Galápagos Archipelago IMMA

Size in Square Kilometres

139 517 km2

Qualifying Species and Criteria

Galápagos fur seal – Arctocephalus galapagoensis 

Criterion A; B (1)

Galápagos sea lion – Zalophus wollebaeki 

Criterion A; B (1)

Blue whale – Balaenoptera musculus 

Criterion A; C (1, 2)

Bryde’s whale – Balaenoptera edeni

Criterion B (2)

 Humpback whale – Megaptera novaeangliae

Criterion C (1)

Sperm whale – Physeter macrocephalus

Criterion A; B (2)

Killer whale – Orcinus orca

Criterion B (2)

Marine Mammal Diversity 

Criterion D (2)

Globicephala macrorhynchus, Grampus griseus, Risso’s dolphin, Tursiops truncatus, Delphinus delphis, Stenella coeruleoalba, Ziphius cavirostris,
Kogia sima, Stenella attenuata, Stenella longirostris

Download fact sheet

Summary

Oceanographic conditions around the Galápagos Archipelago IMMA are conducive to high levels of biological productivity, species diversity, and marine endemism. These waters have been designated as a marine reserve by the government of Ecuador and as a Natural World Heritage Site by UNESCO. Numerous scientific expeditions and other research in the last 40 years have demonstrated the importance of the Galápagos Archipelago for marine mammals. The islands feature populations of two endangered and endemic pinnipeds, the Galápagos fur seal (Arctocephalus galapagoensis) and the Galápagos sea lion (Zalophus wollebaeki). The unique local habitats created by these oceanic islands are also breeding and feeding grounds for Endangered (EN) blue whales (Balaenoptera musculus) migrating from Chile, and Southern humpback whales (Megaptera novaeangliae australis) migrating from the Antarctic Peninsula. The archipelago also hosts aggregations of Bryde’s whales (Balaenoptera edeni brydei), vulnerable sperm whales (Physeter macrocephalus), and killer whales (Orcinus orca) inhabiting the eastern tropical Pacific. The rich oceanic waters surrounding the archipelago also support aggregations of a high diversity of medium and small cetacean species.

Description of Qualifying Criteria

Criterion A – Species or Population Vulnerability

The Galápagos Archipelago contains habitat important for the survival and recovery of four marine mammal species whose conservation status is of concern under the IUCN Red List of Threatened species. The population of Galápagos fur seals (Arctocephalus galapagoensis), listed as Endangered (EN), is estimated at about 10,000 mature individuals and considered to be declining (Trillmich, 2015a). Similarly, the population of Galápagos sea lions (Zalophus wollebaeki), listed as Endangered, is also estimated at about 10,000 mature individuals and considered to be declining (Trillmich, 2015b). Subsequent to these IUCN assessments, more recent data suggest that the populations of both species have somewhat increased, but they continue to be subject to strong inter-annual fluctuations associated with El Niño and La Niña events (Páez-Rosas et al., 2021).

Blue whales (Balaenoptera musculus) have also been assessed as Endangered (EN) on the IUCN Red List of Threatened species (Cooke, 2019). The global estimate for the number of mature blue whales is thought to be in the range 5,000-15,000 individuals, with an increasing trend, while the Chilean blue whale subpopulation is thought to be in the low hundreds (300-450 individuals), with an uncertain population trend (Cooke, 2019). Sperm whales (Physeter macrocephalus) are listed as Vulnerable (VU) on the IUCN Red List (Taylor, 2019). The current global mature population size is thought to be in the 100,000’s, with considerable uncertainty in population trend (Taylor, 2019). The population of sperm whales inhabiting the eastern tropical Pacific was estimated at 22,666 individuals in 1993 (Wade and Gerrodette, 1993) and the number of animals using Galápagos waters was estimated at 1,254 in 1990 (Whitehead et al., 1997). However, the Whitehead et al. (1997) study, as well as a more recent study spanning the period 1985-2014 (Cantor et al., 2017), revealed strong inter-decadal fluctuations in the number of animals that visit Galápagos as a result of movements in and out of the archipelago.

