FY07-09 proposal 200716600
Jump to Reviews and Recommendations
Section 1. Administrative
Proposal title | Lower Columbia River Coastal Cutthroat Trout Population Response to Habitat Restoration |
Proposal ID | 200716600 |
Organization | Columbia River Fisheries Program Office |
Short description | Determine if habitat restoration efforts in the lower Columbia River and estuary are achieving the recovery goals for coastal cutthroat trout, an indicator species, of reversing declining abundance trends and maintaining life history diversity. |
Information transfer | Quarterly, annual and final reports will be provided to contracting agency to meet obligations of contract. Information will be disseminated to scientific community through agency final report, peer reviewed literature, and/or presentation at professional meetings. Updates and final results will be available to scientific community, general public and contracting agency through US Fish and Wildlife Service - Columbia River Fisheries Program Office web site. Final results will provide baseline information toward habitat restoration efforts in the lower Columbia River and estuary as well as information toward refining approach to evaluating response to future habitat restoration efforts. |
Proposal contact person or principal investigator |
Contacts
Contact | Organization | |
---|---|---|
Form submitter | ||
Michael Hudson | USFWS-CRFPO | [email protected] |
All assigned contacts | ||
Robert Haverkate | USFWS-CRFPO | [email protected] |
Michael Hudson | USFWS-CRFPO | [email protected] |
Michael Hudson | USFWS-CRFPO | [email protected] |
Michael Hudson | USFWS-CRFPO | [email protected] |
Michael Hudson | USFWS-CRFPO | [email protected] |
Howard Schaller | USFWS-CRFPO | [email protected] |
Timothy Whitesel | USFWS, CRFPO | [email protected] |
Section 2. Locations
Province / subbasin: Columbia Estuary / Columbia Estuary
Latitude | Longitude | Waterbody | Description |
---|---|---|---|
Abernathy Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Bear Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Big Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Chinook River | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Germany Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Gnat Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Imnaha River | Bull trout effective population size in isolated populations | ||
Mill Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Milton Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
North Scappoose Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
South Scappoose Creek | Lower Columbia River coastal cutthroat trout population response to habitat restoration | ||
Wallacut River | Lower Columbia River coastal cutthroat trout population response to habitat restoration |
Section 3. Focal species
primary: Coastal Cutthroat Southwest Washington/Columbia River ESUsecondary: All Anadromous Salmonids
secondary: Coastal Cutthroat
Section 4. Past accomplishments
Year | Accomplishments |
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Section 5. Relationships to other projects
Funding source | Related ID | Related title | Relationship |
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BPA | 200306300 | Repro Success Abernathy Creek | Maintains PIT tag antenna arrays on Abernathy Creek |
BPA | 200300700 | Lwr Col River/Est Eco Monitor | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
BPA | 200201200 | Lower Columbia Habitat Mapping | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
BPA | 200301500 | Blind Slough Restoration | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
BPA | 200300600 | Effect Monitor Chinook R Est R | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
BPA | 200304500 | Opt of Fcrps Impacts On Salmon | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
BPA | 200300800 | Pres/Restore Col R/Est Willapa | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
BPA | 200301100 | Columbia R/Estuary Habitat | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
Other: USACE | BPS-00-11 | Est Detect PIT salmonid trawl | Provides field support to project through collection of coastal cutthroat trout |
Other: USACE | EST-02-02 | Est Habitat and Juv Salmon | Adds to overall understanding of relationship between estuary habitat and salmonids |
Other: USACE | EST-04-NEW | Eval Ecosystem Response to Restoration | Adds to project specific monitoring efforts by providing biological relevance at the ecosystem level to habitat restoration efforts |
Section 6. Biological objectives
Biological objectives | Full description | Associated subbasin plan | Strategy |
---|---|---|---|
Develop population abundance model. | Develop and utilize a population abundance model for lower Columbia River coastal cutthroat trout to evaluate population response to habitat restoration. | Lower Columbia | R.S5., R.S7., E.S5. |
