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Mean Annual Discharge and System Capacity for Chinook Salmon

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Species Common Name
Chinook Salmon
Latin Name (Genus species)
Oncorhynchus tshawytscha
Stressor Name
Flow; Discharge
Specific Stressor Metric
Mean annual discharge
Stressor Units
%
Vital Rate (Process)
Total number of spawners

Life Stage

Season
All Seasons
Activity
Spawning
Geography
Nicola River, BC, Canada
Detailed SR Function Description
Warkentin et al. (2022) used a time series of adult recruitment from the Nicola River to estimate the effects of August low flows in the brood year (x-axis) on returning adult recruits 4 years later (y-axis). The SR function was derived by regressing the annual residuals from the stock-recruit function on August low flows, reasoning that higher than average adult returns are correlated with higher than average flows in the brood year, and lower than average predicted flows (negative residuals) are correlated with lower flows (See figure 4e in Warkentin et al. 2022 for support of this mechanism). Average adult population size was added to the residuals to generate the final y-values (adult population response) for the final SR function, which was then standardized to a maximum of 1 (or 100% capacity; see Rosenfeld and Enright 2025).
Function Derivation
Observational data (multi-year over time); N = 22
Transferability of Function
Appropriate for late summer low flow spawning impacts on chinook salmon adults; general transferability to other chinooks stocks in unclear, but likely appropriate for other fall-spawning stocks in the B.C. interior (i.e., regions with similar hydrology to the Nicola R.).

The relationship may be unreliable if extrapolated to a flow range outside the original data (see the Average Salmonid flow-ecology SR function entry based on Rosenfeld and Enright (2025) for a more generalizable function across a wider range of flows).
Source of stressor Data
MAD + estimated water usage based off HYDAT hydrometric data and an estimate of annual water usage (unpublished data, Ptolemy; Summit Environmental Consultants Ltd., 2007). See supplement in Warkentin et al. 2022 for further information.

Stressor was then standardized to % MAD.
Function Type
continuous
Stressor Scale
linear
References Cited
Warkentin, L., Parken, C. K., Bailey, R., & Moore, J. W. (2022). Low summer river flows associated with low productivity of Chinook salmon in a watershed with shifting hydrology. Ecological Solutions and Evidence, 3(1), e12124.
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Stressor Response csv data
Data_Chinook_Flow_Nicola_Spawning_0.csv (752 bytes)
PERCENT_MAD Mean System Capacity (%) SD low.limit up.limit
11.65536913 33.7311309 0 0 100
13.49328859 34.6317114 0 0 100
13.51208054 34.6409195 0 0 100
14.38926174 35.0707383 0 0 100
14.99161074 35.3658893 0 0 100
15.65167785 35.6893221 0 0 100
16.8 36.252 0 0 100
16.94630872 36.3236913 0 0 100
20.36946309 38.0010369 0 0 100
22.90268456 39.2423154 0 0 100
23.0385906 39.3089094 0 0 100
25.52885906 40.5291409 0 0 100
26.39899329 40.9555067 0 0 100
28.23993289 41.8575671 0 0 100
29.75268456 42.5988154 0 0 100
29.88288591 42.6626141 0 0 100
33.14295302 44.260047 0 0 100
35.56946309 45.4490369 0 0 100
43.72281879 49.4441812 0 0 100
46.19798658 50.6570134 0 0 100
63.53187919 59.1506208 0 0 100
91.34194631 72.7775537 0 0 100

Stressor Response Chart

Mean Response
±1 Standard Deviation
Upper/Lower Limits
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