FY 2003 Mainstem/Systemwide proposal 198909600
Contents
Section 1. General administrative information
Section 2. Past accomplishments
Section 3. Relationships to other projects
Section 4. Budgets for planning/design phase
Section 5. Budgets for construction/implementation phase
Section 6. Budgets for operations/maintenance phase
Section 7. Budgets for monitoring/evaluation phase
Section 8. Budget summary
Reviews and Recommendations
Additional documents
Title | Type |
---|---|
198909600 Narrative | Narrative |
198909600 Powerpoint Presentation | Powerpoint Presentation |
198909600 Sponsor Response to the ISRP | Response |
FY 2005 Powerpoint Presentation Update for Project 198909600 | Powerpoint Presentation |
FY 2005 Powerpoint Presentation Update for Project 198909600 | Powerpoint Presentation |
Section 1. Administrative
Proposal title | Monitor and evaluate genetic characteristics of supplemented salmon and steelhead |
Proposal ID | 198909600 |
Organization | National Marine Fisheries Service, Northwest Fisheries Science Center (NMFS) |
Proposal contact person or principal investigator | |
Name | Paul Moran And Robin S. Waples |
Mailing address | 2725 Montlake Boulevard East Seattle, WA 98112-2097 |
Phone / email | 2068603245 / paul.moran@noaa.gov |
Manager authorizing this project | Jeffrey J. Hard |
Review cycle | Mainstem/Systemwide |
Province / Subbasin | Mainstem/Systemwide / |
Short description | Direct and indirect estimates for reproductive success. Estimate selection gradients in hatchery and wild. Monitor changes in hatchery, natural (supplemented), and wild (unsupplemented) populations. Evaluate effectiveness of hatchery supplementation. |
Target species | Oncorhynchus tshawytscha (chinook salmon) and O. mykiss (steelhead) |
Project location
Latitude | Longitude | Description |
---|---|---|
Snake River genetic monitoring study sites for chinook salmon and steelhead. All locations represent gene frequency monitoring sites (tier 2) unless noted as reproductive success studies (tier 3). | ||
CHINOOK SALMON | ||
IMNAHA RIVER (spr/sum) | ||
45.1858 | -116.8716 | Imnaha River facility |
45.1081 | -116.9841 | Imnaha River |
46.0718 | -116.9845 | GRANDE RONDE RIVER (spr) |
45.3034 | -117.8599 | Catherine Creek (reproductive success study) |
45.4771 | -117.4268 | Lostine River (reproductive success study) |
45.5314 | -117.7215 | Minam River |
45.9802 | -117.3834 | Upper Grande Ronde River |
45.9454 | -117.4512 | Wenaha River |
45.729 | -117.8578 | Lookingglass facility (formerly Rapid River stock, currently several locally derived stocks) |
45.729 | -117.8578 | Lookingglass Creek |
45.3783 | -115.5122 | SOUTH FORK SALMON RIVER (sum) |
44.935 | -115.4871 | Johnson Creek |
44.6587 | -115.7028 | Knox Bridge |
44.8314 | -115.7038 | Poverty Flat |
45.2297 | -115.8072 | Secesh River |
44.5893 | -115.682 | Stolle Meadows |
44.8874 | -116.1094 | McCall facility (production and conservation stocks) |
45.2972 | -114.5914 | MIDDLE FORK SALMON RIVER |
44.3853 | -115.1575 | Marsh Creek |
45.1008 | -115.3286 | Upper Big Creek |
45.1022 | -114.8535 | Lower Big Creek |
45.856 | -116.7926 | MAINSTEM SALMON RIVER |
43.8371 | -114.752 | Upper Salmon River |
44.2711 | -115.0041 | Upper Valley Creek |
44.2316 | -114.9862 | Lower Valley Creek |
44.1574 | -114.8818 | Sawtooth facility |
45.4168 | -116.3132 | LITTLE SALMON RIVER |
45.3523 | -116.3878 | Rapid River |
45.3523 | -116.3878 | Rapid River Hatchery |
STEELHEAD | ||
45.8172 | -116.7647 | IMNAHA RIVER |
45.624 | -116.9324 | Camp Creek |
45.2587 | -116.9225 | Grouse Creek |
45.1757 | -117.0323 | Lick Creek |
45.4795 | -116.9229 | Little Sheep Creek (reproductive success study) |
46.0718 | -116.9845 | GRANDE RONDE RIVER |
45.6217 | -117.6895 | Big Canyon Creek |
45.7082 | -117.1515 | Chesnimnus Creek |
45.3355 | -117.2315 | Wallowa facility |
46.5575 | -118.174 | TUCANNON RIVER |
46.5372 | -118.1597 | Lower Tucannon River |
46.2206 | -117.7082 | Upper Tucannon River |
46.5848 | -118.2249 | Lyons Ferry facility |
46.4258 | -117.0397 | Clearwater River |
46.3318 | -115.3399 | Lochsa River (Fish Cr.) |
46.0568 | -115.309 | Selway River (Gedney Cr.) |
46.5149 | -116.2939 | Dworshak facility |
Reasonable and Prudent Alternatives (RPAs)
Sponsor-reported:
RPA |
---|
179 |
180 |
182 |
184 |
199, 1036, 1193 |
Tribal Recovery Plan |
Tribal Recovery Plan |
