FY 2002 Mountain Snake proposal 198909800

Section 1. Administrative

Proposal titleIdaho Supplementation Studies
Proposal ID198909800
OrganizationIdaho Department of Fish and Game and Idaho Office of Species Conservation (IDFG/IOSC)
Proposal contact person or principal investigator
NameSam Sharr
Mailing address1414 East Locust Lane Nampa, ID 83686
Phone / email2084658404 / [email protected]
Manager authorizing this projectSteve Yundt
Review cycleMountain Snake
Province / SubbasinMountain Snake / Salmon
Short descriptionEvaluate various supplementation strategies for maintaining and rebuilding spring/summer chinook salmon populations in Idaho. Develop recommendations for using supplementation to reuild naturally spawning populations.
Target speciesSpring/summer chinook salmon
Project location
LatitudeLongitudeDescription
44.1542 -114.8805 Sawtooth emigrant trap 1 and weir
44.1535 -114.8802 Sawtooth emigrant trap 2
44.6808 -114.0337 Pahsimeroi River emigrant trap and weir
44.8715 -113.6247 Lemhi River emigrant trap
44.8588 -113.624 Lemhi River emigrant trap
44.3862 -115.1598 Marsh Creek emigrant trap and weir
44.6548 -115.7013 South Fork Salmon River emigrant trap and weir 1
44.6708 -115.7023 South Fork Salmon River emigrant trap and weir 2
46.5048 -114.6782 Powell acclimation/release ponds
46.533 -114.6745 Crooked Fork Creek emigrant trap
46.5083 -114.6755 Crooked Fork Creek weir
46.5052 -114.6777 Colt Killed Creek emigrant trap
45.8048 -115.4727 Red River emigrant trap
45.7068 -115.337 Red River weir
45.82 -115.5262 Crooked River emigrant trap
Reasonable and Prudent Alternatives (RPAs)

Sponsor-reported:

RPA
Hatchery RPA Action 170
Hatchery RPA Action 173
Hatchery RPA Action 174
RM&E RPA Action 182
RM&E RPA Action 184
Action 169

Relevant RPAs based on NMFS/BPA review:

Reviewing agencyAction #BiOp AgencyDescription
NMFS Action 182 NMFS The Action Agencies and NMFS shall work within regional priorities and congressional appropriations processes to establish and provide the appropriate level of FCRPS funding for studies to determine the reproductive success of hatchery fish relative to wild fish. At a minimum, two to four studies shall be conducted in each ESU. The Action Agencies shall work with the Technical Recovery Teams to identify the most appropriate populations or stocks for these studies no later than 2002. Studies will begin no later than 2003.
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.
NMFS/BPA Action 182 NMFS The Action Agencies and NMFS shall work within regional priorities and congressional appropriations processes to establish and provide the appropriate level of FCRPS funding for studies to determine the reproductive success of hatchery fish relative to wild fish. At a minimum, two to four studies shall be conducted in each ESU. The Action Agencies shall work with the Technical Recovery Teams to identify the most appropriate populations or stocks for these studies no later than 2002. Studies will begin no later than 2003.
NMFS/BPA 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
1991 Identified study areas, brood stocks, facilities to be used.
1991 Began preliminary baseline data collection on all treatment and control streams, target stock history, genetic sampling.
1991 Initiated development of local brood stocks to provide future releases. Full brood stock development requires one generation or five years.
1992 Began supplementation (juvenile releases) and monitoring of treatment streams, and monitoring of control streams. Monitoring includes PIT tagging and juvenile and adult abundance estimates.
1993 Release of progeny from supplementation brood stocks to treatment streams; continued brood stock development.
1994 Release of progeny from supplementation brood stocks to treatment streams; continued brood stock development.
1995 Release of progeny from supplementation brood stocks to treatment streams; continued brood stock development.
1995 Monitored adult returns from prior releases and natural spawning.
1995 Began using adult returns from first generation supplementation brood stock with natural origin recruits to develop further brood stocks and to supplement natural spawning populations.
1996 Completed first series of small scale investigations into chinook salmon supplementation strategies and techniques: 1992-1994. Technical Report. Peery, C.A. and T.C. Bjornn.
1996 Monitored adult returns from prior releases and natural spawning. Continued supplementation brood stock production and juvenile releases.
1997 Monitored adult returns from prior releases and natural spawning. Continued supplementation brood stock production and juvenile releases.
1998 Continued supplementation of treatment streams and monitoring of control streams, continued monitoring of juvenile survival and abundance, and monitoring of adult returns.
1999 Continued supplementation of treatment streams and monitoring of control streams, continued monitoring of juvenile survival and abundance, and monitoring of adult returns.
2000 Five-year Report (1991-1996) completed. Authored and produced by all project cooperators.
2000 Developed final supplementation brood stock for South Fork Salmon River, progeny to be released spring 2002. This completes the primary smolt treatment in the South Fork Salmon River
2001 Continued supplementation brood stock production. Pending assessment of treatment frequency and statistical analyses, other treatments may be terminated after brood year 2001 production (assessed after completetion of 2001 spawning).