Differentiate alternate life history strategies. | Investigate alternative approaches to differentiate between alternate life history strategies in juvenile and adult coastal cutthroat trout. | Lower Columbia | R.S5., R.S7., E.S5. |
Estimate fluvial movements among tributaries. | Estimate rate of juvenile and adult fluvial coastal cutthroat trout movements among neighboring tributaries in four areas of the lower Columbia River. | Lower Columbia | R.S5., R.S7., E.S5. |
Estimate straying by anadromous cutthroat. | Estimate rate of straying by returning anadromous wild coastal cutthroat trout among neighboring tributaries in four areas of the lower Columbia River. | Lower Columbia | R.S5., R.S7., E.S5. |
Estimate survival for coastal cutthroat trout. | Estimate between season and between life stage survival for coastal cutthroat trout. | Lower Columbia | R.S5., R.S7., E.S5. |
Implement robust sampling design. | A robust sampling design will be implemented to estimate population abundance of lower Columbia River coastal cutthroat trout. | Lower Columbia | R.S5., R.S7., E.S5. |
Section 7. Work elements (coming back to this)
Work element name | Work element title | Description | Start date | End date | Est budget |
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Analyze/Interpret Data | Analyze anadromous straying | The rate straying by anadromous individuals will be determined directly from monitoring data generated by PIT tag antennae arrays in streams containing such. | 10/1/2007 | 9/30/2009 | $54,750 |
Biological objectives Estimate straying by anadromous cutthroat. |
Metrics Focal Area: Analyze PIT tag antennae array data |
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Analyze/Interpret Data | Analyze data to develop population abundance model | Program MARK (White and Burnham 1999) will be used to develop a population abundance model incorporating data from the recommended sampling approach, survival, immigration and emigration, and probability of capture to determine an abundance estimate for coastal cutthroat trout in the study area of the lower Columbia River. | 10/1/2008 | 9/30/2009 | $54,750 |
Biological objectives Develop population abundance model. |
Metrics Focal Area: Incorporate all analyzed data into abundance model |
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Analyze/Interpret Data | Analyze electrofishing data | Data to estimate survival between seasons and between life stages will be analyzed using models available in Program MARK (White and Burnham 1999). Data analysis will also generate capture-recapture probabilities that will be necessary for developing the population abundance model. The most effective and efficient sampling approach will be recommended for providing accurate population abundance estimates using the model developed through implementation of this project. | 10/1/2007 | 9/30/2009 | $54,750 |
Biological objectives Estimate survival for coastal cutthroat trout. Implement robust sampling design. |
Metrics Focal Area: Generate survival estimates Focal Area: Identify effective and efficient sampling approach |
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Analyze/Interpret Data | Analyze fluvial movements | The proportion of fish emigrating from streams containing a PIT tag antennae array will be determined directly from monitoring data generated by the antennae. An estimate of fish emigrating from streams without PIT tag antennae arrays will be determined using subsequent electrofishing recaptures, capture efficiencies, and survival rates generated from this project. Spring smolt trap data will be used in addition if that information is available for the stream (i.e., Mill Creek, Germany Creek). The number of coastal cutthroat trout immigrating from neighboring tributaries will be determined directly from monitoring data generated by PIT tag antennae arrays in streams containing such. An estimate of the number of coastal cutthroat trout immigrating from neighboring tributaries for streams not containing PIT tag antennae arrays will be determined using subsequent electrofishing recaptures, capture efficiencies, and survival rates generated from this project. | 10/1/2007 | 9/30/2009 | $54,750 |
Biological objectives Estimate fluvial movements among tributaries. |
Metrics Focal Area: Analyze PIT tag antennae array monitoring data Focal Area: Analyze electrofishing data Focal Area: Analyze spring smolt trap data |