Relevant RPAs based on NMFS/BPA review:
Reviewing agency | Action # | BiOp Agency | Description |
---|---|---|---|
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/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. |
Section 2. Past accomplishments
Year | Accomplishment |
---|---|
1993 | High levels of genetic variability documented within and among Snake River chinook salmon and steelhead populations. This variability shown to be stable through time. |
1993 | Allozyme data supported distinctiveness of Dworshak Hatchery steelhead. Distinctiveness appeared to be ancestral. Provided an improved understanding of the genetic relationship between resident fish in the NF Clearwater and the hatchery population. |
1993 | Estimation of Nm and the critical ratio of Nb/N. Results from this study provide the most comprehensive data available for salmon for these important parameter estimates (updated periodically). |
1995 | Interagency memorandum for USFW and IDFG summarizing genetic relationships among Snake River steelhead populations. |
1996 | Allozyme data played a critical role in the US v. Oregon dispute resolution. Data were provided to the Independent Scientific Review Panel for their own analyses. |
1996 | DNA markers (nonlethally analyzed) provided information on the relative distinctiveness of NE Oregon spring chinook salmon captive brood stock collections as compared to the Rapid River stock spawned at Lookingglass hatchery. |
1996 | Summary of DNA data was requested by ODFW at the outset of the NE Oregon chinook salmon captive brood program to help evaluate the genetic distinctiveness of the populations putatively identified for induction into captivity. |
1997 | Multiplex sets used to collect data for multiple studies related to genetic monitoring. Substantial reductions in time effort and expense associated with genotyping. Multiplex sets are continually expanded and improved. |
1997 | Technological developments in the rapid assay of single nucleotide polymorphisms (SNPs). Results published in peer-reviewed literature (two papers, one republished as a book chapter, a third study nearing completion). Continued efforts ongoing. |
1998 | Developed an analytical solution for the Phelps/Allendorf effect, a common sampling problem associated with the collection of juveniles when population sizes are small. Published in peer-reviewed literature. |
1998 | >95 PCR primer pairs have been made for SNP development in introns, 3' & 5' untranslated regions, random clones, and other noncoding sequences (microsatellite primers not included, see below). |
1998 | Markers and genetic results published in peer-reviewed literature (4 papers). Continued efforts ongoing. Primers distributed to other laboratories, including other researchers funded by BPA (e.g., Matt Powell's group at U of Idaho) |
1998 | Collection of microsatellite and RFLP data (five and five loci, respectively) for over 800 individual chinook salmon from nine populations in NE Oregon across 2 years (1994 and 1995). |
1998 | The geographic distribution of genetic variation revealed in this study was used extensively in the status reviews for both of these species (Busby et al. 1996, NOAA Tech Memo. NMFS-NWFSC-27; Myers et al. 1998, NOAA Tech Memo. NMFS-NWFSC-35). |
1998 | DNA data helped evaluate potential genetic distinctiveness of marked and unmarked fish returning to the trap at the Rapid River Hatchery. Interagency memo provided to Sharon Kiefer and Rick Lowell, IDFG with copies distributed to other comanagers. |
1999 | Periodically updated allozyme data shared widely among comanagers (e.g., CRITFC, Nez Perce, USFWS, Warm Springs, ISRP). |
1999 | Groups of six to twelve microsatellite markers (multiplex sets) developed and implemented in both chinook salmon and steelhead, permitting rapid and efficient genotyping. >90 microsatellite primer pairs made. |
1999 | Non-lethal allozyme genotyping of frozen adult fin clips (peer-reviewed publication) |
1999 | New restriction site markers developed for nuclear DNA loci. Used to describe genetic structure of selected Snake River populations. |
1999 | Collection, DNA extraction, and genotyping (nine loci) of 80 adult steelhead passed over the Little Sheep Creek weir. |
1999 | Collection of 300 juvenile steelhead from dispersed sites above the Little Sheep Creek weir. DNA extraction and genotyping of 24 juvenile steelhead (smaller sized fish likely to be age 0+) for nine loci. |