Criterion B: Distribution and Abundance

Sub-criterion B1: Small and Resident Populations

The Galápagos Archipelago encompasses the primary breeding and feeding habitat for both Galápagos fur seals and Galápagos sea lions (Salazar, 2002). As noted prior, however, oceanographic events such as El Niño and La Niña result not only in strong interannual fluctuations in the populations of these pinnipeds but also in their distribution at sea. Indeed, distant haul-outs and even small temporary breeding colonies of both species have been reported outside Galápagos during anomalous years (e.g., Palacios et al., 1997, Félix et al., 2007, Aurioles-Gamboa et al., 2004, Ceballos et al., 2010, Quintana-Rizzo et al., 2017, Páez-Rosas et al., 2017). Similarly, an influx of atypical pinniped species has been reported in Galápagos during these strong perturbations (e.g., Páez-Rosas et al., 2020, Alava et al., 2022). In all cases, these redistributions appear to be temporary.

Sub-criterion B2: Aggregations

A quantitative analysis of cetacean community structure in the Galápagos demonstrated that a combination of physical and biological factors results in a variety and persistence of ecological niches for a set of species that are numerically abundant within the archipelago (Palacios, 2003). Among these, the Bryde’s whale (Balaenoptera edeni brydei) is seen in feeding aggregations especially on the western part of the archipelago (Palacios et al., 2002, Denkinger et al., 2013), as well as off San Cristóbal Island, in the eastern part (Biggs et al., 2017). Aggregations of female and immature sperm whales (Physeter macrocephalus) are seen in the deeper waters of the archipelago, although their numbers wax and wane over the years as groups of animals move in and out of the area (Whitehead et al., 1997, Cantor et al., 2017).

Killer whales (Orcinus orca) have naturally low abundance and roam broadly in the eastern tropical Pacific. However, they are regularly seen off the Galápagos, and most encounters include observations of feeding. Galápagos harbours abundant populations of prey for killer whales, including teleost and elasmobranch fishes, sea turtles, pinnipeds, and cetaceans, that are otherwise sparsely distributed in the broader eastern tropical Pacific region (Denkinger et al., 2020).Killer whales are commonly seen on the western side of the archipelago, where they are seen preying on a very wide variety of marine species, but they are also regularly observed off Baltra, Santa Cruz, and the San Cristóbal Islands (Denkinger et al., 2020).

Criterion C: Key Life Cycle Activities

Sub-criterion C1: Reproductive Areas

The Galápagos Archipelago is part of the low-latitude range of Chilean blue whales, where they are observed to breed annually during the austral winter (Palacios, 1999; Biggs et al., 2017; Hucke-Gaete et al., 2018). The Galápagos Archipelago is also part of the low-latitude range of Southern Hemisphere humpback whales from IWC Breeding Stock G, where they breed annually during the austral winter (Félix et al., 2011; Biggs et al., 2017).

Sub-criterion C2: Feeding Areas

The Galápagos Archipelago is part of the low-latitude range of Chilean blue whales, where they are observed to feed annually during the austral winter (Palacios, 1999; Biggs et al., 2017; Hucke-Gaete et al., 2018).

