FY 2002 Columbia Plateau proposal 199000500
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 |
---|---|
199000500 Narrative | Narrative |
199000500 Sponsor Response to the ISRP | Response |
Columbia Plateau: Columbia Lower Middle Subbasin Map with BPA Fish & Wildlife Projects | Subbasin Map |
Columbia Plateau: Columbia Lower Middle Subbasin Map with BPA Fish & Wildlife Projects | Subbasin Map |
Section 1. Administrative
Proposal title | Umatilla Fish Hatchery Monitoring and Evaluation |
Proposal ID | 199000500 |
Organization | Oregon Department of Fish and Wildlife (ODFW) |
Proposal contact person or principal investigator | |
Name | Richard W. Carmichael |
Mailing address | 211 Inlow Hall, EOU, 1410 "L" Avenue La Grande, OR 97850 |
Phone / email | 5419623777 / [email protected] |
Manager authorizing this project | Richard W. Carmichael |
Review cycle | Columbia Plateau |
Province / Subbasin | Columbia Plateau / Umatilla |
Short description | Evaluate juvenile rearing, adult survival, stock life history, straying, fish health and sport fishing and catch contribution for salmon and steelhead reared in oxygen supplemented and standard raceways at Umatilla Hatchery. |
Target species | Summer steelhead Spring and Fall Chinook Salmon |
Project location
Latitude | Longitude | Description |
---|---|---|
45.9062 | -119.4951 | Umatilla Hatchery is located on the Columbia River, Irrigon, Oregon. |
Reasonable and Prudent Alternatives (RPAs)
Sponsor-reported:
RPA |
---|
Relevant RPAs based on NMFS/BPA review:
Reviewing agency | Action # | BiOp Agency | Description |
---|---|---|---|
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
Year | Accomplishment |
---|---|
1992 | A study to evaluate rearing chinook salmon and steelhead in standard and oxygen supplemented raceways was initiated. |
1992 | Hatchery monitoring of steelhead revealed severe caudal fin erosion and led to a reduction in rearing densities. |
1992 | Fish health monitoring and evaluation began in the fall of 1991. This was the beginning of systematic documentation for pathogens and disease in the new Umatilla Hatcheries Oregon and Michigan raceways. |
1993 | Body tagging was elimiated from the tagging and marking program because it was found to be too costly and time consuming to be useful as a mass mark.. |
1993 | Determined that spring released, subyearling spring chinook had a higher level of BKD than the fall released group and some reduction in survival was anticipated. |
1993 | A comparison was made between the direct fluorescent antibody test (DFAT) and enzyme-linked immunosorbent assay (ELISA) for the detection of R. salmoninarum. At subclinical infection levels the DFAT was found to be an unreliable indicator of infection. |
1994 | More than 2.4 million fall chinook salmon were marked with blank-wire tags to improve the detection of strays at Snake River dams. |
1994 | Releases of subyearling spring chinook salmon were eliminated based on juvenile rearing evaluations. Growth and juvenile performance were significantly less than expected. |
1994 | There were significantly higher mortalities in Michigan raceways over that in Oregon raceways for the fall release fish, however no differences in mortality rates were found between upper, middle and lower Michigan raceways. |
1995 | Measurements of ATPase showed that smolts reared in standard and high density raceways developed at similar rates, but data obtained did not provide additional information on the optimum release date. |
1995 | Bacterial kidney disease infected a significant number of juvenile spring chinook salmon reared at Umatilla Hatchery. |
1995 | There was no signigicant evidence supporting horizontal transmission of R. salmoninarum between first pass and re-use water raceways at Umatilla Hatchery. |
1996 | Continued production of steelhead in O2-supplemented raceways was recommended. The production per gallon of water in Michigan raceways was 40% greater than Oregon raceways. |
1996 | Angler effort was estimated at >2900 hours and the quota of 206 spring chinook salmon was reached for the 1996 fishery. |
1996 | Samples from marked, returning adult chinook salmon were collected to make assessments of how rearing strategy might be affecting BKD and survival to adulthood. |
1997 | A study to evaluate rearing subyearling fall chinook salmon at three densities was initiated. Growth and condition were similar for fish from all raceways. |
1997 | A recommendation was made to continue wire tagging 100% of fall chinook salmon. Fifty Umatilla fish were detected at Lower Granite Dam. Five of the 50 fish that strayed escaped past the trap at Lower Granite Dam. |
