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Proposal Number:
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RMECAT-2010-030-00 | |
Proposal Status:
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Pending BPA Response | |
Proposal Version:
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Proposal Version 1 | |
Review:
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RME / AP Category Review | |
Portfolio:
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RM&E Cat. Review - RM&E | |
Type:
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Existing Project: 2010-030-00 | |
Primary Contact:
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Dave Fast (Inactive) | |
Created:
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5/27/2010 by (Not yet saved) | |
Proponent Organizations:
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Washington Department of Fish and Wildlife (WDFW) Yakama Confederated Tribes |
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Project Title:
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Project to provided VSP Estimates for Yakima Steelhead MPG | |
Proposal Short Description:
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This proposal expands 199506325 RM&E activities to address significant gaps in estimates of abundance, productivity, spatial structure, and diversity for Yakima steelhead populations. | |
Proposal Executive Summary:
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This proposal expands RM & E activities conducted by the co-managers in the Yakima Basin (Yakama Nation and Washington Department of Fish and Wildlife) to better evaluate VSP parameters (abundance, productivity, spatial structure, and diversity) for Yakima steelhead populations. It was developed to fill critical monitoring gaps identified in the 2009 Columbia Basin monitoring strategy review and the FCRPS Biological Opinion RPA review. This proposal builds upon the infrastructure and monitoring capacities of the YKFP umbrella M&E project (199506325). Data from this project will be used to evaluate population status and trends, inform NOAA status reviews and implementation of the FCRPS Biological Opinion, and address critical uncertainties (e.g., the relationship between resident and anadromous life histories in the Upper Yakima and Naches populations), consistent with the NPCC Fish and Wildlife program, Columbia Basin research plan (uncertainties 3.1, 7.1 & 7.3), NOAA mid-Columbia steelhead recovery plan, and Fish Accords. The improved understanding of steelhead population performance produced by this project will directly inform efforts to recover steelhead populations in the Yakima Basin. Specific proposed activities include: 1. Increased biological and DNA sampling at the Chandler juvenile, and Prosser and Roza adult monitoring facilities (Abundance, Productivity), 2. Adult radio telemetry tagging at Prosser and Roza facilities and subsequent tracking throughout the Yakima Basin (Abundance, Productivity, Spatial Structure), 3. Increased PIT tagging and detection throughout the Yakima Basin (Abundance, Productivity, Spatial Structure), 4. Evaluation of flow and entrainment relationships at the Chandler (Prosser) Diversion Dam to refine steelhead smolt outmigration estimates (Abundance and Productivity), 5. Analysis of existing and additional steelhead DNA samples to improve the genetic profile for all four populations in the MPG (Abundance, Productivity, Diversity, Spatial Structure), 6. Expand spawner surveys and redd counts for steelhead populations (Spatial Structure), 7. Evaluate interactions in the upper Yakima between resident rainbow and steelhead trout (Diversity, Productivity). This project addresses reasonable and prudent alternatives (RPAs) 50 and 62 in the FCRPS biological opinion. |
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Purpose:
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Programmatic | |
Emphasis:
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RM and E | |
Species Benefit:
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Anadromous: 100.0% Resident: 0.0% Wildlife: 0.0% | |
Supports 2009 NPCC Program:
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No | |
Subbasin Plan:
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Fish Accords:
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None | |
Biological Opinions:
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Populations of wild steelhead Oncorhynchus mykiss in the Columbia River Basin have declined dramatically from historical levels (Nehlsen et al. 1991; NRC 1996; Williams et al. 1999). Average abundance of wild steelhead in the Yakima River Subbasin over the last two decades is only 2% of pre-1890 abundance levels reported by Howell et al. (1985). Causes of these declines include a host of environmental and human-induced factors (NRC 1996; Williams et al. 1999, YBFWRB 2009). Stocks originating in mid-Columbia Basin tributaries including the Yakima River were listed as threatened in 1999 (64 FR 14517-14528). No hatchery fish have been released in the Yakima Subbasin since 1993. Regional plans recognize the need to protect and enhance weak upriver steelhead populations and their habitat while maintaining the genetic integrity of those stocks (NPPC 1994).
Steelhead in the Yakima Basin are divided into four populations: the Satus Creek, Toppenish Creek, Naches River, and Upper Yakima River populations. The NOAA Interior Columbia Technical Recovery Team (ICTRT) identifies:
Together these four populations make up the Yakima MPG.
Estimates of the number of adult steelhead returning to the Yakima Basin prior to European settlement range from 20,800 to 100,000 (YBFWRB 2009). In contrast, the number of adults passing fish counting facilities at Prosser Dam (on the mainstem Yakima downstream of virtually all current spawning locations) between 1985 and 2006 has ranged from 450 to 4,491 with an average of 1,764. The ICTRT estimated the 10-year (1996 to 2005) geometric average by population as 379 for the Satus population, 322 for the Toppenish population, 472 for the Naches population, and 85 for the Upper Yakima.
The ICTRT modeled the extent of historically available steelhead habitat. Steelhead spawning is widely distributed throughout the areas accessible to them, except in the lower Yakima River and its tributaries below the Satus Creek confluence. The extent and distribution of spawning in the mainstem from the Columbia to Roza Dam is uncertain. Steelhead currently cannot access the watersheds above Tieton, Bumping, Cle Elum, Kachess, and Kecheelus Dams and a number of significant tributaries (e.g., Wenas, Manastash, and Naneum creeks in the Upper Yakima population area, and until just last year, Cowiche Creek in the Naches population area).
The Yakama Nation and WDFW have emphasized maintaining the natural genetic composition of Yakima Basin steelhead stocks. The last release of hatchery-origin juvenile steelhead in the Yakima Basin occurred in 1993. Stray hatchery-origin fish from other basins made up only 3% of the run from 1999 to 2005.
Instead of dying immediately after spawning like most salmon, steelhead can survive, return to the ocean, and spawn again. The Yakama Nation is currently capturing post-spawning steelhead (i.e., kelts) at Prosser Dam and reconditioning them in hatchery facilities to increase the number that survive to spawn again.
Our knowledge of steelhead status in the upper portions of the basin is complicated by the fact that steelhead and rainbow trout are different forms of the same species that can interbreed. Better understanding of the historic, current, and future potential for steelhead production in these areas will require determining how habitat conditions, intra-specific interactions, genetics, and survival rates for oceangoing smolts interact to affect the balance between resident and anadromous life histories.
