Weir counts have been made on the Klukshu River, part of the Alsek River system, by the Department of Fisheries and Oceans (DFO) in co-operation with the Champagne-Aishihik First Nation, since 1976. A mark-and-recapture program ran from 2000 to 2004, and in 2005 and 2006, the Alsek sockeye population was estimated using tissue sample and catch information from the commercial sockeye fishery in Dry Bay as well as the weir counts. By recommendation by the Northern Fund Committee in 2008, a statistically valid sampling strategy that would provide the foundation for reconstructing sockeye and Chinook returns to the Alsek River was completed. Based on this model, it was proposed that funding be provided to analyze sockeye tissue samples collected in the commercial sockeye fishery in Dry Bay (up to 750 per season), to reconstruct the Alsek sockeye runs as described in Gazey’s analysis. The program has been running successfully each season since 2012.
N17-I16 Alsek Sockeye Run Reconstruction 2017
N16-I49 Alsek Sockeye Run Reconstruction Using GSI 2016
N15-I11 Alsek Sockeye Run Reconstruction 2015. Year 4
N14-I10 Alsek Sockeye Run Reconstruction 2014
N13-I12 Alsek Sockeye Run Reconstruction 2013
N12-I17 Alsek Sockeye Run Reconstruction, 2012
The Northern Boundary Technical Committee’s (NBTC) northern boundary area sockeye reconstruction assessments program has been conducted annually since the mid 1990’s to provide bilaterally agreed data on the sockeye stock composition and escapement for Nass, Skeena, Macdonald, and other US sockeye stocks originating in the northern boundary area.
The key components of the program include: 1) acquiring sockeye escapement, catch and stock composition data from Alaskan and Canadian northern boundary areas, 2) updating databases and providing initial model runs, 3) facilitating the NBTC workshop to provide the bilaterally agreed outcomes on the stock specific abundances 4) provide a report on the final agreed outcomes.
N17-I24 Annual Run Reconstruction Northern Boundary Sockeye Interim Presentation
We propose to use hydroacoustic methodology combined with trawl and gillnet sampling to estimate the limnetic fish species composition in six Skeena River and Nass River watersheds lakes and to estimate the population and rearing densities of age-0 sockeye fry and competitor limnetic species at each surveyed lake. The sockeye trawl and gillnet samples will also provide age and size data for the juvenile sockeye population at each lake. For 2020, we propose to survey Azuklotz, Bear, Damdochax, Lakelse, McDonell, and Wiiminosik lakes.
Sockeye originating from the selected lakes are harvested in both Canadian and American fisheries, and thus relevant to the Pacific Salmon Treaty. Hydroacoustic surveys are a cost effective method for assessing the status of sockeye stocks. Adult escapements for many BC north coast sockeye lakes are currently not determined due to high costs from the remoteness of the lake or due to other factors such as poor visibility for assessing lake spawners. The hydroacoustic methodology allows for a quick and accurate assessment of the stock status of each surveyed lake. For lakes where reliable estimates of adult escapement are available, hydroacoustic fry surveys are useful for quantifying spawner-to-fry productivity. Finally, the estimates of age-0 sockeye fry population can be compared to the lake carrying capacity for each lake.