1997 | More than 10% of returning adult steelhead to the Umatilla River were hatchery strays. As a result, tags from broodstock were examined prior to spawning. |
1997 | Adult spring chinook salmon reared as juveniles at Bonneville and Umatilla Hatcheries, and spawned at South Fork Walla Walla Adult Facility, exhibited low levels of R. salmoninarum. |
1998 | We recommended earlier release of the late-release group of steelhead. Survival of early-release groups averaged 0.83% compared to 0.13% for late group. |
1998 | There was no significant difference in relative survival during migration among PIT-tagged, subyearling fall chinook salmon reared at three densities. |
1999 | Radio telemetry monitoring of steelhead showed poor outmigration performance of groups released in May and management changes to improve survival were recommended. |
1999 | Infectious hematopoietic necrosis virus (IHNV) was found in 42.0% of spring chinook females spawned at South Fork Walla adult facility. |
2000 | Low smolt-to-adult survival of subyearling fall chinook prompted a temporary reduction from 2.7 million to 600 thousand smolts produced at Umatilla Hatchery. Monitoring and evaluation of lower river acclimatation and release strategies is a priority. |
Section 3. Relationships to other projects
Project ID | Title | Description |
---|---|---|
20516 | Umatilla Subbasin | Umatilla Subbasin Umbrella |
8903500 | Umatilla Hatchery O&M | Rearing facility for yearling spring chinook, subyearling fall chinook and summer steelhead released into the Umatilla River. |
8343500 | Umatilla Hatchery Satelite Facilities O&M | The satelite facilities are used for acclimation and releases of Umatilla Hatchery production, and brood stock collection for the chinook and steelhead production programs. |
8902401 | Umatilla River Juvenile Salmonid Outmigration and Survival M&E | The Juvenile Salmonid Outmigration and Survival M&E project operates and maintains the PIT-tag interogation station at West Extension Facility. The Hatchery M&E project relies on PIT-tag detection for hatchery smolt survival estimates. |
9000501 | Umatilla River Natural Production M&E | The Umatilla River Natural Production M&E provides estimates of the Umatilla Hatchery produced fish that spawn and contribute to natural production in the Umatilla River. |
Section 4. Budget for Planning and Design phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2002 cost | Subcontractor |
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Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
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Outyear budgets for Planning and Design phase
Section 5. Budget for Construction and Implementation phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2002 cost | Subcontractor |
---|---|---|---|---|
1. Determine and compare smolt-to-adult survival, life history characteristics and straying of Umatilla Hatchery reared subyearling fall chinook salmon from lower and upper river releases and acclimation strategies. | a. Coded-wire-tag 100% of the production and recover tag data to assess survival, life history information, straying and fishery contribution. | 4 | $113,482 | |
1. | b. PIT-tag salmon from each release and acclimation strategy to determine juvenile migration success in the Umatilla and Columbia Rivers. | 4 | $30,258 | |
2. Determine and compare smolt-to-adult survival, life history characteristics and straying of yearling spring chinook salmon from an overwinter, coldwater acclimation strategy and a spring acclimation strategy. | a. Coded-wire-tag 40% of the production and recover tag data to assess survival, life history information, straying and fishery contribution. | 2 | $42,909 | |
2. | b. PIT-tag salmon from each release and acclimation strategy to determine juvenile migration success in the Umatilla and Columbia Rivers. | 2 | $29,913 | |
3. Determine and compare smolt-to-adult survival, life history characteristics and straying of summer steelhead reared in Michigan raceways and released at lower and upper river sites. | a. Coded-wire-tag 40% of the production and recover tag data to assess survival, life history information, straying and fishery contribution. | 3 | $23,920 | |
3. | b. PIT tag summer steelhead from each release strategy to determine juvenile migration success in the Umatilla and Columbia Rivers. | 3 | $35,783 |
Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
---|---|---|---|
1. Determine and compare smolt-to-adult survival, life history characteristics and straying of Umatilla Hatchery reared subyearling fall chinook salmon from lower and upper river releases and acclimation strategies. | 2003 | 2005 | $457,615 |