Section 3. Relationships to other projects

Project IDTitleDescription
9005500 Steelhead Supplementatin Studies Reciprocal transfer of data/coordination
9107300 Idaho Natural Production Monitoring and Evaluation Reciprocal transfer of data/coordination
8335000 Nez Perce Tribal Hatchery O&M Reciprocal transfer of data/coordination
9405000 Salmon River Habitat Enhancement - O&M, M&E Reciprocal transfer of data/coordination
9705700 Salmon River Production Program Reciprocal transfer of data/coordination
9703000 Monitor Listed Stock Adult Chinook Salmon Escapement Reciprocal transfer of data/coordination
9102800 Monitoring smolt Migration of Wild Snake River Spring/Summer Chinook Salmon Reciprocal transfer of data/coordination
9604300 Johnson Creek Artificial Propagation Enhancement- O&M, M&E Reciprocal transfer of data/coordination

Section 4. Budget for Planning and Design phase

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

Section 5. Budget for Construction and Implementation phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2002 costSubcontractor
1. Monitor and evaluate the effects of supplementation on parr, pre smolt and smolt numbers, and spawning escapements of naturally produced salmon. a. Develop and implement “standardized” spawning, rearing, marking, and release protocols. ongoing $18,691
1 b. Differentially mark all hatchery supplementation and general production fish released in or nearby the study streams. ongoing $19,391
1 c. PIT tag a minimum of 300 to 700 hatchery supplementation and general production fish released in or nearby the study streams. ongoing $55,926
1 d. Release various life stages of chinook salmon. Determine fish numbers for each life stage based on existing natural production and natural rearing capacity. ongoing $15,231
1 e. Estimate late summer parr densities from snorkel surveys. ongoing $29,518
1 f. PIT tag a minimum of 700 naturally produced parr from each treatment and control stream to estimate smolt production and survival. ongoing $279,023
1 g. Use existing weirs to collect, mark (PIT tag), and enumerate emigrating fish and to identify and enumerate returning adults. ongoing $166,146
1 h. Compare natural production of supplemented populations to unsupplemented populations and baseline data. ongoing $41,781
2. Monitor and evaluate changes in natural productivity and genetic composition of target and adjacent populations following supplementation. a. Monitor productivity and genetic indices from supplemented populations and compare baseline and controls. Productivity characteristics will be evaluated as a function of density or percent carrying capacity to minimize density dependent effects ………….. ongoing $65,812
2 b. Monitor straying of hatchery supplementation fish into adjacent and control streams by weirs and carcass surveys. ongoing $59,415
2 c. Determine spawner to recruitment relationship based on determined production and productivity indices (parr and smolt numbers, adult escapements, survival, eggs/spawner etc.). ongoing $43,292
2 d. Predict population viability based on spawner to recruitment relationship to determine if the population will maintain itself through time in the absence of additional supplementation. ongoing $21,572
3. Determine which supplementation strategies (brood stock and release stage) provide the quickest and highest response in natural production without adverse effects on productivity. a. Monitor and evaluate natural production (pre smolt, Smolt and adult numbers) and productivity (survival, life stage characteristics, pathogens, straying, genetic composition) of supplemented populations and compare to baseline and controls. ongoing $53,751
3 b. Use local brood stocks with known natural component from the target population during the second generation of supplementation. 3 $35,488
3 c. Compare natural production and productivity indices of supplemented populations using existing hatchery brood stocks (first generation) to populations using locally developed brood stocks (second generation). ongoing $35,280
3 d. Compare natural production and productivity indices among supplemented populations using parr, pre smolt, and smolt release strategies. ongoing $27,944
4. Develop supplementation recommendations. (Long term). a. Guidelines and recommendations will be developed addressing risks and benefits of supplementation (augmentation and restoration) in general and specific supplementation strategies (brood stock and release stage). ongoing $28,465
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
1. Monitor and evaluate the effects of supplementation on parr, pre smolt and smolt numbers, and spawning escapements of naturally produced salmon. 2003 2006 $2,413,990
2. Monitor and evaluate changes in natural productivity and genetic composition of target and adjacent populations following supplementation. 2003 2006 $760,090
3. Determine which supplementation strategies (brood stock and release stage) provide the quickest and highest response in natural production without adverse effects on productivity. 2003 2006 $632,450
4. Develop supplementation recommendations. (Long term). 2003 2006 $148,470
Outyear budgets for Construction and Implementation phase
FY 2003FY 2004FY 2005FY 2006
$985,000$990,000$990,000$990,000