1999 | Little Sheep microsatellite data used for preliminary power analyses for parentage identification and evaluation of reproductive success. A second multiplex set of eight loci is being added in FY2000. |
1999 | Development of DNA extraction and genotyping of historic scale samples. Methodological experiments completed, published in peer-reviewed literature. |
2000 | Collection, DNA extraction, and genotyping of microsatellite and RFLP loci (9 and 5, respectively) for ~48 steelhead individuals from each of 13 Snake River populations representing four major river drainages. |
2000 | Tissue samples taken for genetic monitoring since 1989 and logged into the archive at NWFSC represent a major component of the largest tissue repository available for Columbia River Pacific salmon (>20,000 samples). |
2000 | Essentially all samples collected through 1998 have been analyzed for allozyme variation. Over 6,500 samples have been DNA-extracted and genotyped. A variety of tissue samples have been made available to collaborators and co-managing agencies. |
2001 | Developed "allele ladders" for both chinook and steelhead to facilitate the interlaboratory standardization of microsatellite data. |
2001 | Determined that it will be difficult or impossible to extract DNA from scales without significantly damaging the scale and likely compromising it's value for subsequent analysis (e.g., laser ablation microelement analysis). |
2001 | Constructed pedigrees and estimated selection gradients for hatchery and natural steelhead spawning above the weir on Little Sheep. Presented preliminary results of parentage analysis at a meeting of comanagers in LaGrande, Oregon April, 2002. |
2002 | Completion of the most comprehensive genetic data set available for Snake River steelhead (includes allozyme, SNP, and microsatellite loci). Population structure and mixed fishery results submitted for publication, distributed to comanagers. |
2002 | Developed an "interagency multiplex" for chinook incorporating 18 of the most widely used, robust, and easily scored microsatellite loci from laboratories coastwide (run in 4 dye colors). Also includes a marker for sex determination. |
2002 | Nearly a thousand chinook salmon were screened for the above interagency loci, including populations from throughout the Columbia River and for coastal populations from Alaska to the Sacramento Valley. |
Section 3. Relationships to other projects
Project ID | Title | Description |
---|---|---|
199226100 | Early life history study of Grande Ronde Basin chinook salmon (ODFW) | We coordinate genetic sampling with sampling from this study. |
199005200 | Performance/stock productivity impacts of supplementation (NBS) | We have shared steelhead samples from this study and we provide NBS results of our genetic analyses for some of their study streams. |
198909800 | Idaho natural production and evaluation (IDFG) | We coordinate genetic sampling with sampling from this study. |
199107300 | Intensive monitoring subproject; ISS (IDFG) | We coordinate genetic sampling with sampling from this study. |
199005500 | Steelhead Supplementation Studies In Idaho Rivers (IDFG) | We coordinate genetic sampling with collections for this program. |
199801001 | Grande Ronde sp. chinook captive broodstock program (LSRCP/NPT/ODFW) | We coordinate genetic sampling with collections for this program. |
198805301 | NE Oregon outplanting facilities plan (NPT) | Sampling is coordinated with this program. |
198805305 | NE Oregon outplanting facilities plan (ODFW) | Sampling is coordinated with this program. |
198805300 | NE Oregon sp. chinook hatchery planning (NPT/ODFW) | We coordinate genetic sampling with this program. |
198712700 | Smolt monitoring by Fish Passage Center (NPT) | Sampling will be coordinated with this program. |
199606700 | Manchester captive broodstock O&M (NMFS) | We coordinate genetic sampling with this program. |
199009300 | Genetic Analysis of Oncorhynchus nerka (Modified to include Chinook Salmon) | We have traded DNA samples and PCR primers with this project, as well as carrying on an ongoing dialog regarding methods and marker classes. |
198900702 | Grande Ronde Supplementation - O&M/M&E | Adult sampling will be coordinated with this project |