2. Determine and compare smolt-to-adult survival, life history characteristics and straying of yearling spring chinook salmon from an overwinter, coldwater acclimation strategy and a spring acclimation strategy. | 2003 | 2003 | $75,007 |
3. Determine and compare smolt-to-adult survival, life history characteristics and straying of summer steelhead reared in Michigan raceways and released at lower and upper river sites. | 2003 | 2004 | $124,833 |
Outyear budgets for Construction and Implementation phase
FY 2003 | FY 2004 | FY 2005 |
---|---|---|
$284,553 | $215,833 | $157,069 |
Section 6. Budget for Operations and Maintenance phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2002 cost | Subcontractor |
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Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
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Outyear budgets for Operations and Maintenance phase
Section 7. Budget for Monitoring and Evaluation phase
Task-based budget
Objective | Task | Duration in FYs | Estimated 2002 cost | Subcontractor |
---|---|---|---|---|
4. Determine and compare smolt-to-adult survival, life history characteristics, straying and cost effectiveness of subyearling fall chinook salmon reared at three densities in Michigan raceways. | a. Recover coded-wire-tag data to assess survival, life history information, straying and fishery contribution. | 4 | $630 | |
4. | b. Attain hatchery records to determine growth rates and food conversion for cost effectiveness estimates | 1 | $4,115 | |
5. Determine and compare smolt-to-adult survival, life history characteristics, and cost effectiveness of subyearling fall chinook salmon reared in Michigan and Oregon raceways. | a. Recover coded-wire tag data to assess survival, life history information, straying and fishery contribution. | 1 | $630 | |
5. | b. Attain hatchery records to determine growth rates and food conversion for cost effectiveness estimates. | 1 | $4,115 | |
6. Determine and compare smolt-to-adult survival, life history characteristics and straying of yearling fall chinook salmon reared at Bonneville Hatchery and subyearling fall chinook reared at Umatilla Hatchery and released in the Umatilla River. | a. Recover coded-wire-tag data to assess survival, life history information, straying and fishery contribution. | 4 | $44,853 | |
6. | b. PIT- tag salmon from each release and acclimation strategy to determine juvenile migration success in the Umatilla and Columbia Rivers. | 4 | $13,416 | |
7. Determine and compare smolt-to-adult survival, life history characteristics, straying and cost effectiveness of yearling spring chinook salmon reared in Michigan and Oregon raceways. | a. Recover coded-wire-tag data to assess survival, life history information, straying and fishery contribution. | 3 | $630 | |
7. | b. Attain hatchery records to determine growth rates and food conversion for cost effectiveness estimates. | 1 | $4,115 | |
8. Determine and compare rearing performance, smolt condition, juvenile migration, smolt-to-adult survival, life history characteristics, and cost effectiveness of yearling spring chinook salmon from Umatilla and Little White Salmon Hatcheries. | a. Recover coded-wire-tag data to assess survival, life history information, straying and fishery contribution. | Ongoing | $630 | |
8. | b. PIT-tag salmon from each release and acclimation strategy to determine juvenile migration success in the Umatilla and Columbia Rivers. | Ongoing | $7,265 | |
8. | c. Attain hatchery records to determine growth rates and food conversion for cost effectiveness estimates. | Ongoing | $2,000 | |
9. Monitor annual recreational fishery for salmon and steelhead in the Umatilla River. | a. Estimate effort, catch, harvest, and number harvested by tag code for all recreational fisheries. | Ongoing | $69,855 | |
10. Participate in planning and coordination activities in the Umatilla basin. | a. Participate in technical work groups and task teams to ensure research findings and activities are incorporated into annual Umatilla Hatchery production plans. | Ongoing | $55,633 | |
11. Disseminate results and recommendations. | a. Prepare annual report, and peer-reviewed journal manuscripts. | Ongoing | $61,816 | |
12. Monitor and evaluate the health and disease status of salmon and steelhead reared at Umatilla Hatchery, fish transferred to acclimation facilities in the Umatilla Basin, and adult broodstock providing gametes for the Umatilla Program. | a. Monitor and evaluate the health of fish reared at Umatilla Hatchery. | Ongoing | $48,126 | |
12. | b. Prior to liberation, conduct fish health examinations | Ongoing | $9,711 | |
