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Enregistrement W4402729845 · doi:10.1111/mms.13187

First documented movement of wild killer whales (<i>Orcinus orca</i>) between Iceland and Norway

2024· article· en· W4402729845 sur OpenAlexaboutno aff
Marie‐Thérèse Mrusczok, Emma Luck, Ted Cheeseman, Jamie Coleman, Javier Cotín, Andrew Peacock, Róbert A. Stefánsson, Menja von Schmalensee

Notice bibliographique

RevueMarine Mammal Science · 2024
Typearticle
Langueen
DomaineEnvironmental Science
ThématiqueMarine animal studies overview
Établissements canadiensnon disponible
Organismes subventionnairesnon disponible
Mots-clésCetaceaWhalePredatorBiologyMovement (music)GeographyFisheryZoologyPredationEcology

Résumé

récupéré en direct d'OpenAlex

Killer whales (Orcinus orca, Linnaeus 1758) are wide-ranging throughout the world's oceans (Forney & Wade, 2006) and can travel over large distances (Dahlheim et al., 2008; Durban & Pitman, 2012). In the North Atlantic, long-distance movements of killer whales have been recorded from the eastern Canadian Arctic to near the Azores (Matthews et al., 2011), from Scotland to Norway (Eve Jourdain, personal communication, November 2022), repeatedly between Iceland and Scotland (Mrusczok & Scullion, 2019; Samarra & Foote, 2015), as well as between Iceland, Scotland, and the Faroe Islands (Scullion et al., 2021; Andrew Scullion, personal communication, November 2022). The longest one-way distance recorded for killer whales was documented with the movement of a male from Iceland via Spain and Italy to Lebanon and Israel traveling over 8,000 km (Mrusczok, Violi, et al., 2022; Mrusczok, von Schmalensee, et al., 2022). An extensive nonstop round-trip movement to subtropical waters has previously been recorded for Antarctic killer whales, with a travel distance of almost 9,400 km from the Antarctic peninsula to the coasts of Uruguay and southern Brazil and back (Durban & Pitman, 2012). The only killer whale previously documented to have swum from Iceland to Norway is the male killer whale Keiko, who was born in the wild near Iceland, captured in 1979, and released back into Icelandic waters in 2002 (Simon et al., 2009). Using satellite telemetry, Keiko was tracked moving from Vestmannaeyjar, southern Iceland, to Kristiansund, western Norway, in 25 days in August 2002 (Simon et al., 2009). The minimum distance between these two locations via sea is 1,390 km. Keiko would therefore have traveled at a minimum average transit speed of 55.6 km per day. Killer whales have been previously documented with an average transit speed of 120–240 km per day (Durban & Pitman, 2012; Hanson et al., 2017). Keiko's transit speed may have been closer to this average, considering the less than direct route indicated via satellite telemetry (Simon et al., 2009). As killer whales are listed as data deficient by the IUCN red list (Reeves et al., 2017), studies that compare identification images of individuals between regions are of great importance for improving knowledge on population characteristics, abundance estimates, ecotypic classification, and, ultimately, for the conservation status of killer whales. It has been suggested that at least two populations of killer whales are present in Icelandic waters (Foote et al., 2011), but their genetic, social, and ecological differentiation largely remains unknown (Jourdain et al., 2019). A study on social and genetic connectivity of killer whales in Norwegian waters indicated the presence of one unique population rather than two different populations (Jourdain et al., 2024). A previously established type classification for North Atlantic killer whales has been questioned (Foote, 2023), emphasizing the need for more detailed analyses of data sets of photo-identification images and behavioral observations. Here, the first photographic match, round-trip, and one-way movement of four wild killer whales between Iceland and Norway are described, with confirmed sightings and observations of these individuals between 2018 and 2024. Georeferenced photo-identification (Bigg, 1982) and behavioral data were obtained by a combination of citizen science and dedicated research cruises along the Icelandic shoreline and in Norwegian waters. In West Iceland, data collection was part of a larger, long-term running photo-identification study (2014–2024; Mrusczok, 2022). Photo-identification images taken of killer whales in Norway were uploaded to the research collaboration and citizen science web platform Happywhale (Cheeseman et al., 2017, 2021). The Happywhale database primarily contains photo-identification images of humpback whales (Megaptera novaeangliae) and opportunistically collects photos of other marine mammal species. The images of the killer whales in Norway were then compared via visual analysis to images from the photo-identification catalog of 987 killer whales in Iceland (Mrusczok, 2022), and to images taken during sightings in West Iceland from 2022 to 2024 that were not yet included in the catalog. Matches were confirmed by two independent researchers trained in photo-identification, which includes analyzing the scarring patterns on the dorsal fin and saddle patch of each individual, the size of the dorsal fin and nicks on the fin, the shape of the saddle patch, and the angle in which the images were taken. Secondary characteristics, such as the size of the dorsal fin, were also used to determine the sex of the individuals (Ford et al., 2000). Subsequently, sightings of the matched individuals in Icelandic waters were added from the West Iceland database and from reports and images from whale watching guides and members of the public in different parts of Iceland. Two of the four individuals matched were listed in the West Icelandic photo-ID catalog: an adult male (Iceland ID number: SNOS1310, former SN1310, nicknamed “Sundfoerr”), and a second individual (SNOS1309, former SN1309, nicknamed “Kisa”), likely to be a female due to body size and the nonchanging size of the dorsal fin over a 5-year period (Figure 1). A third individual, another adult male (SNOS1316, nicknamed “Gwaihir”) and a fourth individual (SNOS1317, nicknamed “Svana”), likely to be another female due to close association with a young calf, were found in unpublished images taken in West Iceland in 2022 and 2024 (Figure 1). Individuals matched were confirmed a total of six times in several areas along the Icelandic coast between 2018 and 2024, but only