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Analyze/Interpret Data | Analyze growth data and stable isotope data | Lengths and weights will provide growth rate measures between initial capture and recapture for various age classes and life history strategies. The null hypothesis for this objective is that no differences in growth rate are detectable among age classes and life history strategies. Age will be determined from scale analysis. Life history strategy (resident, fluvial, anadromous) will be determined from location, mode and timing of recapture (i.e., an anadromous coastal cutthroat trout would be recaptured from the stream it originated in a smolt trap during the spring outmigration). An ANOVA on growth rates among the designated groups will determine if significant differences are present. The anticipated end-product of this task is an index to determine the proportion of anadromous and resident coastal cutthroat trout in a juvenile population prior to smolting. Stable isotope analysis will be conducted on all tissue samples to determine 13C /12C ratios (d13C (‰)) and 15N /14N ratios (d15N (‰)). All samples will be processed by a commercial laboratory (i.e., Colorado Plateau Stable Isotope Laboratory, Northern Arizona University) using an automated continuous flow isotope ratio mass spectrometer. Samples will be processed by a commercial laboratory to expedite analysis. All data will be analyzed using ANOVA to determine if significant differences occur in the relative ratios of stable carbon and nitrogen isotopes with respect to age and life history strategy. The anticipated end-product of this task is an index relating stable isotope ratios in juvenile and adult coastal cutthroat trout to life history strategy. | 10/1/2007 | 9/30/2009 | $54,750 |
Biological objectives Differentiate alternate life history strategies. |
Metrics Focal Area: Analyze/Interpret Growth Data Focal Area: Analyze/Interpret stable isotope data |
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Collect/Generate/Validate Field and Lab Data | Conduct field work to achieve objectives | Juveniles and adults will be captured in identified tributaries during annual fall electrofishing and spring smolt trapping (coordinated with ODFW, WDFW, Sea Resources, CREST, and USFWS-AFTC). In each of the tributaries, up to 1000 coastal cutthroat trout will be tagged annually with individually coded PIT tags (23 mm long, 3.84 mm diameter, 0.6 g) and released back into the general area of capture. Recaptured fish will be determined by scanning all captured coastal cutthroat trout for PIT tags. At this time, length, weight, scale samples and tissue samples will be collected from all fish. Scales will be analyzed to determine age. Tissue samples will be used for stable isotope analysis. Monitoring of fish movements will begin immediately after initial release. Movements will be monitored through the year using this technology to determine the proportion of adults and juveniles emigrating from the stream and the number of fluvial coastal cutthroat trout immigrating from neighboring tributaries as well as the rate of straying by anadromous individuals. Between season and between life stage survival (S) for coastal cutthroat trout will be determined through mark-recapture approaches employed on one stream per group of tributaries multiple times of the year through the duration of the project. Marking approaches will include PIT tagging during fall electrofishing and spring smolt trapping. Recapture approaches will include fall electrofishing, spring smolt trapping, winter adult trapping, and interrogation at stationary PIT tag antennae arrays. Alternative approaches to differentiate between alternate life history stragegies in juvenile and adult coastal cutthroat trout include the use of stable isotope analysis and growth rate analysis. All coastal cutthroat trout collected will be measured, weighed and sampled nonlethally for fin and/or muscle tissue. A robust sampling design will be used to capitalize on the strengths of closed and open population models used to estimate demographic parameters (Pollock 1982, Pollock et al. 1990). Alternative sampling approaches will be investigated for determining population abundance of lower Columbia River coastal cutthroat trout. These approaches will include multiple pass depletion, single pass mark/recapture, multiple pass mark/recapture and mark/resight. The implementation of tasks associated with this objective will be coordinated with activities being conducted to achieve Objectives 1-3. | 10/1/2006 | 9/30/2009 | $610,500 |
Biological objectives Differentiate alternate life history strategies. Estimate fluvial movements among tributaries. Estimate straying by anadromous cutthroat. Estimate survival for coastal cutthroat trout. Implement robust sampling design. |
Metrics Focal Area: Electrofish eleven tributaries Focal Area: Monitor movement through antennae arrays Focal Area: Collect biological information and tissue samples Focal Area: Mark and recapture at smolt and adult traps Focal Area: Process samples for age and isotope analysis |
