Falkland Islands (Malvinas) Inner Shelf Waters IMMA

Size in Square Kilometres

23 643 km2

Qualifying Species and Criteria

Sei whale – Balaenoptera borealis

Criterion A; C (2)

Southern elephant seal – Mirounga leonina

Criterion B (2); C (1)

Peale’s dolphin – Lagenorhynchus australis

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

Commerson’s dolphin – Cephalorhynchus commersonii

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

South American fur seal – Arctocephalus australis

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

South American sea lion – Otaria byronia

Criterion C (1, 2)

Marine Mammal Diversity 

Criterion D (2)

Balaenoptera borealis, Mirounga leonina, Lagenorhynchus australis, Cephalorhynchus commersonii, Arctocephalus australis, Otaria byronia, Eubalaena australis, Orcinus orca, Megaptera novaeangliae, Balaenoptera acutorostrata, Balaenoptera bonaerensis

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This IMMA encompasses inner shelf waters from the coast to 100 m water depth around the Falkland Islands (Malvinas). It supports a globally-significant and annually-persistent seasonal feeding aggregation of Endangered sei whales (Balaenoptera borealis schlegelii), and provides important year-round habitat used for calving and feeding by Peale’s dolphins (Lagenorhynchus australis) and Commerson’s dolphins (Cephalorhynchus commersonii). The coastline provides breeding habitat for a globally-significant South American fur seal (Arctocephalus australis) population, and for the post-sealing recoveries of local breeding populations of southern elephant seal (Mirounga leonina) and South American sea lion (Otaria byronia). It also hosts an important moulting and resting aggregation of southern elephant seals from breeding populations of the South Georgia Stock. The IMMA is occupied by a high diversity of marine mammals, with other regular species including southern right whale (Eubalaena australis), humpback whale (Megaptera novaeangliae), minke whales (Balaenoptera acutorostrata & B. bonaerensis) and the killer whale (Orcinus orca).

Description of Qualifying Criteria

Criterion A – Species or Population Vulnerability

The sei whale is listed as a globally endangered (EN) species by the IUCN. The waters around the Falkland Islands (Malvinas) (hereafter termed ‘the Islands’) comprise a globally-significant feeding habitat (see Criterion B2 and C2 below), important for the southern sei whale’s (B. borealis schlegelii) survival and recovery. The IMMA has already been fully recognised as a Key Biodiversity Area (KBA) (https://www.keybiodiversityareas.org/site/factsheet/49174) for the species using KBA Criterion A (see Weir, 2021 for a full rationale).

 B: Distribution and Abundance

Sub-criterion B2: Aggregations

The IMMA supports a globally-significant seasonal aggregation of sei whales, including mother-calf pairs, juveniles, and adults of both sexes (Weir 2021, 2022a). Robust abundance estimates yielded design- and model-based estimates of 700–900 animals along the west coast of the Islands (Weir et al. 2021). The resulting density was at least two orders of magnitude higher than any recorded during large-scale abundance surveys for this species carried out worldwide (Weir et al. 2021). Habitat modelling and high numbers of incidental sightings in other areas support a likely occurrence of these densities all around the Islands (Baines and Weir 2020, Weir 2021). Movements of animals around the Islands have been evidenced by photo-identification and confirm linkage across the archipelago, supporting a single feeding aggregation (Weir 2022b).

The entire IMMA coastline is a hotspot for the haul out of both sexes and all ages of southern elephant seals during the moult phase (November to April) of their yearly cycle. These haul out sites are also used for the resting phase of juveniles during the winter months. The moulting seals originate from breeding populations of the South Georgia Stock, including at least the Valdes Peninsula, South Georgia, and the South Shetland Islands (King George Island, Livingstone Island and Elephant Island: ESRG, unpublished tagging and re-sighting data). Tagging work has shown that many of the seals visiting the Islands to moult exhibit site fidelity across years, and the IMMA coastlines therefore comprise an important moulting destination for the South Georgia Stock. A full census of the moulting aggregations in the Islands is not yet available, and would be challenging to achieve because different age-sex classes moult at different times of year. However, regular counts at Sea Lion Island and opportunistic counts at other haul out sites have shown that the number of moulters is large, and much higher than the number of breeding seals observed at the same sites. Moreover, detailed daily counts at Sea Lion Island over various seasons to incorporate the timing of different sex and age classes during the moult, indicate that the total number of moulters over a season is approximately four times higher than single counts made during the peak haul out. Altogether, the available information suggests that a very large number (in the order of tens of thousands) of southern elephant seals from the South Georgia Stock use the Islands during their moult, which is a crucial phase of their yearly cycle.