The ICTRT assessed the viability of Yakima Basin steelhead populations and concluded that none currently meet its standards for viability. The Satus population comes nearest to meeting the ICTRT’s standard, while the Upper Yakima population is farthest from the standard. The ICTRT analysis is based on NOAA Fisheries’ Viable Salmonid Population
(VSP) framework, which calls for managing salmon and steelhead populations based on an understanding of their abundance, productivity, spatial structure, and diversity.
Significant resources are being expended to implement on-the-ground recovery actions aimed at improving the viability of the Yakima Steelhead MPG. Resource and land use managers are faced with the challenges of protecting functioning habitats in the face of increased development and climate change. Improved estimates of steelhead population performance and how it responds to these restoration and protection efforts will be required in order to guide future recovery investments.
While some data have been collected on steelhead during ongoing spring Chinook research, monitoring and evaluation (RM & E) activities under the YKFP, significant gaps in most VSP parameters exist for every steelhead population in the major population group. This project seeks to expand existing RM&E work to fill those gaps. It relies on ongoing support for activities already funded via 199506325 and the YKFP program (e.g. operation of fish counting facilities and adult and juvenile fish traps).
Current estimates of steelhead VSP parameters for the Yakima MPG are limited for the following reasons:
1) Steelhead abundance (i.e., run size) is determined at Prosser Dam, but only at the MPG level.
2) No reliable spawner abundance estimates of individual populations exist.
3) Spatial structures of Naches and Upper Yakima populations are unknown.
4) Influence of resident O. mykiss in upper Yakima and Naches is unknown.
5) No estimates of juvenile productivity exist for any population.
6) Limited understanding of the relationship between life stage survival rates and habitat limiting factors.
This proposal uses the methodologies and infrastructure developed under the YKFP M & E umbrella project (199506325) to evaluate VSP parameters for steelhead.
Determine spatial distribution & spawning areas (OBJ-1)
Determine spatial distribution and major (MSA) and minor (MiSA) spawning areas of steelhead spawning populations in the Yakima MPG.
Estimate juvenile and adult abundance (OBJ-2)
Estimate juvenile and adult abundance for individual populations
Generate productivity estimates (OBJ-3)
Generate productivity estimates for individual populations
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Characterize life-history traits (OBJ-4)
Characterize and differentiate phenotypic and genotypic life-history traits within and among Yakima steelhead populations
Evaluate sympatric population dynamics (OBJ-5)
Evaluate sympatric population dynamics and the effects on population viability between resident and anadromous forms of O.mykiss
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To view all expenditures for all fiscal years, click "Project Exp. by FY"
To see more detailed project budget information, please visit the "Project Budget" page
Expense | SOY Budget | Working Budget | Expenditures * |
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FY2019 | $525,107 | $493,888 | |
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BiOp FCRPS 2008 (non-Accord) | $523,000 | $491,906 | |
General - Within Year | $2,107 | $1,982 | |
FY2020 | $538,000 | $569,408 | $508,229 |
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BiOp FCRPS 2008 (non-Accord) | $569,408 | $508,229 | |
FY2021 | $569,408 | $569,408 | $501,285 |
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BiOp FCRPS 2008 (non-Accord) | $569,408 | $501,285 | |
FY2022 | $569,408 | $569,408 | $379,337 |
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BiOp FCRPS 2008 (non-Accord) | $569,408 | $379,337 | |
FY2023 | $569,408 | $569,408 | $690,272 |
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BiOp FCRPS 2008 (non-Accord) | $569,408 | $690,272 | |
FY2024 | $594,462 | $594,462 | $573,109 |
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BiOp FCRPS 2008 (non-Accord) | $594,462 | $573,109 | |
FY2025 | $594,462 | $594,462 | $311,578 |
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BiOp FCRPS 2008 (non-Accord) | $594,462 | $311,578 | |
* Expenditures data includes accruals and are based on data through 31-Mar-2025 |
Cost Share Partner | Total Proposed Contribution | Total Confirmed Contribution |
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There are no project cost share contributions to show. |
Annual Progress Reports | |
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Expected (since FY2004): | 32 |
Completed: | 28 |
On time: | 28 |
Status Reports | |
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Completed: | 134 |
On time: | 78 |
Avg Days Late: | 17 |
Count of Contract Deliverables | ||||||||||||||
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Earliest Contract | Subsequent Contracts | Title | Contractor | Earliest Start | Latest End | Latest Status | Accepted Reports | Complete | Green | Yellow | Red | Total | % Green and Complete | Canceled |
BPA-5546 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2010 | 09/30/2011 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
52040 | 55510, 56662 REL 9, 56662 REL 46, 56662 REL 67, 56662 REL 87, 56662 REL 133, 56662 REL 158, 56662 REL 186, 56662 REL 207, 56662 REL 237, 56662 REL 254, 56662 REL 280, 56662 REL 307, 96889 | 2010-030-00 EXP PROJECT TO PROVIDE VSP ESTIMATE | Yakama Confederated Tribes | 10/15/2010 | 04/30/2026 | Pending | 60 | 155 | 0 | 0 | 3 | 158 | 98.10% | 2 |
50628 | 54906, 59895, 64137, 66986, 70353, 75719, 74314 REL 31, 74314 REL 63, 74314 REL 94, 74314 REL 125, 74314 REL 158, 84042 REL 28, 84042 REL 61, 84042 REL 97 | 2010-030-00 EXP PROJECT TO PROVIDE VSP ESTIMATE | Washington Department of Fish and Wildlife (WDFW) | 11/01/2010 | 03/31/2026 | Issued | 62 | 120 | 0 | 0 | 0 | 120 | 100.00% | 2 |
BPA-6179 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2011 | 09/30/2012 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
46273 REL 39 | 46273 REL 65, 46273 REL 84 | 2010-030-00 EXP NOAA VSP YAK R STEELHEAD | National Oceanic and Atmospheric Administration | 03/15/2012 | 03/31/2015 | Closed | 12 | 13 | 0 | 0 | 0 | 13 | 100.00% | 0 |
BPA-6948 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2012 | 09/30/2013 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-7745 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2013 | 09/30/2014 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-8149 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2014 | 09/30/2015 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-8940 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2015 | 09/30/2016 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-9541 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2016 | 09/30/2017 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-10027 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2017 | 09/30/2018 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-10777 | PIT Tags/Readers - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2018 | 09/30/2019 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-11711 | PIT Tags - VSP Estimates for Yakima Steelhead | Bonneville Power Administration | 10/01/2019 | 09/30/2020 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-12095 | FY21 Pit Tags | Bonneville Power Administration | 10/01/2020 | 09/30/2021 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-12916 | FY22 PIT tags | Bonneville Power Administration | 10/01/2021 | 09/30/2022 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-13272 | FY23 PIT Tags | Bonneville Power Administration | 10/01/2022 | 09/30/2023 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-13825 | FY24 PIT tags | Bonneville Power Administration | 10/01/2023 | 09/30/2024 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
