Mécatina Trough and Strait of Belle Isle IMMA
Size in Square Kilometres
13 317 km2
Qualifying Species and Criteria
Fin Whale – Balaenoptera physalus
Criterion A; Criterion B (2)
Hooded Seal – Cystophora cristata
Criterion A; Criterion C (3)
Humpback Whale – Megaptera novaeangliae
Criterion B (2); Criterion C (2)
Harp Seal – Pagophilus groenlandicus
Criterion B (2); Criterion C (1, 2, 3)
Marine Mammal Diversity
Balaenoptera physalus, Cystophora cristata, Megaptera novaeangliae, Pagophilus groenlandicus, Balaenoptera acutorostrata, Balaenoptera musculus, Delphinus delphis, Globicephala melas, Halichoerus grypus, Lagenorhynchus acutus, Lagenorhynchus albirostris, Orcinus orca, Phoca vitulina, Phocoena phocoena
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Summary
The Mécatina Trough and Strait of Belle Isle IMMA is located in the northeastern Gulf of St. Lawrence, Canada. The area is characterized by persistent aggregations of deep-dwelling zooplankton in the mesoscale basin (Mecatina Trough), where they remain largely trapped due to local bathymetry. Within the IMMA there are: two threatened species; hooded seals (Cystophora cristata) and fin whales (Balaenoptera physalus). The area also serves as a breeding ground for harp seals (Pagophilus groenlandicus), where 10-15% of the pups for the global population of harp seals are produced in good ice years. The area’s high productivity provides a feeding area for humpback (Megaptera novaeangliae) and fin whales (summer/fall), and harp seals (fall/winter). Finally, the area includes a migratory corridor for hooded seals and harp seals. The area appears to sustain a high diversity of marine mammals (15 species), although data remains limited for several species to document their relative abundance or recurrent use of the IMMA.
Description of Qualifying Criteria
Criterion A – Species or Population Vulnerability
Several species in this IMMA are considered threatened with extinction according to the IUCN Red List. Blue whales (Balaenoptera musculus) are considered Endangered globally (Cooke 2018a). Hooded seals (Cystophora cristata) and fin whales (Balaenoptera physalus) are both assessed as Vulnerable (Kovacs 2016; Cooke 2018b).
At the national level in Canada, Northwest Atlantic blue whales (Balaenoptera musculus) are considered Endangered, fin whales and killer whales (Orcinus orca) are of Special Concern, and all three are afforded protection under the Canadian Species at Risk Act. Harbour porpoises (Phocoena phocoena) are listed as Least Concern globally (Braulik et al. 2023), however, they have been assessed as Special Concern in Canada (COSEWIC 2022), and are currently considered for listing under the Species at Risk Act.
Criterion B: Distribution and Abundance
Sub-criterion B2: Aggregations
Basque and Breton whalers and others after them exploited marine mammals in the Mécatina Trough and Strait of Belle Isle area, which was referred to as the Grand Bay at the time (Mitchell and Reeves 1983; Barkham 1984). Following boat-based and aerial surveys of the area in 1981 and 1982, it was recommended to make the Mécatina Trough and Belle Isle Strait a marine park given the observed diversity and abundance of cetaceans (Sears and Williamson 1982). While this testifies to the historical and long-standing abundance of marine mammals in this area, recent data on marine mammal aggregations and relative abundance are scarce given the remoteness of the area.
Large-scale systematic surveys and passive acoustic monitoring indicate that the Mécatina Trough is associated with the highest densities of humpback whales (Megaptera novaeangliae) in the Gulf of St. Lawrence (Lesage et al. 2007) and highest recurrence of presence of humpback whales in eastern Canada (Delarue et al. 2022). An ocean-basin wide mark-recapture study of humpback whales from the 1990’s also supports their high relative abundance in both the Mécatina Trough and Belle Isle Strait, a sampling site chosen specifically for the predicted high abundance of the species (see Smith et al. 1999). Humpback whale calls are heard on, or nearly on, a daily basis in the Mécatina Trough from early summer through early winter (no acoustic data available during winter or from the Belle Isle Strait; Delarue et al. 2022). There is no estimate of abundance specific to the IMMA. However, even though this area was under-sampled compared to others in the Gulf of St. Lawrence, the number of unique individuals identified in the IMMA (500 IDs) was at least 2.5 fold those of any other sampled sites in the Gulf (Ramp 2008).
