Yellowstone Cutthroat Trout Recovery in Yellowstone Lake: Complex Interactions Among Invasive Species Suppression, Disease, and Climate Change

Author:

Glassic Hayley C.1ORCID,Chagaris David D.2ORCID,Guy Christopher S.3ORCID,Tronstad Lusha M.4ORCID,Lujan Dominique R.4,Briggs Michelle A.5ORCID,Albertson Lindsey K.6ORCID,Brenden Travis O.7ORCID,Walsworth Timothy E.8,Koel Todd M.9ORCID

Affiliation:

1. U.S. Geological Survey, Northern Rocky Mountain Science Center 2327 University Way Suite 2 Bozeman MT 59717

2. Nature Coast Biological Station, Institute of Food and Agricultural Sciences University of Florida Cedar Key FL

3. U.S. Geological Survey, Montana Cooperative Fishery Research Unit Montana State University Bozeman MT

4. Wyoming Natural Diversity Database and Department of Zoology and Physiology University of Wyoming Laramie WY

5. Montana Cooperative Fishery Research Unit Montana State University Bozeman MT

6. Department of Ecology Montana State University Bozeman MT

7. Department of Fisheries and Wildlife Quantitative Fisheries Center, Michigan State University East Lansing MT

8. Department of Watershed Sciences and the Ecology Center Utah State University Logan UT

9. National Park Service, Yellowstone Center for Resources, Native Fish Conservation Program Yellowstone National Park WY

Abstract

In Yellowstone Lake, Wyoming, the largest inland population of nonhybridized Yellowstone Cutthroat TroutOncorhynchus clarkii bouvieri, hereafter Cutthroat Trout, declined throughout the 2000s because of predation from invasive Lake TroutSalvelinus namaycush, drought, and whirling diseaseMyxobolus cerebralis. To maintain ecosystem function and conserve Cutthroat Trout, a Lake Trout gill netting suppression program was established in 1995, decreasing Lake Trout abundance and biomass. Yet, the response of Cutthroat Trout to varying Lake Trout suppression levels, collectively with the influence of disease and climate, is unknown. We developed an ecosystem model (calibrated to historical data) to forecast (2020–2050) whether Cutthroat Trout would achieve recovery benchmarks given disease, varying suppression effort, and climate change. Lake Trout suppression influenced Cutthroat Trout recovery; current suppression effort levels resulted in Cutthroat Trout recovering from historical lows in the early 2000s. However, Cutthroat Trout did not achieve conservation benchmarks when incorporating the influence of disease and climate. Therefore, the National Park Service intends to incorporate age‐specific abundance, spawner biomass, or both in conservation benchmarks to provide better indication of how management actions and environmental conditions influence Cutthroat Trout. Our results illustrate how complex interactions within an ecosystem must be simultaneously considered to establish and achieve realistic benchmarks for species of conservation concern.

Funder

Montana Institute on Ecosystems

Publisher

Wiley

Subject

Nature and Landscape Conservation,Aquatic Science

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