Abstract

Sacramento River winter-run Chinook salmon are listed under the Endangered Species Act as Endangered and there are substantial efforts to estimate, predict, and limit mortalities at various stages of their life cycle. One such effort is the annual forecast of the number of juvenile winter-run entering the Sacramento-San Joaquin Delta. The natural-origin Juvenile Production Estimate (JPE) is defined as the number of winter-run juveniles produced from natural spawning areas that enter the Delta, and its forecast is used to determine the allowable level of winter-run incidental take at the state and federal pumping facilities located in the south Delta. Current monitoring programs in the Sacramento Basin do not allow for direct estimation of the JPE and thus various methods have been used to forecast this value annually. Here we describe three alternative methods for forecasting the natural-origin JPE. The methods range from the status quo approach (Method 1), which expresses the JPE forecast only as a point estimate, to two other methods that account for forecast uncertainty to various degrees. A comparison of JPE forecasts for 2018 across the three methods indicates that relative to Method 1, Methods 2 and 3 result in lower JPE forecasts, by 24 and 18 percent, respectively, primarily owing to lower forecasts of the fry-to-smolt transition and the smolt survival rate occurring downstream of Red Bluff Diversion Dam. Because post-hoc estimates of juvenile winter-run abundance at the entrance to the Delta do not currently exist, we are unable to evaluate forecast skill among the three methods.

Highlights

  • Management of fish and wildlife populations relies upon data generated from monitoring programs and analytical tools that use these data to inform decisions

  • Native to the headwaters of the Sacramento River basin in northern California, most winter-run spawning habitat was blocked by the construction of Shasta and Keswick dams on the Sacramento River, and currently the species exists as a single population that spawns in the mainstem Sacramento River near the terminus of fish passage

  • The use of annual smolt survival rates estimated from a mark–recapture model allows variation in detection probabilities to be accounted for, better characterizing the variances that inform the weighted mean approach to forecasting sn

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Summary

Introduction

Management of fish and wildlife populations relies upon data generated from monitoring programs and analytical tools that use these data to inform decisions. SAN FRANCISCO ESTUARY & WATERSHED SCIENCE because management actions can significantly affect population persistence, extinction risk, and the potential for recovery. One such imperiled species is Sacramento River winter-run Chinook Salmon (hereafter winter-run), which has been listed as Endangered under the Endangered Species Act (ESA) since 1994 (Fed Regist 1994). Winter-run persist in the Sacramento River outside of their historic range only because releases from Shasta Dam can be maintained at cool enough temperatures in most years to allow for successful spawning and egg incubation during the summer months (Fisher 1994; Yoshiyama et al 1998; Lindley et al 2007)

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