Harp seals (Pagophilus groenlandicus ) enter the Gulf of St. Lawrence in late fall / early winter to feed and reproduce. The pack ice in the Mécatina Trough represents one of the three main whelping areas for this species (Sergeant 1991; Stenson et al. 1995; 2000; 2022). In good ice years for instance, 10 – 15% of the global pup production is associated with this area (assuming western North Atlantic harp seals represent 80% of the Global population; Kovacs 2015). This means also that at least a similar proportion of reproducing females and of accompanying adult males waiting to mate with females also occur in this area. Late autumn / winter feeding aggregations also form there prior to and after whelping (Sergeant 1991).
Fin whale absolute densities and abundance in the IMMA is unknown. However, a recent study reports daily acoustic detections in the Mécatina Trough from late summer and throughout the fall (no data for other periods; Delarue et al. 2022). Fin whales may be using the Strait of Belle Isle mainly in the fall, as suggested by a one-year mooring in this specific area (summer/fall only; Roy et al. 2018). Whether fin whales use the Strait for feeding, migration, or both is unknown.
Criterion C: Key Life Cycle Activities
Sub-criterion C1: Reproductive Areas
Harp seals whelp in the IMMA when ice conditions are favourable. In 2017 for instance, 100,000 out of 700,000 harp seal pups from the Northwest Atlantic population were counted in this area (Stenson et al. 2022). Given that approximately 200,000 additional pups are produced by the other two populations, this represents more than 10% of the global pup production (Kovacs 2015).
Sub-criterion C2: Feeding Areas
The Mécatina Trough/Strait of Belle Isle area is characterized by persistent aggregations of deep-dwelling zooplankton in the mesoscale basin (Mécatina Trough), where they largely get trapped due to local bathymetry (Sourisseau et al. 2006; DFO 2009). Prey aggregations, however, likely spill out of the Trough into the nearby Strait of Belle Isle given densities of marine mammals observed there during summer (see Lesage et al. 2007; Lawson and Gosselin 2009; Lawson and Stevens 2014). The IMMA is a feeding area for humpback whales and harp seals, and for several other species, including killer whales, minke whales, harbour porpoises, white-beaked dolphins, to name a few (Sears and Williamson 1982). Direct evidence of foraging for these species is however limited, arising from anecdotal reports of surface feeding and coincidence between high prey abundance and use of the area by marine mammals during their feeding period (Sergeant and Fisher 1957; Sears and Williamson 1982).
Sub-criterion C3: Migration Routes
Hooded seals migrate between the Gulf of St. Lawrence where a portion of the population reproduces during winter, and northern latitudes where they feed and moult during the rest of the year. Satellite telemetry data confirms the importance of the Belle Isle Strait as a migratory exit route for animals breeding in the Gulf of St. Lawrence (Bajzak et al. 2009; Vacquié-Garcia et al. 2024).
Satellite telemetry indicates that harp seals also use the Strait of Belle Isle as a migratory route between their whelping area in the Gulf of St. Lawrence and their feeding area in Greenland (Grecian et al. 2022; see also Sergeant 1991).
Criterion D: Special Attributes
Criterion D2 – Diversity
Fifteen species of marine mammals occur on a regular basis in the IMMA, some with more rigorously documented occurrences than others. Such a high diversity of species is among the highest described in eastern Canadian waters (e.g., Lesage et al. 2007; Sears and Williamson 1982; Convention on Biological Diversity 2014). While a wider diversity of marine mammal species likely occurs in warmer ecosystems off the eastern U.S. (e.g., Schick et al. 2011), it appears that the IMMA still stands among the subarctic areas with the highest diversity of marine mammals reported in the literature. Species with well-documented presence in the IMMA include harp and hooded seals, and fin and humpback whales. Other species known to occur on a regular basis in the IMMA, but which are not as well documented, include blue, killer (Orcinus orca) and minke whales (Balaenoptera acutorostrata), harbour porpoises (Phocoena Phocoena), and long-finned pilot whales (Globicephala melas), multiple dolphin species, particularly white-beaked dolphins (Lagenorhynchus albirostris), as well as harbour seals (Phoca vitulina) and grey seals (Halichoerus grypus) (Sergeant and Fisher 1957; Boulva and McLaren 1979; Sears and Williamson 1982; Lesage et al. 2007; Lawson and Stevens 2014).
