Sackville Spur and Orphan Basin IMMA
Size in Square Kilometres
115 402 km2
Qualifying Species and Criteria
Sei whale – Balaenoptera borealis
Criterion A
Blue Whale – Balaenoptera musculus
Criterion C (3)
Fin Whale – Balaenoptera physalus
Criterion A; Criterion C (3)
Long-finned Pilot Whale – Globicephala melas
Criterion B (2)
Northern Bottlenose Whale – Hyperoodon ampullatus
Criterion B (2); Criterion C (2)
Sperm Whale – Physeter macrocephalus
Criterion A; Criterion B (2); Criterion C (2)
Sowerby’s Beaked Whale – Mesoplodon bidens
Criterion B (2); Criterion C (2)
Marine Mammal Diversity
Balaenoptera acutorostrata, Balaenoptera borealis, Balaenoptera physalus, Balaenoptera musculus, Globicephala melas, Hyperoodon ampullatus, Lagenorhynchus acutus, Megaptera novaeangliae, Mesoplodon bidens, Physeter macrocephalus, Ziphius cavirostris
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Summary
The Sackville Spur-Orphan Basin IMMA lies off the northeastern corner of the Grand Banks of Newfoundland. The area includes the Sackville Spur, a long but narrow ridge extending northeastward from the Grand Banks, the Orphan Knoll, an undersea peak rising to about 1,800m from the surface, as well as the shelf edge region and Orphan Basin which lie to the west of the Spur and southwest of the Knoll. The IMMA hosts Endangered blue whales (Balaenoptera musculus) and sei whales (Balaenoptera borealis), and Vulnerable fin (Balaenoptera physalus) and sperm (Physeter macrocephalus) whales. Aggregations of sperm whales, northern bottlenose whales (Hyperoodon ampullatus) and pilot whales (Globicephala melas) have been documented, all of which likely use the productive waters for feeding along with other species, including Sowerby’s beaked whales (Mesoplodon bidens). A high diversity of at least 11 species of marine mammals regularly occurs in the area. The area overlaps with the “Orphan Spur” EBSA.
Description of Qualifying Criteria
Criterion A: Species or Population Vulnerability
The blue (Balaenoptera musculus) and sei whale (Balaenoptera borealis) are listed as Endangered on the Red List globally (Cooke 2018a,b), and the fin whale (Balaenoptera physalus) and sperm whale (Physeter macrocephalus) are both listed as Vulnerable on the Red List globally (Cooke 2018c, Taylor et al. 2019).
Criterion B: Distribution and Abundance
Sub-criterion B2: Aggregations
Sighting rates of groups (per hour equivalent in excellent conditions) from a 12m research sailing vessel between 2001-2017 from June to August were considerably higher in and around the Sackville Spur-Orphan Basin region (149 hours effort) than other areas along the edge of the Newfoundland Shelf (140 hours effort) for the following species: pilot whales (Globicephala melas; 0.355 vs 0.043); northern bottlenose whales (Hyperoodon ampullatus; 0.194 vs 0.000); sperm whales (0.321 vs 0.036) (Whitehead and Feyrer unpublished). Additionally, a comprehensive habitat analysis identified this region as the second most important year-round habitat for northern bottlenose whales in the western North Atlantic after the eastern canyons region of the Scotian Shelf, and also highlighted this area as part of important habitat for Sowerby’s beaked whales (Mesoplodon bidens; Feyrer et al. 2024). An analysis of 25 acoustic recorders deployed off eastern Canada between May 2015 and November 2017 identified the Sackville Spur area as especially important for northern bottlenose whales year-round with northern bottlenose whale foraging clicks detected on 25-75% of recording days for two hydrophones deployed in the eastern and western ends of the area in all four seasons (Delarue et al. 2024). Drivers of enhanced densities of marine mammals in the Sackville Spur-Orphan Basin region are not clear, but likely relate to the cold, southeast-flowing Labrador Current interacting with the complex bathymetry on the northeast corner of the Grand Banks (Maillet et al. 2006).
Criterion C: Key Life Cycle Activities
Sub-criterion C2: Feeding Areas
The strong, cold Labrador Current which flows southeast along the edge of the continental shelf off Labrador and northeast Newfoundland creates highly productive conditions when it encounters the rises of the Sackville Spur and Orphan Knoll at the northeast corner of the Grand Banks (Maillet et al. 2006). Northern bottlenose whales and sperm whales have been frequently observed feeding in the Sackville Spur region (Hal Whitehead, pers. comm). Northern bottlenose whales and Sowerby’s beaked whales were also acoustically detected foraging in the area year-round (Delarue et al. 2024, Feyrer et al. 2024).
