Bouvetøya and Surrounding Waters IMMA

Size in Square Kilometres

817,702 km2

Qualifying Species and Criteria

Antarctic fur seal – Arctocephalus gazella

Criterion B (2); C (1; 2)

Southern elephant seal – Mirounga leonina   

Criterion C (1; 2)

Marine Mammal Diversity 

Megaptera novaeangliae, Ommatophoca rossii

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Bouvetøya (Bouvet Island) is one of the most isolated islands on earth. Situated in the southern Atlantic Ocean, it hosts the second largest breeding population of Antarctic fur seals (Arctocephalus gazella) in the world as well as a small breeding population of southern elephant seals (Mirounga leonina). The isolation of the island accentuates its importance as a breeding haulout for pinnipeds that forage in the region. Tracking data has demonstrated how the waters surrounding the island within a radius of around 400 km serve as foraging grounds for resident Antarctic fur seals and elephant seals, but also pinnipeds that breed elsewhere, but visit these rich feeding grounds (e.g. Ross seals, Ommatophoca rossii, from Antarctica). Humpback whales (Megaptera novaeangliae) that breed along the coast of Africa also forage on the dense krill (Euphausia superba) biomass in the waters around the island. Despite being declared a Norwegian Nature Reserve in 1971, the waters surrounding the island have experienced significant illegal and unreported fishing activity, justifying further conservation status efforts.

Description of Qualifying Criteria

Criterion B: Distribution and Abundance

Sub-criterion B2: Aggregations 

Nyrøysa beach, on the west coast of Bouvet, represents arguably the largest single Antarctic fur seal aggregation globally (Hofmeyr et al. 2005). This one breeding aggregation presumably established in the mid-1950’s when a large landslide created the available substrate at Nyrøysa, has increased rapidly and currently supports ~2.5% of the global breeding population of the species.

Criterion C: Key Life Cycle Activities

Sub-criterion C1: Reproductive Areas

Antarctic fur seal pup production at Bouvet Island increased rapidly in the 1980s and 1990s, and has since stabilized at around 15000 pups per year (1996-2002), indicating a total population of about 66000 at the single site (Nyrøysa) monitored on the island (Hofmeyr et al. 2005). While the Bouvet population is (at least) the second largest for this species, pup production at the Nyrøysa beach monitoring site accounts for ~2.5% of the global total. The most recent estimations of pup production during expeditions in 2007, 2014 and 2017 seem to indicate continued stability or possibly a slight decline in pup production (Norwegian Polar Institute, unpublished data).

A small population of southern elephant seals breed and moult on the beaches of Nyrøysa, Bouvetoya (Kirkman et al. 2001). Expedition timing has precluded consistent or confident enumeration of the breeding population of elephant seals, although the total island population certainly contributes a small percentage to the global total (McMahon et al. 2005). However, the remoteness of this site provides the only potential breeding or moulting substrate for land-breeding pinnipeds within this vast oceanic sector – functionally surpassing its apparent numerical importance in a global perspective.

Sub-criterion C2: Feeding Areas

Tracking data show that lactating Antarctic fur seals that pup at Nyrøysa forage in an area within 200 km around Bouvet Island, ranging from over the mid-Atlantic ridge to the north of the island, to roughly equidistant regions west, south and to a lesser extent east of the island (Biuw et al. 2009, Blanchet et al. 2013, Lowther et al. 2014; see Figs 1-3).

Antarctic fur seals feed mainly on krill in waters around Bouvetøya, though they also do take variable amounts of myctophid fish (Kirkman et al. 2000, Tarroux et al. 2016). Subadult male (n = 7) and adult female (n = 12) southern elephant seals tracked after moulting (2007/2008) from Bouvet foraged in a vast expanse of ocean over a period spanning ~ 10 months. Males foraged all the way south to the Antarctic continent, while females tended to stay north of the ice edge or alternatively remained close to Bouvetøya, targeting the ACC (Biuw et al. 2010, Fig 4). Southern elephant seals from other populations, notably the Prince Edward Islands, also forage close to Bouvet Island (e.g. McIntyre et al. 2017).