Section 4. Budget for Planning and Design phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2003 cost | Subcontractor |
---|---|---|---|---|
1. Collect samples | b. Obtain appropriate collection permits and complete collection reports (NMFS Sec 10 permit and USFWS Sec 7 consultation will require modifications for expansion of reproductive success studies) | 5 | $2,500 |
Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
---|---|---|---|
1. b. Obtain appropriate collection permits and complete collection reports | 2004 | 2007 | $6,370 |
Outyear budgets for Planning and Design phase
FY 2004 | FY 2005 | FY 2006 | FY 2007 |
---|---|---|---|
$1,500 | $1,560 | $1,620 | $1,690 |
Section 5. Budget for Construction and Implementation phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2003 cost | Subcontractor |
---|---|---|---|---|
1. Collect samples | a. Consult comanagers and conduct preseason evaluations of previous year escapements to identify optimal sampling strategy | 5 | $1,500 | |
1. | b. Obtain appropriate collection permits and complete collection reports | 5 | $3,300 | |
1. | c. Coordinate sampling efforts to maximum extent possible with other ongoing projects | 5 | $2,100 | |
1. | d. Collect samples from hatchery, natural, wild, and captive populations, including historical scales | 5 | $175,800 | Yes |
2. Conduct genetic analyses | a. Perform genotyping and DNA sequencing (includes purchase of an additional ABI 3100 electrophoresis instrument) | 5 | $239,900 | |
2. | b. Perform quality control tests on preliminary data | 5 | $11,000 | |
2. | c. Cooperate with other laboratories in data standardization, development of new genetic markers | 5 | $29,500 | |
3. Measure levels of genetic variation in each population | a. Quantify percent polymorphic loci, heterozygosity, number of alleles per locus | 5 | $2,300 | |
3. | b. Compare values in hatchery, natural, and wild populations | 5 | $1,500 | |
3. | c. Evaluate pattern of change in genetic variability over time | 5 | $1,500 | |
4. Estimate effective population size (Ne) and the ratio Ne/N for each population | a. Compute F, a measure of temporal change in allele frequency | 5 | $2,000 | |
b. Compute r^2, a measure of gametic disequilibrium | 5 | $1,000 | ||
4. | c. Use temporal and disequilibrium methods to obtain a combined estimate of Ne for each population | 5 | $4,200 | |
4. | d. Estimate total population size (N) based on redd counts, spawner surveys, or population enumeration | 5 | $1,000 | |
4. | e. Compute ratio Ne/N | 5 | $1,000 | |
5. Describe population genetic structure of natural and wild populations | a. Compute indices of genetic differentiation among natural and wild populations | 5 | $2,000 | |
5. | b. Perform hierarchical gene diversity analyses to partition genetic differences into various components (e.g., spatial and temporal) | 5 | $5,200 | |
5. | c. Estimate levels of gene flow among populations based on genetic data | 5 | $2,000 | |
6. Document genetic effects and selective forces associated with supplementation in both target and non-target populations | a. Identify parents of parr collected above the weir from the pool of potential parents passed upstream, conduct parallel analyses in the hatchery | 5 | $40,200 | |
6. | b. Compare results with theoretical expectations derived using both probabilistic and deterministic models | 5 | $3,800 | |
6. | c. Estimate the relative reproductive success of hatchery and wild fish | 5 | $8,700 | |
6. | d. Compare indices of genetic differentiation between hatchery, natural, and wild populations | 5 | $2,000 | |
6. | e. Compare patterns of genetic change over time in hatchery populations with those in natural and wild populations | 5 | $3,100 | |
6. | c. Publish characterization of spatial and temporal genetic differences between hatchery and natural populations, as well as estimated selection gradients, and including consideration of accuracy and precision | 5 | $28,200 |
Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
---|---|---|---|
1. Collect samples | 2004 | 2007 | $806,900 |
2. Conduct genetic analyses | 2004 | 2007 | $575,900 |
3. Measure levels of genetic variation in each population | 2004 | 2007 | $23,400 |
4. Estimate effective population size (Ne) and the ratio Ne/N for each population | 2004 | 2007 | $40,600 |
5. Describe population genetic structure of natural and wild populations | 2004 | 2007 | $40,630 |