The total global population size of South American fur seals is around 219,000 animals (Cárdenas-Alayza et al. 2016), and the Islands host 50% of that population (Bayliss et al. 2021). The IMMA is therefore a globally-important aggregation site for that species, and is used for reproduction, foraging, moulting and resting behaviours (see C1 and C2).

The inner shelf waters around the Islands are occupied year-round by important proportions of the global populations of Peale’s dolphin and Commerson’s dolphin. The distribution of Peale’s dolphins around the Islands extends continuously from the coast to the 200 m depth isobath (White et al. 2002). Habitat modelling predicts high occurrence of the species along many of the exposed coastlines (Baines and Weir 2020) and in more pelagic areas adjacent to the 100 m depth isobath (Franchini et al. 2020). Combined abundance estimates for Peale’s dolphins in the Atlantic part of their range are of ~21,800 animals (Heinrich and Dellabianca 2019), of which an estimated 1,896 animals (CV = 0.33) occurred in coastal waters around the Islands (Costa and Cazzola 2018). The proposed site therefore includes a significant proportion (8.7%) of the known Atlantic population of the species, which only occurs around the southern region of South America. Many of the same individuals have been photographed in coastal study areas over multiple years (Costa and Cazzola 2018, Falklands Conservation unpublished data), indicating long-term residency.

Densities of Commerson’s dolphins around the Islands are highest in coastal and shallow shelf waters (White et al. 2002). Habitat modelling also supports the importance of inshore habitat for the species (Baines and Weir 2020, Franchini et al. 2020). Despite their discrete distribution, genetic analysis does not support the existence of a distinct subspecies around the Islands but rather indicates some migration between the Islands and South America (Kraft et al. 2021). Surveys of Argentinean waters (which comprise the majority of the global species range) from the coast to the 100 m isobath, estimated the abundance of Commerson’s dolphin as ~40,000 animals (Pedraza 2008) and 21,933 animals (Dellabianca et al. 2016) respectively; those estimates resulted from different methods and surveyed areas, but are in the same order of magnitude (Crespo et al. 2018). In that context, the 5,789 animals (CV=0.18: Costa and Cazzola 2018) animals recorded in coastal waters around the Islands represents a meaningful proportion of the known Atlantic population. Many of the same individuals have been photographed over multiple months and years supporting their seasonal and long-term residency in the region (Costa and Cazzola 2018, Weir 2018, Falklands Conservation unpublished data).

Criterion C: Key Life Cycle Activities

Sub-criterion C1: Reproductive Areas

South American fur seals breed on islands and rocky outcrops around the coastline of the Islands, forming dense colonies at some localities. Following heavy exploitation by 19th Century sealers, the Islands now host the world’s largest breeding population of the species, with an estimated pup abundance in 2018 of ~36,500 animals (Baylis et al. 2019a) and in 2021 of ~44,000 animals (Baylis et al. 2021). The Jasons in the north-west of the Islands are particularly important, accounting for 97% of total pup production in the Islands (Baylis et al. 2019a, 2021). Pups are born in the austral summer and are dependent on their mothers for approximately 11 months. Adult females also mate in the area shortly after giving birth. The Islands therefore represent an important reproductive habitat used by a large proportion of the species for mating, pupping and a prolonged nursing period.

