Shetland and Fair Isle IMMA

Size in Square Kilometres

14,208 km2

Qualifying Species and Criteria

Harbour seal – Phoca vitulina

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

Harbour porpoise – Phocoena phocoena

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

Grey Seal – Halichoerus grypus

Criterion C (1)

Killer whale – Orcinus orca

Criterion C (1,2)

Minke whale  – Balaenoptera acutorostrata

Criterion C (2)

Humpback whale – Megaptera novaeangliae

Criterion C (2,3)

Marine Mammal Diversity 

Criterion D (2)

Phoca vitulina, Phocoena phocoena, Orcinus orca, Halichoerus grypus, Balaenoptera acutorostrata, Grampus griseus, Megaptera novaeangliae, Lagenorhynchus acutus ,Lagenorhynchus albirostris

 

Summary

The IMMA of Shetland and Fair Isle comprises an archipelago of >100 islands situated 75km from the continental shelf edge. Its northerly position, exposure to Atlantic currents and varied habitats support a diverse range of marine mammals. Cetacean species such as killer whales (Orcinus orca), Risso’s dolphins (Grampus griseus) and harbour porpoises (Phocoena phocoena) are found here. Some pods of killer whales are considered semi-resident, Risso’s dolphins have shown site fidelity to particular areas and harbour porpoises are present year-round and form large aggregations of up to 200 individuals in the autumn and winter. Other cetaceans occur seasonally including common minke whales (Balaenoptera acutorostrata), which aggregate in the late summer/autumn, and humpback whales (Megaptera novaeangliae), which use Shetland to rest and feed during migration. This area is also an important pupping and haul-out area for seals, particularly harbour seals (Phoca vitulina), which, around Shetland, are an important part of the inshore killer whale diet. The continental shelf and nearshore deep-water areas it are important for large baleen whales, deep diving species and occasional large pods of pelagic dolphins, such as Atlantic white-sided dolphin (Lagenorhynchus acutus).

Description of Qualifying Criteria

Criterion B: Distribution and Abundance

Sub-criterion B2: Aggregations

The area provides important habitat for harbour porpoises (Phocoena phocoena), occurring year-round within the proposed IMMA (Waggitt et al., 2020). Seasonal aggregations have been recorded for the species including estimated aggregations of 50-100 individuals within sheltered bays in Shetland (Shetland Cetacean Group /SBRC/ UHI Shetland, unpublished data), and loose groups numbering 100 to 200 individuals have been recorded on occasions during a four-year porpoise study (1992-95) (Evans, 1997a; Sea Watch sightings database). Density distribution maps have been produced for several cetacean species including the harbour porpoise (Waggitt et al., 2020: Evans et al., 2021). These incorporate environmental variables into the density models and indicate the importance of the shelf seas around the Northern Isles (Shetland and Orkney) with above average densities of harbour porpoises. Modelling temporal changes between the 1980s and 2010s from surveys shows that densities of porpoises in summer months were higher in the region in earlier decades (1980s-90s), as reflected also in the abundance estimates from SCANS surveys between 1994 and 2016 (Hammond et al., 2002, 2013, 2017).

Although depleted by around 40% compared to the early 2000s, there is still a relatively high abundance of harbour seals (Phoca vitulina) at haul out sites in Shetland. The population is estimated to be almost 4,500 individuals (Special Committee on Seals (SCOS) 2022) which accounts for around 10% of the UK harbour seal population.  There are two Special Areas of Conservation (SACs) designated for harbour seal, one Site of Special Scientific Interest (SSSI) for grey seal and 47 designated seal haulouts.

Criterion C: Key Life Cycle Activities

Sub-criterion C1: Reproductive Areas

Harbour porpoises are known to utilise this area for mating, as observed directly during studies on the species in 1990-94 (Evans, 1997b), and shown by recent drone footage and visual observations collected by UHI Shetland and community members as part of a dedicated porpoise study. Small calves of harbour porpoises are regularly recorded in summer throughout the region (Evans 1996; 1997b; WDC, unpublished data; Shetland Cetacean Group, unpublished data) and the Scottish Marine Animal Strandings Scheme has several reports of porpoise neonates.