Supporting Information
Bajzak, C., Côté, S.D., Hammill, M.O., Stenson, G.B. 2009. Intersexual differences in the postbreeding foraging behaviour of the Northwest Atlantic hooded seal. Mar. Ecol. Prog. Ser. 385: 285-294.
Barkham, S. H. 1984. The Basque whaling establishments in Labrador 1536-1632 — A summary. Arctic 37: 515-519. https://pubs.aina.ucalgary.ca/arctic/Arctic37-4-515.pdf
Boulva, J., McLaren, I.A. 1979. Biology of the harbour seal, Phoca vitulina, in Eastern Canada, Bulletin of the Fisheries Research Board of Canada 200: 25 p.
Braulik, G.T., Minton , G., Amano, M. & Bjørge, A. 2023. Phocoena phocoena (amended version of 2020 assessment). The IUCN Red List of Threatened Species 2023: e.T17027A247632759. https://dx.doi.org/10.2305/IUCN.UK.2023-1.RLTS.T17027A247632759.en
Convention on Biological Diversity. 2014. Northwest Atlantic regional workshop to facilitate the description of Ecologically or Biologically Significant marine Areas, Montreal, 24 to 28March 2014 https://www.cbd.int/doc/meetings/mar/ebsaws-2014-02/official/ebsaws-2014-02-04-en.pdf
Cooke, J.G. 2018a. Balaenoptera musculus (errata version published in 2019). The IUCN Red List of Threatened Species 2018: e.T2477A156923585. https://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T2477A156923585.en
Cooke, J.G. 2018b. Balaenoptera physalus. The IUCN Red List of Threatened Species 2018: e.T2478A50349982. https://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T2478A50349982.en
COSEWIC. 2022. COSEWIC assessment and status report on the Harbour Porpoise Phocoena phocoena, Northwest Atlantic population, in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xii + 46 pp.
Delarue, J.J.-Y., Moors-Murphy, H., Kowarski, K.A., Davis, G.E., Urazghildiez, I.R., Martin, S.B. 2022. Acoustic occurrence of baleen whales, particularly blue, fin, and humpback whales, off eastern Canada, 2015−2017. Endang Species Res 47: 265-289. https://doi.org/10.3354/esr01176
DFO. 2009. Conservation objectives for the Ecologically and Biologically Significant Areas (EBSA) of the Estuary and Gulf of St. Lawrence. DFO Can. Sci. Advis. Sec. Sci. Advis. Rep. 2009/049. https://waves-vagues.dfo-mpo.gc.ca/library-bibliotheque/338284.pdf
Grecian WJ et al. 2022. Environmental drivers of population-level variation in the migratory and diving ontogeny of an Arctic top predator. R. Soc. Open Sci. 9: 211042. https://doi.org/10.1098/rsos.211042
Kovacs, K.M. 2015. Pagophilus groenlandicus. The IUCN Red List of Threatened Species 2015: e.T41671A45231087. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T41671A45231087.en
Kovacs, K.M. 2016. Cystophora cristata. The IUCN Red List of Threatened Species 2016: e.T6204A45225150. https://dx.doi.org/10.2305/IUCN.UK.2016-1.RLTS.T6204A45225150.en
Lawson. J.W., and Gosselin, J.-F. 2009. Distribution and preliminary abundance estimates for cetaceans seen during Canada’s marine megafauna survey – A component of the2007 TNASS. DFO Can. Sci. Advis. Sec. Res. Doc. 2009/031. vi + 28 p. https://waves-vagues.dfo-mpo.gc.ca/library-bibliotheque/338449.pdf
Lawson, J.W., Stevens, T.S. 2014. Historic and current distribution patterns, and minimum abundance of killer whales (Orcinus orca) in the north-west Atlantic. J. Mar. Biol. Assoc. UK 94: 1253–1265. https://doi.org/10.1017/S0025315413001409
Lesage, V., Gosselin, J.-F., Hammill, M.O., Kingsley, M.C.S., Lawson, J.W. 2007. Ecologically and Biologically Significant Areas (EBSAs) in the Estuary and Gulf of St. Lawrence – A marine mammal perspective. CSAS Res Doc. 2007/046. 94 p. https://waves-vagues.dfo-mpo.gc.ca/library-bibliotheque/331137.pdf
Lesage, V., Gosselin, J.-F., Lawson, J.W., McQuinn, I., Moors-Murphy, H., Plourde, S., Sears,R., Simard, Y. 2018. Habitats important to blue whales (Balaenoptera musculus) in the western North Atlantic. DFO Can. Sci. Advis. Sec. Res. Doc. 2016/080. iv + 50 p. https://waves-vagues.dfo-mpo.gc.ca/library-bibliotheque/40681373.pdf
Mitchell, E., Reeves, R.R. 1983. Catch history, abundance, and present status of Northwest Atlantic humpback whales. Rep. Int. Whal. Commn (Spec. Iss.) 5: 153-212.
