the current ISRP reply to the YKFP responses provided.

OBJECTIVE

ISRP COMMENT

1.Natural Production

 

1a. Natural Production & Modeling:

YKFP managers should clarify why EDT data collection and modeling is not described in more detail and/or included under a separate proposal. While the response provided was extensive, it very definitely demonstrated why a more comprehensive proposal and review for this activity is necessary in the future. The ISRP identified numerous technical questions about the material received, but do not wish to initiate another series of reviews and responses. Fundable

1b. Yakima Fall chinook survival study

This task is not adequately described, particularly if feasibility work has been conducted. The response agreed with the ISRP comments and provided adequate clarification. Fundable

1c. Spring chinook micro-habitat use

This task is likely to be largely descriptive but may also be useful in EDT assessments... proceed given the modest cost. Fundable

1d. Spring chinook PIT tagging & CWT application

Recommend continuation. Further, authors must also clarify the basis of the tagging cost projected. The response noted the error in presentation and provided adequate response. The ISRP noted though that the power to detect a 50% effect size indicates that their procedures are going to be fairly insensitive to change. Whether this is adequate depends on the management application. Fundable

1e. Roza PIT tagging of W & H spring chinook

Re-state and clarify the hypothesis ... as stated it is not clear how this hypothesis relates to the task. Recommend continuation. Response provided a series of simple hypotheses that were more correctly stated. Fundable

1f. Chandler monitoring

Recommend continuation and refinement of smolt estimation procedures. Adequate response. Fundable

1g. Accelerated rearing of Fall chinook

The response provided a correctly stated hypothesis and we agree with the additional comments provided. Fundable

1h. Coho stock and date of release study

Clarify the present intent of this study. The response agreed that there had been an error in the description of this project and provided adequate response. Fundable

 

1i. Spring chinook juvenile behavior

We place a lower priority on this work compared to other tasks. The brevity of the ISRP comments obviously lead to a misunderstanding ... for this we apologize. Our comment centered on identifying one behavioral trait that can be associated with a change in overall survival. We certainly do not contest the issue of behavioral differences between treatments, but what is the likelihood that one trait can be directly associated with smolt-to-adult survival? This is particularly true when the comparisons are made after release and adjustment of smolts to the riverine environment. Consequently, as described, we continue to place a lower priority on this project. The study design does not ensure that they will produce valuable results. They will likely be chasing hypotheses. They need to describe an explicit set of hypotheses to test at the onset of the experiment, these were not adequately presented. Not fundable.

1j. Spring chinook morphometric and coloration

Comparison of body morphology and coloration in wild fish and hatchery fish reared under OCT and SNT. As in task 1i. We place a lower priority on this work compared to other tasks (but these costs are substantially less than for task 1i.). No response. Fundable at low priority

1k. Smolt physiology

Not considered in this proposal. No money requested for this task in this proposal.

1l. Adult monitoring at Prosser Dam

Recommend continuation. No additional comments. Fundable

1m. Adult monitoring at Roza and Cowiche dams

Recommend continuation. No additional comments. Fundable

1n. Spawning ground surveys

While the ISRP strongly supports this task, we question whether sufficient resources are assigned to this task. This response is inadequate as the surveys as described cannot answer the hypotheses (or issues) stated as examples. Further, the response does not address other spring stocks, coho, or steelhead. This task is central and critical to the YKFP but we continue to recommend that the YKFP review these programs to ensure they provide the necessary data. Consideration of whether indices and trends are adequate or more quantitative data are needed is critical in this review. Fundable, but a report from these considerations is recommended.

1o. Natural spawning observations

Response is adequate, presuming that this work is conducted. No associated budget was requested.

1p. Spring chinook residuals & precocial study

Recommend completing this investigation. No further comment. Fundable

 

1q. Hatchery / Wild reproductive success

Recommend proceeding with research on spring chinook.

We do not support the coho task as presently described.

The response acknowledged the need to clarify the coho portion of this project and identified two activities: identification of spawning and acclimation sites, and evaluation of reproductive success of introduced hatchery coho salmon. The initial challenge for coho salmon is simply to get naturalized spawners back into the Yakima system ... and initial returns have been encouraging. The study of how a "domesticated hatchery" coho stock could re-adjust to natural conditions would be an interesting investigation but the baseline for such a study should already have been collected (or being so). The ISRP continues to recommend proceeding with the spring chinook work (Fundable), and we continue to have many comments on the coho project (Not fundable without further review). For example, the approach to use one large acclimation site does not seem designed to match the life history and behavior of coho. The approach of using numerous, small-scale, local, temporary acclimation facilities on tributaries is better suited to coho life history patterns.

