Introduction

The 2024 Annual Implementation Report summarizes progress toward recovery of ESA-listed spring Chinook salmon and steelhead in the Upper Columbia region of Washington. Recovery actions are guided by the 2007 Upper Columbia Spring Chinook Salmon and Steelhead Recovery Plan, which emphasizes coordinated efforts across the “Four H’s” of salmon recovery: habitat restoration, hydropower system impacts, hatchery management, and harvest management. The report summarizes adult returns, environmental conditions, and management actions affecting salmon and steelhead populations.

Adult Returns

Spawner escapement estimates describe the number of adult salmon and steelhead returning to spawn in Upper Columbia tributaries. Estimates are based on redd counts and population models depending on available data.

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In 2024, an estimated 707 natural-origin spring Chinook salmon returned to spawn. This represents the third consecutive year of declining returns and the lowest count since 2020, although still slightly higher than the lows observed between 2017 and 2020. The current 12-year average remains well below the recovery plan target of 4,500 natural-origin spawners needed for delisting. Hatchery-origin returns totaled 2,019, producing 2,721 total spawners in the region. Natural-origin returns declined in the Wenatchee and Methow basins but increased slightly in the Entiat.

 

Steelhead returns improved in 2024. An estimated 1,819 natural-origin steelhead returned to spawn, the highest wild return since 2016 and above the recent 12-year average. However, this number remains below the recovery target of 3,000 natural-origin spawners. Hatchery-origin steelhead totaled 2,456, bringing the regional total to 4,274 spawners. Most Upper Columbia subbasins experienced increases compared to 2023.

Figure 1. Upper Columbia spring Chinook salmon and steelhead return spawners (left axis) between 2000-2024 for natural-origin (colored bars) and hatchery-origin (gray bars) fish, and percent hatchery-origin spawners (right axis; light gray fill) by year. The black line indicates the 12-year geometric mean of natural-origin spawners, and the dashed line is the abundance delisting target for natural-origin fish. Note the difference in axes among plots and a break in the y-axis for Methow Chinook and steelhead and Okanogan steelhead. Source: WDFW 2024 SPI data, Hillman et al. 2025, Snow et al 2025

Habitat Conditions in 2024

Snowpack and Streamflow

Environmental conditions in 2024 were generally challenging for spring Chinook and steelhead. Winter conditions were warmer than average with below-average precipitation and snowpack approximately 28% below normal. Peak snowpack occurred earlier than average, contributing to reduced spring runoff.

Streamflow across the Upper Columbia was about 36% below normal at peak flow, with overall annual flows approximately 24% below average. Low summer flows were widespread, and August flows averaged 37% below normal. Warmer air temperatures contributed to higher stream temperatures at most monitoring sites, with several locations exceeding temperatures considered stressful or lethal for salmonids

Upper Columbia peak flows averaged 36% below normal.

Columbia River summer water temperatures peaked at 2.0°F above average below Rocky Reach Dam.

Figure 2. Map of the four major Upper Columbia River subbasins showing the location of SNOTEL sites where snow-water equivalent is assessed (circles) and USGS stream gages where flow is measured (triangles). The color ramp indicates the percent difference from annual average for each of the two measurements. Source: USGS, 2025; NRCS, 2024.

Wildfire

Wildfire is a major driver of aquatic habitat in the Upper Columbia and has the potential to both degrade habitat through large amounts of fine sediment and loss of riparian shading, or to improve habitat by increased streamflow and large wood additions from downed trees. The 2024 wildfire season was relatively mild, and most fires did not significantly affect salmon-bearing floodplains or habitat.

Ocean Conditions

Ocean conditions for salmon were relatively poor in 2024 compared to recent years. Reduced ocean productivity and warmer waters limited food availability for juvenile salmon during their first year at sea. Ocean conditions strongly influence future adult returns, and recent variability may contribute to fluctuations in salmon and steelhead abundance.

 

See more information on habitat in the UCSRB Habitat Background Summary.

 
Figure 3. Ocean ecosystem indicators of the Northern California Current from 1998 – 2024. Colored squares indicate either positive (green), neutral (yellow), or negative (red) conditions for salmonids entering the ocean.

Harvest

Harvest of salmon and steelhead in tributaries to the Columbia River is managed by the state of Washington and tribal fishery managers to limit impacts on ESA-listed species. In 2024, recreational fisheries occurred for non-listed species such as sockeye and hatchery salmon, while wild Chinook and steelhead were largely protected through mandatory release requirements. In 2024, an estimated 1,609 wild spring Chinook entered the Columbia River destined for the Upper Columbia, along with an additional 16,615 hatchery fish, including fish from the Chief Joseph hatchery. The estimated number of wild fish taken by non-treaty wild harvest was 12 (0.7% of the wild run) and treaty harvest through ceremonial and subsistence (C&S) fisheries accounted for 97 fish (6.0% of the run).

