Abstract

Increasing human population size and mobility have accelerated the translocation of nonnative species globally, which has become a major threat to conservation of biodiversity and ecosystem services. Introduced species can disrupt species interactions of the recipient ecosystem, triggering system-wide events, and amplify or dampen effects of existing pressures. We show how two pervasive intercontinental invasive consumers in North American lakes, dreissenids (filter-feeding mussels) and Bythotrephes (carnivorous zooplankton), nonlinearly modify consumer-resource dynamics and undermine management interventions to rebuild cold-water predatory fish biomass. Synthesizing 30yr (1986-2015) of lake-wide monitoring data with a dynamic mass-balance food-web model (consisting of 61 species and trophic groups), we reconstructed historical food-web dynamics of Lake Simcoe, a large, temperate lake in Ontario, Canada that has shifted from a turbid to clear-water state. We then analyzed patterns of biomass fluctuations of three recreationally harvested, ecologically connected populations; lake trout (Salvelinus namaycush, a piscivore), lake whitefish (Coregonus clupeaformis, a benthivore), and cisco (C.artedi, a planktivore) before and after the invasions by testing hypotheses on their delayed recoveries under management interventions-predator manipulations (fishery removal and stocking) and nutrient (phosphorus)load reduction. Analyses suggest that fishery harvest primarily regulated early recovery trajectories of the piscivore and planktivore, weakening top-down control prior to the establishment of the invasive consumers. By contrast, the benthivore biomass patterns were shaped, in part, by the invasive mussels (via diet shift), independently of management actions. Although improved water quality (with reduced hypoxia in deeper water) and, in turn, higher macrophyte production are projected to expand the predation refuge for young fish, intensified planktivory (by Bythotrephes) and herbivory (by dreissenids) have triggered shifts in community composition (from pelagic to demersal dominance). These system-wide shifts, in turn, have substantially diminished ecosystem productivity, thereby shrinking fishery yields. Novel consumers can rewire food webs, disrupt energy flows, and suppress predator recoveries, underscoring the need to account for altered ecological reality when sustainably managing fishery resources in invaded ecosystems.

Highlights

  • Humans have manipulated lake ecosystems for millennia by modifying species composition and interactions, reshaping food webs (Boivin et al 2016, Bartley et al 2019) through activities that promote socioeconomicManuscript received 6 October 2019; revised 4 April 2020; accepted 16 April 2020

  • We found that non-consumptive effects of dreissenids mediated through changes in primary producers and habitat complexity played a key role in regulating the post-invasion food-web dynamics when tested against the historical data

  • The model with both the dreissenid forcing function for primary producers and the macrophyte forcing function for consumers performed better than the models with either function alone or no mediation (Table 1). These indirect processes played a larger role in biomass dynamics of lake trout and lake whitefish than they did for cisco (Fig. 3)

Read more

Summary

Introduction

Humans have manipulated lake ecosystems for millennia by modifying species composition and interactions, reshaping food webs (Boivin et al 2016, Bartley et al 2019) through activities that promote socioeconomic. Manuscript received 6 October 2019; revised 4 April 2020; accepted 16 April 2020. Ecological Applications Vol 0, No 0 base or predation pressure), triggering cascades that can lead to loss of biodiversity and ecosystem services (Strayer et al 2006). Some introductions have contributed to ecologically and socioeconomically catastrophic events such as the massive extinction of Lake Victoria cichlid fishes in the 1980s following Nile perch (Lates niloticus) introduction (Balirwa et al 2003)

Methods
Results
Conclusion

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call

Disclaimer: All third-party content on this website/platform is and will remain the property of their respective owners and is provided on "as is" basis without any warranties, express or implied. Use of third-party content does not indicate any affiliation, sponsorship with or endorsement by them. Any references to third-party content is to identify the corresponding services and shall be considered fair use under The CopyrightLaw.