Criterion D: Special Attributes

Sub-criterion D2: Diversity

Twelve qualifying species denotes the evidence that the Galápagos Archipelago IMMA supports an important diversity of marine mammal species. An analysis of community structure based on cetacean sightings data demonstrated that the high diversity of species regularly present in Galápagos is supported by a combination of physical and biological factors that result in a variety and persistence of ecological niches (core habitats) around the archipelago (Palacios, 2003). A separate study of cetacean strandings in Galápagos indicated a pattern consistent with the sighting record (Palacios et al., 2004). Additional studies have documented cetacean species occurrence in Galápagos waters (Day, 1994, Smith and Whitehead, 1999, Palacios et al., 2002, Denkinger et al., 2013). In addition to the species mentioned prior, under the previous criteria descriptions, short-finned pilot whales (Globicephala macrorhynchus) and Risso’s dolphins (Grampus griseus) are commonly found in offshore waters, especially along the steep slopes of the western side of the archipelago (Palacios et al., 2002). Common bottlenose dolphins (Tursiops truncatus) are the most commonly sighted species in nearshore waters of the archipelago, with aggregations being reported from the waters between Isabela and Floreana Islands, north of Santa Cruz Island, in the Bolivar Channel between Fernandina and Isabela Islands, between Santiago and Pinzón Islands, and around the islets of Roca Redonda, Wolf, and Darwin (Palacios et al., 2002). This coastal distribution is consistent with the island-associated ecotype that has been reported around other oceanic islands, and it is possible that with more research, common bottlenose dolphins may qualify for Criterion B1 (Small and Resident Populations) in a future assessment. Finally, large aggregations of short-beaked common dolphins (Delphinus delphis) and striped dolphins (Stenella coueruleoalba) are common in offshore waters of the archipelago, especially in the western and northern parts where topographic upwelling of the Equatorial Undercurrent is strongest (Palacios et al., 2002, Palacios, 2003, Palacios and Forney, 2008). It is also probable that at least half a dozen beaked whale species occur in Galápagos waters but these are reported only infrequently due to their cryptic behaviour and difficulty in identifying species at sea. While the relative sighting frequency of each species may vary between studies, they all conclude that the Galápagos Archipelago is an area that attracts and sustains an outstanding diversity of marine mammals.

Supporting Information

Alava, J.J., Riofrío-Lazo, M., Reygondeau, G., Rosero, P., Avila, I.C., Lara, D., Gil, F., Yaipen-Llanos, C. F., Elorriaga-Verplancken, F. R. and Páez-Rosas, D. 2022. ‘Southern elephant seals (Mirounga leonina) in the Galapagos Islands and the eastern tropical Pacific amid ocean environmental changes: towards a habitat suitability index’. Aquatic Mammals, 48(5): 418–431.

Aurioles-Gamboa, D., Schramm, Y. and Mesnick, S. 2004. ‘Galapagos fur seals, Arctocephalus galapagoensis, in Mexico’. Latin American Journal of Aquatic Mammals, 3(1):77–80.

Biggs, D.C., Durkacz, S.M., Martin, L.M., Narvaez, M., De La Garza, A., Lombraña, Z. and Santos, M. 2017. ‘Bryde’s whales (Balaneoptera brydei) in an area of upwelling off Isla San Cristóbal, Galápagos’. Neotropical Biodiversity, 3(1):189–195.

Cantor, M., Eguiguren, A., Merlen, G. and Whitehead, H. 2017. ‘Galápagos sperm whales (Physeter macrocephalus): waxing and waning over three decades’. Canadian Journal of Zoology, 95(9), 645–652.

Ceballos, G., Pompa, S., Espinoza, E. and García, A. 2010. ‘Extralimital distribution of Galapagos (Zalophus wollebaeki) and northern (Eumetopias jubatus) sea lions in Mexico. Aquatic Mammals, 36(2):188–194.

Cooke, J.G. 2018. ‘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 13 September 2022.

Day, D. 1994. List of Cetaceans seen in Galápagos. Noticias de Galápagos, 56:5–6.

Denkinger, J., Oña, J., Alarcón, D., Merlen, G., Salazar, S. and Palacios, D.M. 2013. ‘From whaling to whale-watching: cetacean presence and species diversity in the Galapagos Marine Reserve’. In: S.J. Walsh and C.F. Mena (eds) Science and Conservation in the Galapagos Islands: Social and Ecological Interactions in the Galapagos Islands, vol. 1, pp. 217–235. New York: Springer Science+Business Media, LLC.

Denkinger, J., Alarcón, D., Espinosa, B., Fowler, L., Manning, C. and Palacios, D.M. 2020. ‘Social structure of killer whales (Orcinus orca) in a variable environment, the Galápagos Archipelago’. Marine Mammal Science, 36(3):774–785.

Edgar, G.J., Banks, S., Fariña, J.M., Calvopiña, M. and Martínez, C. 2004. ‘Regional biogeography of shallow reef fish and macro-invertebrate communities in the Galapagos archipelago’. Journal of Biogeography, 31:1107–1124.