Supporting Information

Barendse J, Carvalho I. 2016. A conservation assessment of Megaptera novaeangliae. In Child MF, Roxburgh L, Do Linh San E, Raimondo D, Davies-Mostert HT, editors. The Red List of Mammals of South Africa, Swaziland and Lesotho. South African National Biodiversity Institute and Endangered Wildlife Trust, South Africa

Biuw M, Nøst OA, Stien A, Zhou Q, Lydersen C, Kovacs KM. 2010. Effects of Hydrographic Variability on the Spatial, Seasonal and Diel Diving Patterns of Southern Elephant Seals in the Eastern Weddell Sea. PLoS ONE 5: e13816

Biuw M, Krafft BA, Hofmeyr GJG, Lydersen C, Kovacs KM. 2009. Time budgets and the at-sea behaviour of lactating female Antarctic fur seals Arctocephalus gazella at Bouvetøya. Marine Ecology Progress Series 385: 271-284.

Blanchet M-A, Biuw M, Hofmeyr GJG, de Bruyn PJN, Lydersen C, Kovacs KM. 2013. At-sea behaviour of three krill predators breeding at Bouvetøya – Antarctic fur seals, macaroni penguins and chinstrap penguins. Marine Ecology Progress Series 477: 285-302.

Blix AS, Nordoy ES. 2007. Ross seal (Ommatophoca rossii) annual distribution, diving behaviour, breeding and moulting, off Queen Maud Land, Antarctica. Polar Biology 30: 1449-1458.

Hoffman JI et al. 2018 A global cline in a colour polymorphism suggests a limited contribution of gene flow towards the recovery of a heavily exploited marine mammal. Royal Society Open Science 5: 181227.

Hofmeyr GJG, Krafft BA, Kirkman SP, Bester MN, Lydersen C, Kovacs KM. 2005. Population changes of Antarctic fur seals at Nyrøysa, Bouvetøya. Polar Biology 28: 725-731.

Kirkman SP, Hofmeyr GJG, Bester MN, Isaksen K. 2001. Counts of southern elephant seals, Mirounga leonina, at Bouvet Island. Polar Biology 24: 62-65.

Kirkman SP, Wilson W, Klages NTW, Bester MN, Isaksen K. 2000. Diet and estimated food consumption of Antarctic fur seals at Bouvetøya during summer. Polar Biology 23: 745-752.

Krafft BA, Melle W, Knutsen T, Bagøien E, Broms C, Ellertsen B, Siegel V. 2010. Distribution and demography of Antarctic krill in the Southeast Atlantic sector of the Southern Ocean during the austral summer 2008. Polar Biology 33: 957-968.

Lowther AD, Lydersen C, Biuw M, de Bruyn PJN, Hofmeyr GJG, Kovacs KM. 2014. Post-breeding at-sea movements of three central-place foragers in relation to submesoscale fronts in the Southern Ocean around Bouvetøya. Antarctic Science 26: 533-544.

McIntyre T, Bester MN, Bornemann H, Tosh CA, de Bruyn PJN. 2017. Slow to change? Individual fidelity to three-dimensional foraging habitats in southern elephant seals, Mirounga leonina. Animal Behaviour 127: 91-99.

McMahon CR, Bester MN, Burton HR, Hindell MA, Bradshaw CJA. 2005. Population status, trends and a re-examination of the hypotheses explaining the recent declines of the southern elephant seal Mirounga leonina. Mammal Review 35:82-100

Padilla A, Zeller D, Pauly D. 2015. The fish and fisheries of Bouvet Island. In: Palomares MLD and Pauly D (eds), Marine Fisheries Catches of Sub-Antarctic Islands, 1950-2010, p. 21-30. Fisheries Centre Research Report 23(1). Fisheries Centre, University of British Columbia, Vancouver, BC

Rosenbaum HC, Maxwell SM, Kershaw F, Mate B. 2014. Long-range movement of humpback whales and their overlap with anthropogenic activity in the South Atlantic Ocean. Conservation Biology 28:604-615.

Tarroux A, Lowther AD, Lydersen C, Kovacs KM. 2016. Temporal shift in the isotopic niche of female Antarctic fur seals from Bouvetøya. Polar Research 35: 31335.


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