Mating activity by killer whales (Orcinus orca) has also been observed in the area (Walker and Harrop, 2003), whilst small calves are documented within a few weeks of being born and can be tracked for years as they remain with the mothers (see Scottish Killer Whale Photo ID catalogue). Studies undertaken as part of the Ecological Consequences of Orca Predation on Seals project (ECOPredS) have documented mating attempts, calf nursing and provided insight into family lineages. The animals seen in Shetland waters are split into three groups based on photo-ID evidence: offshore animals that associate with the herring and mackerel fisheries; ‘transient’ or Icelandic animals that have been recorded travelling between Scotland and Iceland; and others that, as “semi- residents,” – spend the bulk of their time in Scottish waters (Bolt et al., 2009; Deecke et al., 2011; Luque et al., 2006; Samarra and Foote, 2015). Three main pods are deemed to be semi-resident and are present in the proposed area year-round.

The resident harbour seal population breeds on the islands, although there are no recent pupping counts (SCOS, 2022). Two Special Areas of Conservation (SAC) are designated for harbour seal – Mousa SAC and Yell Sound Coast SAC.  Small numbers of grey seals (Halichoerus grypus) also breed in Shetland and are surveyed every year, weather permitting. However, there has been no recent estimate of overall pup production for Shetland due to the difficulties in obtaining repeat counts at remote colonies (SCOS, 2022).  A Site of Special Scientific Interest (SSSI) is designated in North Fetlar and a number of breeding haulouts are designated under the Marine Scotland Act 2010.

Sub-criterion C2: Feeding Areas

The combination of coastal and deep-sea features in such close proximity around Shetland provides important habitat for a diverse range of marine mammal prey species including sand eels (family Ammodytidae e.g. Mousa to Boddam MPA for sandeel grounds) and also commercial fish species such as herring (Clupea harengus) and mackerel (Scomber scombrus). Fish sonar surveys undertaken between 1992 and 1995 in south-east Shetland revealed significant associations between harbour porpoises and sandeels, in areas where several sandeel spawning grounds are located (Evans & Borges, 1995; Borges & Evans, 1997). Although sandeels have declined in abundance in the region since the early 1990s (Poloczanska et al., 2004; Lynam et al., 2013), the area remains important for porpoises, possibly related to a recovery in herring stocks in the region (Heessen et al., 2013; Evans & Waggitt, 2020a; Napier, 2022).

Minke whales (Balaenoptera acutorostrata) have been observed lunge feeding on shoals of fish in east Shetland such as Out Skerries, Whalsay, Mousa Sound and off Sumburgh Head (Evans, 1997a, b; Sea Watch, unpublished data; Shetland Cetacean Group, unpublished data), and stomach content analysis of minke whales shows that the predominant prey in the region are sandeels, herring and sprat (Clupea sprattus) (Olsen & Holst., 2001; Pierce et al., 2004).

Similarly, sightings of humpback whales (Megaptera novaeangliae) in Shetland have often included observations of feeding behaviour with minkes also feeding actively in the vicinity (Evans & Baines, 2010; Sea Watch Foundation sightings database). From shore-based watches, there are notable peaks in sightings and animal densities in late summer and autumn (Evans, 1997a, b; Sea Watch Foundation, unpublished data; WDC unpublished data; Shetland Cetacean Group unpublished data). Minke whales and humpback whales also show peak sightings that align with increases in sandeels and movements of sprats, herring and mackerel inshore.

The marine mammal species which come to feed on these prey, notably seals and harbour porpoises, in turn become prey to killer whales (Bolt et al., 2009). Studies undertaken as part of the Ecological Consequences of Orca Predation on Seals project (ECOPredS) have documented predation events through visual observations from land and drone footage from 2019 to present.  Observations have shown that the inshore groups of killer whale (both the semi-resident pods and the pods that travel to Iceland) regularly target both seal species and porpoises and that this occurs year-round.  In addition, the offshore group of killer whales have been observed offshore north and east of Shetland taking mackerel and herring from trawlers where numbers recorded closely associating with vessels are in the tens to low hundreds (Luque et al., 2006). The winter (October-March) pelagic trawl fishery for mackerel was identified as showing the strongest associations; During 33 hauls over 13 trips in January to February 2006, a total of 513 killer whales were observed, mainly north and east of Shetland (Luque et al., 2006). The authors concluded that during the mackerel fishing season, the whales were obtaining a significant proportion of their daily energy requirements from this source.