12. | c. Implement disease control measures and recommend adjustments to rearing strategies | Ongoing | $6,817 | |
12. | d. Monitor returning adults for R. salmoninarum. | Ongoing | $7,115 | |
13. Monitor and evaluate the health of hatchery or natural migrants from the Umatilla River. | a. Conduct fish health examinations on mortalities provided by the Umatilla River outmigration and survival project | Ongoing | $8,441 |
Outyear objectives-based budget
Objective | Starting FY | Ending FY | Estimated cost |
---|---|---|---|
4. Determine and compare smolt-to-adult survival, life history characteristics, straying and cost effectiveness of subyearling fall chinook salmon reared at three densities in Michigan raceways. | 2003 | 2004 | $2,006 |
5. Determine and compare smolt-to-adult survival, life history characteristics, and cost effectiveness of subyearling fall chinook salmon reared in Michigan and Oregon raceways. | 2002 | 2002 | $0 |
6. Determine and compare smolt-to-adult survival, life history characteristics and straying of yearling fall chinook salmon reared at Bonneville Hatchery and subyearling fall chinook reared at Umatilla Hatchery and released in the Umatilla River. | 2003 | 2005 | $185,507 |
7. Determine and compare smolt-to-adult survival, life history characteristics, straying and cost effectiveness of yearling spring chinook salmon reared in Michigan and Oregon raceways. | 2003 | 2004 | $1,317 |
8. Determine and compare rearing performance, smolt condition, juvenile migration, smolt-to-adult survival, life history characteristics, and cost effectiveness of yearling spring chinook salmon from Umatilla and Little White Salmon Hatcheries. | 2003 | 2006 | $40,393 |
9. Monitor annual recreational fishery for salmon and steelhead in the Umatilla River | 2003 | 2006 | $301,015 |
10. Participate in planning and coordination activities in the Umatilla basin. | 2003 | 2006 | $239,730 |
11. Disseminate results and recommendations. | 2003 | 2006 | $266,374 |
12. Monitor and evaluate the health and disease status of salmon and steelhead reared at Umatilla Hatchery, fish transferred to acclimation facilities in the Umatilla Basin, and adult broodstock providing gametes for the Umatilla Program. | 2003 | 2006 | $309,262 |
13. Monitor and evaluate the health of hatchery or natural migrants from the Umatilla River. | 2003 | 2006 | $36,736 |
Outyear budgets for Monitoring and Evaluation phase
FY 2003 | FY 2004 | FY 2005 | FY 2006 |
---|---|---|---|
$346,828 | $357,015 | $366,819 | $311,314 |
Section 8. Estimated budget summary
Itemized budget
Item | Note | FY 2002 cost |
---|---|---|
Personnel | $239,460 | |
Fringe | $94,757 | |
Supplies | $153,292 | |
Travel | 60% of this item is for creel surveys | $17,760 |
Indirect | $101,559 | |
Capital | $0 | |
NEPA | $0 | |
PIT tags | # of tags: 8600 | $19,350 |
Subcontractor | $0 | |
Other | $0 | |
$626,178 |
Total estimated budget
Total FY 2002 cost | $626,178 |
Amount anticipated from previously committed BPA funds | $0 |
Total FY 2002 budget request | $626,178 |
FY 2002 forecast from 2001 | $765,532 |
% change from forecast | -18.2% |
Reason for change in estimated budget
The most significant change in cost is from the temporary reduction of subyearling fall chinook production from 2.7 million to 600 thousand fish at Umatilla Hatchery. The National Marine Fisheries Service mandates 100% wire tagging of all fall chinook produced at Umatilla Hatchery, NMFS Biological Opinion, Section 7 consultation.
Cost sharing
Organization | Item or service provided | Amount | Cash or in-kind |
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Reviews and recommendations
This information was not provided on the original proposals, but was generated during the review process.
Fundable only if response is adequate
Jun 15, 2001
Comment:
Fundable if adequate responses are given to ISRP concerns. There is a need for hatchery monitoring and evaluation. However, the project should be redirected to address more pressing, current issues. The proposal produces the usual hatchery release data, smolt numbers, eggs, health checks, etc., which is required, but what of the real goal, i.e., adult returns and catch? The HGMP seems thorough however, but with conflicting goals. Note that the system produces about 50,000 wild smolts (is that near capacity?) while 150,000 hatchery steelhead smolts are released, yet the return is reported to be comprised of 25% hatchery fish. (0.08 to 0.9%, 1991 to 1995), from 110 wild and 15 hatchery broodstock (why the latter?). In other words, the returns are only just above replacement for hatchery recruitment in some years. Would it have been better to let the wild broodstock spawn naturally?