6. Document selective forces and genetic effects of supplementation on target and non-target populations | 2004 | 2007 | $82,100 |
Outyear budgets for Construction and Implementation phase
FY 2004 | FY 2005 | FY 2006 | FY 2007 |
---|---|---|---|
$439,700 | $457,300 | $475,600 | $493,600 |
Section 6. Budget for Operations and Maintenance phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2003 cost | Subcontractor |
---|---|---|---|---|
Not applicable | $0 |
Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
---|
Outyear budgets for Operations and Maintenance phase
Section 7. Budget for Monitoring and Evaluation phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2003 cost | Subcontractor |
---|---|---|---|---|
7. Evaluate effectiveness and utility of various genetic monitoring methods | a. Evaluate combined power of genetic markers (DNA+allozymes) to provide monitoring and evaluation information that is useful for an adaptive management approach to supplementation. | 5 | $3,100 | |
7. | b. Evaluate power and utility of exclusion versus probablistic approaches to parentage assignment, as well as discrete and fractional assignment in estimating selection gradients | 5 | $3,700 | |
7. | c. Explore sources of variation and establish confidence limits on parentage assignment (e.g., number of loci, level of polymorphism, genotyping error rates, percentage of missing parents, etc.) | 5 | $4,600 | |
7. | d. Provide recommendations (in peer-reviewed literature) regarding alternative analytical methods for the measurement of gene flow/detection of migrants | 5 | $7,200 |
Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
---|---|---|---|
7. Evaluate effectiveness and utility of various genetic monitoring methods | 2004 | 2007 | $82,100 |
Outyear budgets for Monitoring and Evaluation phase
FY 2004 | FY 2005 | FY 2006 | FY 2007 |
---|---|---|---|
$19,300 | $20,100 | $20,900 | $21,800 |
Section 8. Estimated budget summary
Itemized budget
Item | Note | FY 2003 cost |
---|---|---|
Personnel | FTE: 1.15 | $76,700 |
Fringe | 24% of personnel | $18,400 |
Supplies | $63,000 | |
Travel | $9,700 | |
Indirect | 51.2% + 9.5% of personnel | $46,600 |
Capital | $150,000 | |
NEPA | $2,500 | |
PIT tags | $0 | |
Subcontractor | Sampling of adults and smolts (CTUIR, NPT, ODFW), lab service contracts, waste disposal | $227,000 |
Other | $0 | |
$593,900 |
Total estimated budget
Total FY 2003 cost | $593,900 |
Amount anticipated from previously committed BPA funds | $0 |
Total FY 2003 budget request | $593,900 |
FY 2003 forecast from 2002 | $253,000 |
% change from forecast | 134.7% |
Reason for change in estimated budget
The budget for this project increases at this time because of the addition of two critically important studies of the reproductive success in wild, conventional and captive broodstock chinook salmon spawning in Lostine River and Catherine Creek. We also propose expansion of the steelhead reproductive success research in Little Sheep Creek to including fitness study of the hatchery broodstock and the recording of digital images of all adults ($15k) for morphometric analysis. We also request a smolt trap in Little Sheep Creek ($115k/year) to provide an additional samping point for evaluating differential parr-to-smolt survival. The volume of samples to be genotyped for this study exceeds the capacity of our current instruments and will reguire an additional ABI 3100 capillary electrophoresis unit ($150k, one-time cost, FY03 only).
Reason for change in scope
We have tracked genetic changes in the Lostine River and Catherine Creek popultions since 1989 and 1990, respectively. We find however, that interpretation of those allele frequency data is complicated by variable returns and highly variable proportions of hatchery spawners. Hatchery fish are certainly contributing to natural production, but the extent to which they are interbreeding with wild fish remains unclear. There is now the opportunity to apply the technology we have already demonstrated in Little Sheep Creek steelhead to these important chinook populations. By creating pedigrees in natural and hatchery populations we will provide specific information regarding the success or failure of supplementation efforts and perhaps also an understanding of the biological reasons for that success or failure.