Sub-criterion C3: Migration Routes

The proposed area is an important habitat for migrating humpback whales, particularly in spring and autumn. Photo-ID research has recorded individuals present in Shetland which have also been photographed in Guadeloupe, the Azores, Cape Verde, Ireland and Norway, including the UK ‘s first match to both breeding and feeding grounds (Guadeloupe and Skerjvoy, Norway) (Jones et al., 2017; Scottish Humpback Photo ID catalogue). There have also been repeat matches between years of the same individuals returning to Shetland during their migration.  Approximately 50% of the individual animals in the Scottish Humpback Photo ID catalogue (currently numbering 116 individuals) have been sighted in Shetland waters. Although, humpbacks can be sighted throughout the year, there are clear peaks particularly in the autumn which correspond with their migration to feeding areas; Shetland Cetacean Group, unpublished data)

A WWF report Protecting Blue Corridors highlighted that Shetland is within the migratory corridor for humpback whales (see Johnson et al., 2022). This report used satellite tagging data from a variety of sources including Whaletrack. UiT – The Arctic University of Norway, which has had tagged whales transiting close to Shetland along with a wealth of other scientific studies to identify migratory routes that require protection.

Criterion D: Special Attributes

Sub-criterion D2: Diversity

Seventeen species of cetacean and seven species of pinniped) have been recorded in these waters, of which at least nine species of cetaceans and two species of seals occur regularly in the area, making it one of the most species-diverse areas in the British Isles (Evans, 1997a; Evans & Waggitt, 2020b). Shetland’s proximity to the continental shelf edge and deep bottom topography support multiple species with varied habitat preferences. Habitats range from the continental slope down to 500 m depth, the shelf edge, shelf seas, islands and skerries and shallow coastal waters including fjords (locally referred to as voes). Regular species here include harbour porpoises, minke whales, humpback whales, killer whales, Risso’s dolphins (Grampus griseus), white-beaked dolphins (Lagenorhynchus albirostris), Atlantic white-sided dolphins (Lagenorhynchus acutus), harbour seals and grey seals (Evans & Waggitt, 2020a, b; SCOS, 2022).

Shetland and Orkney are the most important areas in the UK for killer whales (Evans & Waggitt, 2020b), listed as Data Deficient by the IUCN Red List of Threatened Species (Reeves et al., 2017). Photo-ID data around Scottish waters have been compiled into a Scottish Killer Whale Photo ID Catalogue (Scullion et al., 2021), which contained around 220 individuals as of 2021. With the exception of the small ‘West coast community’ that occurs outside the boundaries of this IMMA, the majority of photo-identified individuals have been recorded in Shetland waters. The animals seen around Shetland are split into three groups based on photo-ID evidence: offshore animals that associate with the herring and mackerel fisheries, ‘transient’ or Icelandic animals that have been recorded travelling between Scotland and Iceland; and others that, as “semi- residents,” – spend the bulk of their time in Scottish waters (Bolt et al., 2009; Deecke et al., 2011; Luque et al., 2006; Samarra and Foote, 2015). Three main pods are deemed to be semi-resident and are present year-round in the waters around Shetland & Orkney.

Other species that are sighted occasionally on the shelf-slopes and deeper water at the edge of the IMMA include fin whales (Balaenoptera physalus), sei whales (Balaenoptera borealis), long-finned pilot whales (Globicephala melas), sperm whales (Physeter macrocephalus), and common dolphins (Delphinus delphis) (Evans & Waggitt, 2020b). Shetland also accounts for the majority of records in the UK of vagrant arctic seals (bearded seal, ringed seal, hooded seal, harp seal, and walrus) (Hall, 2008; Crawley et al., 2020). The shelf slope is important habitat for migrating great whales, and a century ago, supported a major whaling industry (Thompson,1928; Brown, 1976; Ryan et al., 2022), taking, particularly, fin whales in the Shetland-Faroe Channel.

Supporting Information

Bolt, H.E., Harvey, P.V., Mandleberg, L. and Foote, A.D. 2009. Occurrence of killer whales in Scottish inshore waters: temporal and social patterns relative to the distribution of declining harbour seal populations. Aquatic Conservation: Marine and Freshwater Ecosystems 19: 671-675.

Borges. L. and Evans, P.G.H. 1997. Spatial Distribution of the Harbour Porpoise and Fish Prey and their Associations in Southeast Shetland. N. Scotland. European Research on Cetaceans, 10: 262-265.

Brown, S.G. 1976. Modern whaling in Britain and the north-east Atlantic Ocean. Mammal Review, 6: 25-36.

Carter, M.I.D., L. Boehme, Cronin, M.A., Duck, C.D., Grecian, W.J., Hastie, G.D., Jessopp, M., Matthiopoulos, J., McConnell, B.J., Miller, D.L., Morris, C.D., Moss, S.E.W., Thompson, D., Thompson, P.M., and Russell, D.J.F. 2022. Sympatric Seals, Satellite Tracking and Protected Areas: Habitat-Based Distribution Estimates for Conservation and Management. Frontiers in Marine Science 9.

