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Authors
Duali, Jelany
DeLuca, William V.
Mackenzie, Stuart A.
Tremblay, Junior A.
Drolet, Bruno
Haché, Samuel
Roberto-Charron, Amélie
Holguín-Ruiz, Maira
Boardman, Rinchen
Cooke, Hilary A.
Rimmer, Christopher C.
McFarland, Kent P.
Marra, Peter P.
Taylor, Philip D.
Norris, D. Ryan https://orcid.org/0000-0003-4874-1425
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Article History
Received: 2 July 2024
Accepted: 21 November 2024
First Online: 4 December 2024
Declarations
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: The author(s) declare no competing interests.
: All geolocator deployments and recoveries made as part of this study were made under the appropriate government and academic permits, and birds were manipulated following national ethical guidelines. Deployments in British Colombia and Yukon in 2018, were carried out under an Environmental and Climate Change Canada (ECCC) permit to capture and band migratory birds (10169 BZ). Deployments in Denali National Park, in 2018, were performed under a United States Geological Survey Bird Banding Permit (24141) and National Park Service Institutional Animal Care and Use Committee authorization (“AK DENA WRST McIntyre Birds 2018.A3”). Deployments in Québec, in 2019, occurred under two ECCC Canada Animal Care Committee permits (19JT05 and 20JT05). Deployments in Newfoundland, in 20219, were performed with an ECCC permit (10616). Deployments in Yellowknife, in 2019, occurred with authorization from the Government of the Northwest Territory Wildlife Care Committee (NWTWCC 2019–011) and a Government of the Northwest Territory Wildlife Research Permit (WL500745). Deployments in Colombia, in 2020, were carried out by SELVA under a permit from the Autoridad Nacional de Licencias Ambientales (ANLA) under Resolución 00874 issued in 2018.