The coast of the IMMA is used for reproduction by southern elephant seals, with the two main current breeding colonies comprising Sea Lion Island with 730 breeding females in 2022 and Carcass Island with 173 breeding females in 2016 (Galimberti and Boitani 1999, ESRG, unpublished data), and small scattered pockets of breeding seals elsewhere. These colonies comprise only a small proportion of the regional population, where the two major breeding areas are located at South Georgia (113,000 breeding females: Boyd et al. 1996) and at the Valdés Peninsula in Argentina (14,000 breeding females: Lewis et al. 2004). However, they are a remnant of previously-large breeding populations in the Islands that were decimated by intensive and indiscriminate sealing in the 1800s (Strange 1972), and their slow recovery is therefore considered an important contribution to local biodiversity and to maintaining a demographic and genetic link between the South Georgia and Valdés Peninsula breeding areas (Fabiana et al. 2003).

A total of 5,375 (preliminary figure) southern sea lion pups were counted at 72 breeding sites around the coast of the Islands during the 2021 census (Baylis et al. 2021). This species experienced an order-of-magnitude decline in the Islands between the 1930s and 1960s due to commercial sealing and environmental factors, and the 5,375 pups counted in 2021 represent ~7% of the 1930s estimate of 80,555 pups (Baylis et al. 2015). The IMMA comprises an important regional reproductive area that is supporting recovery of the population within the Islands.

Inshore waters around the Islands are used year-round by significant populations of Peale’s dolphins and Commerson’s dolphins (see Criterion B1). The IMMA comprises core habitat used by both species for mating, calving and nursing (Costa and Cazzola 2018, Weir 2018, Falklands Conservation unpublished data), with young calves being observed particularly between December and March over the austral summer and autumn.

Sub-criterion C2: Feeding Areas

The IMMA comprises an important Southern Hemisphere feeding area for sei whales, and is one of few neritic feeding grounds documented for the species globally. Research since 2017 has shown that feeding aggregations of the species use the area between (at least) November and June each year (Weir 2022a). Faecal sampling, suction cup tagging and observations of surface feeding, indicate that sei whales in the Islands predate crustaceans including squat lobster krill and amphipods including Themisto gaudichaudii (Weir et al. 2019, Jackson et al. 2022, Segre et al. 2022, Weir 2022a). The seasonal foraging aggregations are persistent across years, and photo-identification has evidenced the same animals returning in different years, confirming long-term site fidelity to this feeding ground (Weir 2022b).

The Islands are used year-round by resident populations of Peale’s dolphins and Commerson’s dolphins. Feeding has been difficult to observe in these species, although Commerson’s dolphins have occasionally been seen predating schools of small (unidentified) fish in shallow areas (Falklands Conservation, unpublished data). However, it is reasonable to presume that both species feed within the IMMA given the high site fidelity of individual animals over both the short (days) and long (years) term. Killer whales also feed throughout the region, on prey known to include pinnipeds and cetaceans including sei whales (Falklands Conservation, unpublished data).

Telemetry studies have shown that the inner shelf waters around the Islands comprise important foraging habitat for South American fur seals, particularly over the months where adult females are lactating (especially early in the season in summer and autumn) and remain closer to shore (Thompson et al. 2003). The majority of foraging dives occur in waters <100 m depth, although that varies between colonies (Thompson et al. 2003, Bayliss et al. 2018). The IMMA also has high overlap with areas used for foraging by South American sea lions from haul outs located within the Islands, although those foraging areas continue into deeper waters beyond the proposed IMMA boundaries (Bayliss et al. 2019b). While southern elephant seals do forage in the south-east region of the IMMA, the majority of their feeding occurs in deeper slope waters located south and south-west of the Islands (Augé et al. 2018; Baylis et al. 2019b) and that area is proposed as a separate IMMA. Criterion D: Special Attributes

Sub-criterion D2: Diversity

The shallow shelf waters of the IMMA provide important habitat for a high diversity of marine mammal species. Regionally-important populations of three species of pinniped (South American fur seal, southern elephant seal and South American sea lion) and two species of dolphin (Peale’s dolphin and Commerson’s dolphin) both breed and forage in the IMMA, as described under Criteria B and C.

