|Scientific Name:||Mirounga angustirostris|
|Species Authority:||(Gill, 1866)|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Facilitator/Compiler(s):||Lowry, L., Ahonen, H., Chiozza, F. & Battistoni, A.|
The Northern Elephant Seal has recovered from near extinction and population growth is expected to continue over the coming decades. Due to its large and increasing population, expanding range and lack of foreseeable threats, the Northern Elephant Seal is listed as Least Concern.
|Previously published Red List assessments:||
|Range Description:||Northern Elephant Seals are a wide ranging pelagic species that occurs throughout most of the eastern Pacific Ocean north of the 27°N latitude, from the coast of Baja California to the Gulf of Alaska and the Aleutian Islands, westward to about the International Dateline (180° longitude) (Le Boeuf et al. 2000, Robinson et al. 2012). Breeding takes place on offshore islands and at a few mainland localities from central Baja California, Mexico, to Northern California, USA. The species breeds at over 15 discrete locations, of which a dozen are well-known and occur mostly on islands of southern California and Baja California (Lowry et al. 2014). A few pups are born in Oregon, Washington, and southern British Columbia.
Adult Northern Elephant Seals migrate to and from their rookeries twice a year, returning once to breed during December-March and again later in the year (April-August) for several weeks to molt, at different times depending on sex and age (LeBeouf et al. 2000). They also show up at additional coastal sites as far north as southern Oregon for molting. Their post-breeding and post-molt migrations take most females north and west to oceanic areas of the North Pacific and Gulf of Alaska twice a year (LeBeouf et al. 2000, Robinson et al. 2012). Adult males, on the other hand, tend to occupy the shelf break along the Aleutian Islands. Few movement data are available for younger age classes and consequently their at-sea distribution is poorly known. Vagrants have been documented in Japan and at the Midway Islands.
Native:Canada; Mexico; United States
|FAO Marine Fishing Areas:||
Pacific – northwest; Pacific – northeast; Pacific – eastern central
|Estimated area of occupancy (AOO) - km2:||10461516|
|Extreme fluctuations in area of occupancy (AOO):||No|
|Continuing decline in extent of occurrence (EOO):||No|
|Extreme fluctuations in extent of occurrence (EOO):||No|
|Continuing decline in number of locations:||No|
|Extreme fluctuations in the number of locations:||No|
|Upper elevation limit (metres):||5|
|Lower depth limit (metres):||1700|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Northern Elephant Seals were a prime target for commercial sealing, and the population was nearly extirpated by hunting during 1818-1869. Due to their pelagic nature, the fact that most animals spend 80% or more of their lives at sea, and that they do all not return to their rookeries at the same time, a few individuals were able to survive the wholesale slaughters at rookery sites. By 1890 only one group of about 100 animals was known to exist (Bartholomew and Hubbs 1990). Following a slow recovery in the early 1900s, Northern Elephant Seals recolonized formerly used sites throughout the 1980s. The total population size in 2010 was estimated to be between 210,000 and 239,000 animals (Lowry et al. 2014). Information for the population in Mexico needs to be updated, but at least for US waters most of the growth in population size has been associated with an increase in the size and number of rookeries in southern California’s Channel Islands. At rookeries in the USA, the population grew at a rate of 17% per year during 1958-1987, slowing to a growth rate of 3.8% per year during 1988-2010 (Lowry et al. 2014).|
|Current Population Trend:||Increasing|
|Habitat and Ecology:||Northern Elephant Seals are the second largest species in the order Pinnipedia and they display significant sexual dimorphism in size and secondary sexual characteristics (Deutsch et al. 1994). Males are three to four times heavier, and nearly 1.5 times the length, of adult females. Adult males reach 4.2 m in length and a maximum weight of 2,500 kg. Mean length for males is 3.85 m and mean weight is 1,844 kg. Maximum weight is seen when the bulls are newly arrived for the breeding season after a summer and fall largely spent feeding (Deutsch et al. 1990). The mean length of adult females is 2.65 m, and they can reach a length of 2.82 m. Mean mass is 488 kg, with a maximum recorded mass of 710 kg, both values are from shortly after females give birth. Newborn pups are about 1.25 m long and weigh 30-40 kg. Pups are born in a long woolly black lanugo coat that is shed without the epidermis starting at about 4-5 weeks and usually lasting several weeks until after the pup is weaned (Reiter et al. 1981). After molting, the newly weaned juvenile’s coat is made up of short hairs like those found on adults and they are counter shaded dark grey above and silver grey below.
During the time on land for breeding or molting, Elephant Seals undergo a complete fast (no food or water) and their body weight declines dramatically due to the demands of lactation (females) and defending territories (males) in the breeding season, and growth of new hair and skin during the molt (Champagne et al. 2012). Adult females can lose almost half their mass during lactation, when they take their single pup from birth to weaning in approximately 25 days. The situation is similar for breeding males, which also lose about half their mass while ashore for periods that can exceed three months.