once in Norway in June 2022 (Figures 1 and 2, Table 1). No further accounts of the four killer whales were found in the Happywhale database. No previous records of the four individuals exist in the Norwegian killer whale database holding photo-identification images of 1,325 individuals for the period 2005–2022, nor in the historical Norwegian killer whale photo-ID catalog for the years 1986–2005 (Eve Jourdain, personal communication, September 2024). Three of the four killer whales were photographed in West Iceland in April 2022, before being sighted again 45 days later in Norway in June 2022 (Figure 2, Table 1). During this time, the whales traveled a minimum distance of 1,740 km which would equate to 38.7 km per day, if the whales traveled the shortest possible route along the north coast of Iceland (Figure 2). The same individuals were then observed again in March 2023 in North Iceland, having traveled at least 1,330 km from Norway over 264 days. In this round trip from Iceland to Norway and back, the three killer whales covered a minimum distance of 3,070 km in a maximum time span of 309 days, calculated from the last day they were seen in Iceland in 2022, to the first day they were observed in Icelandic waters again in 2023 (Figure 2, Table 1). It is possible that SNOS1309, SNOS1310, and SNOS1316 are more regularly present in Icelandic than in Norwegian waters, as they were spotted along the Icelandic shoreline several times between 2018 and 2024 but were documented in Norway only once, in 2022. Sightings success may, however, largely depend on how regularly those areas have been surveyed. Whereas regular data collection is conducted onboard Icelandic whale watching vessels in the areas in which these individuals were spotted, and dedicated research surveys have been carried out in West Iceland, the sighting in Central Norway was entirely opportunistic. A fourth individual, SNOS1317, was only photographed twice, in Norway in June 2022 and in Iceland in March 2024, confirming at least one transit from Norway to Iceland (Figure 2, Table 1). It is possible that SNOS1317 was present in previous encounters in Iceland but may have been undocumented because not all individuals were photographed during encounters in Iceland from 2022 to 2023 (Table 1). The four matched individuals were observed as part of larger groups of killer whales both in Iceland and Norway (Table 1). How SNOS1309, SNOS1310, SNOS1316, and SNOS1317 relate to any of the additionally documented individuals or to each other is unknown. SNOS1317 was photographed with a young calf in the echelon position in the 2024 Iceland encounter, but the calf was not documented in any of the photographs from Norway. Both the Icelandic and the Norwegian photo-identification databases hold images of over 1,000 wild killer whales (Mrusczok, 2022; M.-T.M., unpublished data; Eve Jourdain, personal communication, November 2022), but this is the first time the same individuals could be found in both Icelandic and Norwegian waters, despite previous efforts (Foote et al., 2010). Notwithstanding the great number of individuals documented in both databases, they may only be a fraction of the individuals occurring in Iceland and Norway, and round trips between the two countries may have taken place previously and may not be as rare as currently suggested. Though acoustic studies suggest a lack of or little connection through call types between killer whales from Icelandic and Norwegian waters (Bellon, 2023; Selbmann et al., 2020), the photo-identification matches of the four individuals may indicate more spatial overlap between killer whales in Iceland and Norway than previously thought. Range overlap between populations previously thought to be isolated could imply that total killer whale abundance assuming closed populations has been overestimated. In West Iceland, individual killer whales have been photographed and added to the data set each year between 2014 and 2024 (Mrusczok, 2022; M.-T.M., unpublished data), but the total number of individuals regularly occurring in Icelandic waters is still unknown. Ongoing efforts for data collection, to determine the regularity of long-distance and round-trip movements through international collaboration, will aid in our understanding of killer whale populations and their conservation status in the North Atlantic. Increased sharing of data through publicly accessible photo-identification catalogs and collaboration between scientists, engagement from platforms of opportunity (e.g., whale-watching vessels), as well as contributions from the public via citizen science, are invaluable to our understanding of these far-ranging animals. Data collection in West Iceland was possible only thanks to the past and ongoing support of Láki Tours whale watching and Gísli Ólafsson, who provided a platform for Orca Guardians' research from the very beginning of our efforts. Thank you to Lindblad Expeditions for facilitating data collection onboard the National Geographic Resolution in Norway, and to all citizen science contributors of North Atlantic killer whale images, especially naturalist guides. We would like to thank Helen Alexander and Christian Schmidt for additional images and sightings information, as well as Elding Adventure at Sea and North Sailing for permitting data collection onboard their whale watching vessels in Icelandic waters. We are grateful to Eve Jourdain and Andrew Scullion for sharing insights into their respective data sets. Thank you to Stefan Wrabetz for grammatical corrections. The authors declare there are no competing interests. The authors have no relevant financial or nonfinancial interests to disclose. No funding was received for conducting this study. Data generated or analyzed during this study are provided in full within the article. Marie-Thérèse Mrusczok: Conceptualization; data curation; formal analysis; investigation; project administration; visualization; writing – original draft. Emma Luck: Conceptualization; data curation; formal analysis; investigation; writing – review and editing. Ted Cheeseman: Data curation; investigation; writing – review and editing. Jamie Coleman: Investigation; writing – review and editing. Javier Cotín: Investigation; writing – review and editing. Andrew Peacock: Investigation; writing – review and editing. Robert A. Stefansson: Supervision; writing – review and editing. Menja von Schmalensee: Supervision; writing – review and editing.