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Develop RM&E Methods and Designs | Develop and implement robust sampling design and data analysis | A robust sampling design will be used to capitalize on the strengths of closed and open population models used to estimate demographic parameters (Pollock 1982, Pollock et al. 1990). Alternative sampling approaches will be investigated for determining population abundance of lower Columbia River coastal cutthroat trout. These approaches will include multiple pass depletion, single pass mark/recapture, multiple pass mark/recapture and mark/resight. The implementation of tasks associated with this objective will be coordinated with activities being conducted to achieve Objectives 1-3. The most effective and efficient sampling approach will be recommended for providing accurate population abundance estimates using the model developed through implementation of this project. Program MARK (White and Burnham 1999) will be used to develop a population abundance model incorporating data from the recommended sampling approach, survival, immigration and emigration, and probability of capture to determine an abundance estimate for coastal cutthroat trout in the study area of the lower Columbia River. The resulting model will be available for widespread use to assess habitat restoration activities of the lower Columbia River mainstem and estuary in the future as well as to assist in the management of coastal cutthroat trout. The final results and recommendations will be available in publication and online. | 10/1/2006 | 9/30/2009 | $91,250 |
Biological objectives Develop population abundance model. Implement robust sampling design. |
Metrics |
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Disseminate Raw/Summary Data and Results | Produce quarterly and annual reports on findings to date | Quarterly and annual reports will be produced to update interested parties on the progress of the proposed work. A final report will be generated following final analysis and interpretation of the complete data set. | 10/1/2006 | 9/30/2009 | $136,875 |
Biological objectives Develop population abundance model. Differentiate alternate life history strategies. Estimate fluvial movements among tributaries. Estimate straying by anadromous cutthroat. Estimate survival for coastal cutthroat trout. Implement robust sampling design. |
Metrics |
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Install Fish Monitoring Equipment | Install PIT tag antennae array | A new PIT tag antennae array will be installed on North Scappoose Creek. Antennas will be constructed as open coil inductor loops with PVC-coated multi-strand wire strung through PVC pipe. Each antenna will be connected to a Destron-Fearing reader that emits a 134.2 kHz electromagnetic energizing signal through the antenna. Readers and computers will be powered by AC power supply where available. When AC power is not available, multiple 12-V deep cycle marine batteries (60 ampere hours each) will be used and replaced with fresh batteries on a weekly basis. If feasible, a solar trickle charger will be used to extend battery life. A field PC will receive serial data output from the reader at each site; detected tag identification numbers, date and time of detection will be recorded. The readers, batteries and/or power supplies, and PCs will be housed within a weather-proof box located outside of the immediate flood zone of the streams. | 10/1/2006 | 2/28/2007 | $92,625 |
Biological objectives Differentiate alternate life history strategies. Estimate fluvial movements among tributaries. Estimate straying by anadromous cutthroat. Estimate survival for coastal cutthroat trout. |
Metrics |
Section 8. Budgets
Itemized estimated budget
Item | Note | FY07 | FY08 | FY09 |
---|---|---|---|---|
Personnel | Project Lead, GS-11 (0.75) | $44,108 | $47,934 | $52,092 |
Personnel | Project Biologist, GS-9 (0.5) | $24,303 | $26,412 | $28,703 |
Personnel | Project Techs, GS-6 (2.0) | $69,099 | $75,093 | $81,107 |
Fringe Benefits | 30% | $41,253 | $44,832 | $48,571 |
Supplies | PIT tag antennae array | $30,000 | $0 | $0 |
Supplies | GPS Receivers | $10,000 | $0 | $0 |
Supplies | Backpack electrofisher | $10,000 | $0 | $0 |
Supplies | PIT Tags | $15,000 | $15,000 | $15,000 |
Supplies | Equipment maintenance | $2,500 | $2,500 | $2,500 |
Travel | Field Work - Vehicle lease, fuel, etc. | $15,600 | $15,600 | $15,600 |
Supplies | Sampling supplies | $2,500 | $2,500 | $2,500 |
Other | Stable Isotope Analysis | $0 | $15,000 | $15,000 |
Overhead | Admin and Regional Office | $149,137 | $138,129 | $147,427 |
Totals | $413,500 | $383,000 | $408,500 |
Total estimated FY 2007-2009 budgets
Total itemized budget: | $1,205,000 |
Total work element budget: | $1,205,000 |
Cost sharing
Funding source/org | Item or service provided | FY 07 est value ($) | FY 08 est value ($) | FY 09 est value ($) | Cash or in-kind? | Status |
---|---|---|---|---|---|---|
CREST | Project coordination; Field assistance during fall electrofishing and spring smolt trapping | $5,000 | $5,000 | $5,000 | In-Kind | Confirmed |
ODFW-Corvallis Research Lab | Project coordination; Field assistance during fall electrofishing and spring smolt trapping | $5,000 | $5,000 | $5,000 | In-Kind | Confirmed |
ODFW-North Coast Watershed District | Project coordination; Field assistance during fall electrofishing and spring smolt trapping | $5,000 | $5,000 | $5,000 | In-Kind | Confirmed |