Females reach sexual maturity at the age of 3-4 years and males at 7-9 years. Gestation lasts 11.3 months, including a delay of implantation. The annual pregnancy rate of mature females is 95%. Longevity is more than 14 years for males and 21 years for females (Condit et al. 2013).
Northern Elephant Seals are highly polygynous, but not strictly territorial. Males compete for access to females by ranking themselves in a hierarchy. There is much male-male fighting, vocalizing, and displaying during the breeding season, when bulls may be ashore for months at a time (LeBeouf 1972). One of the most impressive displays occurs when a male rears up on his hindquarters, thrusts one half to two-thirds of his body upward and produces a distinctive clap threat vocalization as a challenge to other bulls. The sound is a rolling, resonant, metallic-sounding series of backfire-like sounds punctuated with pauses (Sanvito and Galimberti 2003).
Females give birth within a few days of coming ashore, from late December to March. They have a throaty sputtering growl, made with the mouth wide-open, which is used as threat signal. Females and pups have a warbling scream that they use to call to each other, and in the case of the pup, to notify its mother when it is disturbed (LeBeouf 1972). Mother and pup form a strong bond immediately after birth, and females aggressively bite other pups that approach them, occasionally killing them with bites to the head (LeBeouf 1972). However, bulls are a greater source of pup mortality as they regularly crush pups when they charge through aggregations of mothers and pups to chase off or fight encroaching males, or when approaching females for mating. Occasionally, bulls suffocate pups by stopping on top of them and not moving again soon enough (Spraker et al. 2014).
Northern Elephant Seals are one of the deepest and longest diving marine mammals. Time-depth recording devices have documented dives deeper than 1,700 m and as long as 109 minutes by adult females. Rest intervals at the surface are usually short, lasting only several minutes between dives that have an average duration of 23 minutes and depth of 520 m (Robinson et al. 2012). After leaving the rookeries, most Elephant Seals spend 80-90% of their time underwater, helping explain why they are infrequently seen at sea.
The diet of Northern Elephant Seals is largely unknown due to difficulties associated with identifying prey for such a wide-ranging species. Observations based on scat and stomach content analysis of animals on land have identified squid and mesopelagic fish as the main items consumed. New evidence from animals sampled at the Año Nuevo colony (northern California) on diet composition from biochemical techniques indicates that adult females are eating approximately 51% squid, 23% myctophids, and other mesopelagic fish (C. Goetsch pers. comm.).
Great White Sharks and Killer Whales are predators on Northern Elephant Seals (Jefferson et al. 1981). Recent work at the rookeries has revealed that large Great White Sharks aggregate around these sites when Elephant Seals return to haul out (Klimley et al. 2001). Seals that swim at or near the surface as they are approaching or departing the islands are particularly vulnerable to ambush attacks by fast-rising sharks that patrol near the bottom in waters 7-10 meters deep.
|Continuing decline in area, extent and/or quality of habitat:||No|
|Generation Length (years):||8.7|
|Movement patterns:||Not a Migrant|
|Congregatory:||Congregatory (and dispersive)|
|Use and Trade:||The Northern Elephant Seal was heavily exploited for its oil during 1818-1869, after which it was commercially extinct (Bartholomew and Hubbs 1960). Few animals remained and in the 1900s they were completely protected by both Mexico and the U.S.|
Incidental take of Northern Elephant Seals does occur in a variety of coastal net fisheries, but at low levels. This is assumed to be because they move offshore rapidly after leaving colonies to minimize their risk of predation. Anecdotal information points out to an increase in the number individuals observed entangled on land, perhaps as a consequence of the overlap between their at-sea foraging range and the “North Pacific garbage patch”. Some of the lesions caused by these entanglements could lead to the death of individuals, but there are no data on the rate of animals entangled and their survival. Most of the prey of the Northern Elephant Seal is either of low or no commercial fishery value. If the population continues to expand there will likely be new rookeries on mainland beaches, and there will be additional challenges to keep conflicts with humans and domestic and feral animals to a minimum. The risk of transfer of diseases, such as morbillivirus from domestic animals to Northern Elephant Seals, is unknown, but the species is considered to be one of several pinnipeds at high risk of disease outbreaks because of their rapidly expanding population and environmental changes associated with global warming (Lavigne and Schmitz 1990). Tourism at several mainland locations in the United States is extremely popular but highly regulated and is not considered a major threat to the species. Tourist access to nearly all of the islands occupied by Elephant Seals is controlled by law or otherwise regulated in the United States and Mexico, although a number of Mexican islands are inhabited either year round or most of the year by fishermen and their families.
