BPA Fish and Wildlife FY 1997 Proposal
Section 1. Administrative
Section 2. Narrative
Section 3. Budget
see CBFWA and BPA funding recommendations
Section 1. Administrative
Title of project
Colville Tribal Fish Hatchery
BPA project number 8503800
Business name of agency, institution or organization requesting funding
Colville Confederated Tribes
Sponsor type WA-Tribe
Proposal contact person or principal investigator
Name | Kirk Truscott | |
Mailing address | Colville Confederated Tribes
P.O. Box 150 Nespelem, WA 99155 | |
Phone | 509/634-8845 |
BPA technical contact Marcella Lafayette, EWP 503/230-3781
Biological opinion ID Long term O&M agreement
NWPPC Program number 10.8B.2
Short description
The Colville Tribal Fish Hatchery is located in the blocked area above Chief Joseph and Grand Coulee Dam and is a resident fish substitution measure as partial mitigation for anadromous fish losses due to the Federal hydropower system. The program goal is to produce 22,679 kg (50,000 lbs.) of resident fish that include brook trout, rainbow trout and lahontan cutthroat trout. All the fish will be released into reservation waters, including boundary waters in as effort to provide a successful subsistence/recreational fishery for Colville Tribal members as well as a successful non-member sport fishery. The majority of the fish distributed are intended to provide a “carry-over” fishery. Fish from this program are intended to be capable of contributing to the natural production component of the reservation fish populations. Contribution to the natural production component will be achieved by producing and releasing fish of sufficient quality and quantity to survive to spawning maturity, to spawn in existing and future available habitat while meeting other program objectives. Hatchery stocking efforts and operational procedures will help enhance broodstock sources for all three species reared at the hatchery by stocking high quality fish and allowing natural selection to influence the population over time. The broodstock sources will be of natural lake origin (i.e. not on-station captive brood).
Project start year 1989 End year 2039
Start of operation and/or maintenance 1989
Project development phase Maintenance
Section 2. Narrative
Related projects
N/A
Project history
This project is a long-term O&M project (25 year agreement between BPA and Colville Tribe) and was previously funded under O&M agreement # DE-MS79-88BP92434.
Biological results achieved
This program has met the production goal (22,679 kg) for every year of operation.
The stocking efforts from the hatchery have maintained at least maintained the CPUE and condition factor of fish caught in the sport and subsistence fishery since the termination of the USFWS stocking efforts (Winthrop National Fish Hatchery). The brook trout fishery in Twin Lakes and Owhi Lake have improved substantially since the first stocking from the Colville Tribal Fish Hatchery as has the lahontan cutthroat trout fishery in Omak Lake.
The development of the rainbow trout broodstock program has yet to be realized partly due to our cautious approach to utilizing the SanPoil River stock ( genetic and disease precautions). The Tribe is however gaining knowledge of current broodstock potential from other reservation sources as well as the SanPoil River stock (i.e. adult spawning escapement and stocking efforts.
Annual reports and technical papers
An Annual Operating Plan is developed for each year of operation detailing goals and objectives, production and outplanting plans, broodstock development activities, monitoring activities, projected hatchery operations, annual operating budget and water quality and quantity criteria to be supplied at the hatchery.
An annual production/operations report is completed each year detailing the past years operation and the progress towards the goal. This reporting was not required until FY-96, however the Tribe believed it should be part of the program requirements to evaluate the programs progress towards the goal and objectives.
In addition to the above reporting requirements the Tribe will now begin to submit quarterly reports as to the programs progress and activities.
Management implications
Artificial stocking efforts can and do contribute to creel catches of resident fish, particularly in closed lake systems subject to substantial fishing pressure and limited natural production capabilities.
Monitoring and evaluation should be a part of all hatchery production programs.
The goal of hatchery programs should not be to produce only a given amount for fish, but to provide a fish that will satisfy specific management objectives, such as CPUE’s, high quality fish in the creel, low mortality during hatchery rearing, good conversion to creel, contribution to the natural production component ( in some circumstances)
Specific measureable objectives
(1) Produce 22,679 kg of resident fish
(2) CPUE 1.0 fish/Hr. of greater (subsistence fishery)
(3) CPUE .8-1.0 fish/Hr. or greater (sport fishery)
(4) Rainbow trout C values greater than 5,500 X 10-7
(5) Brook trout C values greater than 5,500 X 10-7
(6) lahontan cutthroat trout C values greater than 4,500 X 10-7
(7) Increase natural production for rainbow trout by 15% by the year 2010
(8) Increase natural production of brook trout by 10% by the year 2010
(9) Obtain 130,000 rainbow trout eggs from reservation brood source by 2000
(10) continue the experimental otolith marking program (M&E)
(11) Perform otolith recovery efforts (M&E)
(12) Develop and utilize a pre-release fish condition index (M&E)
(13) Provide rearing conditions that lessen the occurrence of bacterial, viral and parasitic infestations.
(14) Monitor and enumerate adult adfluvial rainbow trout in selected tributaries as well as other spring spawning stocks within the reservation.