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
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Outyear budgets for Monitoring and Evaluation phase

Section 8. Estimated budget summary

Itemized budget
ItemNoteFY 2002 cost
Personnel FTE: 14.8 $424,666
Fringe $140,140
Supplies $44,625
Travel $8,515
Indirect $167,019
Capital PIT-tag field computer and CWT detectors (CWT/no-fin-clip tagging recently implemented) $33,400
PIT tags # of tags: 24000 $54,000
Other $124,361
$996,726
Total estimated budget
Total FY 2002 cost$996,726
Amount anticipated from previously committed BPA funds$0
Total FY 2002 budget request$996,726
FY 2002 forecast from 2001$975,000
% change from forecast2.2%
Reason for change in estimated budget

Cost of living increase for personnel and increased operating costs (mainly fuel costs for travel). Purchase of more PIT tags than in FY01 to adapt to increased production from 2001 spawners.

Reason for change in scope

No change in scope.

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:
Sep 28, 2001

Comment:

Idaho Supplementation Studies

A response is needed for the set of Idaho Supplementation Study Projects.

Background

Supplementation of natural stocks is not a mandated mitigation objective, but has become an important part of the hatchery programs. Idaho has outplanted (i.e. off-site releases) over 5.5 million chinook fry, approximately 8 million smolts, and 8,000 adults into the Salmon River drainage since 1977 (IDFG et. Al. 1990). During the same period, over 17 million fry, 3 million smolts, and 2,000 adults were outplanted into the Clearwater River drainage (Nez Perce Tribe et. Al. 1990). In spite of widespread outplanting activities there has been little scientific evaluation of supplementation on rebuilding or influencing natural salmon populations both in Idaho and basin wide. Furthermore, despite these hatchery mitigation efforts, anadromous fish stocks in Idaho continued to decline.

The Idaho Department of Fish and Game (IDFG) spearheaded development of the Idaho Supplementation Studies (ISS) to address questions identified in the Supplementation Technical Work Group (STWG) Five Year Workplan (STWG 1988), as well as help define the potential role of supplementation in managing Idaho's anadromous fisheries and as a recovery tool for the basin. The goal of the Idaho Supplementation Studies is to evaluate various supplementation strategies for maintaining and rebuilding spring/summer chinook salmon populations in Idaho and to develop recommendations for using supplementation to rebuild naturally spawning populations.

Projects directly involved in the ISS are:

  1. Project ID: 198909800. Idaho Supplementation Studies. Sponsor: Idaho Department of Fish and Game and Idaho Office of Species Conservation. Subbasin: Salmon.
  2. Project ID: 198909801. Evaluate Supplementation Studies in Idaho Rivers (ISS). Sponsor: U.S. Fish and Wildlife Service - Idaho Fishery Resource Office. Subbasin: Clearwater.
  3. Project ID: 198909802. Evaluate Salmon Supplementation Studies in Idaho Rivers- Nez Perce Tribe. Sponsor: Nez Perce Tribe. Subbasin: Salmon.
  4. Project ID: 198909803. Salmon Supplementation Studies in Idaho- Shoshone-Bannock Tribes. Sponsor: Shoshone-Bannock Tribes. Subbasin: Salmon
  5. Project ID: 199005500. Steelhead Supplementation Studies in Idaho Rivers. Sponsor: Idaho Department of Fish and Game and Idaho Office of Species Conservation. Subbasin: Clearwater
  6. Project ID: 199604300. Johnson Creek Artificial Propagation Enhancement Project. Sponsor: Nez Perce Tribe. Subbasin: Salmon.