N19-I43 Skeena Sockeye Lakes Hydroacoustic Surveys 2019 Report
N18-I34 Skeena Sockeye Lakes Hydroacoustic Surveys Report 2018
N17-I32 Skeena Sockeye Lakes hydroacoustic surveys 2017
N16-I09 Skeena Sockeye Lakes Hydroacoustic Surveys Report Year 4 0f 5
N15-I16 2015 Skeena Sockeye Lakes Hydroacoustic Surveys. Year 3 of 5
N14-I14 Skeena Sockeye Lakes Juvenile Sockeye Hydroacoustic Surveys. Year 2 of 5
N13-I20 Skeena Sockeye Lakes Juvenile Sockeye Hydroacoustic Surveys. Year 1 of 5
The Waanukv/Owikeeno watershed historically supported one of the largest sockeye populations in BC, currently supports some of the largest Chinook salmon found in the eastern Pacific and has unknown numbers of coho, pink and chum salmon. Prior to implementing the DIDSON and ARIS sonar monitoring systems on the Waanukv River annual estimates of Chinook and sockeye
escapements to the Waanukv/Owikeeno watershed were highly uncertain. The 2012-19 projects have provided the first reliable escapement estimates for Waanukv Chinook since the mark-recapture studies conducted in the 1990’s. The 2014-19 projects have provided the first estimates of the total sockeye escapement to the Owikeeno watershed that were based on quantitative daily counts for the entire sockeye run. Historical escapement estimates for Waanukv Chinook were derived from deadpitch surveys and estimates for Rivers Inlet Sockeye were derived by expanding visual escapement estimates for a few of the tributaries to Owikeeno Lake where spawners could be seen. The results from this project will be used to refine escapement goals and direct restoration and enhancement efforts for each salmon species.
N19-I47 Waanukv River Multi-Species Escapement Monitoring System Using DIDSON, ARIS Sonar, and Test Fishing, 2019 Report
N18-I36 Multi-species salmon assessment for the Wannock River Report 2018
N17-I34 Multi-species salmon assessment for the Waanukv (Wannock) River Report 2017
N16-I13 Multi-species salmon assessment for the Wannock River 2016 Year 3 of 3
N15-I20 Multi-species salmon assessment for the Wannock River, 2015. Year 2 of 3
This project proposes to continue an assessment program to estimate the survival and exploitation rates of an outer Central Coast chum stock at McLoughlin Creek (Bella Bella). Production from the Heiltsuk CEDP hatchery at Bella Bella has sustained this stock to a point where it has been able to consistently support both a commercial and FSC harvest in recent years. Starting in brood year 2008, production from this facility was doubled to 2M fed fry released. Returns in recent years have suggested outer coast chum may be surviving at a higher rate than inner coast chum stocks. This project will estimate the survival and exploitation rate of this stock, which can inform both hatchery production as well as fishery management decisions for both inner and outer Central Coast chum stocks. Years 1 and 2 (2012 (2011BY)), 2013 (2012BY) of this project consisted solely of juvenile salmon marking, while year 3 (2014 (2013BY)) was the first and only year with both juvenile marking, as well as adult return assessment components. Years 4-6 (2015-2017) consist solely of assessment of adult returns.
N17-I33 McLoughlin Creek Enhanced Chum Assessment Report 2017
N16-I07 McLoughlin Creek Enhanced Chum Assessment Report 2016
N15-I12 McLoughlin Creek Enhanced Chum Salmon Assessment. Year 4 of 6
N14-I11A McLoughlin Creek Enhanced Chum Salmon Assessment. (DFO Component) Year 3
N13-I13 McLoughlin Creek Enhanced Chum Assessment. Year 2
N12-I21 McLoughlin Creek Enhanced Chum Assessment
To counter recent reductions in federal funds, and to provide adequate non-federal matching funds this Northern Fund grant is used to augment the existing Alaska Department of Fish & Game Chinook salmon program budget by providing funding for: (1) analysis of data for use by the Chinook Technical Committee (CTC), the Transboundary Technical Committee (TTC) and for other relevant Pacfic Salmon Treaty activities; and (2) analysis of aerial survey, age, sex, and length composition, mark-recapture, smolt, and harvest data for South East Alaska indicator stocks.