ODFW-North Willamette Watershed District | Project coordination; Field assistance during fall electrofishing and spring smolt trapping | $5,000 | $5,000 | $5,000 | In-Kind | Confirmed |
Sea Resources | Field assistance during fall electrofishing and spring smolt trapping | $5,000 | $5,000 | $5,000 | In-Kind | Confirmed |
USFWS-Abernathy Fish Technology Center | Field assistance during fall electrofishing and spring smolt trapping | $10,000 | $10,000 | $10,000 | In-Kind | Confirmed |
USFWS-Columbia River Fisheries Program Office | Project coordination; Field assistance during fall electrofishing and spring smolt trapping | $10,000 | $10,000 | $10,000 | In-Kind | Confirmed |
Volunteers | Field assistance | $10,000 | $10,000 | $10,000 | In-Kind | Confirmed |
WDFW | Field assistance during spring smolt trapping | $10,000 | $10,000 | $10,000 | In-Kind | Confirmed |
Totals | $65,000 | $65,000 | $65,000 |
Section 9. Project future
FY 2010 estimated budget: $0 FY 2011 estimated budget: $0 |
Comments: |
Future O&M costs:
Termination date: 9/30/2009
Comments:
Final deliverables: A final report will be provided to contracting agency to meet obligations of contract. Information will be disseminated to scientific community through agency final report, peer reviewed literature, and/or presentation at professional meetings. Final results will be available to scientific community, general public and contracting agency through US Fish and Wildlife Service - Columbia River Fisheries Program Office web site. Final results will provide baseline information toward habitat restoration efforts in the lower Columbia River and estuary as well as information toward refining approach to evaluating response to future habitat restoration efforts.
Section 10. Narrative and other documents
Revised narrative for proposal 200716600 | Jul 2006 |
Response to ISRP comments on proposal 200716600 | Jul 2006 |
Reviews and recommendations
FY07 budget | FY08 budget | FY09 budget | Total budget | Type | Category | Recommendation |
---|---|---|---|---|---|---|
NPCC FINAL FUNDING RECOMMENDATIONS (Oct 23, 2006) [full Council recs] | ||||||
$0 | $0 | $0 | $0 | Expense | ProvinceExpense | Do Not Fund |
NPCC DRAFT FUNDING RECOMMENDATIONS (Sep 15, 2006) [full Council recs] | ||||||
$0 | $0 | $0 | $0 | ProvinceExpense | ||
Comments: OR and WA same |
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NPCC DRAFT FUNDING RECOMMENDATIONS (Sep 15, 2006) [full Council recs] | ||||||
$0 | $0 | $0 | $0 | ProvinceExpense | ||
Comments: WA |
ISRP PRELIMINARY REVIEW (Jun 2, 2006)
Recommendation: Response requested
NPCC comments: Data on cutthroat trout in the Columbia River estuary and tributaries off the lower Columbia River are required to complement the work being done on the more numerous salmonid species, and this would help round out an ecosystem approach. There is scope for preliminary studies on tagging and migration on cutthroat but because the species is not abundant it may not be suitable as an indicator. The proposed work is related to the Fish and Wildlife Program and numerous parts of several lower Columbia subbasin plans. The proponents describe close collaboration with seven other agencies and organizations. There may be opportunities to focus the study in particular areas where restoration activities have targeted on habitat that is of particular value to this species. The proposed work should provide much needed information on the Columbia River estuary and tributary cutthroat trout populations but there are a number of methodological issues that need to be addressed: 1. More details on the proposed tagging work are required to understand the proposal: a. Given the apparent low or declining abundance of cutthroat trout, will the proposed sample size (1000 fish) for pit tagging in each tributary be achievable? Will tag retention/mortality related to pit tagging be assessed? b. What are the assumptions of the mark-recapture methodology (“Mark”) and will they be satisfied by the proposed approach? The proposal would be improved by an explanation of the sample size chosen for the mark-recapture work. Can the proponents defend the number of degrees of freedom? How will mark-recapture abundance be estimated given the possibility of multiple life histories, straying and possibly spawning in different stream in different years? What is the actual “population” whose abundance will be estimated? Is it all fish within a given stream at a given time? If so, how will movement into and out of the stream be accounted for in the estimate? c. What animal care protocols will be used to ensure the health of tagged fish? Electrofishing and trapping may harm focal (e.g., coho) or non-focal species in the streams – what precautions will be taken to avoid this? 2. What were the selection criteria used to select the four sites (lower estuary, middle estuary, upper estuary, mainstem) chosen? How do they relate to restoration sites? 