ISS also coordinates field activities and data collection efforts with the Idaho Habitat/ Natural Production Monitoring project (199107300). ISS also coordinates with and transfers data to projects in the Salmon River subbasin including the Monitoring Smolt Migration of Wild Snake River Spring/Summer Chinook Salmon (199102800), Salmon River Habitat Enhancement (9405000), and Salmon River Production Program (199705700). ISS also works closely with the Lower Snake River Compensation Plan (LSRCP) to coordinate on hatchery supplementation treatments and evaluations.

Presently, there are eleven state and federal anadromous hatcheries operating in Idaho: Clearwater, Oxbow, Rapid River, McCall, Sawtooth, Pahsimeroi, Dworshak, Kooskia, Hagerman National, Niagara Springs, and Magic Valley. There are also three satellite rearing ponds: Powell, Red River, and Crooked River operated in conjunction with the Clearwater Hatchery. These hatcheries have the combined capacity to produce 8.5 million spring chinook smolts, 2 million summer chinook smolts, 6.7 million A-run steelhead O. mykiss smolts, and 4 million B-run steelhead smolts annually.

ISS Study Design

The ISS study design called for a minimum of 15 years (three generations) of research (Bowles and Leitzinger 1991). Sampling was initiated in 1991, and implementation began in 1992. Supplementation effects are monitored and evaluated by comparing juvenile production and survival, fecundity, age structure, and genetic structure and variability in treatment and control streams of similar ecological parameters.

Due to the large geographic scope of this study, study streams were partitioned among four resource management entities for implementation. These include Idaho Department of Fish and Game, Nez Perce Tribe, Shoshone-Bannock Tribe, and the U.S. Fish and Wildlife Service-Idaho Fishery Resource Office. Allocations were based on interest, integration with ongoing programs, cost efficiency, logistics and, to a lesser extent, relative equity. Approximately one-half of the study will be implemented by Idaho Department of Fish and Game through the ISS contract with BPA. The Nez Perce Tribe and Shoshone-Bannock Tribe have similar commitments to ISS, each comprising approximately 20% of the study. Both of these components rely heavily on integration of existing or proposed tribal programs. The U.S. Fish and Wildlife Service-Idaho Fishery Resource Office implements about ten percent of the project. The Idaho Department of Fish and Game is the lead agency regarding project development, coordination, and implementation.

The ISS Experimental Design was completed and published in 1991. Baseline data collection and development of supplementation brood stocks (Phase I) began in 1991. Over a period of about five years, supplementation brood stocks were developed for seven hatchery trap/release locations as identified in the experimental design:

Artificial Production Facilities

  1. Sawtooth Fish Hatchery - Upper Salmon River
  2. Pahsimeroi Fish Hatchery - Pahsimeroi River
  3. McCall Fish Hatchery - South Fork Salmon River
  4. Clearwater Fish Hatchery Satellites
  5. Crooked River
  6. Red River
  7. Powell (Colt-killed Creek)
  8. Clear Creek - Kooskia National Fish Hatchery

As adult fish began to return from the Phase I supplementation brood stock juvenile releases, the project progressed into Phase II. Phase II utilizes the returning adults to supplement natural origin recruits in treatment streams and maintains supplementation brood stocks for juvenile production and release. Juvenile fish releases through brood year 1996 include 1,281,755 fish in the Clearwater River basin and 1,954,048 fish in the Salmon River basin.

This project is now transitioning from Phase II to Phase III, monitoring the effects of supplementation. In Phase III juvenile releases from supplementation brood stocks are eventually terminated, returning adults from prior juvenile releases are released to supplement spawning of natural origin recruits, and monitoring of production and productivity response variables in control and treatment streams continues. In 2000, juvenile releases were maintained at levels similar to releases in 1999.

