Gulf of Mexico Outer Continental Shelf and Continental Slope IMMA

Size in Square Kilometres

509 644 km2

Qualifying Species and Criteria

Sperm Whale – Physeter macrocephalus

Criterion A, Criterion B (2)

Rice’s Whale – Balaenoptera ricei

Criterion A; Criterion B (1)

Marine Mammal Diversity 

Balaenoptera ricei, Physeter macrocephalus, Kogia sima, Kogia breviceps, Ziphius cavirostris, Mesoplodon europaeus, Mesoplodon densirostris, Peponocephala electra, Feresa attenuata, Pseudorca crassidens, Orcinus orca, Globicephala macrorhynchus, Grampus griseus, Steno bredanensis, Lagenodelphis hosei, Stenella attenuata, Stenella frontalis, Stenella coeruleoalba, Stenella longirostris, Stenella clymene, Tursiops truncatus

 

Summary

The area covers the Gulf of Mexico outer continental slope (100-200 m depth) continental slope (200-2000 m depth) and a portion of the abyssal plain (2000 – 2500 m depth). Critically Endangered Rice’s whales (Balaenoptera ricei) are known to primarily inhabit the Gulf of Mexico where they are associated with upwellings of cold, high-salinity water, and seasonal inputs of highly productivity water from coastal sources. This species is not known to migrate and move outside of the Gulf of Mexico, and apparently forages exclusively, or at least primarily, within the boundary of the IMMA.

The IMMA also hosts a population of Vulnerable sperm whales (Physeter macrocephalus). Both of these species feed and reproduce in these waters, with limited movements outside of the Gulf. The area sustains a high diversity and density of other cetaceans (21 species) that include beaked whales (Ziphius cavirostris, Mesoplodon europaeus, M. densirostris), short-finned pilot whales (Globicephala macrorhynchus), killer whales (Orcinus orca), Risso’s dolphins (Grampus griseus), melon-headed whales (Peponocephala electra), Clymene dolphins (Stenella clymene), spinner dolphins (Stenella longirostris), and pantropical spotted dolphins (Stenella attenuata).

A Biologically Important Area (BIA) has been delimited based on ship- and aerial based sighting data in the northeastern part of the Gulf.

Description of Qualifying Criteria

Criterion A: Species or Population Vulnerability

This IMMA is designed to encompass the habitat of the Rice’s whale (Balaenoptera ricei), which is listed as Critically Endangered on the IUCN Red List of Threatened Species (Rosel et al. 2022), and listed as Endangered under the U.S. Endangered Species Act.  Rice’s whale was only recently recognized as distinct from other species in the “Bryde’s whale complex” and with a population size below 100 whales (Rosel et al. 2022), it is the most threatened whale species in the world.

The sperm whale (Physeter macrocephalus) is listed as Vulnerable on the IUCN Red List of Threatened Species and as Endangered under the U.S. Endangered Species Act (ESA).

Criterion B: Distribution and Abundance

Sub-criterion B1: Small and Resident Populations

Rice’s whales are only known to reside in the Gulf of Mexico. Rice’s whale occurrence in the northern Caribbean and the southeast U.S. Atlantic is not well understood. There are four confirmed stranding records (Brownell et al. 2024) and potential sightings of Rice’s whales in the Atlantic off the southeastern U.S. (NOAA Southeast Fisheries Science Center, unpublished data), but opportunistic passive acoustic recordings in these waters have not detected Rice’s whale calls. At this time, there is insufficient evidence to support their regular occurrence in the southeast U.S. Atlantic.

The core habitat where the highest densities have been recorded lies primarily between the 100 and 400m isobaths (Soldevilla et al. 2017, Garrison et al. 2024, Rosel et al. 2022), which corresponds to an area of 49,359km2 in the northeastern portion of the Gulf of Mexico. The currently accepted population estimate for Rice’s whales is 51 individuals (95% CI: 20–130 individuals) based on large-vessel line transect surveys conducted in 2017 and 2018 (Garrison et al. 2020). An estimate from a habitat model using data collected between 1992 and 2009 produced an abundance estimate of 44 (CV=0.27, Roberts et al. 2015, 2016). The Gulf of Mexico is the only location where Rice’s whales are known to occur and this species is not known to undertake any migration (Rosel et al. 2022). Movements and site fidelity are unknown, but an analysis of photo-identification data is currently underway, and it is expected that the animals will prove to be essentially resident in the area delineated by the IMMA boundary (NOAA Southeast Fisheries Science Center, unpublished data).  Data from a time-depth recorder deployed on several individuals suggest that Rice’s whales undertake deep dives during the day (200-250m) to forage, whereas resting was primarily observed within 0-15m at night (Soldevilla et al. 2017). Recent evidence suggests that Rice’s whales feed in the Gulf of Mexico, particularly within their core range.  Bayesian stable carbon and nitrogen isotope mixing models from skin biopsy samples suggest that the diet of Rice’s whales is dominated by silver-rag driftfish (Ariomma bondi) (66.8% relative contribution), a schooling fish occurring near the bottom of the continental shelf/upper slope waters of the Gulf (Kiszka et al. 2023).  Recent habitat models suggest that surface chlorophyll-a concentration, bottom temperature, and bottom salinity are important environmental parameters in defining the habitat of Rice’s whales (Garrison et al. 2024). Those conditions are consistent with the presence of upwellings along the continental shelf break, which would promote the presence of small pelagic fish species consumed by Rice’s whales in the area (Garrison et al. 2024, Kiszka et al. 2023).