In this final review, we have two suggestions for the coho project: separate this restoration activity into a separate project description so that the basis of the plan can be more fully described and reviewed, and as part of the YKFP annual program review, organize a comprehensive review of the coho restoration program. This program could then be submitted to Council for review and funding.

1s. Scale analysis

Response is adequate. Fundable

1t. Fish Health

Not included in the budget, work coordinated with samples already available from Chandler facility and analyzed by USFWS

1w. Sediment impacts on habitat

This task is poorly described. Authors must clarify before support is recommended. The response notes that this program is basically a monitoring program ... but is the data collected incorporated into any restoration programs. Once an area of sediment problem is identified how is it addressed, or is it simply incorporated as a limiting factor into the EDT model. Clarification of how this data will be used would strengthen this project. The ISRP recommends proceeding with this task. Fundable

2. Harvest

 

2a. Out-of-Basin monitoring

While there are no costs associated with this task, are there information needed by investigators that they presently do not have? The response noted it is "difficult" to obtain data but did not comment on whether there is data that is necessary and not provided by outside agencies.

2b. In-basin monitoring

The response is adequate but we have two comments: a 10% sampling rate is less than conducted in many other fisheries but could be appropriate in these fisheries if the marking rate is high, the need for incidental mortality information depends on the management requirements. We would recommend that the number of tags being recovered with a 10% sampling rate be reviewed to ensure that objectives are being met, and that a program to examine incidental mortality rates be implemented. The latter will soon be required under the total mortality management provision of the Pacific Salmon Treaty. Fundable

3. Genetics

 

3a. DNA data collection & analysis

Recommend funding for analyses but reporting required before continued funding is provided ... however we would expect this monitoring to continue beyond the "first full cycle of adult returns" as suggested in the text. The response is adequate but we note that no comment is provided on the publication of results, and that only 250 "returnees" will be sampled under this budget. How can this be an adequate sample size to determine the pedigree data? We would strongly recommend a review of sample allocation within this budget to ensure that the priority tasks are being addressed first. Fundable, following review of sample allocation.

 

3b. Stray recovery ...

Recommend a preliminary investigation for the suggested budget.

A good response was provided for this task, the ISRP recommends proceeding. Fundable

3c. Domestication study

As the ISRP has commented above, we believe there is an immediate need to establish a pure hatchery stock within the Cle Elum facility in order to study domestication and contrast with the supplementation groups currently being reared in the facility. The response acknowledged the importance of this issue, and the ISRP appreciated the detailed response. However, we feel the response misrepresented an important point of the original review. Within the comments on project 3c (Domestication), the ISRP recommended HxH control lines ... but in our general comments on supplementation the ISRP strongly recommended both a HxH and WxW comparisons. The ISRP in NOT recommending only a HxH line, nor the HS design as stated. The response identified three concerns about domestication research: direct measurement, disruption to supplementation effort, and limitations due to life history. While direct comparison is the essence of our comments and is essential, none of the other comments are really limitations to implementing what the ISRP recommended. While we acknowledge that the WxW "line" will not be a fully controlled experiment as the HxH line could be, we continue to recommend this as an essential feature of the experimental design.

Not fundable until an adequate experimental design is achieved that includes a HxH and WxW control, or fully justifies why not.

4. Ecological Interactions

Most of these tasks could be considered individual research studies and may be more thoroughly described in a separate project. Our concern was that such a brief statement does not provide any insight into the activity or provide any technical basis for review. We agree that potential impact of supplementation on non-target species is an important issue and merits investigation ... but our task is to advise on the science applied to assess these impacts. A project proposal must provide the basis for review. Given the scope and costs of projects under Ecological Interactions, we suggest that one comprehensive proposal would be more informative and appropriate for this process. Fundable in concept but the methods must described in detail sufficient to allow for scientific review.

4a. Avian predation index

Recommend support for a few years, but the need for an on-going continual program is uncertain. The response agreed with ISRP comments. Fundable

4b. Fish predation index

The response agreed with ISRP comments and the YKFP has been developing plans to "implement experimental management" of fish predators. Fundable

4c. Indirect predation

We place a lower priority on this work compared to other tasks. The ISRP comments about the budget stemmed from not fully understanding the procedures to be used. Again this is an example of providing limited information on procedures due to combining all activities into one large project. The response adequately clarified our concerns and we recommend support. Fundable

4d. Competition / Prey index

No further comments. Fundable

4e. NTTOC

We do not have adequate information upon which to evaluate methods, impacts, etc. Good response, Fundable.