The area is used as a neritic feeding ground by several species of baleen whale, particularly high densities of the endangered sei whale. Additionally, southern right whales (Eubalaena australis) use the area as a feeding ground during summer and autumn, and during their seasonal migrations (Weir and Stanworth 2020). While no humpback whales (Megaptera novaeangliae) were recorded during targeted boat-based whale surveys within the site in 2017 to 2020, an influx of this species occurred during 2021 (Weir 2022a) and involved individuals actively lunge-feeding along the edges of giant kelp beds (Macrocystis pyrifera) and occurring as feeding aggregations in more open waters. While both right whales and humpback whales forage in the IMMA, robust information on their abundance and the importance of the site as a feeding ground for those species is not yet available. However, a strip of habitat located close to the north-east coast of the Islands is known to comprise an important winter reproductive area for southern right whales, and that area is proposed as a separate IMMA. The site is also used by minke whales (Balaenoptera acutorostrata / B. bonaerensis), potentially for both feeding (indicated by summer sightings close to kelp beds) and reproductive activity (calls have been recorded in winter during acoustic monitoring: Falklands Conservation unpublished data).

Killer whales (Orcinus orca) also inhabit the IMMA, and the waters around Sea Lion Island (located off the south coast of the Islands) are used extensively by a small number of animals that prey on pinnipeds breeding on the island (http://www.eleseal.org/). Sea Lion Island is a discrete and important marine mammal habitat for which a separate IMMA is proposed, but the species is also known to range throughout the shelf shallow waters of this proposed site (e.g. Weir 2018).

A variety of other marine mammal species are occasionally seen or stranded in the cIMMA, but are considered rare and are therefore not included under D2.

Supporting Information

Arkhipkin, A., Brickle, P. and Laptikhovsky, V. 2018. Links between marine fauna and oceanic fronts on the Patagonian Shelf and Slope. Arquipelago. Life and Marine Sciences, 30:19–37.

Augé, A.A., M.P. Dias, B. Lascelles, A.M.M. Baylis, A. Black, P.D. Boersma, P. Catry, S. Crofts, F. Galimberti, J.P. Granadeiro, A. Hedd, K. Ludynia, J.F. Masello, W. Montevecchi, R.A. Phillips, K. Pütz, P. Quillfeldt, G.A. Rebstock, S. Sanvito, I.J. Staniland, A. Stanworth, D. Thompson, M. Tierney, P.N. Trathan and J.P. Croxall. 2018. Framework for mapping key areas for marine megafauna to inform Marine Spatial Planning: The Falkland Islands case study. Marine Policy, 92:61–72.

Baines, M. and Weir, C.R. 2020. Predicting suitable coastal habitat for sei whales, southern right whales and dolphins around the Falkland Islands. PLOS ONE, 15(12):e0244068. https://doi.org/10.1371/journal.pone.0244068

Baylis, M.M., Orben, R.A., Arnould, J.P.Y., Christiansen, F., Hays, G.C. and Staniland, I.J. 2015. Decline of sea lions. The Bulletin of the Ecological Society of America, 96(4):635–638.

Baylis, A.M.M., Tierney, M., Orben, R.A., Staniland, I.J. and Brickle, P. 2018. Geographic variation in the foraging behaviour of South American fur seals. Marine Ecology Progress Series, 596:233–245.

Baylis, A.M.M., Orben, R.A., Arkhipkin, A.A., Barton, J., Brownell, R.J. Jr., Staniland, I.J. and Brickle, P. 2019a. Re‐evaluating the population size of South American fur seals and conservation implications. Aquatic Conservation: Marine and Freshwater Ecosystems, 29(11):1988–1995.

Baylis, A.M.M., M. Tierney, R.A. Orben, V. Warwick-Evans, E. Wakefield, W.J. Grecian, P. Trathan, R. Reisinger, N. Ratcliffe, J. Croxall, L. Campioni, P. Catry, S. Crofts, P.D. Boersma, F. Galimberti, J.P. Granadeiro, J. Handley, S. Hayes, A. Hedd, J.F. Masello, W.A. Montevecchi, K. Pütz, P. Quillfeldt, G.A. Rebstock, S. Sanvito, I.J. Staniland and P. Brickle. 2019b. Important at-sea areas of colonial breeding marine predators on the Southern Patagonian Shelf. Scientific Reports, 9:8517. https://doi.org/10.1038/s41598-019-44695-1

Baylis, A., Poncet, L. and Orben, R. 2021. 2021 census of southern sea lions and South American fur seals breeding at the Falkland Islands: preliminary results. ESB funding report to Falkland Islands Government. Available at:


Boyd, I.L., Walker, T.R. and Poncet, J. 1996. Status of southern elephant seals at South Georgia. Antarctic Science, 8(3):237–244.