BPA-14186 | FY25 PIT Tags | Bonneville Power Administration | 10/01/2024 | 09/30/2025 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
Project Totals | 134 | 288 | 0 | 0 | 3 | 291 | 98.97% | 4 |
View full Project Summary report (lists all Contracted Deliverables and Quantitative Metrics)
Explanation of Performance:Assessment Number: | 2010-030-00-NPCC-20230316 |
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Project: | 2010-030-00 - Yakima Steelhead VSP Project |
Review: | 2022 Anadromous Fish Habitat & Hatchery Review |
Approved Date: | 4/15/2022 |
Recommendation: | Implement |
Comments: |
Bonneville and Sponsor to take the review remarks into consideration in project documentation. [Background: See https://www.nwcouncil.org/2021-2022-anadromous-habitat-and-hatchery-review/] |
Assessment Number: | 2010-030-00-ISRP-20230323 |
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Project: | 2010-030-00 - Yakima Steelhead VSP Project |
Review: | 2022 Anadromous Fish Habitat & Hatchery Review |
Completed Date: | 3/23/2023 |
Final Round ISRP Date: | 2/10/2022 |
Final Round ISRP Rating: | Meets Scientific Review Criteria |
Final Round ISRP Comment: | |
The Yakima Steelhead VSP Project provides valuable information for tracking the viability of ESA-listed steelhead in the Yakima subbasin while also evaluating the effects of critical factors such as flow and habitat quality in the Yakima River mainstem, climate change, survival in the mainstem Columbia and at sea, and the important contribution of resident trout to steelhead production. This steelhead VSP project is closely aligned with the 199506325 Yakima Klickitat Fisheries Project - Monitoring and Evaluation, and other Yakama Nation projects, but it is a separate project at the request of BPA. This project strives to track steelhead population trends in relation to ESA recovery goals. Overall, this is a strong project that shows adaptive decision making and application of advanced analytical protocols. This project provides important data collection and analyses including telemetry, PIT-tag detection arrays, and life-cycle modeling to monitor and assess steelhead escapement and outmigration survival for all four populations of the Yakima subbasin. The direct connection with gathering VSP data to supply information needs for assessing Yakima steelhead MPGs makes this proposal highly relevant to the recovery of Middle Columbia River Steelhead. The proponents recognize the importance of steelhead and trout density, which expresses a strong relationship. For example, the project annual report states that productivity appears to peak at about 1,000 to 1,500 spawners and declines at higher spawner abundances. This information could be used to evaluate changes in steelhead capacity in response to ongoing restoration efforts in the subbasin. The project report notes problems with aging of steelhead in the past, which is critical for evaluating productivity trends in response to environmental stressors. M&E matrix - support. As habitat projects and monitoring projects are not presented as part of an integrated proposal or plan, the need for a crosswalk to identify the linkages between implementation and monitoring is extremely important for basins or geographic areas. The ISRP is requesting a response from the Yakima Basin Habitat Project (199705100) to summarize the linkages between implementation and monitoring projects in the Yakima River basin. During the response loop (September 24 to November 22, 2021), as a key M&E project and partner in the basin, we ask your project to assist them in creating the summary and provide information to them about what, where, and when your monitoring occurs and what is being monitored for and shared with implementation projects in the basin. A map or maps of locations of monitoring actions would be helpful in this regard. To strengthen future proposals, annual reports, and work plans, the proponents should address and include the following elements:
Q1: Clearly defined objectives and outcomes The vision for this project is to provide long-term population monitoring for steelhead in the Yakima MGP and to document their status relative to recovery objectives. Specific recovery objectives are outlined in the Yakima Steelhead Recovery Plan and in the Middle Columbia Steelhead Recovery Plan. The minimum delisting threshold is to achieve a 10-year average spawner abundance of greater than 500, 250, 1500, and 500 fish for the Status, Toppenish, Naches, and Upper Yakima populations, respectively. In addition, two of the populations should achieve a “viable” rating. The remaining populations should at minimum, be rated as “maintained” in their status assessments. The proposal provides an excellent summary of past work and outcomes, which formed a solid basis for understanding the future direction of the project. The ISRP commends the definitive and direct connection of their work with recovery goals of Yakima MGPs for steelhead and the Middle Columbia River Steelhead Recovery Plan. Explicit statements of the project’s Goal and Objectives are not provided. Instead, the reader is referred to other and more generalized documents for these important ingredients. While at the grand scale the objectives are to see certain levels of steelhead abundance, productivity, etc., this project's objectives are not to help populations achieve this but to monitor how they are doing. The proponents should provide an appropriate number of stated Objectives with a description of the expected outcomes on an annual basis for the next five years (e.g., re-runs of models with an additional year of data, reports produced). The following is an example of a SMART Objective (X=1,2,3,….N) coupled with a set of Implementation Objectives: Objective X. Document status and trends of adult steelhead abundance by MPG on an annual basis. Implementation Objective X.1. Generate an annual adult abundance with Coefficient of Variation (CV) for each MPG from the available data. Implementation Objective X.2. Conduct analyses to assess status and trends of adult steelhead abundance by MPG on an annual basis using all available years of data available. Key monitoring actions for population-level monitoring include 1) documenting status/trend of natural-origin spawners, 2) determining proportion of hatchery-origin returns, 3) documenting age structure, 4) determining harvest mortality, and 5) understanding the influence of population supplementation efforts. Q2: Methods This is a well-established monitoring and evaluation project for steelhead. The introductory information on outcomes produced is excellent. The discussion provides a broad and complete description of information needs, which includes 1) adult and juvenile life history status and trend monitoring, 2) use of the DABON patch occupancy model, 3) a disentangling of the genetic and environmental drivers by modeling the survival and migration histories of PIT tagged O. mykiss, 4) an analysis to evaluate how the proposed action changes water flows throughout the Yakima basin during outmigration, and 5) survival relationships to estimate steelhead survival in seven contiguous river reaches from Roza Dam on the Yakima River to McNary Dam on the Columbia River. The proposal does not provide a description of methods to be used associated