2019 N15-I13 Southeast Alaska Chinook Salmon Stock Assessment 2019 Report
2018 N15-I13 Southeast Alaska Chinook Salmon Stock Assessment Interim Report Years 4-7
N14-I12 Southeast Alaska Chinook Salmon Stock Assessment. Year 3
N13-I14 Southeast Alaska Chinook Salmon Stock Assessment. Year 2
Coho salmon returning to the Taku River pass through an offshore troll fishery before entering inside waters where they encounter seine, drift gillnet, and recreational fisheries. After entering the river, the remaining coho salmon encounter drift/set gillnet fisheries in Canada. Such a resource is worthy of a stock assessment program that directly estimates production parameters such as harvest, escapement, exploitation rate, smolt production, survival rates and brood year production. This project will provide annual estimates of escapement necessary to refine escapement goals and forecast runs. Improved escapement goals and run forecasts along with inseason abundance estimates allow implementation of abundance-based management. These combined efforts in-river along with adult sampling programs in the various marine fisheries allow detailed stock assessment analyses.
2019 N15-I05A Taku River Coho Salmon Smolt Tagging Augmentation 2019 Report
2018 - N15-I04B Taku River Coho Adult Augmentation Report
2018 - N15-I05A Taku River Coho Salmon Smolt Tagging Augmentation Report
N17-I21A Taku River Coho Adult Augmentation - Final
N17-I22 Taku River Coho Smolt Tagging Augmentation - Final
N16-I44B Taku River Coho Salmon Escapement and Adult Augmentation Report. Year 10
N16-I45B Taku River Coho Salmon Smolt Tagging Augmentation Report. Year 10
N15-I04A Taku River Coho Salmon Adult Tagging Augmentation. Year 9 (DFO Component)
N15-I04B Taku River Coho Adult Augmentation 2015-2017. Years 9-11 (ADFG Component)
N15-I05B Taku River Coho Salmon Smolt Tagging Augmentation. Year 9 (DFO Component)
N14-I04 Taku River Coho Salmon Escapement and Smolt Tagging Augmentation. Year 8
N13-I04 Taku River Coho Salmon Escapement and Smolt Tagging Augmentation. Year 7
N12-I09 Taku River Coho Salmon Escapement and Smolt Tagging Augmentation, 2012. Year 6
N11-I09A Taku River Coho Salmon Escapement and Smolt Tagging Augmentation (ADFG Component), 2011
N11-I09B Taku River Coho Salmon Escapement and Smolt Tagging Augmentation (DFO Component)
N10-I15 Taku River Coho Salmon Escapement and Smolt Tagging Augmentation (DFO Component)
N06-I08A Taku River Coho Salmon Escapement and Smolt Tagging Augmentation
N06-I08B Taku River Coho Salmon Escapement and Smolt Tagging Augmentation
Funding of this proposal will augment the existing joint Canada and US coded wire tagging programme and serve to provide the resources to meet the Stikine River chinook and coho salmon smolts tagging objectives. The data derived will be used to determine the distribution, run timing, marine survival, and magnitude of marine catches of adult Stikine River chinook salmon, and distribution and run timing adult Stikine River coho salmon. This project is directly linked to the requirement in Annex IV, Chapter 1, paragraph 3(a)(2&3) of the PST to develop and implement abundance-based management regimes for Stikine chinook and coho salmon.
N19-I18 Stikine River Coded Wire Tagging 2019 Report
N18-VHP04 Stikine Coded Wire Tagging Report 2018
N17-VHP09 Stikine River Coded Wire Tagging Augmentation 2017. Year 10
N16-I03 Stikine River Coded Wire Tag Augmentation 2016. Year 9
N15-I03 Stikine River Coded Wire Tag Augmentation, 2015. Year 8
N14-I03 Stikine River Coded Wire Tag Augmentation, 2014. Year 7
N13-I03 Stikine River Coded Wire Tag Augmentation, 2013. Year 6
N12-I03 Stikine River CWT Augmentation, 2012
N11-I07 Stikine River CWT Augmentation 2011
N10-I05 Stikine River CWT Augmentation 2010
N08-I37 Stikine River CWT Augmentation 2008
N07-I15 Stikine River CWT Augmentation 2007
N06-I16 Stikine River CWT Augmentation 2006
Hydroacoustic programs have been conducted on the Fraser River at Mission, B.C. by the International Pacific Salmon Fisheries Commission (1977-1985) and the Pacific Salmon Commission (PSC; 1986 to the present) to estimate gross upstream passage of Fraser River sockeye salmon. The estimates of daily salmon passage provided by the hydroacoustics program, combined with information from test fishery, stock identification, and catch monitoring programs are used in models to provide estimates of stock abundance, timing, and escapement that are vital to the in-season management of Fraser River Sockeye Salmon.