Treatment (e.g. supplementation in general, supplementation with a particular life stage, supplementation with a particular brood source) effects will be tested directly by hypotheses. In general, treatments will be applied for one to two generations (5-10 years) following approximately one generation of pretreatment data. Population responses to supplementation will be monitored a minimum of one generation (5 years) following supplementation. It is important that the original study design be maintained. Reducing sample size (number of treatment streams) can potentially impair the sensitivity of the design. Reducing to five treatment streams provides only a 60% chance of detecting a 25% change in production, whereas we would still have over 95% chance of detecting a 50% change.

Related projects

Several additional projects are related to the ISS. The monitoring and evaluation portion of the Johnson Creek Artificial Propagation Enhancement project (199604300) conducts the juvenile emigration and survival, adult escapement (weir and spawning ground surveys), and genetic monitoring associated with the ISS project in Johnson Creek. The Nez Perce Tribal Hatchery Monitoring and Evaluation project (198335003) collects the data associated with the ISS project in Lolo Creek, Eldorado Creek, and Newsome Creeks in the Clearwater River subbasin. The Nez Perce Tribe Monitoring of Listed Stock Chinook Salmon Escapement project (BPA Number 199703000) operates a video camera and weir to passively monitor and enumerate adults returning to Lake Creek and upper Secesh River. This project collects data on adult abundance and migration timing of chinook salmon.

ISRP Preliminary Recommendations:

As initially planned, the Idaho Supplementation Study (ISS) was probably the best supplementation study among the Provinces. It should be continued, but the ISRP has a number of concerns that should be addressed while there is still time. This study addresses the critical issue of the efficacy of supplementation to restore populations and many resources have been committed to it. With the experimental design of the Yakima Hatchery in question (no wild/wild and no hatchery/hatchery controls), retaining the integrity of this experiment is crucial. It is important that the Idaho Supplementation Studies be completed following the original approved experimental design.

The most critical ISRP concerns are:

  1. the effect of the loss of Johnson Creek (previously a control stream) from the experimental design, and
  2. the effect of straying of hatchery fish into Lake Creek, the Secesh River, and other designated "controls".

As currently planned in project #199604300"Johnson Creek Artificial Propagation Enhancement Project", Johnson Creek is neither a treatment nor a control stream in the ISS because the criteria for stopping supplementation has been changed and does not appear to match the timetable in the ISS. Supplementation activities in Johnson Creek should cease immediately for the duration of the ISS study design, allowing Johnson Creek to continue to be used as a 'control' stream, even given the recent limited supplementation of it. (Note: a portion of the 2001 returning jacks are the first returning fish from the limited Johnson Creek supplementation effort.)

To do minimal damage to the ISS study design, the ISRP recommends that Johnson Creek now be considered a control stream (at least by year class!) and that supplementation be stopped in Johnson Creek in accordance with the original timetable in the ISS. The number of wild returning adults we observed earlier this month spawning in Johnson Creek, and the number we are likely to observe next year, argue that supplementation of Johnson Creek is not needed as an emergency action for a declining stock at least through the duration of the ISS experiment.

As we understand the situation, the decision to remove Johnson Creek from the study was beyond the control of some proponents of the ISS project. Nevertheless, we find it unacceptable that the experimental design for study of such a critical issue as supplementation would be compromised by a decision to remove a control stream from the study. The only conclusion we can come to is that the proponents of the decision to remove Johnson Creek from the supplementation study believe that they already know the result, i.e., they believe supplementation works. A broad base of the scientific community is in extreme disagreement with this conclusion, and it is unacceptable that the best-designed study of supplementation would be compromised.

Other ISRP concerns: The proponents should list the initial control and treatment streams and the current treatments and controls. How has the overall design changed? What is the current timetable to stop supplementation in the treatment streams and to evaluate the effect on natural production? In the control streams, what effect do the straying rates have on the analysis? What would be the effect of changing Johnson Creek from a "control" to a "treatment" stream on the statistical power of the study?

The results of this project should help determine whether supplementation is a viable restoration strategy and as such should inform the RPA four-step safety net process.

There may be a need for ongoing input from an over-site committee with members outside those participating in the study to monitor the progress. Has this been planned for or considered?