As the species has now recovered from a very small number of survivors, it has likely lost a considerable amount of diversity from passing through this genetic bottleneck, and may now be at greater risk from disease outbreaks and environmental change.
In the USA, Northern Elephant Seals are fully protected by the Marine Mammal Protection Act. In Mexico, Elephant Seals are protected from direct harvest under the Norma Oficial Mexicana (NOM-059-ECOL-2001). Additionally, Elephant Seal rookeries and haul out sites are protected under Natural Protected Areas established by the Mexican government.
Bartholomew, G.A. and Hubbs, C.L. 1960. Population growth and seasonal movements of the northern elephant seal, Mirounga angustirostris. Mammalia 24: 313-324.
Champagne, C.D., Crocker, D.E., Fowler, M.A. and Houser, D.S. 2012. Fasting physiology of the pinnipeds: the challenges of fasting while maintaining high energy expenditure and nutrient delivery for lactation. In: M.D. McCue (ed.), Comparative Physiology of Fasting, Starvation, and Food Limitation, pp. 309-336. Springer , Berlin.
Condit, R., Reiter, J. and Morris, P. 2013. Lifetime survival rates and senescence in northern elephant seals. Marine Mammal Science 30: 122-138.
Deutsch, C.J., Crocker, D.E., Costa, D.P. and le Boeuf, B.J. 1994. Sex- and age-related variation in reproductive effort of northern elephant seals. In: B.J. Le Boeuf & R M. Laws (ed.), Elephant seals: Population ecology, behavior, and physiology, pp. 169-210. University of California Press.
Deutsch, C.J., Haley, M.P. and Le Boeuf, B.J. 1990. Reproductive effort of male northern elephant seals: Estimates from mass loss. Canadian Journal of Zoology 68: 2580-2593.
IUCN. 2015. The IUCN Red List of Threatened Species. Version 2015.2. Available at: www.iucnredlist.org. (Accessed: 23 June 2015).
Jefferson, T.A., Stacey, P.J. and Baird, R.W. 1991. A review of Killer Whale interactions with other marine mammals: predation to co?existence. Mammal Review 21(4): 151-180.
Klimley, A.P., Le Boeuf, B.J., Cantara, K.M., Richert, J.E., Davis, S.F., Van Sommeran, S. and Kelly, J.T. 2001. The hunting strategy of white sharks (Carcharodon carcharias) near a seal colony. Marine Biology 138(3): 617-636.
Lavigne D.M. and Schmitz, O.J. 1990. Global warming and increasing population densities: a prescription for seal plagues. Marine Pollution Bulletin 21: 280-284.
Leboeuf, B.J. 1972. Sexual behavior in the northern elephant seal Mirounga angustirostris. Behavior 41: 1-26.
LeBoeuf B.J., Crocker D.E., Costa D.P., Blackwell S.B., Webb P.M. and Houser D.S. 2000. Foraging ecology of northern elephant seals. Ecological Monographs 70(3): 353-382.
Lowry, M.S., Condit, R., Hatfield, B., Allen, S.G., Berger, R., Morris, P.A., Le Boeuf, B.J. and Reiter, J. 2014. Abundance, Distribution, and Population Growth of the Northern Elephant Seal (Mirounga angustirostris) in the United States from 1991 to 2010. Aquatic Mammals 40: 20-31.
Reiter, J., Panken, K.J. and LeBoeuf, B. 1981. Female competition and reproductive success in Northern elephant seals. Animal Behavior 29: 670-687.
Robinson, P.W., Costa, D.P., Crocker, D.E., Gallo-Reynoso, J.P., Champagne, C.D., Fowler, M.A., Goetsch, C., Goetz, K.T., Hassrick, J.L., Hückstädt, L.A. Kuhn, C.E. Maresh, J.L. Maxwell, S.M. McDonald, B.I. Peterson, S.H., Simmons, S.E,. Teutschel, N.M., Villegas-Amtmann, S. and Yoda, K. 2012. Foraging behavior and success of a mesopelagic predator in the northeast Pacific Ocean: insights from a data-rich species, the northern elephant seal. PLoS One 7:e36728.
Sanvito, S. and Galimberti, F. 2003. Source level of male vocalisations in the genus Mirounga: repeatability and correlates. Bioacoustics 14(1): 47-59.
Spraker, T.R., Lyons, E.T., Kuzmina, T.A., Tift, M.S., Raverty, S., Jaggi, N. and Crocker, D.E. 2014. 2014. Causes of death in preweaned northern elephant seal pups (Mirounga angustirostris, Gill, 1866), Año Nuevo State Reserve, California, 2012. Journal of Veterinary Diagnostic Investigations 1040638714523427.
|Citation:||Hückstädt, L. 2015. Mirounga angustirostris. The IUCN Red List of Threatened Species 2015: e.T13581A45227116. . Downloaded on 25 November 2015.|
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