Ramp, C. (2008) Population dynamics and social organisation of humpback whales (Megaptera novaeangliae) in the Gulf of St. Lawrence – a long-term study. PhD thesis. University of Bremen, Germany http://nbn-resolving.de/urn:nbn:de:gbv:46-diss000111355
Roy N., Simard, Y., Aulanier, F., Giard, S. 2018. Fin whale continuous frequentation of St. Lawrence habitats detected from multi-year passive acoustic monitoring (PAM). DFO Can. Sci. Advis. Sec. Res. Doc. 2018/059. iv + 14 p
Sears, R., Williamson, J.M. 1982. A preliminary aerial survey of marine mammals for the Gulf of St. Lawrence to determine their distribution and relative abundance. Unpublished Report prepared under contract 81-1272 for Parks Canada. 84 p.
Schick, R.S., Halpin, P.N., Read, A.J., Urban, D.L., Best, B.D., et al. 2011. Community structure in pelagic marine mammals at large spatial scales. Mar Ecol Prog Ser 434: 165-181.
Sergeant, D.E., Fisher, H.D. 1957. The smaller cetacea of eastern Canadian waters. J. Fish. Res. Bd Canada 14: 83-115.
Sergeant, D.E. 1991. Harp seals, man and ice. Spec. Publ. Can. Fish. Aquat. Sci. 114 : 153 p. https://publications.gc.ca/collections/collection_2016/mpo-dfo/Fs41-31-114-eng.pdf
Simard, Y., Roy N., Aulanier, F., Giard, S. 2016. Blue whale continuous frequentations of St. Lawrence habitats from multi-year PAM series. DFO Can. Sci. Advis. Sec. Res. Doc. 2016/091. v + 14 p.
Smith, T.D. et al. 1999. An ocean-basin-wide mark-recapture study of the North Atlantic humpback whales (Megaptera novaeangliae). Mar. Mamm. Sci. 15 : 1-32.
Sourisseau, M., Simard, Y., and Saucier, F. J. 2006. Krill aggregation in the St. Lawrence system, and supply of krill to the whale feeding grounds in the estuary from the gulf. Mar. Ecol. Prog. Ser. 314: 257-270. https://doi.org/10.3354/meps314257
Stenson, G.B, Sjare, B., Warren, W.G., Myers, R.A. 1995. 1994 Pup production of the Northwest Atlantic harp seal, Phoca groenlandica. NAFO Sci. Counc. Studies 26: 47-61.
Stenson, G. et al. 2000. 1994 Pup production of harp seal, Phoca groenlandica, in the Northwest Atlantic. DFO Can. Sci. Advis. Sec. Res. Doc. 2000/080.
Stenson, G.B., Gosselin, J.-F., Lawson, J.W., Buren, A., Goulet P., Lang, S.L.C., Nissen, K.T., Hammill, M.O. 2022. Pup production of Harp Seals in the Northwest Atlantic in 2017 during a time of ecosystem change. NAMMCO Scientific Publications 12. https://doi.org/10.7557/3.6214
Vacquié-Garcia, J., Spitz, J., Hammill, M.O., Stenson, G.B., Kovacs, K.M., Lydersen, C., Chimienti, M., Renaud, M., Mendez Fernendez, P., Jeanniard du Dot, T. 2024. Foraging habits of Northwest Atlantic hooded seals over the past 30 years: Future habitat suitability under global warming. Glob. Change Biol. 2024;30:e17186. https://doi.org/10.1111/gcb.17186
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