Cárdenas-Alayza, S., Oliveira, L. and Crespo, E. 2016. Arctocephalus australis. The IUCN Red List of Threatened Species 2016: e.T2055A45223529. https://dx.doi.org/10.2305/IUCN.UK.2016-1.RLTS.T2055A45223529.en. Accessed on 08 December 2022.

Costa, M. and Cazzola, M. 2018. Dolphins of the kelp: Data priorities for Falkland’s inshore cetaceans. Darwin Plus: Final Report. Accessed on 25 February 2020 from: https://www.south-atlantic-research.org/wp-content/uploads/2019/05/DPLUS042_Final_Report_31Dec18.pdf

Crespo, E., Olavarria, C., Dellabianca, N., Iñíguez, M., Ridoux, V. and Reeves, R. 2018. Cephalorhynchus commersonii (errata version published in 2018). The IUCN Red List of Threatened Species 2017: e.T4159A128963283. Accessed on 27 October 2022.

Dellabianca, N.A., Pierce, G.J., Raya Rey, A., Scioscia, G., Miller, D.L., Torres, M.A., Paso Viola, M.N., Goodall, R.N.P. and Schiavini, A.C.M. 2016. Spatial models of abundance and habitat preferences of Commerson’s and Peale’s dolphin in southern Patagonian waters. PLoS ONE,11(10):e0163441. doi:10.1371/journal.pone.0163441.

Fabiani, A., Hoelzel, A.R., Galimberti, F. and Meulbert, M.M.C. 2003. Long-range paternal gene flow in the southern elephant seal. Science, 299(5607):676. doi: 10.1126/science.299.5607.676.

Franchini, F., Smout, S., Blight, C., Boehme, L., Munro, G., Costa, M. and Heinrich, S. 2020. Habitat partitioning in sympatric delphinids around the Falkland Islands: predicting distributions based on a limited data set. Frontiers in Marine Science, 7:277. doi: 10.3389/fmars.2020.00277

Galimberti, F. and Boitani, L. 1999. Demography and breeding biology of a small, localized population of southern elephant seals (Mirounga leonina). Marine Mammal Science, 15(1):159–178. doi: 10.1111/j.1748-7692.1999.tb00787.x

Heinrich, S. and Dellabianca, N. 2019. Lagenorhynchus australis. The IUCN Red List of Threatened Species 2019: e.T11143A50361589. https://dx.doi.org/10.2305/IUCN.UK.2019-1.RLTS.T11143A50361589.en. Accessed on 27 October 2022.

Jackson, J.A., Buss, D.L., Carroll, E.L. and Weir, C.R. 2022. Genetics. In: Conserving Falklands’ whale populations: addressing data deficiencies for informed management, Weir, C.R. (ed.), pp. 152–164. Technical Report for DPLUS082. Falklands Conservation, Stanley, Falkland Islands. Version 2, 25 Oct 2022. http://www.ketosecology.co.uk/PDF/DPLUS082_Tech_Rep_FINAL.pdf

Kraft, S., Pérez-Alvarez, M., Olavarría, C., Moraga, R., Baker, C.S., Steel, D., Tixier, P., Guinet, C., Viricel, A., Brickle, P., Costa, M., Crespo, E., Durante, C., Loizaga, R. and Poulin, E. 2021. From settlers to subspecies: genetic differentiation in Commerson’s dolphins between South America and the Kerguelen Islands. Frontiers in Marine Science, 8:782512. doi: 10.3389/fmars.2021.782512

Lewis, M., Campagna, C. and Zavatti, J. 2004. Annual cycle and inter-annual variation in the haul out pattern of an increasing southern elephant seal colony. Antarctic science, 16(3):219–226.