Récupéré en direct depuis OpenAlex et désinversé. Les résumés ne sont pas conservés dans cette base de données : les index inversés représentent 8,6 Go des 9,3 Go de texte de la base, et le serveur dispose de 13 Go libres.

Comment cette classification a été obtenuedéplier

Prédiction distillée sur la base complète

Imitation des enseignants

Ni prévalence calibrée, ni vérité terrain. Validation humaine à venir. Apprise à partir de 10 348 étiquettes directes de Codex et de 10 348 étiquettes directes de Gemma. Le mode candidate est l'union des têtes enseignantes seuillées; le consensus est leur intersection. Ces sorties portent le statut machine_predicted_unvalidated et ne sont ni des étiquettes humaines ni des étiquettes directes de modèles de pointe.

score de la tête « metaresearch » (Codex)0,001
score de la tête « metaresearch » (Gemma)0,000
Version: codex-gemma-dda1882f352aStatut de validation: machine_predicted_unvalidated
Catégories candidatesCharge utile insuffisante (le modèle a refusé de juger)
Catégories consensuellesaucune
DomaineSignal candidat: aucune · Signal consensuel: aucune
Devis d'étudeSignal candidat: Observationnel · Signal consensuel: Observationnel
GenreSignal candidat: Empirique · Signal consensuel: Empirique
Score de désaccord entre enseignants0,106
Score d'incertitude au seuil0,997

Scores Codex et Gemma par catégorie

CatégorieCodexGemma
Métarecherche0,0010,000
Méta-épidémiologie (sens strict)0,0000,000
Méta-épidémiologie (sens large)0,0000,000
Bibliométrie0,0000,001
Études des sciences et des technologies0,0000,001
Communication savante0,0000,000
Science ouverte0,0010,003
Intégrité de la recherche0,0000,000
Charge utile insuffisante (le modèle a refusé de juger)0,0040,000

Scores machine (provisoires)

Les deux têtes enseignantes du modèle étudiant, lues sur ce travail. Un score ordonne la base pour la relecture; il n'affirme jamais une catégorie, et le statut de validation accompagne chaque rangée tel quel.

Scores de référence d'un modèle non mature (critères de maturité non atteints, 7 itérations). Un score ordonne; il n'affirme jamais une catégorie.

Tête enseignante Opus0,010
Tête enseignante GPT0,230
Écart entre enseignants0,220 · la distance entre les deux têtes enseignantes sur ce seul travail
Statut de validationscore_only:v0-immature-baseline · tel quel depuis la passe de notation : score_only signifie que le nombre peut ordonner les travaux, et qu'aucune étiquette de catégorie n'en découle

Classification

machine, non validée

Prédiction automatique; un appel candidat d’une seule tête enseignante, pas un consensus.

Devis d'étudeObservationnel
Domainenon disponible
GenreEmpirique

Le détail, modèle par modèle et score par score, se trouve en fin de page sous « Comment cette classification a été obtenue ».

En bref

Citations1
Publié2024
Routes d'admission1
Résumé présentoui

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