Following years of discrepancies between the Mission and spawning ground estimates investigations have been undertaken to determine the causes of the discrepancies between these two estimates. As part of the investigations into these discepancies DFO conducted a 5-year experimental program from 1993-1998 at Qualark Creek to design, test and perfect specialized in-river equipment and analytical protocols for riverine acoustic measurements. When Qualark was in monitoring mode in the 1990’s, the pattern of upstream passage tended to track that at Mission, but occasionally showed noticeable differences.
DFO reactivated the Qualark Hydroacoustic Site in 2008 to test the feasibility of the site for estimating salmon abundance with dual-frequency imaging sonar (DIDSON). The daily salmon flux has been estimated in-season using a DIDSON system on each bank of the river between 2008 and 2016. Assessing the performance of the Qualark program through these operational years, DFO has concluded that the site at Qualark is an excellent location for acoustic enumeration of salmon flux in the Fraser River. The site has the ideal characteristics for detecting and tracking Sockeye Salmon as they move upstream, and produces reliable in-season estimates of salmon flux.
Qualark’s sampling system includes 2 DIDSON acoustic units, deployed one on each bank of the Fraser River and operated 24 hours per day during the period of Sockeye Salmon migration. The sampling system also includes integration of catch data from the the daily test fishing operation conducted at the Qualark site on the Fraser River by the Yale First Nation. Daily salmon migration flux is derived by simple time expansion of sub-sampled salmon flux over 3 acoustic data range bins.
S17-I28 Qualark 2017 Summary Report
S16-I18A Qualark Acoustics: Estimating Daily Salmon Passage in the Fraser River Near Yale, BC Report 2016. Year 5
S15-I04A Qualark Acoustics: estimating daily salmon passage in the Fraser River near Yale, BC in 2015. Year 4
S14-I09A Qualark Acoustics: Estimating Daily Salmon Passage in the Fraser River Near Yale, BC. 2014. Year 2
S13-I15A Qualark Acoustics: Estimating Daily Salmon Passage in the Fraser River Near Yale, BC. 2013
The primary goals of the Chilko River Chinook Salmon Mark-Recapture Project are to develop and estimate the spawning abundance that meets or exceeds the Chinook Technical Committee data standard for escapement indicator stocks. Specifically to determine:
1) estimates of spawning escapement by age and sex that will, on average, attain a coefficient of variation (CV) of 15% or less on the spawner estimates; and
2) consistent estimates that are asymptotically unbiased.
Additional objectives include bias testing of application and recovery data, and improving the efficiency of the study in-season and annually.
SSP14-01 Chilko River Chinook Salmon Mark-Recapture (Fraser River Summer-run Age 1.3 Stock Group). Year 5
SSP13-04 Chilko River Chinook Salmon Mark-Recapture (Fraser River Summer-run Age 1.3 Stock Group). Year 4
SSP12-02 Chilko River Chinook Salmon Mark-Recapture (Fraser River Summer-run Age 1.3 Stock Group). Year 3
SSP11-05 Chilko River Chinook Salmon Mark-Recapture (Fraser River Summer-run Age 1.3 Stock Group). Year 2
SSP10-06 Chilko River Chinook Salmon Mark-Recapture (Fraser River Summer-run Age 1.3 Stock Group). Year 1