See more information on harvest in the UCSRB Harvest Background Summary.

Hydrosystem Survival

Salmon and steelhead from Upper Columbia populations migrate through the Columbia River hydrosystem during their emigration to the ocean as juveniles and again as adults returning to their stream of origin. Survival during migration may be influenced by environmental conditions and operations associated with the dams and reservoirs encountered prior to ocean entry and upon return up the Columbia River. Below-average river flows in 2024 reduced spill and increased migration travel times for juvenile fish. Downstream survival estimates for hatchery Chinook from release sites to Bonneville Dam were 38%, one of the lowest values since ESA listing. Hatchery steelhead survival declined even further to 14%, the lowest recorded since listing.

 

See more information on hydropower in the UCSRB Hydropower Background Summary.

Hatcheries

Upper Columbia hatchery programs released approximately 3.4 million spring Chinook and 759,000 steelhead in 2024 to support conservation, harvest, and reintroduction objectives. Hatchery fish contribute substantially to total returns but also influence the genetic composition of natural populations. Metrics such as the proportion of hatchery fish spawning in the wild and the proportionate natural influence (PNI) are used to evaluate genetic risk. While some populations show improvement, many remain below recommended thresholds where natural selection dominates population adaptation.

 

See more information on hatcheries in the UCSRB Hatchery Background Summary.

Habitat

Habitat restoration and protection projects in the Upper Columbia are tracked in the Salmon Recovery Portal database, administered by the State of Washington Governor’s Salmon Recovery Office (GSRO). All habitat projects that could benefit salmon, steelhead, and bull trout, regardless of funder or sponsor, are tracked through this database. This information is used to track our progress toward implementing habitat goals in the Upper Columbia Spring Chinook Salmon and Steelhead Recovery Plan (Recovery Plan) and the Upper Columbia Biological Strategy.

2024 Habitat Accomplishments

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relocated

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acquired for protection or restoration

In 2024, partners completed 37 projects across all four major subbasins (Figure 4), with nine projects implemented in the Methow, 17 in the Wenatchee, four in the Entiat, six in the Okanogan, and one project that was a combination of the Wenatchee and Entiat subbasins. In comparison, the number of projects completed in 2023 was 47. Of the completed 2024 projects, 25 were restoration, seven were design/planning, two were assessments, and three were protection, or acquisition. Of the 37 completed projects, five were primarily funded by the BPA Upper Columbia Programmatic, which are reported annually to the Bonneville Power Administration. In addition, there were two projects completed in the Moses Coulee watershed. These projects were included in the completed projects table (Attachment 1) but were not included in any of the calculations presented in this report.

Since 1998, there have been 764 projects completed in the region, most of which (57%) were implemented within the last 12 years. The total projects completed in 2024 is similar to the 10-year average of 33 projects per year. Over the past five years, an average of 36 projects have been completed annually. As noted in previous annual reports, the scope and scale of current projects is significant based on the cost of recently completed projects. In 2024, the combined cost of all 37 projects totaled about $13.8 million (Figure 5), with four projects each costing $1 million or more. The average funding per project was approximately $370,000. A complete list of projects completed in 2024 is provided in Attachment 1. 

Projects Completed in 2024

Figure 4. Map of the Upper Columbia region showing the location and type of projects completed in 2024 within each of the four major subbasins.

Of the 28 total restoration and protection projects in 2024, most targeted a combination of ESA-listed fish species, with seven primarily focused on spring Chinook and steelhead, and another eight focused on spring Chinook, steelhead, and bull trout. Steelhead alone was listed as the primary species of interest in an additional nine projects. One project, in Upper Bonaparte Creek, was primarily focused on rainbow trout. Of the projects that benefited steelhead, the majority (15 of 25) were completed in a high priority assessment unit, with an additional ten completed in a medium priority area. Similarly, of the 16 projects benefiting spring Chinook, ten were completed in a high, five in a medium, and one in a low priority assessment unit. While bull trout were a primary species of interest in only eight projects, most of these were completed in a high priority assessment unit as well.

See more information on habitat in the UCSRB Habitat Background Summary

Total Number of Projects and Money Spent By Year

Figure 5. Total number of habitat projects completed (blue bars; left axis) and money spent in millions (orange line; right axis) annually from 1998 through 2024.