Sub-criterion B2: Aggregations

All evidence indicates that the female and subadult portion of the northern Gulf of Mexico sperm whale population are resident to the Gulf of Mexico.  Tracks from 39 sperm whales satellite tagged during 2002-2005 and monitored for up to 607 days show that only one, a male, briefly left the Gulf of Mexico (Jochens et al. 2008).  Photo-identification studies compared 285 whales from the Gulf to 2,500 from the Atlantic and Mediterranean Sea and found no matches (Jochens et al. 2008). The best abundance estimate (Nest) for northern Gulf of Mexico sperm whales is 1,180 (CV=0.22). This estimate is from summer 2017 and summer/fall 2018 oceanic surveys covering waters from the 200-m isobath to the seaward extent of the U.S. EEZ (Garrison et al. 2020). Movements of sperm whales between the eastern Caribbean, Gulf of Mexico, and western Atlantic may occur but are not believed to be common. No match between photo-identified individuals from the eastern Caribbean islands was found with individuals from the Gulf of Mexico and the Sargasso Sea (Gero et al. 2007).

Criterion D: Special Attributes

Sub-criterion D2: Diversity

The outer continental slope and continental slope in the Gulf of Mexico have high primary productivity due to the input of nutrients from rivers systems which allow an abundance of concentrated prey (Ramírez-León et al. 2021). The IMMA’s waters include a significant part of the range for sperm whales (VU) and, and host a diversity of 21 marine mammals. The waters >200 m deep host the highest density of marine mammals in the Gulf of Mexico (Roberts et al. 2016, Ramírez-León et al. 2021, Rappucci et al. 2023).  The species that occur regularly include beaked whales (Ziphius cavirostris, Mesoplodon europaeus, M. densirostris), short-finned pilot whales (Globicephala macrorhynchus), killer whales (Orcinus orca), Risso’s dolphins (Grampus griseus), melon-headed whales (Peponocepha electra), Clymene dolphins (Stenella clymene), spinner dolphins (S. longirostris), and pantropical spotted dolphins (S. attenuata) (Würsig et al. 2000).  The density of most of these species including sperm whales, short-finned pilot whales, Risso’s dolphins, spinner dolphins and pantropical spotted dolphins is highest in continental slope waters (Roberts et al. 2016).  The most abundant species in this area in the northern Gulf of Mexico is by far the pantropical spotted dolphin but all of these species have regularly been sighted since surveys began in 1990 (e.g., Mullin and Fulling 2004, Rappucci et al. 2023). However, some of the less common species such as the killer whales and Fraser’s dolphins (Lagenodelphis hosei) are not sighted during every survey.

Supporting Information

Biggs, D.C., Leben, R.R., and Ortega-Ortiz, J.G. 2000. Ship and satellite studies of mesoscale circulation and sperm whale habitats in the northeast Gulf of Mexico during GulfCet II. Gulf of Mexico Science, 18:1522.

Brownell, Jr., S.D. Mallette, and D. Cholewiak. 2024. Stranded medium-sized baleen whales (sei, Bryde’s, Rice’s) in US western North Atlantic waters. International Whaling Commission Paper SC/69B/NH/04.

Engelhaupt, D., Hoelzel, A.R., Nicholson, C., Frantzis, A., Mesnick, S., Gero, S., Whitehead, H., Rendell, L., Miller, P., De Stefanis, R., Cañadas, A., Airoldi, S., and Mignucci-Giannoni, A.A. 2009. Female philopatry in coastal basins and male dispersion across the North Atlantic in a highly mobile marine species, the sperm whale (Physeter macrocephalus). Molecular Ecology, 18:4193–4205.

Garrison, L.P., Ortega-Ortiz, J.  and Rappucci, G. 2020. Abundance of marine mammals in the waters of the U.S. Gulf of Mexico in the summer of 2017 and 2018. Southeast Fisheries Science Center, Protected Resources and Biodiversity Division, 75 Virginia Beach Dr., Miami, Florida 33140. PRBD Contribution # PRBD-2020-07. 55pp. Available from: https://repository.library.noaa.gov/view/noaa/26505.

Jochens, A., Biggs, D., Benoit-Bird, K., Engelhaupt, D., Gordon, J., Hu, C., Jaquet, N., Johnson, M., Leben, R., Mate, B., Miller, P., Ortega-Ortiz, J., Thode, A., Tyack, P., and Würsig, B.  2008. Sperm whale seismic study in the Gulf of Mexico: Synthesis report. U.S. Dept. of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, Louisiana. OCS Study MMS 2008-006. 341pp.

Kiszka, J.J., Caputo, M., Vollenweider, J., Heithaus, M.R., Aichinger Dias, L. and Garrison, L.P., 2023. Critically Endangered Rice’s whales (Balaenoptera ricei) selectively feed on high-quality prey in the Gulf of Mexico. Scientific Reports, 13: 6710.