Félix, F., Palacios, D.M., Salazar, S.K., Caballero, S., Haase, B. and Falconí, J. 2011. ‘The 2005 Galápagos Humpback Whale Expedition: A first attempt to assess and characterize the population in the archipelago’. Journal of Cetacean Research and Management (Special Issue 3):291–299.

Félix, F., Jiménez, P., Falconí, J., and Echeverry, O. 2007. ‘New records and first births of the Galapagos fur seal, Arctocephalus galapagoensis (Heller, 1904), from the mainland coast of Ecuador’. Revista de Biologa Marina y Oceanografía, 42(1):77–82.

Forryan, A., Naveira Garabato, A.C., Vic, C. Nurser, A.J.G. and Hearn, A.R. 2021. ‘Galápagos upwelling driven by localized wind–front interactions’. Scientific Reports, 11:1277.

Harris, M.P. 1969. ‘Breeding seasons of sea-birds in the Galapagos Islands’. Journal of Zoology, 159:145–165.

Hucke-Gaete, R., Bedriñana-Romano, L., Viddi, F.A., Ruiz, J.E., Torres-Florez, J.P. and Zerbini, A.N. 2018. ‘From Chilean Patagonia to Galapagos, Ecuador: novel insights on blue whale migratory pathways along the Eastern South Pacific’. PeerJ, 6(2):e4695–22.

McKinley, S.J., Saunders, B.J., Rastoin-Laplane, E., Salinas-de-León, P. and Harvey, E.S. 2022. ‘Functional diversity of reef fish assemblages in the Galapagos Archipelago’. Journal of Experimental Marine Biology and Ecology, 549:151695.

Páez-Rosas, D., Valdovinos, L.A. and Elorriaga-Verplancken, F.R. 2017. ‘Northernmost record of the Galapagos fur seal (Arctocephalus galapagoensis): A consequence of anomalous warm conditions around the Galapagos Archipelago’. Aquatic Mammals, 43(6):629–634.

Páez-Rosas, D., Pazmiño, D.A. and Riofrío-Lazo, M. 2020. ‘Unprecedented records of Guadalupe and Juan Fernández fur seals in the Galapagos Archipelago’. Aquatic Mammals, 46(6):549–555.

Páez-Rosas, D., Torres, J., Espinoza, E., Marchetti, A., Seim, H. and Riofrío-Lazo, M. 2021. ‘Declines and recovery in endangered Galapagos pinnipeds during the El Niño event’. Scientific Reports, 11(1):8785.

Palacios, D.M., Félix, F., Florez-González, L., Capella, J.J., Chiluiza, D. and Haase, B. 1997. ‘Sightings of Galápagos sea lions (Zalophus californianus wollebaeki) on the coasts of Colombia and Ecuador’. Mammalia, 61(1):114–115.

Palacios, D.M. 1999. ‘Blue whale (Balaenoptera musculus) occurrence off the Galápagos Islands, 1978-1995’. Journal of Cetacean Research and Management ,1(1):41–51.

Palacios, D.M. and Salazar, S. 2002. ‘Cetáceos’. In: E. Danulat, and G.J. Edgar (eds.), Reserva Marina de Galápagos, Línea Base de la Biodiversidad, pp. 291–304. Santa Cruz (Galápagos, Ecuador): Fundación Charles Darwin/Servicio Parque Nacional Galápagos.

Palacios, D.M. 2003. Oceanographic conditions around the Galapagos Archipelago and their influence on cetacean community structure. Ph.D. Dissertation. Corvallis:Oregon State University.

Palacios, D.M. 2004. ‘Seasonal patterns of sea-surface temperature and ocean color around the Galápagos: regional and local influences’. Deep-Sea Research II: Topical Studies in Oceanography, 51(1–3):43–57.

Palacios, D.M., Salazar, S.K., and Day, D. 2004. ‘Cetacean remains and strandings in the Galápagos Islands, 1923-2003’. Latin American Journal of Aquatic Mammals, 3(2):127–150.

Palacios, D.M., Bograd, S.J., Foley, D.G. and Schwing F.B. 2006. ‘Oceanographic characteristics of biological hot spots in the North Pacific: A remote sensing perspective’. Deep-Sea Research II: Topical Studies in Oceanography, 53(3–4):250–269.