Recommendation:
High Priority
Date:
Nov 30, 2001

Comment:

This project addresses RPAs 174, 182 and 184.
Recommendation:
Do Not Fund
Date:
Dec 21, 2001

Comment:

Idaho Supplementation Studies

Background

Supplementation of natural stocks is not a mandated mitigation objective, but has become an important part of the hatchery programs. Idaho has outplanted (i.e. off-site releases) over 5.5 million chinook fry, approximately 8 million smolts, and 8,000 adults into the Salmon River drainage since 1977 (IDFG et. al. 1990). During the same period, over 17 million fry, 3 million smolts, and 2,000 adults were outplanted into the Clearwater River drainage (Nez Perce Tribe et. al. 1990). In spite of widespread outplanting activities there has been little scientific evaluation of the efficacy of supplementation on rebuilding or influencing natural salmon populations both in Idaho and basin wide. Furthermore, despite these hatchery mitigation efforts, anadromous fish stocks in Idaho continued to decline.

The Idaho Department of Fish and Game (IDFG) spearheaded development of the Idaho Supplementation Studies (ISS) to address questions identified in the Supplementation Technical Work Group (STWG) Five Year Workplan (STWG 1988), as well as help define the potential role of supplementation in managing Idaho's anadromous fisheries and as a recovery tool for the basin. The goal of the Idaho Supplementation Studies is to evaluate various supplementation strategies for maintaining and rebuilding spring/summer chinook salmon and steelhead populations in Idaho and to develop recommendations for using supplementation to rebuild naturally spawning populations.

Projects directly involved in the ISS are:

  1. Project ID 198909800. Idaho Supplementation Studies. Sponsor: Idaho Department of Fish and Game and Idaho Office of Species Conservation. Subbasin: Salmon.
  2. Project ID 198909801. Evaluate Supplementation Studies in Idaho Rivers (ISS). Sponsor: U.S. Fish and Wildlife Service - Idaho Fishery Resource Office. Subbasin: Clearwater.
  3. Project ID 198909802. Evaluate Salmon Supplementation Studies in Idaho Rivers- Nez Perce Tribe. Sponsor: Nez Perce Tribe. Subbasin: Salmon.
  4. Project ID 198909803. Salmon Supplementation Studies in Idaho- Shoshone-Bannock Tribes. Sponsor: Shoshone-Bannock Tribes. Subbasin: Salmon
  5. Project ID 199005500. Steelhead Supplementation Studies in Idaho Rivers. Sponsor: Idaho Department of Fish and Game and Idaho Office of Species Conservation. Subbasin: Clearwater
  6. Project ID 199604300. Johnson Creek Artificial Propagation Enhancement Project. Sponsor: Nez Perce Tribe Subbasin: Salmon.

ISS coordinates field activities and data collection efforts with the Idaho Habitat/ Natural Production Monitoring project (199107300). ISS also coordinates with and transfers data to projects in the Salmon River subbasin including the Monitoring Smolt Migration of Wild Snake River Spring/Summer Chinook Salmon (199102800), Salmon River Habitat Enhancement (9405000), and Salmon River Production Program (199705700). ISS also works closely with the Lower Snake River Compensation Plan (LSRCP) to coordinate on hatchery supplementation treatments and evaluations.

Presently, there are eleven state and federal anadromous hatcheries operating in Idaho: Clearwater, Oxbow, Rapid River, McCall, Sawtooth, Pahsimeroi, Dworshak, Kooskia, Hagerman National, Niagara Springs, and Magic Valley. There are also three satellite rearing ponds: Powell, Red River, and Crooked River operated in conjunction with the Clearwater Hatchery. These hatcheries have the combined capacity to produce 8.5 million spring chinook smolts, 2 million summer chinook smolts, 6.7 million A-run steelhead O. mykiss smolts, and 4 million B-run steelhead smolts annually.

ISS Study Design

The ISS study design called for a minimum of 15 years (three generations) of research (Bowles and Leitzinger 1991). Sampling was initiated in 1991, and implementation began in 1992. Supplementation effects are monitored and evaluated by comparing juvenile production and survival, fecundity, age structure, and genetic structure and variability in treatment and control streams of similar ecological parameters.