3. How will it be known that fish initially captured and tagged in a stream actually spawned in that stream? How will capture efficiencies and survival rates, rates of straying, etc. be calculated (e.g., give equations or cite and briefly summarize published methods)? 4. The life history component of the study needs further development and justification. The quest for an index of cutthroat life history strategy using stable isotope analysis (SIA) is poorly described and the proposal would be improved if the proponents expanded on this aspect. Specifically, the proposal would be improved if the proponents could expand on why they chose stable isotopes of carbon and nitrogen to determine anadromy. Other workers have used strontium or other elements associated with seawater, and this could be a more effective method. There is only reference to the use of stable isotope analysis to separate anadromous and non-anadromous populations of trout and char but there are several papers and approaches on this problem in the literature. Have the proponents considered the use of tissue samples for genetic analysis to see if the populations and possibly even life history types are distinguishable? Genetic work would couple nicely with the work on straying. 5. The sponsors need to justify the reliability of using scales for aging cutthroat. What are the detailed scale and tissue sampling methods/aging methods to be used? 6. The proposal would be improved if more details on the proposed "robust sampling design" and alternative sampling approaches (multiple pass depletion, single pass mark/recapture, multiple pass mark/recapture and mark/resight) for population estimates were provided. How will these approaches be evaluated for effectiveness and efficiency? 7. The proposal would be improved if more detailed information were provided on information transfer, publication of results, plans for data and meta-data storage were described.
ISRP FINAL REVIEW (Aug 31, 2006)
Recommendation: Not fundable
NPCC comments: The ISRP agrees data on cutthroat trout in the Columbia River estuary and tributaries off the lower Columbia River are required to complement the work being done at restoration projects on the more numerous salmonid species, and this would help round out an ecosystem approach. The responses to ISRP's questions were not explicit and required reading of the revised narrative. Taking both documents into account, the proponents have addressed some questions satisfactorily. Concerns about animal care protocols, rationale for using stable isotope analysis as method to investigate life history, aging techniques, and identification difficulties were addressed satisfactorily. However, there are still major problems with the overall design and concept of the project as a scientific program to evaluate coastal cutthroat response to restoration in the estuary and lower river. On this basis, the ISRP concludes the project is not fundable. The project is unlikely to succeed for the following reasons: The species is not abundant, occupies a variety of habitats, and the life history (e.g., migration patterns) is relatively unknown, and complex, compared to other salmonids. The ISRP asked about the sample size proposed for the PIT tagging and straying work to investigate migration rates and was not convinced the sample size of 1000 fish in each tributary was adequate. The ISRP asked about the selection criteria used to identify study sites. The response mentions four widely spaced restoration sites (Lower Chinook River/Baker Bay, Blind Slough, Crims Island, and Scappoose Bay). These sites were chosen pragmatically as they are some of the larger restoration projects in the lower river and estuary. The ISRP remains concerned about the conceptual basis of actually bounding the population at these restoration sites. The ISRP asked for further details on the proposed tagging work to do this and the responses did not allay concerns about problems with the mark-recapture methodology, the assumptions behind it, and how results would be used. The sponsor’s statement, "We do not presume to identify what a population is at this time (e.g., one stream v. multiple streams). Population abundance estimates will be point estimates for a given point in time for all juvenile and adult coastal cutthroat trout in the stream at that time" is particularly troubling and indicates the population estimate objective has not been well thought out. Even if population estimates were obtained it is not clear how they would relate to the restoration projects. In addition, even in the revised narrative, details on the model MARK were not given. The ISRP should not have to dig into the literature for the information. The ISRP recognizes that investigations of alternative approaches to differentiate between alternate life history strategies in juvenile and adult coastal cutthroat trout in the lower Columbia River and estuary are needed. Some of this work may be possibly supportable by agencies concerned with basic life history and descriptive ecology of this important species.