with each SMART objective (also lacking—see above). The methods provided are incomplete summaries of what the proponent plans to do over the next five years, and the reader is referred to protocols under the PNAMP website rather than describing them in the proposal at hand. A number of protocols are referenced, as is the monitoring guidance document issued by NMFS for monitoring of ESA-listed salmonids. Additional description of the overall sampling strategy for monitoring VSP would have been useful in the proposal to show how the overall effort worked together to provide VSP metrics. For example, residence time (age) of steelhead in fresh water and at sea is key for documenting productivity (smolts per spawner; adult return per spawner), but aging methods are not described. The project report notes that age was not determined every year (at least in the past) and average age is used when developing recruitment curves. This approach will affect trends, as noted by the proponents. Aging methodology should be described. An earlier ISRP review raised questions about adequate sample sizes. The ISRP finds few details on sample sizes in this proposal or much in the way of details about other methods. There is considerable discussion of PIT tagging but not much in the way of details other than locations. The proposal references Project 199506325 for methods, but relevant methods are not covered by that project. Q3: Provisions for M&E This VSP monitoring and evaluation project is closely aligned with the YKFP and benefits from the management structure of the larger YKFP project. The YKFP management structure includes a Monitoring and Implementation team (MIPT) made of project specialists from both internal project staff as well as external entities (Tribal, State, Federal, higher ed, and private). The MIPT group reviews project progress annually and advises the project on issues of concern, project implementation, and technical matters. The project participates in the annual YKFP internal project reviews. The project disseminates project information to a wide audience by submitting annual technical reports that are published on the Columbia Basin Fish & Wildlife Website, peer reviewed literature, and via numerous oral presentations at professional/scientific conferences and meetings. The proponents describe a process that should allow for adjustments to the project. For example, the proponents show model results of how climate change may impact the probability of O. mykiss emigration (i.e., steelhead) while also showing how a 10% improvement in habitat conditions may offset adverse climate impacts. The project proponents have nimbly adjusted their project actions to meet a full spectrum of information needed for tracking status and trends of steelhead in the Yakima subbasin. The proponents are to be commended on their climate change analysis and how they used EDT to incorporate scenarios for different climate changes. The proponents clearly work hard at refining methods and making adjustments. One of the things that would be helpful is a table that summarizes how they are measuring (and what they are measuring) for the VSP parameters. For example, adult spawner distribution is only one of the ways to look at spatial structure. One can also use distribution of juvenile rearing, and this could be done at the population level or the MPG looking at all four populations at once. Same thing with diversity, for example, diversity can be biological or genetic or related to habitat conditions. Mapping of life history trajectories should consider estuary and ocean as well. Q4: Results – benefits to fish and wildlife The project provides both qualitative life history information and quantitative data regarding abundance and productivity of steelhead in relation to quantitative recovery goal objectives. Key metrics include adult natural and hatchery-origin steelhead for the subbasin and in select tributaries (no hatchery steelhead released since 1993), juvenile abundance and productivity, spatial distribution, and diversity. Using genetic analyses, the project has demonstrated significant contributions of resident O. mykiss to steelhead production, especially in years when SARs are low. However, smolts that include one or two resident parents tend to have lower survival, potentially a result of past hatchery stocking of trout that have lower fitness in nature. Recent abundance trends (return years 2018-2021) show a significant, persistent decline in nearly all steelhead populations in the Yakima subbasin. Although survival at sea is an issue, the project also shows adverse effects of regulated flows on smolt survival from Roza Dam to McNary Dam. The proponents report encouraging production potential for the upper Yakima steelhead population when favorable environmental conditions are encountered, and they suggest recovery delisting thresholds are achievable. However, the findings also indicate the severity and consequential effects that low outmigration survival (mainstem Yakima River) can have on adult abundance, particularly if migratory smolts encounter less than favorable Columbia River conditions and/or ocean conditions simultaneously. Poor survival across the migratory and ocean rearing life-stages highlights the importance of achieving or maintaining habitat quality and quantity in the Yakima subbasin to sustain a high level of intrinsic freshwater productivity, which may allow for population persistence and resiliency against major environmental perturbations. The ISRP commends the project for its application of telemetry, PIT-tag detection arrays, and a life-cycle model to monitor and assess steelhead escapement and outmigration survival in all four populations. The direct connection with gathering VSP data to supply information needs for assessing Yakima steelhead MPGs makes this proposal highly relevant to the recovery of Middle Columbia River Steelhead. Furthermore, the degree of past documentation of approach and outcomes is exemplary and serves as an important guide for other work in the Columbia River Basin. The project examined PIT tags versus radio tags for estimating steelhead abundance values in four tributaries. With greater sampling and tagging rate for PIT tagging vs. radio tagging, the expanded population estimates for PIT tags provided a higher level of precision compared to the radio-tagged expanded estimates. With the instream PIT-tag arrays performing at a high level, the project adopted the use of these and added additional PIT-tag arrays for the purpose of long-term steelhead abundance monitoring at the population scale. Does this mean that radio tags are no longer deployed so that funding can be used for other issues? It would be useful to see greater coordination effort between the proponents of this proposal and the proponents from Washington Resource Conservation and Development and their proposal (200739800) for tributary access and habitat improvement. There is likely much mutual benefit to plan and work together to understand direct effects of the fish passage and habitat projects. For example, the installation of PIT-tag detectors and PIT tagging aligned with the boundaries and influence of these projects will go a long way to understand the benefits of the work. |
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Documentation Links: |
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Assessment Number: | 2010-030-00-ISRP-20100622 |
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Project: | 2010-030-00 - Yakima Steelhead VSP Project |
Review: | Fast Track ISRP Review 2010 |
Completed Date: | None |
First Round ISRP Date: | 2/24/2010 |
First Round ISRP Rating: | Response Requested |