4f. Pathogen sampling

This seems to be an obvious source of concern in an otherwise comprehensive set of tasks ... and should be clarified. Adequate response, Fundable.

   

The ISRP is increasingly concerned about funding supplementation experiments if the project sponsors have not fully thought about the design and evaluation of these programs. To us, these programs must, at least, express:

  1. a comprehensible and relevant statement of hypotheses that address key questions,
  2. a thorough design capable of testing these hypotheses,
  3. a technically acceptable assessment of the size of the effect that the design is capable of resolving,
  4. a credible argument that the design is sufficient to test these hypotheses, and
  5. a clear statement of how supplementation will be evaluated and how "success" or "failure" in the experiment will be determined.

It is very difficult to make a concluding comment on a project as large and complex as the YKFP Monitoring and Evaluation project. Many of the programs and monitoring sites are being well managed, and we believe that important information can be gained from these programs and in this system. At present, the YKFP has the potential to be the most comprehensive study of supplementation on the west coast. Unfortunately, the issue of the experimental design and the fundamental need to assess supplementation tends to overshadow these positive features. Since most of the M&E projects are related to the supplementation program, should the ISRP recommend not funding any projects until an acceptable experimental design is agreed and implemented? From a strictly scientific perspective this may be appropriate, but the Basin already has a major investment in the Cle Elum facility and this study. Consequently, we recommend tentative funding of this project (except for the tasks noted as not fundable in the above table), with funding contingent upon an immediate resolution of the supplementation evaluation design. The timeframe and review process should be determined by the responsible management and funding agencies. If an agreed design is not achieved within the fiscal planning cycle, then it is certainly possible to terminate production while maintaining some monitoring and evaluation programs.


See detailed ISRP comments on the YKFPs.
Recommendation:
Date:
Oct 1, 2001

Comment:

Statement of Potential Biological Benefit to ESU
Provides greater understanding of hatchery-wild fish interactions in the Yakima and Klickitat sub-basins, by evaluating the effectiveness and impact of ongoing supplementation programs. Information gained will enable more effective recovery planning in this and other subbasins.

Comments
Well-designed research project; already underway; providing important information that will be applicable to listed ESUs.

Already ESA Req? no

Biop? yes


Recommendation:
Rank A
Date:
Oct 16, 2001

Comment:

No cost-share. This project funds 42 FTE. The project incorporates the biologists and techs that perform the various duties called for in collecting and analyzing performance data that will guide the YKFP managers in adaptive management of the program. The M&E plan for the project calls for a major monitoring effort and this project is designed to fulfill this objective. As per the ISRP review, the spring chinook juvenile behavior objective should not be funded.
Recommendation:
Fund
Date:
Jan 3, 2002

Comment:

ISRP "fund in part" recommendations for Yakima Fisheries Project monitoring an evaluation; Project 199506325

This program monitors efforts in the Yakima River associated with natural production, artificial production initiatives, harvest, ecological and genetic impacts. The proposed budget requests $3,708,932 in FY 2002 and $12,934,574 over three years.

The ISRP review (p. 9-19) was generally favorable to the core proposals for the Yakima/Klickitat Fisheries Project (YKFP) and their accomplishments to date. The ISRP's primary concern was associated with the current inadequacies of this project in the experimental design to assess the artificial production initiatives in the basin. The ISRP provided extensive task specific comments and recommendations, and recommended tentative funding for the project conditioned on the resolution of the evaluation design.

The YKFP monitoring and evaluation project is large and complex. In addition the history of the project is equally complex. There is a need in the short term to make a determination on the link of the current experimental design to what was expressed and approved in the master plan by the Council in October 1987 and the Environmental Impact Statement completed by Bonneville in 1996. During the EIS's preparation period, the Council endorsed the managers' proposal to "tier" the Project's production and research activities by bringing them online in gradual stages. The first (tier) targeted the supplementation of depressed populations of upper Yakima River spring chinook. This initial phase also included research designed to determine the feasibility of re-establishing a naturally spawning population and a significant fall fishery of coho salmon in the Yakima Basin (previously Evaluate the Feasibility and Potential Risks of Restoring Yakama River Coho Project #199603302 - High Priority Supplementation Project #12). Additional tiers of the YKFP include the supplementation of fall chinook (previously Supplementation and Enhance the Two Existing Stocks of Yakama River Fall Chinook Project #199603301 - High Priority Supplementation Project #13) and steelhead.