Cost sharing
Organization | Item or service provided | Amount | Cash or in-kind |
---|---|---|---|
Not applicable | $0 | cash |
Other budget explanation
This budget reflects a major shift in commitment of funds toward DNA-related reseach relative to the allozyme markers that have been the cornerstone of this project since its inception in 1989. In Part 2 we explain our division of effort between DNA and allozymes and between the new pedigree-based research and more traditional allele frequency monitoring. DNA technology has matured to the point that it can fill both its new role in parentage determination and quantitative genetic analysis, as well as an ongoing role in future allele frequency monitoring studies. We propose continuation of limited allozyme sampling over approximately 3-year intervals from at least some locations. This limited sampling will permit continued utility of the substantial Snake River allozyme data set, a virtually unbroken genetic record going back to the late 1980s for many of the most threatened Snake River populations. All other future sampling for this study will employ nonlethal fin clips. Increased costs in this budget cycle result from ambitious expansion of the current pedigree-based research in Little Sheep Creek steelhead and implementation of two new similar studies in chinook salmon (Lostine River and Catherine Creek). We propose continuation and expansion of multibasin allele frequency monitoring with DNA markers because we believe the allele frequency monitoring provides a broader geographic and programatic perspective to genetic monitoring (see Part 2 for detail).
Reviews and recommendations
This information was not provided on the original proposals, but was generated during the review process.
Fundable - no response required
Aug 2, 2002
Comment:
Fundable, no response needed. This is an excellent, important, and well-written proposal. Summary statements of findings were provided showing significant progress over the history of the project. Several papers based on the results have been published in peer-reviewed journals, which indicate acceptance of the work by the scientific community. The study continues to make an important contribution to the understanding of the genetic structure of Columbia River anadromous salmonids.Expansion of the budget is explained and justified. It includes both an actual expansion of the data collection and lab analysis to the Lostine River, Catherine Creek, and Little Sheep Creek steelhead, as well as expanding the project to include the development of pedigree analysis and a strategy shift to increasing reliance on microsatellite DNA analysis rather than allozyme analysis. In particular, the latter change is justified and warranted. Shifting to the pedigree/paternity analysis is needed in order to investigate the more subtle effects of hatchery/wild fish interactions through supplementation to which the allozyme results were relatively insensitive. Microsatellite DNA pedigree analysis should be insightful for this purpose. At the same time, continuing the allozyme data collection at a base level is warranted in order to retain continuity of data over time (nearing two decades).
This proposal is well written and the researchers have maintained a very high level of scientific productivity. We would like the project sponsors to consider the following few comments:
- Our most basic concern is for the scope and size of this one project. The proposal provides very little in terms of numbers of samples taken, capability for timely processing of these samples, and technical basis of the sample sizes. The tier 2 sample sizes seem particularly small, but no basis for the determinations of these samples was provided.
- Section 9, page 16, Methods states that the captive brood chinook will not be sampled for DNA "because family-specific success data are already available through segregated rearing, marking, and enumeration." It is not evident from this statement whether that family-success is based on breeding programs or a different DNA sampling task? If these fish have not been sampled for DNA and are released into Catherine and Lostine rivers they could not be included in the pedigree analyses. This point should be clarified to ensure there is no oversight.
- Section 9, page 12 Objective 1 Assumption. The authors suggest only partial sampling of potential parents can be compensated for by increasing samples sizes of offspring or the number of loci used. Increased sample size could improve precision, but we do not see how sample size alone can compensate for unknown parental genotypes? Increasing the number of loci sampled may assist if there are differences detected that are useful, but they also may not. The intention of this comment should be clarified.
- Two major cost items included were a new ABI 3100 capillary electrophoresis unit ($150k, one-time cost, FY03 only) and the provision of an additional smolt weir in the Imnaha system ($115K). There is essentially no justification for these major expenses, what are the consequences of not funding? Is the smolt trapping coordinated (and agreed) with by others in the basin and why is it essential?
Action Agency/NMFS RME Group Comments:
HARVEST AND HATCHERY SUBGROUP -- Address critical element of RPA? Relevant to both RPAs. The proposal applies to RPA 182, since it includes the study of reproductive success. Little Sheep steelhead portion addresses this RPA well.
The proposal applies to RPA 184, as well. It relates to conservation hatcheries as a recovery tool (and the extent to which it might contribute). Some hatchery reforms are directed at reducing gene flow from hatchery fish to wild fish.