LaBrecque, E., Curtice, C., Harrison, J., Van Parijs, S.M. and Halpin, P.N., 2015. 3. Biologically Important Areas for Cetaceans Within US Waters-Gulf of Mexico Region. Aquatic Mammals, 41(1), p.30.

Lohrenz, S.E., D. A. Wiesenburg, R.A. Arnone, and X. Chen. 1999. ‘What controls primary production in the Gulf of Mexico?’ In: H. Kumpf, K. Steidinger, and K. Sherman (eds). The Gulf of Mexico large marine ecosystem: assessment, sustainability, and management, pp 151-170. Malden: Blackwell Science.

Martínez-López, B., and Zavala-Hidalgo, J. 2009. Seasonal and interannual variability of crossshelf transports of chlorophyll in the Gulf of Mexico. Journal of Marine Systems, 77:120.

Ramírez-León, M. R., García-Aguilar, M.C.,Romo-Curiel,  A.E., Ramírez-Mendoza, Z., Fajardo-Yamamoto, A. and Sosa-Nishizaki, O. 2021. Habitat suitability of cetaceans in the Gulf of Mexico using an ecological niche modeling approach. PeerJ, 9:e10834.

Rappucci, G., Garrison, L. P., Soldevilla, M., Ortega-Ortiz, J., Reid, J., Aichinger-Dias, L., Mullin K., and Litz, J. 2023. Gulf of Mexico Marine Assessment Program for Protected Species (GoMMAPPS): marine mammals. Volume 1: report. New Orleans (LA): US Department of the Interior, Bureau of Ocean Energy Management. 104 p. Obligation No.: M17PG00013. Report No.: OCS Study BOEM 2023-042.

Roberts, J.J., Best, B.D., Mannocci, L., Fujioka, E., Halpin, P.N., Palka, D.L., Garrison, L.P., Mullin, K.D., Cole, T.V.N., Khan, C.B., McLellan, W.A., Pabst, D.A., Lockhart, G.G. 2015. Density model for Bryde’s whale (Balaenoptera edeni) in the U.S. Atlantic: Supplementary Information, Version 1.3, 2015-09-26. Marine Geospatial Ecology Lab, Duke University, Durham, North Carolina.

Roberts, J.J., Best, B.D., Mannocci, L., Fujioka, E., Halpin, P.N., Palka, D.L., Garrison, L.P., Mullin, K.D., Cole, T.V.N., Khan, C.B., McLellan, W.A., Pabst, D.A., and Lockhart, G.G.  2016.  Habitat-based cetacean density models for the U.S. Atlantic and Gulf of Mexico.  Scientific Reports 6, 22615; doi: 10.1038/srep22615.

Rosel, P.E. and Wilcox, L.A., 2014. Genetic evidence reveals a unique lineage of Bryde’s whales in the northern Gulf of Mexico. Endangered Species Research25: 19-34.

Rosel, P., Corkeron, P. & Soldevilla, M. 2022. Balaenoptera riceiThe IUCN Red List of Threatened Species 2022: e.T215823373A208496244. https://dx.doi.org/10.2305/IUCN.UK.2022-1.RLTS.T215823373A208496244.en. Accessed on 16 May 2024.

Rosel, P.E., Wilcox, L.A., Yamada, T.K. and Mullin, K.D., 2022. A new species of baleen whale (Balaenoptera) from the Gulf of Mexico, with a review of its geographic distribution. Marine Mammal Science, 37(2), pp.577-610.

Soldevilla, M.S., Hildebrand, J.A., Frasier, K.E., Dias, L.A., Martinez, A., Mullin, K.D., Rosel, P.E. and Garrison, L.P., 2017. Spatial distribution and dive behavior of Gulf of Mexico Bryde’s whales: potential risk of vessel strikes and fisheries interactions. Endangered Species Research, 32, pp.533-550.

Soldevilla, M.S., Ternus, K., Cook, A., Hildebrand, J.A., Frasier, K.E., Martinez, A. and Garrison, L.P., 2022. Acoustic localization, validation, and characterization of Rice’s whale calls. The Journal of the Acoustical Society of America, 151(6), pp.4264-4278.

Soldevilla, M.S., Debich, A.J., Garrison, L.P., Hildebrand, J.A. and Wiggins, S.M., 2022. Rice’s whales in the northwestern Gulf of Mexico: Call variation and occurrence beyond the known core habitat. Endangered Species Research, 48, pp.155-174.

Soldevilla, M.S., Debich, A.J., Pérez‐Carballo, I., Jarriel, S., Frasier, K.E., Garrison, L.P., Gracia, A., Hildebrand, J.A., Rosel, P.E. and Serrano, A., 2024. Rice’s whale occurrence in the western Gulf of Mexico from passive acoustic recordings. Marine Mammal Science. DOI: 10.1111/mms.13109

Würsig, B., Jefferson, T.A., and Schmidley, D.  2000. Marine mammals of the Gulf of Mexico. Texas A & M University Press, College Station, TX.

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