Due to the large geographic scope of this study, study streams were partitioned among four resource management entities for implementation. These include Idaho Department of Fish and Game, Nez Perce Tribe, Shoshone-Bannock Tribe, and the U.S. Fish and Wildlife Service-Idaho Fishery Resource Office. Allocations were based on interest, integration with ongoing programs, cost efficiency, logistics, and, to a lesser extent, relative equity. Approximately one-half of the study will be implemented by Idaho Department of Fish and Game through the ISS contract with BPA. The Nez Perce Tribe and Shoshone-Bannock Tribe have similar commitments to ISS, each comprising approximately 20% of the study. Both of these components rely heavily on integration of existing or proposed tribal programs. The U.S. Fish and Wildlife Service-Idaho Fishery Resource Office implements about ten percent of the project. The Idaho Department of Fish and Game is the lead agency regarding project development, coordination, and implementation.

The ISS Experimental Design was completed and published in 1991. Baseline data collection and development of supplementation brood stocks (Phase I) began in 1991. Over a period of about five years, supplementation brood stocks were developed for seven hatchery trap/release locations as identified in the experimental design:

Artificial Production Facilities

  1. Sawtooth Fish Hatchery - Upper Salmon River
  2. Pahsimeroi Fish Hatchery - Pahsimeroi River
  3. McCall Fish Hatchery - South Fork Salmon River
  4. Clearwater Fish Hatchery Satellites

  5. Crooked River
  6. Red River
  7. Powell (Colt-killed Creek)
  8. Clear Creek - Kooskia National Fish Hatchery
As adult fish began to return from the Phase I supplementation brood stock juvenile releases, the project progressed into Phase II. Phase II utilizes the returning adults to supplement natural origin recruits in treatment streams and maintains supplementation broodstocks for juvenile production and release. Juvenile fish releases through brood year 1996 include 1,281,755 fish in the Clearwater River basin and 1,954,048 fish in the Salmon River basin. This project is now transitioning from Phase II to Phase III, monitoring the effects of supplementation. In Phase III juvenile releases from supplementation brood stocks are to be eventually terminated, returning adults from prior juvenile releases are released to supplement spawning of natural origin recruits, and monitoring of production and productivity response variables in control and treatment streams continues. In 2000, juvenile releases were maintained at levels similar to releases in 1999. Treatment (e.g. supplementation in general, supplementation with a particular life stage, supplementation with a particular brood source) effects will be tested directly by hypotheses. In general, treatments will be applied for one to two generations (5-10 years) following approximately one generation of pretreatment data. Population responses to supplementation will be monitored a minimum of one generation (5 years) following supplementation. It is important that the original study design be maintained. Reducing sample size (number of treatment streams) can potentially impair the sensitivity of the design. Reducing to five treatment streams provides only a 60% chance of detecting a 25% change in production, whereas we would still have over 95% chance of detecting a 50% change. Related projects Several additional projects are related to the ISS. The monitoring and evaluation portion of the Johnson Creek Artificial Propagation Enhancement project (199604300) conducts the juvenile emigration and survival, adult escapement (weir and spawning ground surveys), and genetic monitoring associated with the ISS project in Johnson Creek. The Nez Perce Tribal Hatchery Monitoring and Evaluation project (198335003) collects the data associated with the ISS project in Lolo Creek, Eldorado Creek, and Newsome Creeks in the Clearwater River subbasin. The Nez Perce Tribe Monitoring of Listed Stock Chinook Salmon Escapement project (BPA Number 199703000) operates a video camera and weir to passively monitor and enumerate adults returning to Lake Creek and upper Secesh River. This project collects data on adult abundance and migration timing of chinook salmon. ISRP Final Recommendation: Not fundable until the ISRP concerns are adequately addressed. The experimental design has not been adhered to over the years and from the response to our preliminary review, the ISRP is not confident it will be in the future. In fact, the current experimental design is not adequately defined. There does not appear to be commitment to treatment durations, particularly to the Phase III portion of the study design, where supplementation ceases, so that treatment effects can be analyzed. From communications that occurred during the ISRP site visit, it appears the project sponsors should be able to specify timelines for termination of the treatments for each treatment stream. A table needs to be developed for Phase III implementation that describes when the treatments will stop on a stream-by-stream basis. In the past, sponsors have not stuck with agreed upon control streams. How confounded are the treatment and control streams? This points to the need for submittal of a certified statistical design. Projects 198909800 through 198909803 and 199005500 are fundable after adequately addressing the following constraints.
  1. A written protocol for complete statistical analysis, certified by an independent statistician team should be presented to Council during the contracting period. The ISRP is not comfortable with the implications that "problems" with the study design can be "fixed" during the statistical analysis stage. Considerable thought and effort should be placed in planning the statistical analyses of these potentially controversial data before final decisions are made on criteria for stopping supplementation and before data are available.
  2. The protocol for statistical analysis must indicate how straying of hatchery fish into "control streams" and "partial treatments" will be analyzed. For example, the response to the ISRP preliminary review indicated that the straying rate of hatchery fish into the Secesh River from 1996-2001 varied from 0.83% to 14.71%. This is in fact, de facto supplementation. It is unclear to the ISRP how partial treatment and de facto supplementation of control streams will be addressed in the statistical analysis of the ISS.
  3. Development of a specific stream-by-stream protocol and timetable for implementation of Phase III of the ISS. Included in this is the immediate cessation of supplementation activities in Johnson Creek (see comments below on proposal 199604300) and inclusion of Johnson Creek once again as a control stream in the ISS experimental design.