Featured Projects

Attachment 1

Table of Information for Projects Completed in 2024

Upper Columbia projects completed in 2024. Source: Salmon Recovery Portal database (January 2026). Projects are shaded by subbasin. CCD = Cascadia Conservation District; CCNRD= Chelan Country Natural Resources Department; CF= Cascade Fisheries; CTCR = Confederated Tribes of the Colville Reservation; MSRF= Methow Salmon Recovery Foundation; OCD= Okanogan Conservation District; TU = Trout Unlimited; WDFW = Washington Dept of Fish and Wildlife; YN = Yakama Nation.

Citations

Columbia Basin Research. University of Washington, School of Aquatic & Fishery Sciences. Retrieved from https://www.cbr.washington.edu/

DeHart, J. 2025. Fish Passage Center: 2024 Annual Report. Fish Passage Center. BPA Contract # 78040 REL 63.

DeHart, J. 2024. Fish Passage Center: 2023 Annual Report. Fish Passage Center. BPA Contract # 78040 REL 54.

Hatchery Scientific Review Group (HSRG). 2009. Columbia River Hatchery Reform System-Wide Report. Prepared by the Hatchery Scientific Review Group.

Hillman, T., M. Miller, K. Shelby, M. Hughes, J. Williams, C. Deason, M. Tonseth, K. See, C. Willard, R. Renick, J. Caisman, T. Taylor, and R. O’Connor. 2025. Monitoring and evaluation of the Chelan and Grant County PUDs hatchery programs: 2024 annual report. Report to the HCP and PRCC Hatchery Committees, Wenatchee and Ephrata, WA.

McCann, J., B. Chockley, E. Cooper, G. Scheer, J. Harris, B. Lessard, T. Copeland, J. Ebel, A.. Storch, and K. See. 2025. Comparative Survival Study Oversight Committee and Fish Passage Center, Comparative Survival Study of PIT-Tagged Spring/Summer/Fall Chinook, Summer Steelhead, and Sockeye: 2025 Annual Report. Fish Passage Center. BPA Contract #19960200.

National Oceanographic and Atmospheric Association (NOAA). 2025a. National Weather Service Climate Prediction Center. College Park, MD, USA. Retrieved from https://www.cpc.ncep.noaa.gov/products/analysis_monitoring/ensostuff/ONI_v5.php

National Oceanographic and Atmospheric Association (NOAA) Fisheries. 2025b. Ocean Indicators Summary for 2024. Retrieved from https://www.fisheries.noaa.gov/west-coast/science-data/2024-summary-ocean-ecosystem-indicators

Natural Resource Conservation Service (NRCS). 2024. National Water and Climate Center – Snow Telemetry (SNOTEL) and Snow Course Data and Products. https://www.wcc.nrcs.usda.gov/snow/

Northwest Interagency Coordination Center. 2024. Northwest Annual Fire Report 2024. Portland, OR, USA.

Oregon Department of Fish and Wildlife and Washington Department of Fish and Wildlife (ODFW & WDFW). 2025. 2025 Joint Staff Report: Stock Status and Fisheries for Spring Chinook, Summer Chinook, Sockeye, Steelhead, and Other Species. Joint Columbia River Management Staff. Washington Dept. of Fish and Wildlife and Oregon Dept. of Fish and Wildlife.

Paquet, P. J., T. Flagg, A. Appleby, J. Barr, L. Blankenship, D. Campton, M. Delarm, T. Evelyn, D. Fast, J. Gislason, P. Kline, D. Maynard, L. Mobrand, G. Nandor, P. Seidel, and S. Smith. 2011. Hatcheries, conservation, and sustainable fisheries – achieving multiple goals: results of the Hatchery Scientific Review Group’s Columbia River Basin review. Fisheries 36:547-561.

Snow, C., D. Grundy, B. Goodman, L. Ciepiela, and J. Rohrback. 2025. Monitoring and evaluation of the Wells Hatchery and Methow Hatchery programs: 2024 annual report. Report to Douglas PUD, Grant PUD, Chelan PUD, and the Wells and Rocky Reach HCP Hatchery Committees, and the Priest Rapids Hatchery Subcommittees, East Wenatchee, WA.

Widener, D. L., J. R. Faulkner, S. G. Smith, R. M. Gleason, and A. L. Barenberg. 2025. Survival Estimates for the Passage of Spring- Migrating Juvenile Salmonids Through Snake and Columbia River Dams and Reservoirs, 2024. U.S. Department of Commerce, NOAA Contract Report NMFS-NWFSC-CR-2025-04.

United States Geological Survey (USGS). 2025. U.S. Department of the Interior. Retrieved from https://waterdata.usgs.gov/nwis/sw.

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