First Round ISRP Comment: | |
This proposal addresses several key uncertainties relative to population structure of Yakima River steelhead/rainbow population but this proposal lacked some details about methods - specifically, sample sizes, specific study locations, and the division of labor among cooperators. A revised proposal narrative providing this information is necessary to conduct a complete scientific review. The following modifications of the proposal are necessary for the ISRP to complete its review: 1) More information is required on the relationship of this project to ongoing efforts. A very clear description of how this project addresses specific RPA commitments is required. Some discussion of the relationship to the ISEMP work that is taking place in neighboring subbasins and to steelhead recovery efforts in the adjacent Wenatchee subbasin also should be added. 2) Information should be provided to specifically indicate how this project addresses gaps not addressed by project #19956325. Inclusion of a more detailed presentation of the results generated by project #19956325 to date would provide a much stronger justification for this project that is provided in the current proposal. 3) An indication of the number of samples to be collected for each work element, and some rationale as to why the project proponents feel this number of samples will be adequate, should be included in the proposal. 4) Provide more detail on the design and methods of the radio telemetry study for adult steelhead (Biological Objective 1). 5) Include more detail on the proposed GSI work including study design, number of samples and genetic markers types. 6) Provide a clear indication of the allocation of responsibilities among the organizations participating in this study. 1. Technical Justification, Program Significance and Consistency, and Project Relationships The justification for this project is framed in terms of existing recovery programs for steelhead in the Yakima River subbasin, but it needs to be more tightly linked to RPAs in the BiOp. It appears that this project generally responds to BiOp RPA 50 and 62, but the description of how this project will contribute to these RPAs is insufficient. Quite a few projects are listed as being related to this one but only in the most general way. A more thorough description of how this project will coordinate and share data, especially with project #199506325 should be included. The proposal also does not acknowledge the ISEMP work that is taking place in neighboring subbasins. It would have been helpful to discuss how this project relates to steelhead recovery efforts in the adjacent Wenatchee subbasin. 2. Project History and Results This is a new project, but it proposes to build on work that has been previously conducted in the Yakima watershed or is ongoing, especially project #199506325. A more thorough review of the results from project #199506325 would have given a more complete indication of the “gaps” in the current effort and provided a more compelling justification for this project. 3. Objectives, Work Elements, and Methods The proposal provides a reasonable description of the work that will be done for some of the objectives; however, there is insufficient information provided on a number of work elements to enable technical review. Failure to specify sampling effort for many of the work elements is a common issue. The number of fish to be fitted with radio transmitters, the numbers to be PIT-tagged, or the number of samples to be obtained for genetic analysis are often not provided in the proposal and when provided, little indication is given as to why this level of sampling effort is sufficient to answer the questions being asked. This deficiency makes it difficult for the ISRP to evaluate the adequacy of the sampling protocols. Obtaining adequate samples in a river system as large as the Yakima presents some daunting challenges. An indication of the number of samples to be collected for each work element, and some rationale as to why the project proponents feel this number of samples will be adequate, should be included in the proposal. For example, under work task 2B (calculate entrainment rates) it is stated that a pilot study will use acoustic tags and arrays to increase the precision of irrigation canal entrainment, but there are no details given regarding where this would take place or a ballpark figure of the number of acoustically tagged steelhead that will be needed. The Work Elements in Biological Objective 1 (Determine spatial distribution and major (MSA) and minor (MiSA) spawning areas of steelhead spawning populations in the Yakima MPG (RPA 50.6, 62.5)) require some additional elaboration. The radio telemetry study design and specific methods to be used are not well described. For example the proponents state that "We propose to conduct a three year radio telemetry project in the Yakima River Basin (upstream of Prosser Dam). We will use methods similar to those described in Karp et al. (2009)." A thorough description of these methods in the proposal, or at least a link to this document, is needed. It also is not clear why it was decided that 450 - 500 adult steelhead would be tagged. As noted above, some rationale as to why this number of tags was considered appropriate for this task should have been presented. Also, given that the average number of adult steelhead returning to the Yakima in recent years is 1,764 fish, this number of tags represents a significant proportion of the total population. As these fish are part of an ESA-listed ESU, it seems that there might be some concern about handling this many fish. No indication was given as to whether or not the required permits had been obtained for this activity. Also, an indication of how frequently ground surveys for acoustic tags (Work Element 1a) will be conducted should be included. The work proposed for GSI was also not described in sufficient detail to enable a thorough technical review. The discussion of GSI in the proposal is pretty generic. In addition to the problem noted above regarding a lack of specificity and justification on numbers of samples, more detail on marker types (microsats or SNPs) and details of the sampling design needs to be included in the proposal. Also, the Anderson et al (2008) and Kalanowski (2007) papers cited in the text are not included in the citations. Finally, it was unclear which organization would have the responsibility for the various aspects of field data collection or data analyses. Section I (key personnel) gives a list of the project staff members but does not identify their involvement in the various work elements of this project. More detail should be included regarding the division of labor. |
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Documentation Links: |
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Assessment Number: | 2010-030-00-NPCC-20110627 |
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Project: | 2010-030-00 - Yakima Steelhead VSP Project |
Review: | RME / AP Category Review |
Proposal: | RMECAT-2010-030-00 |
Proposal State: | Pending BPA Response |
Approved Date: | 6/10/2011 |
Recommendation: | Fund (Qualified) |
Comments: | See Programmatic issue #2. Also see Fast Track April-May 2010 Council decision. |
Conditions: | |
Council Condition #1 Programmatic Issue: RMECAT #2 Habitat effectiveness monitoring and evaluation—1 | |
Council Condition #2 Per Fast Track April-May 2010 Council decision - The Council recommends this project for implementation. This recommendation is based on the condition that the capacity issue is resolved in contracting. In addition, the linkages to other projects are to be addressed in a form of an addendum as part of the RM&E/Artificial Production Category Review. |
