Southern Labrador Pack Ice Whelping Area IMMA
Size in Square Kilometres
78 436 km2
Qualifying Species and Criteria
Harp seal – Pagophilus groenlandicus
Criterion C (1)
Hooded seal – Cystophora cristata
Criterion A; Criterion C (1)
Polar Bear – Ursus maritimus
Criterion A; Criterion C (2)
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Summary
The Southern Labrador Pack Ice IMMA is located off the coast of southern Labrador and northeastern Newfoundland, from south of Hamilton Inlet to north of Notre Dame Bay. The boundary of the IMMA extends from the coast to approximately 150 nautical miles offshore although the exact location of the pack ice within it varies among and within years. This area is critical for pupping and breeding of Northwest Atlantic harp seals (Pagophilus groenlandicus) and hooded seals (Cystophora cristata), which are ice-dependent during these life stages. Both populations represent the largest aggregations for the respective species in the world. This area is also an important feeding area for Davis Strait polar bears (Ursus maritimus) that migrate annually from as far away as Baffin Island. As such it has been identified as an EBSA by the Canadian government.
Description of Qualifying Criteria
Criterion A: Species or Population Vulnerability
Two of the Qualifying Species within the Southern Labrador Pack Ice IMMA are considered threatened with extinction according to the IUCN Red List. Polar bears (Ursus maritimus) and hooded seals (Cystophora cristata) are both assessed as Vulnerable (Wig et al 2015, Kovacs 2016).
The polar bear is listed as Threatened under the USA Endangered Species Act and Special Concern by the Committee on the Status of Endangered Species (COSEWIC) in Canada. In 2011 it was formally listed as Special Concern under the Canadian Species at Risk Act. In Newfoundland and Labrador, polar bears are listed as Vulnerable (COSEWIC 2018).
Criterion C: Key Life Cycle Activities
Sub-criterion C1: Reproductive Areas
Harp (Pagophilus groenlandicus) and Hooded seals are endemic to the North Atlantic. With a total abundance of 6.5 million animals (ICES 20231), harp seals are the most abundant marine mammals in the North Atlantic. At approximately 4.7 million animals, Northwest Atlantic harp seals account for 72% of the global population (ICES 20231; Tinker et al 2023). Harp seals only haul out on ice to give birth and to rest. Northwest Atlantic harp seals pup on the pack ice off southern Labrador/northeast Newfoundland (referred to as the Front) and in the Gulf of St. Lawrence (Gulf). This population has been impacted by climate change both directly through increased pup mortality associated with reduced ice, and indirectly through changes in prey availability resulting in increased late-term abortions (Stenson et al 2014; Tinker et al 2023). Since 1990, the proportion of the NW Atlantic population pupping on the pack ice at the Front has increased from ~80% of total pupping to ~96% in 2017 (69% of the world’s total now pups off Newfoundland), due to a significant reduction of ice in the Gulf (Stenson et al 2022). The southern Gulf component of this population is likely to disappear as seals move to the Labrador area to pup.
The estimated total global abundance of hooded seals is 670,300 animals (ICES 2023, Hammill and Stenson 2006). The Northwest Atlantic population accounts for 89% of the total, but this population has not been assessed since 2006. The 2006 NE Atlantic hooded seal population estimate was 88,300 animals, much smaller than the abundance estimate for NW Atlantic hooded seals at the time (ICES 2008, Hammill and Stenson 2006). Hooded seals also pup on the southern Labrador pack ice in areas close to the harp seal concentrations. Historically there are two other whelping (i.e. pupping) areas, the southern Gulf of St. Lawrence and in the Davis Strait, but a 2005 survey of all three areas found that>91% of the pups were born off southern Labrador (Stenson et al 2006). Davis Strait pupping had declined since a previous survey and poor ice in the Gulf of St. Lawrence has likely reduced pupping there. As a result, almost the entirety of the NWA hooded seal population now pups in the southern Labrador pack ice area IMMA.