Palacios, D.M. and Forney, K.A. 2008. ‘Cetacean abundance on the western side of the Galápagos Islands during April 2000’. Paper SC/60/SM7 presented to the IWC Scientific Committee Annual Meeting, June 2008, Santiago, Chile. 12 pp.

Palacios, D.M., Bograd, S.J., Foley, D.G. and Schwing, F.B. 2006. ‘Oceanographic characteristics of biological hot spots in the North Pacific: A remote sensing perspective’. Deep-Sea Research II: Topical Studies in Oceanography, 53(3-4):250–269.

Quintana-Rizzo, E., Garcia, L., López, R.J., Tobar-Hurtado, S. and López-Roulet, A. 2017. ‘First record of a Galapagos fur seal (Arctocephalus galapagoensis) in Guatemala’. Marine Biodiversity Records, 10(1):1–8.

Salazar, S. 2002. ‘Lobo marino y lobo peletero’. In: E. Danulat, and G.J. Edgar (eds.), Reserva Marina de Galápagos, Línea Base de la Biodiversidad, pp. 267–290. Santa Cruz (Galápagos, Ecuador): Fundación Charles Darwin/Servicio Parque Nacional Galápagos.

Schaeffer, B.A., Morrison, J.M., Kamykowski, D., Feldman, G.C., Xie, L., Liu, Y., Sweet, W., McCulloch, A. and Banks, S. 2008. ‘Phytoplankton biomass distribution and identification of productive habitats within the Galapagos Marine Reserve by MODIS, a surface acquisition system, and in-situ measurements’. Remote Sensing of Environment, 112(6):3044–3054.

Smith, S.D. and Whitehead, H. 1999. ‘Distribution of dolphins in Galápagos waters’. Marine Mammal Science, 15(2):550–555.

Sweet, W.V., Morrison, J.M., Kamykowski, D., Schaeffer, B.M., Banks, S. and McCulloch, A. 2007. ‘Water mass seasonal variability in the Galapagos Archipelago’. Deep-Sea Research I, 54:2023–2035.

Trillmich, F. 2015a. ‘Arctocephalus galapagoensis’. The IUCN Red List of Threatened Species 2015: e.T2057A45223722. https://dx.doi.org/10.2305/IUCN.UK.2015-2.RLTS.T2057A45223722.en. Accessed on 13 September 2022.

Trillmich, F. 2015b. ‘Zalophus wollebaeki’. The IUCN Red List of Threatened Species 2015: e.T41668A45230540. https://dx.doi.org/10.2305/IUCN.UK.2015-2.RLTS.T41668A45230540.en. Accessed on 13 September 2022.

Taylor, B.L., Baird, R., Barlow, J., Dawson, S.M., Ford, J., Mead, J.G., Notarbartolo di Sciara, G., Wade, P. and 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 13 September 2022.

Torres-Florez, J. P., Olson, P.A., Bedriñana-Romano, L., Rosenbaum, H., Ruiz, J., LeDuc, R. and Hucke-Gaete, R. 2015. ‘First documented migratory destination for eastern South Pacific blue whales’. Marine Mammal Science, 31(4):1580–1586.

Wade, P.R. and Gerrodette, T. 1993. ‘Estimates of cetacean abundance and distribution in the eastern tropical Pacific’. Reports of the International Whaling Commission, 43:477–493.

Wellington, G.M., Strong, A.E. and Merlen, G. 2001. ‘Sea surface temperature variation in the Galápagos Archipelago: a comparison between AVHRR night-time satellite data and in-situ instrumentation (1982–1988)’. Bulletin of Marine Research, 69:27–42.

Whitehead, H., Christal, J. and Dufault, S. 1997. ‘Past and distant whaling and the rapid decline of sperm whales off the Galapagos Islands’. Conservation Biology, 11(6):1387–1396.

Downloads

Download the full account of the Galápagos Archipelago IMMA using the Fact Sheet button below:

To make a request to download the GIS Layer (shapefile) for the Galápagos Archipelago IMMA please complete the following Contact Form:

    * Required fields



    Please read the User Licence Agreement and IMMA Layer Metadata Description