ID | Title | Type | Period | Contract | Uploaded |
P123255 | Resident/Anadromous O. mykiss Interactions Studies in the Upper Yakima Basin, Washington | Progress (Annual) Report | 11/2010 - 10/2011 | 50628 | 10/11/2011 3:42:58 PM |
P126465 | Yakima Steelhead Viable Salmonid Population (VSP) Status and Trends Monitoring; 10/15/10 - 12/14/11 | Progress (Annual) Report | 10/2010 - 12/2011 | 52040 | 5/9/2012 12:10:05 PM |
P126934 | Yakima Steelhead Viable Salmonid Population (VSP) Monitoring: Resident/Anadromous Interactions | Progress (Annual) Report | 11/2011 - 10/2012 | 6/12/2012 1:46:27 PM | |
P129955 | Yakima Steelhead Viable Salmonid Population (VSP) Monitoring: Resident/Anadromous Interactions; 11/10 - 10/11 | Progress (Annual) Report | 11/2010 - 10/2011 | 54906 | 1/7/2013 7:39:34 AM |
P129970 | Yakima Steelhead VSP Status & Trends Monitoring;10/10 - 10/11 | Progress (Annual) Report | 10/2010 - 10/2011 | 55510 | 1/7/2013 10:59:19 AM |
P132992 | Yakima Steelhead VSP Project: Resident/Anadromous Interactions Monitoring | Progress (Annual) Report | 11/2011 - 10/2012 | 59895 | 7/29/2013 3:29:18 PM |
P136505 | Yakima Steelhead VSP Project: Resident/Anadromous Interactions Monitoring | Progress (Annual) Report | 01/2013 - 12/2013 | 64137 | 4/22/2014 10:23:49 AM |
P137985 | Yakima River Steelhead Population Status and Trends Monitoring; 10/11 - 10/12 | Progress (Annual) Report | 10/2011 - 10/2012 | 56662 REL 46 | 8/11/2014 10:41:23 AM |
P142746 | Yakima Steelhead Project: Resident/Anadromous Interactions Monitoring | Progress (Annual) Report | 01/2014 - 12/2014 | 66986 | 4/16/2015 8:55:17 AM |
P143527 | Yakima River Steelhead Population Status and Trends Monitoring; 10/12 - 10/14 | Progress (Annual) Report | 10/2012 - 10/2014 | 56662 REL 67 | 6/1/2015 1:50:43 PM |
P148507 | Yakima Steelhead VSP Project: Resident Anadromous Interactions Monitoring | Progress (Annual) Report | 01/2015 - 12/2015 | 70353 | 3/15/2016 2:58:13 PM |
P153378 | Yakima Steelhead VSP Project: Resident/Anadromous Interactions Monitoring; 1/16 - 12/16 | Progress (Annual) Report | 01/2016 - 12/2016 | 70353 | 3/9/2017 11:18:16 AM |
P153716 | Yakima River Steelhead Population Status and Trends Monitoring; 10/14 - 10/15 | Progress (Annual) Report | 10/2014 - 10/2015 | 56662 REL 87 | 3/31/2017 1:06:04 PM |
P159723 | Yakima Steelhead VSP Project: Resident/Anadromous O. mykiss Status and Trend Monitoring | Progress (Annual) Report | 01/2017 - 12/2017 | 75719 | 3/15/2018 1:31:03 PM |
P164724 | Yakima Steelhead VSP Project; 1/18 - 12/18 | Progress (Annual) Report | 01/2018 - 12/2018 | 56662 REL 158 | 4/2/2019 12:29:52 PM |
P171973 | Yakima Steelhead VSP Project; 1/19 - 12/19 | Progress (Annual) Report | 01/2019 - 12/2019 | 74314 REL 63 | 3/31/2020 12:41:55 PM |
P171974 | Yakima Steelhead VSP Project; 1/19 - 12/19 | Progress (Annual) Report | 01/2019 - 12/2019 | 56662 REL 186 | 3/31/2020 12:49:54 PM |
P175809 | Resident/Anadromous O. mykiss Interactions Studies in the Upper Yakima Basin, Washington | Photo | - | 5/7/2020 5:44:05 PM | |
P175810 | Resident/Anadromous O. mykiss Interactions Studies in the Upper Yakima Basin, Washington | Photo | - | 5/7/2020 5:44:05 PM | |
P191080 | Yakima River Steelhead Population Status and Trends Monitoring | Progress (Annual) Report | 01/2020 - 12/2020 | 56662 REL 207 | 3/24/2022 11:25:25 AM |
P191505 | VSP_Annual_Report_2021_Final | Progress (Annual) Report | 01/2021 - 12/2021 | 56662 REL 237 | 4/12/2022 10:11:01 AM |
P197147 | Yakima Steelhead VSP Project: Resident/Anadromous O. mykiss Status and Trends Monitoring | Progress (Annual) Report | 01/2022 - 12/2022 | 74314 REL 158 | 1/30/2023 3:33:47 PM |
P208462 | Yakima Steelhead VSP Project: Annual Report 2023 | Progress (Annual) Report | 01/2022 - 12/2023 | 56662 REL 280 | 4/11/2024 8:45:56 AM |
Project Relationships: | None |
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Additional Relationships Explanation:
Funding source -- Project ID -- Project Title -- Relationship
BPA -- 199506325 -- Yakima Klickitat Fisheries Project - Monitoring and Evaluation - Yakima Basin -- Umbrella RME project in Yakima Basin that has collected (and will continue to collect) much of the baseline information relevant to this project.
BPA -- 198812025 -- YKFP Management, Data, and Habitat -- Core management and Administrative Support Services for all YKFP Tasks; includes habitat restoration and data management activities
BPA -- 199603501 -- Yakama Reservation Watersheds Project -- This is a watershed scale restoration project intended to protect and enhance habitat for the native threatened summer steelhead stock, and a variety of cultural and
natural resources.
BPA -- 199701325 -- Yakima Klickitat Fisheries Project - Operations and Maintenance - Yakima Basin -- This proposal supports O & M for facilities used in this project.
BPA -- 200001700 -- Recondition Wild Steelhead Kelts -- Continue to test and evaluate methods to recondition steelhead kelts, generate science-based management recommendations, and assist in their implementation to rebuild wild steelhead populations throughout the Columbia Basin. A large part of this work is conducted in the Yakima Subbasin.
BPA -- 200306200 -- Evaluate Reproductive Success Kelt Steelhead -- This evaluation program is designed to investigate the reproductive success of hatchery-reared, natural-origin, and reconditioned kelt steelhead Oncorhynchus mykiss in three different evolutionary significant units (Upper Columbia, Mid Columbia, and Snake River) under natural conditions. The two major goals are 1)directly examine reproductive success in several streams; and, 2)replicate and evaluate kelt reconditioning procedures and protocols at a variety of locations. A large part of this work is conducted in the Yakima Subbasin.
Work Classes
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Work Elements
RM & E and Data Management:
70. Install Fish Monitoring Equipment157. Collect/Generate/Validate Field and Lab Data 158. Mark/Tag Animals 162. Analyze/Interpret Data |
For the juvenile PIT tagging study associated with the resident/anadromous component of our proposal, we selected our sample size based upon 1) the number of fish that could feasibly be captured and tagged in the various stream reaches, and 2) statistical power to detect differences in life history expression associated with this sample size. Preliminary power analysis indicates the minimum detectable difference in the proportions of anadromous juveniles versus resident fish produced in the Middle Fork Teanaway River is approximately 1.7% in 2 years (a=0.05, B=0.1). We used the observed number of PIT tagged O. mykiss detected at some downstream interrogation station (migrant) divided by the total number of PIT tags deployed the previous year to generate an index of the proportion of steelhead versus resident fish production in the Middle Fork Teanaway River (we did not partition tags to correct for cohort structure, however, similar numbers of fish were tagged for 4 consecutive years). We subjected the data to the arcsine square root transformation to satisfy parametric test assumptions (ZAR 1999). We then used equation 8.23 as presented in ZAR (1999) to determine the minimum effect size we could detect given our sample data with a maximum Type I error rate established as 0.05, and maximum Type II error rate as 0.10 (Power = 0.90). The result from the computation was transformed back to a proportion following equation 13.6 in Zar (1999). The results we observed suggest we have adequate power to detect fairly small shifts in the life history proportions present in our tributary streams.