Crawley, D., Coomber, F., Kubasiewicz, L., Harrower, C., Evans, P., Waggitt, J., Smith, B., and Mathews, F. (Editors) Atlas of the Mammals of Great Britain and Northern Ireland. Published for The Mammal Society by Pelagic Publishing, Exeter. 205pp.

Deecke, V.B., Nykänen, M., Foote, A.D., and Janik, V.M. 2011. Vocal behaviour and feeding ecology of killer whales Orcinus orca around Shetland, UK. Aquatic Biology, 13: 79-88.

Evans, P.G.H. 1996. Identifying areas of summer concentrations for cetaceans in the Shetland Islands, North Scotland. Report to WWF-UK. Sea Watch Foundation, Oxford. 30pp

Evans, P.G.H. 1997a. Whales, dolphins and porpoises. Chapter 5.15. Pp. 126-130. In: Coasts and Seas of the United Kingdom. Region 1. Shetland. (Editors J.H. Barne, C.F. Robson, S.S. Kaznowska and J.P. Doody). Joint Nature Conservation Committee, Peterborough.

Evans, P.G.H. 1997b. Ecological studies of the Harbour Porpoise in Shetland, North Scotland. World Wide Fund for Nature, UK. 106pp.

Evans, P.G.H. and Borges, L. 1995. Associations between Porpoises, Seabirds and Their Prey in South-East Shetland, N. Scotland. European Research on Cetaceans, 9: 173-178.

Evans, P.G.H and Waggitt, J.J. 2020a. Impacts of climate change on marine mammals, relevant to the coastal and marine environment around the UK. MCCIP Science Review 2020, 421–455. doi: 10.14465/2020.arc19.mmm

Evans, P.G.H. and Waggitt, J.J. 2020b. Cetaceans. Pp. 134-184. In: Crawley, D., Coomber, F., Kubasiewicz, L., Harrower, C., Evans, P., Waggitt, J., Smith, B., and Mathews, F. (Editors) Atlas of the Mammals of Great Britain and Northern Ireland. Published for The Mammal Society by Pelagic Publishing, Exeter. 205pp.

Evans, P.G.H., Carrington, C., and Waggitt, J. 2021. Risk Assessment of Bycatch of Protected Species in Fishing Activities. European Commission, Brussels. 213pp.

Hall, A.J. 2008. Vagrant seals. Pp. 547-550. In: Mammals of the British Isles. (Eds. S. Harris and D.W. Yalden). Handbook. 4th Edition. The Mammal Society, Southampton. 800pp.

Hammond, P.S., Berggren, P., Benke, H., Borchers, D.L., Collet, A., Heide-Jørgensen, M.P., Heimlich, S., Hiby, A.R., Leopold, M.F., and Øien, N. 2002. Abundance of harbour porpoise and other cetaceans in the North Sea and adjacent waters. Journal of Applied Ecology, 39: 361-376.

Hammond, P.S., Macleod, K., Berggren, P., Borchers, D.L., Burt, M.L., Cañadas, A., Desportes, G., Donovan, G.P., Gilles, A., Gillespie, D., Gordon, J., Hiby, L., Kuklik, I., Leaper, R., Lehnert, ., Leopold, M., Lovell, P., Øien, N., Paxton, C.G.M., Ridoux, V., Rogan, E., Samarra, F., Scheidat, M., Sequeira, M., Siebert, U., Skov, H., Swift, R., Tasker, M.L., Teilmann, J., Van Canneyt, O. and Vázquez, J.A. 2013. Cetacean abundance and distribution in European Atlantic shelf waters to inform conservation and management. Biological Conservation, 164: 107–122.

Hammond, P.S., Lacey, C., Gilles, A., Viquerat, S., Borjesson, P., Herr, H., Macleod, K., Ridoux, V., Santos, M.B., Scheidat, M., Teilmann, J., Vingada, J., and Øien, N. 2021. Estimates of cetacean abundance in European Atlantic waters in summer 2016 from the SCANS-III aerial and shipboard surveys. Available at https://synergy.standrews.ac.uk/scans3/files/2017/05/SCANS-III-design-based-estimates-2017-05-12-final revised.pdf.