1 Assuming an adult to pup ratio of 5:1 to estimate Barents Sea harp seal abundance (ICES 2023)
Sub-criterion C2: Feeding Areas
The global abundance of polar bears (Ursus maritimus) is estimated to be 23,300 animals (Hamilton and Derocher 2018). The Davis Strait (DS) population accounts for approximately 9% of the global total or 2200 animals (Hamilton and Derocher 2018; Peacock et al 2013). The southern Labrador pack ice is an important feeding area for polar bears from the DS population. Bears migrate annually from northern Labrador and Baffin Island to the harp and hooded seal whelping concentrations on the southern Labrador pack ice, where they feed intensively during March on the energy-rich harp and hooded seal pups. The energy gained off southern Labrador maintains the bears for much of the year. The proportion of the DS polar bear population migrating south to the harp and hooded seal breeding ice is not known, but increased survival and reproduction of the bears in southern Davis Strait population has been linked to changes in the abundance breeding harp seals in Labrador (Peacock et al 2013).
Supporting Information
Burns, JM, K Lestyk, D. Freistroffer and MO Hammill. 2015. Preparing Muscles for Diving: Age-Related Changes in Muscle Metabolic Profiles in Harp (Pagophilus groenlandicus) and Hooded (Cystophora cristataˆ) Seals. Physiol. And Biochem. Zool. 88:167-182
COSEWIC. 2018. COSEWIC assessment and status report on the Polar Bear Ursus maritimus in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xv + 113 pp.
Department of Fisheries and Oceans (DFO). 2013. Identification of Additional Ecologically and Biologically Significant Areas (EBSAs) within the Newfoundland and Labrador Shelves Bioregion. DFO Canadian Science Advisory Secretariat Science Advisory Report 2013/048.
Dunham, K.D., M.G. Dyck, J. Ware, A.E. Derocher, E.V. Regehr, H.L. Stern, G. B. Stenson and D. N. Koons. 2024 A demographic survey of the Davis Strait polar bear subpopulation using physical and genetic capture-recapture-recovery sampling. Marine Mammal Science 2024;e13107.
Hammill, M.O. and G. Stenson. 2006 Abundance of Northwest Atlantic hooded seals (1960-2005). DFO Canadian Science Advisory Secretariat Research Document 2006/068.
Hamilton, S. G. and A.E. Derocher. 2018. Assessment of global polar bear abundance and vulnerability. Animal Conservation 22:83-95. doi:10.1111/acv.12439
ICES. 2008. Report of the Working Group on ICES/NAFO Working Group on Harp and Hooded Seals (WGHARP), 12-16 June 2006, ICES Headquarters. ICES CM 2006/ACFM:32. 28 pp.
ICES. 2023. Report of the Joint ICES/NAFO/NAMMCO Working Group on Harp and Hooded Seals (WGHARP). ICES Scientific Reports. 5:96. 75 pp. https://doi.org/10.17895/ices.pub.24306100
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
Peacock, E., M.K. Taylor, J. Laake and I. Stirling 2013 Population ecology of polar bears in Davis Strait, Canada and Greenland” Polar bears in Davis Strait. J. Wildl. Manage 77(3):463-476.
Stenson, G.B. and M.O. Hammill. 2014. Can ice breeding seals adapt to habitat loss in a time of climate change? ICES J. Mar. Sci. 71:1977-1986.
Stenson, G.B., A.D. Buren and M. Koen-Alonso. 2016. The impact of changing climate and abundance on reproduction in an ice-dependent species, the Northwest Atlantic harp seal, Pagophilus groenlandicus. ICES. J. Mar. Sci. 73:250-262.
Stenson, G., J.-F. Gosselin, J. Lawson, A. Buren, P. Goulet, S. Lang, K.T. Nilssen and M. Hammill. 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
Stenson, G.B., M. O. Hammill, J. Lawson. and J. F. Gosselin. 2006. 2005 Pup Production of Hooded Seals, Cystophora cristata, in the Northwest Atlantic. DFO Canadian Science Advisory Secretariat Research Document 2006/067.
Stenson, G.B., T. Haug, and M.O. Hammill. 2020. Harp seals: monitors of change in differing ecosystems. Frontiers in Marine Science. 7:569258. https://doi.org/10.3389/fmars.2020.569258
Tinker, M.T., G.B. Stenson, A. Mosnier and M.O. Hammill, 2023. Estimating abundance of Northwest Atlantic harp seal using a Bayesian modelling approach. DFO Canadian Science Advisory Secretariat Research Document 2023/068. iv + 56 p.
Wiig, Ø., Amstrup, S., Atwood, T., Laidre, K., Lunn, N., Obbard, M., Regehr, E. & Thiemann, G. 2015. Ursus maritimus. The IUCN Red List of Threatened Species 2015: e.T22823A14871490. https://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22823A14871490.en
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