Name (Identifier) | Area Type | Source for Limiting Factor Information | |
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Type of Location | Count | ||
Upper Yakima (17030001) | HUC 4 | EDT (Ecosystem Diagnosis and Treatment) | 193 |
Naches (17030002) | HUC 4 | EDT (Ecosystem Diagnosis and Treatment) | 101 |
Lower Yakima, Washington (17030003) | HUC 4 | EDT (Ecosystem Diagnosis and Treatment) | 113 |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Research, Monitoring, and Evaluation + Data Management |
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Project Deliverables | How the project deliverables help meet this objective* |
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Install Permanent PIT tag array's (DELV-1) | |
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Reporting (Progress and Annual) (DELV-3) | |
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Present Resident/Anadromous Results at YBS&M Conference in June 2011 (DELV-4) | |
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Generate population specific adult abundance estimates with Genetic Stock Identification (GSI) techniques and PIT-Tag interrogation histories (DELV-5) | |
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Conduct Radio Telemetry Study (DELV-7) | |
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Conduct Spawner surveys (DELV-8) | |
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Continuation of VSP project FY 2014 (DELV-19) | |
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VSP project continuation in FY 2015 (DELV-20) | |
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Continue VSP project in FY 2016 (DELV-21) | |
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Continue VSP project in FY 2017 (DELV-22) | |
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continue VSP data collection in FY 2018 (DELV-23) | |
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Continue VSP project in FY 2019 (DELV-24) | |
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Continuation of VSP project in FY 2020 (DELV-25) | |
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Project Deliverables | How the project deliverables help meet this objective* |
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Install Permanent PIT tag array's (DELV-1) | |
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Reporting (Progress and Annual) (DELV-3) | |
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Present Resident/Anadromous Results at YBS&M Conference in June 2011 (DELV-4) | |
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Generate population specific adult abundance estimates with Genetic Stock Identification (GSI) techniques and PIT-Tag interrogation histories (DELV-5) | |
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Estimate juvenile abundance and life history traits for Upper Yakima (DELV-6) | |
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Conduct Radio Telemetry Study (DELV-7) | |
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Estimate juvenile entrainment rates and Yakima River MPG smolt abundance (DELV-9) | |
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Generate population specific juvenile abundance estimates with Genetic Stock Identification (GSI) techniques (DELV-10) | |
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Refine and complete Genetic Stock Identification for individual populations (DELV-17) | |
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Continuation of VSP project FY 2014 (DELV-19) | |
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VSP project continuation in FY 2015 (DELV-20) | |
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Continue VSP project in FY 2016 (DELV-21) | |
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Continue VSP project in FY 2017 (DELV-22) | |
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continue VSP data collection in FY 2018 (DELV-23) | |
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Continue VSP project in FY 2019 (DELV-24) | |
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Continuation of VSP project in FY 2020 (DELV-25) | |
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Project Deliverables | How the project deliverables help meet this objective* |
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Install Permanent PIT tag array's (DELV-1) | |
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Capture and PIT tag O. Mykiss (DELV-2) | |
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Reporting (Progress and Annual) (DELV-3) | |
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Present Resident/Anadromous Results at YBS&M Conference in June 2011 (DELV-4) | |
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Generate population specific adult abundance estimates with Genetic Stock Identification (GSI) techniques and PIT-Tag interrogation histories (DELV-5) | |
|
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Conduct Radio Telemetry Study (DELV-7) | |
|
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Estimate juvenile entrainment rates and Yakima River MPG smolt abundance (DELV-9) | |
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Generate population specific juvenile abundance estimates with Genetic Stock Identification (GSI) techniques (DELV-10) | |
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Generate population specific adult to adult productivity estimates (DELV-11) | |
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Generate population specific juvenile productivity estimates (DELV-12) | |
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Estimate juvenile out-migration survival and smolt-to-adult return rates (SARs) (DELV-13) | |
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Refine and complete Genetic Stock Identification for individual populations (DELV-17) | |
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Continuation of VSP project FY 2014 (DELV-19) | |
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VSP project continuation in FY 2015 (DELV-20) | |
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Continue VSP project in FY 2016 (DELV-21) | |
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Continue VSP project in FY 2017 (DELV-22) | |
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continue VSP data collection in FY 2018 (DELV-23) | |
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Continue VSP project in FY 2019 (DELV-24) | |
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Continuation of VSP project in FY 2020 (DELV-25) | |
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Project Deliverables | How the project deliverables help meet this objective* |
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Install Permanent PIT tag array's (DELV-1) | |
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Capture and PIT tag O. Mykiss (DELV-2) | |
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Reporting (Progress and Annual) (DELV-3) | |
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Present Resident/Anadromous Results at YBS&M Conference in June 2011 (DELV-4) | |
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Conduct phenotypic, genotypic and life history analysis on Yakima River MPG steelhead populations (DELV-14) | |
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Experimental breeding study (DELV-18) | |