Heessen, H.J.L., Daan, N., and Ellis, J.R. 2015. Fish atlas of the Celtic Sea, North Sea and Baltic Sea. Wageningen Academic Publishers, KNNV Publishing, Wageningen, The Netherlands. 572pp.

Johnson, C.M., Reisinger, R.R., Palacios, D.M., Friedlaender, A.S., Zerbini, A.N., Willson, A., Lancaster, M., Battle, J., Graham, A., Cosandey-Godin, A., Jacob, T., Felix, F., Grilly, E., Shahid, U., Houtman, N., Alberini, A., Montecinos, Y., Najera, E., and Kelez, S. 2022. Protecting Blue Corridors – Challenges and solutions for migratory whales navigating national and international seas. Zenodo. https://doi.org/10.5281/zenodo.6196131

Jones, L, Bouveret, L, Stevick, P, Thomason B, Wenzel F, and Whooley, P. 2017. First humpback whale resighting from the British Isles to a breeding ground. Poster, 22nd Biennial Conference on the Biology of Marine Mammals DOI: 10.13140/RG.2.2.10831.18086

Luque, P.L., Davis, C.G., Reid, D.G., Wang, J.J., and Pierce, G.J. 2006. Opportunistic sightings of killer whales from Scottish pelagic trawlers fishing for mackerel and herring off North Scotland (UK) between 2000 and 2006. Aquatic Living Resources 19: 403–410. https ://doi.org/10.1051/ alr:2007009.

Lynam, C.P. Halliday, N.C., Höffle, H., Wright, P.J., van Damme, C.J.G., Edwards, M., and Pittoise, S.G. 2013. Spatial patterns and trends in abundance of larval sandeels in the North Sea: 1950–2005. ICES Journal of Marine Science, 70(3): 540-553. Available at: https://academic.oup.com/icesjms/article/70/3/540/916327.

Napier, I.R. 2022. Shetland Fisheries Statistics. University of Highlands & Islands Shetland, Scalloway, Shetland. 32pp, Available at: https://www.shetland.uhi.ac.uk/t4-media/one-web/shetland/research/statistics/shetland-fisheries-statistics/Shetland-Fisheries-Statistics-2021.pdf

Olsen, E. and Holst, J.C. 2001. A note on common minke whale (Balaenoptera acutorostrata) diets in the Norwegian Sea and the North Sea. Journal of Cetacean Research and Management, 3(2): 179–183.

Pierce, G.J, Santos. M.B, Reid. R.J, Patterson. I.A.P and Ross. H.M. 2004. Diet of minke whales Balaenoptera acutorostrata in Scottish (UK) waters with notes on strandings of this species in Scotland 1992–2002. Journal of the Marine Biological Association of the UK, 84: 1241–1244.

Poloczanska, E.S., Cook, R.M., Ruxton, G., and Wright, P. 2004. Fluctuations in sandeel biomass at Shetland: implications for the commercial fishery and breeding seabirds. ICES Journal of Marine Science, 61: 788-797. Available at:  https://www.researchgate.net/publication/230648157_Fluctuations_in_sandeel_biomass_at_Shetland_implications_for_the_commercial_fishery_and_breeding_seabirds

Ryan, C., Calderan, S., Allison, C., Leaper, R., and Risch, D. 2022. Historical occurrence of whales in Scottish Waters inferred from whaling records. Aquatic Conservation: Marine & Freshwater Ecosystems, 32: 1675–1692.

SCOS 2022. Scientific Advice on Matters Related to the Management of Seal Populations: 2022. Natural Environmental Research Council Special Committee on Seals, Sea Mammal Research Unit. University of St Andrews.

Samarra F.I.P., and Foote, A.D. 2015 Seasonal movements of killer whales between Iceland and Scotland. Aquatic Biology, 24: 75–79. https ://doi.org/10.3354/ab00637

Scullion, A.J., Harrop, H.R., Munro, K., Truluck, S.R., and Foote, A.D. 2021. Scottish Killer Whale Photo Identification Catalogue 2021. Accessed from Scottish Killer Whale Photo Identification Catalogue 2021.pdf

Waggitt, J.J., Evans, P.G.H., Andrade, J., Banks, A.N, Boisseau, O., Bolton, M., Bradbury, G., et al. 2020. Distribution maps of cetacean and seabird populations in the North-East Atlantic. Journal of Applied Ecology, 57: 253-269. doi: 10.1111/1365-2664.13525.

Walker, D and Harrop, H (2003), Notes on the social behaviour of Killer Whales off Shetland. Shetland Sea Mammal Report 2001 & 2002.

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