Otley, H., Munro, G., Clausen, A. and Ingham, B. 2008. Falkland Islands State of the Environment Report 2008. Falkland Islands Government and Falklands Conservation, Stanley.

Pedraza, S.N. 2008. Ecología poblacional de la tonina overa Cephalorhynchus commersonii (Lacépède, 1804) en el litoral Patagónico. Ph.D. Thesis, University of Buenos Aires.

Peterson, R.G. and Whitworth, T. 1989. The Subantarctic and Polar fronts in relation to deep water masses through the Southwestern Atlantic. Journal of Geophysical Research, 94:10817–10838.

Segre, P.S. and Weir, C.R. 2022. Suction cup tagging. In: Conserving Falklands’ whale populations: addressing data deficiencies for informed management, Weir, C.R. (ed.), pp. 165–174. Technical Report for DPLUS082. Falklands Conservation, Stanley, Falkland Islands. Version 2, 25 Oct 2022. http://www.ketosecology.co.uk/PDF/DPLUS082_Tech_Rep_FINAL.pdf

Strange, I. 1972. Sealing industries of the Falkland Islands. The Falkland Islands Journal, 1972:13–21.

Thompson, D., Moss, S.E.W. and Lovell, P. 2003. Foraging behaviour of South American fur seals Arctocephalus australis: extracting fine scale foraging behaviour from satellite tracks. Marine Ecology Progress Series, 260:285−296

Weir, C.R. 2018. A preliminary assessment of endangered sei whales (Balaenoptera borealis) in two candidate Key Biodiversity Areas in West Falkland (Falklands Conservation report, Version 1.2). Available at: https://www.ketosecology.co.uk/research/sei-whales/

Weir, C.R. 2021. Supporting evidence for the proposal of Falkland Islands Inner Shelf Waters as a KBA for endangered sei whales (Balaenoptera borealis). Falklands Conservation, Stanley, Falkland Islands. 36pp. Available at: http://www.ketosecology.co.uk/PDF/Weir(2021)_KBA_TechRep.pdf

Weir, C.R. 2022a. Whale distribution during small boat surveys. In: Weir, C.R. (ed.), Conserving Falklands’ whale populations: addressing data deficiencies for informed management, pp. 22–87. Technical Report for DPLUS082. Falklands Conservation, Stanley, Falkland Islands. Version 2, 25 Oct 2022. 231 pp. Available at: http://www.ketosecology.co.uk/PDF/DPLUS082_Tech_Rep_FINAL.pdf

Weir, C.R. 2022b. Photo-identification. In: Weir, C.R. (ed.), Conserving Falklands’ whale populations: addressing data deficiencies for informed management, pp. 88–122. Technical Report for DPLUS082. Falklands Conservation, Stanley, Falkland Islands. Version 2, 25 Oct 2022. 231 pp. Available at: http://www.ketosecology.co.uk/PDF/DPLUS082_Tech_Rep_FINAL.pdf

Weir, C.R. and Stanworth, A. 2020. The Falkland Islands (Malvinas) as sub-Antarctic foraging, migratory and wintering habitat for southern right whales. Journal of the Marine Biological Association of the United Kingdom, 100:153–163.

Weir, C.R., Stanworth, A., Cartwright, S., Jelbes, P.A.Q., Taylor, M. and Pompert, J. 2019. Distribution and movements of sei whales (Balaenoptera borealis) on coastal feeding grounds in the Falkland Islands (Malvinas). World Marine Mammal Conference, Barcelona, Spain, December 2019.

Weir, C.R., Taylor, M., Jelbes, P.A.Q., Stanworth, A. and Hammond, P.S. 2021. Distribution and abundance of sei whales off the west coast of the Falkland Islands. Marine Mammal Science, 37:919–933. DOI: 10.1111/mms.12784

White, R.W., Gillon, K.W., Black, A.D. and Reid, J.B. 2002. The distribution of seabirds and marine mammals in Falkland Islands waters. JNCC Report. ISBN 1 86107 534 0.


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