Recommendation:
Date:
Feb 1, 2002

Comment:

Statement of Potential Biological Benefit to ESU
Benefits are indirect. Evaluate the usefulness of supplementation as a recovery/restoration strategy for depressed stocks of spring and summer chinook salmon in Idaho.

Comments
Supplementation of natural stocks has become an important part of the hatchery programs. However, in spite of widespread outplanting activities there has been little scientific evaluation of supplementation on rebuilding or influencing natural salmon populations. The results of these projects should help determine whether supplementation is a viable restoration strategy, a subject which NMFS is currently researching.

Already ESA Req? No

Biop? Yes


Recommendation:
A Conditional
Date:
Feb 11, 2002

Comment:

Recommend funding of ongoing scope of work only after ISRP concerns are addressed and conditioned upon timely submission of reports for implementation of RPAs 182 and 184. We note that this project has consistently struggled with timely submission of annual progress reports. This project now proposes additional objectives that may have merit and could be considered after the ISRP's concerns are addressed and a regional RM&E plan is developed.

BPA RPA RPM:
182, 184

NMFS RPA/USFWS RPM:
182, 184


Recommendation:
Fund
Date:
Apr 19, 2002

Comment:

Council recommendation: The Council recommends funding for these projects [198909800, 198909801, 198909802, 199604300, 198909803] after the ISRP concerns detailed in programmatic issue 10 are addressed. The sponsors are requested to document their responses, and provide them to the Council for ISRP review. If the ISRP concerns are addressed, only previously approved and ongoing objectives should be funded. NMFS comments provide that these projects address RPAs 182 and 184. Bonneville's "A conditional" rating and comments are consistent with the Council recommendation. All of these proposals are held to funding levels approved by the Council in Fiscal Year 2001 plus 3.4%. The Council also notes that the sponsors need to consider how Johnson Creek will continue to be used in the ISS study as part of its response (this relates to the ISRP's third question on page 45 of its final report and Salmon Issue 8 below) [see Council comments on project 199604300].
Recommendation:
Fund
Date:
Jun 13, 2002

Comment:

Fund ongoing scope of work only after ISRP concerns are addressed and conditioned upon timely submission of reports for implementation of RPA's 182 and 184.
Recommendation:
Date:
May 22, 2003

Comment:

[See full document for review of all Idaho Supplementation Studies (ISS) Projects]
Recommendation:
Fund
Date:
Sep 20, 2003

Comment:

No contract yet. M&E on schedule. Additional review for final design requested by Council (June 04). Increase due to salary increases, fleet increases, computer, facility rates, juvenile and adult equipment replacement…Final design review due by June 04
Recommendation:
Date:
Sep 20, 2003

Comment:

Increases needed to offset: 1) increased employee salaries and benefit rates, 2) increase fleet rental rates, 3) increased computer equipment rental rates, 4) increased facility lease and utilities charges, 5) juvenile and adult equipment replacement costs, and 6) increased biometrics costs associated with peer review and interim reports in response to those reviews.
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:
$990,000 $990,000 $990,000

Sponsor comments: See comment at Council's website