Abstract

The Sacramento-San Joaquin Delta is a major survival bottleneck for imperiled California salmonid populations, which is partially due to a multitude of non-native fish predators that have proliferated there throughout the 20th century. Understanding the diets of salmonid predators is critical to understanding their individual impacts, role in the food web, and the implications for potential management actions. We collected the stomach contents of Striped Bass Morone saxatilis, Largemouth Bass Micropterus salmoides, Channel Catfish Ictalurus punctatus and White Catfish Ameiurus catus sampled from three 1-km reaches in the lower San Joaquin River in 2014 and 2015 during the peak juvenile salmon outmigration period. We tested each stomach (n = 582) for the presence of juvenile Chinook Salmon Oncorhynchus tshawytscha and other prey items using a genetic barcoding technique. Channel Catfish had significantly higher frequency of Chinook Salmon in their stomachs (27.8% of tested Channel Catfish contained Chinook Salmon DNA), compared to the other three predators (2.8% to 4.8%). However, non-native fish species occurred at greater frequencies in the diets of all four predator species than salmon. Using depletion estimation from electrofishing, we were able to generate population densities for Striped Bass and Largemouth Bass in our reaches. Largemouth Bass were evenly distributed throughout all three reaches, at a mean density of approximately 333 (± 195 SE) per km of river. Striped Bass were patchily distributed, ranging from 21 to 1,227 per km. Extrapolating the frequency of salmon detected in stomachs to the predator abundance estimates, we estimate that the population of Largemouth Bass we sampled consumed between 3 and 5 Chinook Salmon per day per 1-km study reach (consumption rate of 0.011 salmon per predator per day), whereas the Striped Bass population consumed between 0 and 24 Chinook Salmon per day (0.019 salmon per predator per day).

Highlights

  • Understanding predator–prey relationships is essential for understanding the ecology and population dynamics of organisms (Lamberti and Resh 1983; Lindström et al 1994; Krebs et al 2001)

  • What are the abundances of the different non-native fish predator species within three study reaches on the lower San Joaquin River? Second, how frequently do these predator species consume native salmonids and other fish prey species? Third, how can we extrapolate these findings to estimate total salmonids consumed per study reach per predator species? we provide a framework for discerning population-level effects of different predator species on San Joaquin Delta salmonid populations

  • Of particular interest in this study is the contribution of salmonids to the diets of different predator species: we found that 27.7% of Channel Catfish (CHC) diets tested positive for Chinook Salmon, followed by 4.8% of Striped Bass (STB) diets, 4.7% of White Catfish (WHC) diets, and 2.8% of Largemouth Bass (LMB) diets

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Summary

Introduction

Understanding predator–prey relationships is essential for understanding the ecology and population dynamics of organisms (Lamberti and Resh 1983; Lindström et al 1994; Krebs et al 2001). Predators can dramatically affect prey populations, and have ecosystem-level effects (Estes et al 2011). Freshwater ecosystems are sensitive to invasions by non-native predators, which can be attributed to the accentuated naïveté of the prey species from the allopatric insularity of freshwater systems compared to continental terrestrial or marine ecosystems (Cox and Lima 2006). It is problematic for native species when a freshwater ecosystem is subjected to extreme numbers of predator invasions. The Sacramento–San Joaquin Delta (part of California’s Central Valley watershed) has more nonnative fish species than native species (Brown and Michniuk 2007), and is part of what is considered to be the most invaded estuary in the world, the San Francisco Estuary (Cohen and Carlton 1998)

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