Testable hypothesis
The successful completion of actions associated with the aforementioned objectives. Asuccessful subsistence and sport fishery must utilize both hatchery and natural production components to achieve long-term viability.
Underlying assumptions or critical constraints
Adequate funding will continue to be made available to successfully operate the facility.
Current creel census provided by the tribe will continue and used to help monitor the fishery.
Thermal otolith marking becomes viable method of mark - recovery to access the hatchery contribution to the fishery as well as natural production.
Anglers (subsistence and sport) exhibit similar tendencies in future years as they have in past years.
Reservation waters and watersheds remain in current condition of improve in the future.
Methods
Culture techniques standard for the profession with the water source being single pass. Contribution to the hatchery will be analyzed using standard angler creel surveys. Otoliths will be collected during the creel surveys and with standard horizontal gillnet surveys. Statistical analysis will be used to determine significance of contribution to the fishery of various groups of fish (statistical method undetermined at this time). All fish will be resident salmonids (brook trout, lahontan cutthroat trout and rainbow trout). For more detail on hatchery operations, otolith marking, creel census and species number/distribution refer to the Colville Tribal Hatchery Annual Operating Plan # 88BI92434.
Brief schedule of activities
Distribution of fingerling brook trout, rainbow trout and lahontan cutthroat trout (March - May 1997)
Lahontan cutthroat trout spawning (April - May 1997)
Monitor adult rainbow trout escapement (March - June 1997)
Distribution of legal size rainbow trout (April 1997)
Distribution of sub-catchable brook trout and rainbow trout (October - December 1997)
Brook trout spawning (November 1997)
Otolith marking of brook and rainbow trout (December - January 1997)
Creel census surveys (April - October 1997)
Gillnet surveys (June 1997)
Development/negotiation of AOP and budget ( March - June 1997)
Annual production/operations report ( December 1997 )
Quarterly progress reports
Biological need
The Colville Tribe was and still is a fishing culture and relied heavily upon the salmon resources of the Columbia River. The Construction of Grand Coulee Dam completely blocked the historic migrations of anadromous fish the this area. This project partially mitigates for the loss of anadromous fish in the blocked area. The freshwater environment that remains can not supply the demand for fish and fishing opportunities or the biomass to compensate for the loss of anadromous fish via natural production. Artificial production and increased natural production (supplementation) can provide substantial numbers of fish and fishing opportunities while partially mitigating for anadromous fish losses.
Critical uncertainties
What size hatchery fish contributes to the fishery ( both creel and natural supplementation ) to the individual lakes and streams of the reservation?
What are the acceptable maximum stocking rates for individual water bodies on the reservation?
Will the hatchery program successfully trap sufficient numbers of spring spawning rainbow trout ( adfluvial stock) to supply the rainbow trout egg requirement?
Summary of expected outcome
(1) Produce 22,679 kg of resident fish
(2) CPUE 1.0 fish/Hr. of greater (subsistence fishery)
(3) CPUE .8-1.0 fish/Hr. or greater (sport fishery)
(4) Rainbow trout C values greater than 5,500 X 10-7
(5) Brook trout C values greater than 5,500 X 10-7
(6) lahontan cutthroat trout C values greater than 4,500 X 10-7
(7) Increase natural production for rainbow trout by 15% by the year 2010
(8) Increase natural production of brook trout by 10% by the year 2010
(9) Obtain 130,000 rainbow trout eggs from reservation brood source by 2000
Dependencies/opportunities for cooperation
AOP development/negotiation
Prioritization process
Unforeseen/emergency maintenance at the facility
Risks
None
Monitoring activity
Creel census activities and gillnet surveys will be the basis to monitor and evaluate the success of the hatchery contribution to the fishery. Adult enumeration, spawning ground and juvenile production surveys will provide the basis for broodstock development and natural production component of the program. Fish health monitoring and fish health index will be utilized to monitor the relative health of the fish prior to distribution. Otolith mark and recovery efforts through creel and gillnrt surveys will be utilized to determine the most appropriate size of fish to stock for maximum potential in the fishery (creel) and to meet natural production (supplementation) objectives.
Section 3. Budget
Data shown are the total of expense and capital obligations by fiscal year. Obligations for any given year may not equal actual expenditures or accruals within the year, due to carryover, pre-funding, capitalization and difference between operating year and BPA fiscal year.Historic costs | FY 1996 budget data* | Current and future funding needs |
1985: 94,777 1986: 340,492 1987: 49,571 1988: 3,499,437 1989: 390,072 1990: 278,926 1991: 303,668 1992: 293,382 1993: 311,972 1994: 286,477 1995: 289,491 1996: 333,961 |
Obligation: 0 Authorized: 335,000 Planned: 335,000 |
1997: 350,000 1998: 355,000 1999: 360,000 2000: 365,000 2001: 370,000 |
* For most projects, Authorized is the amount recommended by CBFWA and the Council. Planned is amount currently allocated. Contracted is the amount obligated to date of printout.
Funding recommendations
CBFWA funding review group Resident Fish
Recommendation Tier 1 - fund
Recommended funding level $350,000
BPA 1997 authorized budget (approved start-of-year budget) $350,000