The use of oxygen has been demonstrated to increase the carrying capacity of raceways sufficiently that more returning adults will result per unit of water used. This is particularly important in the Umatilla Hatchery where the water supply is only 1/3 of what was planned for the facility. Given the experience with the use of oxygen here and elsewhere it is now time to move on to address other questions. A summary report and review of literature should be published. The SRT (1999) brought forward some guidelines for research to resolve questions about the technology and management of hatcheries. One crucial problem the SRT identified was the absence of measurement of the full contribution of individual hatcheries to fisheries and to spawning escapement. A full accounting for removals by any and all sources of mortality is needed. They also pointed out the need for more information on relative return rates of fish released at different times and or sizes, particularly in the context of the timing and size of smolts produced in the wild. More information is needed on effects of planted fish on smolts already in the stream, both as to their migratory behavior and survival. This proposal should demonstrate close coordination with # 199000501, Umatilla Basin Natural Production Monitoring and Evaluation Project.
The response should outline a process for obtaining the new kinds of data suggested by the ISRP, or a process for redirecting the emphasis of the studies. The oxygen study, if any, should be correlated with the Willamette Michigan Raceway studies.
Comment:
Comment:
Not fundable as stands. Fundable if a more detailed review of the project is provided that addresses the ISRP questions. ODFW responded to all of the ISRP questions. It would also assist reviewers if the goals were clearly stated based on a review of the available evidence and literature, presentation of available data, and with well-defined experimental designs to assess the achievement of these goals. What is the desired hatchery:wild ratio and why? Would wild adult returns remain constant (as they appear to have been from 1992 to 1999), increase, decrease or otherwise be unaffected by hatchery fish presence compared to controls? What is the number of replicates needed to answer this question? The monitoring should continue but there must be more effort in either the presentation of the evaluation process or in development of it. For example, an experiment to assess the contribution of hatchery fish to the natural spawning of summer steelhead (a goal of this proposal) may require some or all of the information that is proposed to be collected, but perhaps an alternative approach is available that addresses the numerical (abundance and survival) and biological (morphology and genetics) response, and population fitness in the longer term.Investigators in the Tucannon have concluded that supplementation does not work, and this study shows that survival of hatchery fish relative to wild is low. The latter may also degrade natural production. How do these results influence the goals and objectives of this program?
Comment:
Statement of Potential Biological Benefit to ESUAssesses the reproductive success of natural spawning hatchery fish.
Comments
Potential for also contributing to RPA 182 (assessing reproductive success of hatchery fish). MULTIPLE refers to MCR SH and MCR SCH; SR FC and SSCH
Already ESA Req? NO
Biop? NO
Comment:
A considerable amount of the research here is a comparison of different types of hatchery raceways. We need to consider whether enough knowledge has been gained given the number of years this evaluation has been funded. Before funding, ODFW and CTUIR should prepare an efficiency analysis. In addition, this project's focus has moved from evaluating the lower river facilities to assisting in tagging additional fish in a cooperative effort with CTUIR. Perhaps it's time to refocus all research in the Umatilla basin. It appears that the CTUIR and ODFW have arbitrarily divided the duties between ODFW (hatchery evaluation) and natural production (CTUIR). With the winding down of hatchery evaluations, ODFW is refocusing and is doing more 'natural production' work. This project might be fundable if a more detailed project description addressed the questions raised by the ISRP.Comment:
ISRP" Disagree - Not Fundable" recommendation for the Umatilla Fish Hatchery Monitoring and Evaluation - Project 199000500.
Evaluate juvenile rearing, adult survival, stock life history, straying, fish health and sport fishing and catch contribution for salmon and steelhead reared in oxygen supplemented and standard raceways at Umatilla Hatchery.
Staff recommendation: A determination is needed to ensure that the stated purpose for the artificial production initiative and specific goal and objectives can be assessed under the current study designs. This determination needs to be completed prior to future commitment to the program and Council staff suggests that this be conducted by the ISRP. This review needs to address not only the overarching goal of the assessment, but also the specific questions in the ISRP review (ISRP Document 2001-8). In addition the long-term outcome from the evaluation as it relates to the artificial production initiative being monitored needs to be addressed. Budget reflects the anticipation of the project Implementation and out-year-funding dependant on the review.
Council staff and ISRP will determine an approach to conduct an additional review. This will most likely will involve an additional submittal and may involve ISRP and sponsor interaction via teleconference.
Budget effect on base program (Project 199000500):
FY 2002 | FY 2003 | FY 2004 |
---|---|---|
Increase $626,178 | Increase $631,381 | Increase $572,848 |
Comment:
Comment:
Have not marked spring chinook yet, so late accrual. Project subject to programmatic issue of study design for M&E.Comment:
FY 04 increase above recommended due to greater cost of marking and tagging of spring chinook. FY05 cost increase due to COLANW 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: |
$572,848 | $572,848 | $572,848 |
Sponsor comments: See comment at Council's website