Staff recommendation: The staff recommendation does not have a significant impact on the amount of funding proposed for this project. However, what follows is an extensive and detailed staff recommendation for the implementation of this proposal that is based on the ISRP recommendations and staff communication with the project sponsors.

A determination is needed to ensure that the stated purpose for the artificial production initiative(s) and specific objectives can be assessed under the current study design and that it is linked to approved documents. This determination needs to be completed prior to future commitment to the program and Council staff suggests that this be conducted by the ISRP with initial interpretation provided by Bonneville (i.e. utilizing historical documents and environmental reviews). In the meantime, the Council asks Bonneville to reserve a placeholder for the project pending ISRP review and a positive funding recommendation regarding the issue raised by the ISRP under Section 7, objective 3, task c. Council staff and ISRP will determine an approach to conduct an additional review. This will most likely involve an additional submittal and may involve ISRP and sponsor interaction via teleconference. Cost associated with this effort will be determined during the review and secured through prioritization of the objectives and task of the budget recommended for this project. In addition the ISRP in their review provided task specific recommendations. Council staff concurs with this recommendations, and request Bonneville to ensure these recommendations are addressed and implemented in contracting

Additional information regarding Section 7, objectives 3 and 4 is needed to understand the linkage of the individual task and priority to the overall assessment of the project. These objectives need to be included in the overall determination of the association to previous review and approvals and the necessity of the tasks to assess the program. Sampling allocation as defined in Section 7, objective 3, task a need to be reviewed prior to funding. This can be accomplished in the review by the ISRP as mentioned above.

The remaining objectives and tasks are not as clearly defined in their current form. There is need to separate out species specific efforts targeted for the particular efforts going (i.e. spring chinook, coho, fall chinook and steelhead). As part of the planning efforts staff requests that specific objectives, tasks and budgets be developed for each of the identified species (i.e. spring chinook, coho and steelhead). As expressed to the Yakama Nation and The Washington Department of Fish and Wildlife on March 22, 2000 in a Fish and Wildlife committee decision on March 21, 2000 regarding the use of the Yakima Trout Facility for rearing coho, there is a need to do a comprehensive review of the other restoration activities that are currently being pursued (i.e. coho and fall chinook). This aggregation of the various species under one project, without clearly articulating goals and objectives, has raised significant concerns regarding the alignment of the current study design and the development of other production initiatives without a master plan and fiscal planning. Therefore, given that this project (1) is addressing an "experimental" phase for artificial intervention into other species and continues to grow (e.g. cost) and change, (2) has recently been reviewed in conjunction to the provincial review which identified the need to clarify the intent regarding coho, and (3) also is addressing other species in the subbasin, it appears valuable to take up the issues regarding these other species in a step review process. These step reviews need to address all species, except for spring chinook, and address master planning elements as provide to the Yakama nation by letter on February 20, 1998. Future funding for these objectives and tasks are conditioned on the submittal and favorable review of master plans. To a lesser extent this needs to address elements of Section 4, objective 1, task a, and Section 7, objective 1, task n that address all the species. Also see Yakima Issue 2 regarding the capital requests associated with the other species.

Budget effect on base program (Project 199506325):

FY 2002 FY 2003 FY 2004
No effect No effect No effect

Recommendation:
Fund
Date:
Mar 6, 2002

Comment:


Recommendation:
Fund
Date:
Sep 20, 2003

Comment:

04 and 05 now includes Yakama, WDFW and BPA direct pay for PIT tags. Accrual for WDFW potion for 03 is captured in project 199506424. Accrual is through 4/30 period. Invoice just submitted and others in process.
Recommendation:
Date:
Sep 20, 2003

Comment:

This amount is for the Yakama Nation Component only, an amount for BPA Direct Pay and WDFW is the balance, these amounts will increase the overall Monitoring & Evaluation project budget total. (Budget amounts changed at province meetings from submittal)
REVIEW:
NW Power and Conservation Council's FY 2006 Project Funding Review
Funding category:
expense
Date:
May 2005
FY05 NPCC start of year:FY06 NPCC staff preliminary:FY06 NPCC July draft start of year:
$4,100,251 $4,100,251 $4,100,251

Sponsor comments: See comment at Council's website