Criterion D: Special Attributes
Sub-criterion D2: Diversity
With regular presence of more than 11 marine mammal species, this area supports a high species diversity. This is evidenced by a concentration of cetacean sighting records of free-swimming cetaceans collected during the post-whaling period (1975 – 2015) (Gomez et al, 2020). As discussed above, sighting rates from vessel-based surveys conducted over multiple years within this area were found to be higher for northern bottlenose, Sowerby’s beaked, sperm, and pilot whales than other deep-water areas off Newfoundland (Whitehead and Feyrer unpublished). Multi-year passive acoustic monitoring efforts within the area also demonstrate regular presence of the echolocation (foraging) clicks of these species as well as Cuvier’s beaked whales (Ziphius cavirostris) (Delarue et al. 2024, Feyrer et al. 2024). Minke whales (Balaenoptera a. acutorostrata) and Atlantic white-sided dolphins (Lagenorhynchus acutus) have also been reported within the area (Gomez et al 2020). Data from passive acoustic monitoring also provides evidence for the regular presence of baleen whales in this area, especially fin whales throughout most of the year, blue whales in fall and winter and humpback whales (Megaptera novaeangliae) in winter (Delarue et al. 2022). Sei whales were mainly heard in the autumn (Macklin 2022). There are more occasional sightings of other species such as killer whales (Orcinus orca), common dolphins (Delphinus delphis), bottlenose dolphins (Tursiops truncatus), white-beaked dolphins, (Lagenorhynchus albirostris), and harbour porpoises (Phocoena phocoena) (Gomez et al, 2020).
Supporting Information
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. Accessed on 29 March 2024.
Cooke, J.G. 2018b. Balaenoptera borealis. The IUCN Red List of Threatened Species 2018: e.T2475A130482064. https://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T2475A130482064.en. Accessed on 17 April 2024.
Cooke, J.G. 2018c. 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. Accessed on 29 March 2024.
Delarue, J.J.-Y., Moors-Murphy, H., Kowarski, K.A., Davis, G.E., Urazghildiiev, I.R., and Martin, B. 2022. Acoustic occurrence of baleen whales, particularly blue, fin, and humpback whales, off eastern Canada, 2015–2017. Endangered Species Research. 47: 265-289. DOI: 0.3354/esr01176.
Delarue, J., Moors-Murphy, H., Kowarski, K., Maxner, E., Davis, G., Stanistreet, J., & Martin, S. 2024. Acoustic occurrence of beaked whales off eastern Canada, 2015-2017. Endangered Species Research, 53, 439–466. https://doi.org/10.3354/esr01314
Gomez, C., Konrad, C.M., Vanderlaan, A., Moors-Murphy, H.B., Marotte, E., Lawson, J., Kouwenberg, A-L., Fuentes-Yaco, C., Buren, A. 2020. Identifying priority areas to enhance monitoring of cetaceans in the Northwest Atlantic Ocean. Can. Tech. Rep. Fish. Aquat. Sci. 3370: vi + 103 p.
Feyrer, L.J., Stanistreet, J.E., Gomez, C., Adams, M., Lawson, J.W., Ferguson, S.H., Heaslip, S.G., Lefort, K.J., Davidson, E., Hussey, N.E. and Whitehead, H., 2024. Identifying important habitat for northern bottlenose and Sowerby’s beaked whales in the western North Atlantic. Aquatic Conservation: Marine and Freshwater Ecosystems, 34: e4064
Macklin, G. 2022. Spatiotemporal patterns in acoustic presence of sei whales (Balaenoptera borealis) in Atlantic Canada. MSc Thesis, Dalhousie University. 125 pp. Available online: https://dalspace.library.dal.ca/handle/10222/81559?show=full
Maillet, G. L., Pepin, P., Craig, J. D. C., Fraser, S., & Lane, D. 2005. Overview of biological and chemical conditions on the Flemish Cap with comparisons of the Grand Banks shelf and slope waters during 1996-2003. Journal of Northwest Atlantic Fishery Science, 37, 29–45. https://doi.org/10.2960/J.v37.m561
Taylor, B.L., Baird, R., Barlow, J., Dawson, S.M., Ford, J., Mead, J.G., Notarbartolo di Sciara, G., Wade, P. & Pitman, R.L. 2019. Physeter macrocephalus (amended version of 2008 assessment). The IUCN Red List of Threatened Species 2019: e.T41755A160983555. https://dx.doi.org/10.2305/IUCN.UK.2008.RLTS.T41755A160983555.en. Accessed on 18 November 2024.
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