Scope? [ESU's covered, Transferability, Species covered] Target species are chinook salmon and steelhead. It covers most of an ESU and two listed species. Results should be broadly applicable.
Study design adequate, as is, or as may be modified? Regarding Sheep Creek, the data presented at the captive brood workshop showed limited success at assigning parentage, an issue that requires further discussion with investigators. This may be exacerbated for steelhead, where the genetic exchange with resident fish may be fluid, and where precocial and resident males are likely to contribute genetically. In general, good use of techniques available to determine contribution at this time. Incorporates latest genetic technology plus parentage analysis. This may provide the most powerful insight to relative fitness of hatchery vs. wild spawners.
It resembles some of the M&E programs addressing genetic effects from hatcheries - it describes basic genetic metrics (Ne, Fst, etc.), then tracks change over time. Continues long genetic data set, giving this special monitoring/evaluation value. For chinook, good monitoring for supplemented versus unsupplemented areas in the Grande Ronde (although straying into unsupplemented areas has occurred, and will cloud results).
ISRP Remarks on RME Group Comments:
The RME group comments on 198909600 are consistent with the ISRP's review comments. The BPA comments regarding Sheep Creek and the data presented at the captive brood workshop which showed limited success at assigning parentage, may be an issue that requires further consideration by the investigators. As noted in the RME group comments, the issue may be exacerbated for steelhead, where the genetic exchange with resident fish may be fluid, and where precocial and resident males are likely to contribute genetically.
Comment:
There has been a substantial increase in the funding level.Comment:
In summary, it was clear to the project sponsors early in the proposal process that funds would be extremely tight in this cycle. Therefore, they drafted a lean study that is tightly integrated and simply does not have room for budget reductions without significant sacrifices in the central goals of the project. For detailed comments refer to the full response to CBFWA.Comment:
Fundable. We agree with the CBFWA review and the Urgent priority ranking. This is an excellent, important, and well-written proposal. The researchers have maintained a very high level of scientific productivity. A response was not needed; however, the project sponsors subsequently responded thoughtfully to the preliminary ISRP review comments.The proposal provided summary statements of findings that showed significant progress over the history of the project. Several papers based on the results have been published in peer-reviewed journals, which indicate acceptance of the work by the scientific community. The study continues to make an important contribution to the understanding of the genetic structure of Columbia River anadromous salmonids.
Expansion of the budget is explained and justified. It includes both an actual expansion of the data collection and lab analysis to the Lostine River, Catherine Creek, and Little Sheep Creek steelhead, as well as expanding the project to include the development of pedigree analysis and a strategy shift to increasing reliance on microsatellite DNA analysis rather than allozyme analysis. In particular, the latter change is justified and warranted. Shifting to the pedigree/paternity analysis is needed in order to investigate the more subtle effects of hatchery/wild fish interactions through supplementation to which the allozyme results were relatively insensitive. Microsatellite DNA pedigree analysis should be insightful for this purpose. At the same time, continuing the allozyme data collection at a base level is warranted in order to retain continuity of data over time (nearing two decades).
If funded, this project should be coordinated with other monitoring projects to ensure compatibility of objectives, common methods, and protocols. This coordination could be accomplished under the favorably reviewed CBFWA proposal #35033.
Comment:
Statement of Potential Biological BenefitIndirect. Will evaluate the genetic effects of outplanting hatchery reared fish on natural and wild populations of spring/summer chinook salmon and steelhead in the Snake River Basin.
Comments
NMFS proposal. Inappropriate to comment.
Already ESA Required?
No
Biop?
Yes
Comment:
Category:1. Council Staff preferred projects that fit province allocation
Comments:
Comment:
Steelhead objective within this project on Little Sheep Creek is priority. Could be reduced in scope. Spring/summer chinook objectives may be redundant with Tucannon River spring/summer chinook objectives in proposal 35027. Budget consistent with NPCC recommendation.Comment:
NW Power and Conservation Council's FY 2006 Project Funding Review
expense
May 2005
FY05 NPCC start of year: | FY06 NPCC staff preliminary: | FY06 NPCC July draft start of year: |
$460,500 | $460,500 | $460,500 |
Sponsor comments: See comment at Council's website