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Continuation of VSP project FY 2014 (DELV-19) | |
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VSP project continuation in FY 2015 (DELV-20) | |
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Continue VSP project in FY 2016 (DELV-21) | |
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Continue VSP project in FY 2017 (DELV-22) | |
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continue VSP data collection in FY 2018 (DELV-23) | |
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Continue VSP project in FY 2019 (DELV-24) | |
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Continuation of VSP project in FY 2020 (DELV-25) | |
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Project Deliverables | How the project deliverables help meet this objective* |
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Install Permanent PIT tag array's (DELV-1) | |
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Capture and PIT tag O. Mykiss (DELV-2) | |
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Reporting (Progress and Annual) (DELV-3) | |
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Present Resident/Anadromous Results at YBS&M Conference in June 2011 (DELV-4) | |
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Estimate juvenile abundance and life history traits for Upper Yakima (DELV-6) | |
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Upper Yakima spatial structure and spawner interaction analysis (DELV-15) | |
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Develop and refine Sympatric O.mykiss life history model (DELV-16) | |
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Experimental breeding study (DELV-18) | |
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Continuation of VSP project FY 2014 (DELV-19) | |
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VSP project continuation in FY 2015 (DELV-20) | |
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Continue VSP project in FY 2016 (DELV-21) | |
|
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Continue VSP project in FY 2017 (DELV-22) | |
|
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continue VSP data collection in FY 2018 (DELV-23) | |
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Continue VSP project in FY 2019 (DELV-24) | |
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Continuation of VSP project in FY 2020 (DELV-25) | |
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RM&E Protocol | Deliverable | Method Name and Citation |
Resident/Anadromous (2010-030-00) v1.0 | ||
VSP data collection (2010-030-00) v1.0 |
Project Deliverable | Start | End | Budget |
---|---|---|---|
Install Permanent PIT tag array's (DELV-1) | 2011 | 2013 | $273,897 |
Capture and PIT tag O. Mykiss (DELV-2) | 2011 | 2013 | $375,163 |
Reporting (Progress and Annual) (DELV-3) | 2011 | 2013 | $18,000 |
Present Resident/Anadromous Results at YBS&M Conference in June 2011 (DELV-4) | 2011 | 2011 | $1,800 |
Generate population specific adult abundance estimates with Genetic Stock Identification (GSI) techniques and PIT-Tag interrogation histories (DELV-5) | 2011 | 2013 | $90,731 |
Estimate juvenile abundance and life history traits for Upper Yakima (DELV-6) | 2011 | 2013 | $57,841 |
Conduct Radio Telemetry Study (DELV-7) | 2011 | 2013 | $657,755 |
Conduct Spawner surveys (DELV-8) | 2012 | 2013 | $58,304 |
Estimate juvenile entrainment rates and Yakima River MPG smolt abundance (DELV-9) | 2011 | 2020 | $0 |
Generate population specific juvenile abundance estimates with Genetic Stock Identification (GSI) techniques (DELV-10) | 2011 | 2013 | $183,693 |
Generate population specific adult to adult productivity estimates (DELV-11) | 2012 | 2013 | $8,856 |
Generate population specific juvenile productivity estimates (DELV-12) | 2012 | 2013 | $8,856 |
Estimate juvenile out-migration survival and smolt-to-adult return rates (SARs) (DELV-13) | 2011 | 2013 | $37,134 |
Conduct phenotypic, genotypic and life history analysis on Yakima River MPG steelhead populations (DELV-14) | 2011 | 2013 | $26,247 |
Upper Yakima spatial structure and spawner interaction analysis (DELV-15) | 2011 | 2013 | $21,980 |
Develop and refine Sympatric O.mykiss life history model (DELV-16) | 2012 | 2013 | $17,713 |
Refine and complete Genetic Stock Identification for individual populations (DELV-17) | 2011 | 2011 | $23,600 |
Experimental breeding study (DELV-18) | 2015 | 2020 | $60,000 |
Continuation of VSP project FY 2014 (DELV-19) | 2014 | 2014 | $500,018 |
VSP project continuation in FY 2015 (DELV-20) | 2015 | 2015 | $502,518 |
Continue VSP project in FY 2016 (DELV-21) | 2016 | 2016 | $515,331 |
Continue VSP project in FY 2017 (DELV-22) | 2017 | 2017 | $528,465 |
continue VSP data collection in FY 2018 (DELV-23) | 2018 | 2018 | $541,926 |
Continue VSP project in FY 2019 (DELV-24) | 2019 | 2019 | $555,724 |
Continuation of VSP project in FY 2020 (DELV-25) | 2020 | 2020 | $569,868 |
Total | $5,635,420 |
Fiscal Year | Proposal Budget Limit | Actual Request | Explanation of amount above FY2010 |
---|---|---|---|
2011 | $606,214 | Need does not reflect actaul award amount due to Taurus breakout of three year period above. Input was adjusted to get rid of bananas both here, and in the Line item budgets | |
2012 | $627,679 | Need does not reflect actaul award amount due to Taurus breakout of three year period above. Input was adjusted to get rid of bananas both here, and in the Line item budgets | |
2013 | $627,677 | Need does not reflect actaul award amount due to Taurus breakout of three year period above. Input was adjusted to get rid of bananas both here, and in the Line item budgets | |
2014 | $500,018 | ||
2015 | $512,518 | ||
2016 | $525,331 | ||
2017 | $538,465 | ||
2018 | $551,926 | ||
2019 | $565,724 | ||
2020 | $579,868 | ||
Total | $0 | $5,635,420 |
Item | Notes | FY 2011 | FY 2012 | FY 2013 | FY 2014 | FY 2015 | FY 2016 | FY 2017 | FY 2018 | FY 2019 | FY 2020 |
---|---|---|---|---|---|---|---|---|---|---|---|
Personnel | $146,365 | $172,993 | $180,580 | $187,112 | $191,739 | $196,483 | $201,347 | $206,330 | $211,438 | $216,676 | |
Travel | $366 | $376 | $384 | $393 | $403 | $414 | $423 | $434 | $445 | $456 | |
Prof. Meetings & Training | $0 | $0 | $0 | $0 | $0 | $0 | $0 | $0 | $0 | $0 | |
Vehicles | $7,792 | $15,987 | $16,386 | $16,795 | $17,265 | $17,745 | $18,238 | $18,744 | $19,262 | $19,793 | |
Facilities/Equipment | (See explanation below) | $173,788 | $254,828 | $255,982 | $164,957 | $169,081 | $173,308 | $177,641 | $182,082 | $186,634 | $191,300 |
Rent/Utilities | $0 | $0 | $0 | $0 | $0 | $0 | $0 | $0 | $0 | $0 | |
Capital Equipment | Radio Telemetry and PIT-Tag array field equipment | $177,920 | $15,375 | $16,022 | $0 | $0 | $0 | $0 | $0 | $0 | $0 |
Overhead/Indirect | $78,983 | $96,595 | $105,510 | $108,147 | $110,851 | $113,622 | $116,463 | $119,374 | $122,359 | $125,418 | |
Other | Radio Telemetry Sub-contract for equipment installation assistance and data management | $0 | $50,000 | $30,750 | $0 | $0 | $0 | $0 | $0 | $0 | $0 |
PIT Tags | $21,000 | $21,525 | $22,063 | $22,614 | $23,179 | $23,759 | $24,353 | $24,962 | $25,586 | $26,225 | |
Total | $606,214 | $627,679 | $627,677 | $500,018 | $512,518 | $525,331 | $538,465 | $551,926 | $565,724 | $579,868 |