Mammal Species of the World
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- Original description: Gill, T., 1866. Prodome of a monograph of the Pinnepedes. Proceedings of the Essex Institute, Salem Communications, p. 13. 5:3-13.
Northern elephant seals are found in the coastal waters of the Pacific Ocean from the Gulf of Alaska down to Baja California. Foraging migrations by males and females are made seperately, two times yearly. Males journey north to the Aleutian Islands and the Gulf of Alaska. Females don't travel as far north, but instead migrate further west to more open ocean. The total linear distances migrated by these animals each year has been recorded at 21,000 km. Seals can be seen on shore most often from December through March, during the mating season and again beginning in April and continuing through August as they haul out for moulting.
Biogeographic Regions: nearctic (Native ); oceanic islands (Native ); pacific ocean (Native )
- Feldhamer, G., L. Drickamer, S. Vessey, J. Merritt. 1999. Mammalogy: Adaptation, Diversity, and Ecology. Boston: McGraw Hill.
- Le Boeuf, B., D. Crocker, D. Costa, S. Blackwell, P. Webb. 2000. Foraging ecology of northern elephant seals. Ecological Monographs, 70 (3): 353-382.
- McConnaughey, B., E. McConnaughey. 1997. Pacific Coast. New York: Alfred A. Knopf, Inc..
- Reeves, R., B. Stewart, S. Leatherwood. 1992. The Sierra Club Handbook of Seals and Sirenians. San Francisco: Sierra Club Books.
Northern elephant seals migrate to and from their rookeries twice a year, returning once to breed from December to March and again later for several weeks to molt, at different times depending on sex and age. They also show up at additional coastal sites as far north as southern Oregon for moulting. Their post-breeding and post-moult migrations take most seals north and west to oceanic areas of the North Pacific and Gulf of Alaska twice a year. Adult males tend to travel further north and west than adult females. Wanderers have been found as far away as Japan and the Midway Islands.
occurs (regularly, as a native taxon) in multiple nations
Regularity: Regularly occurring
Type of Residency: Transient
Regularity: Regularly occurring
Type of Residency: Year-round
Global Range: Northern elephant seals range widely in the North Pacific (regularly north to British Columbia), with males ranging farther north (as far as Gulf of Alaska and Aleutian Islands) than females. Breeding sites are distributed on islands and the mainland from the central Baja California coast north to California, including islas Guadalupe, San Benito, Cedros, Natividad (few), San Martin (few), and Coronado (few) in Mexico; and Santa Barbara, San Nicolas, San Miguel, Santa Rosa, San Clemente (few), Ano Nuevo, and Southeast Farallon islands, and Ano Nuevo Point, Point Reyes, and Piedras Balncas, in the United States; recently, pupping was observed at Shell Island, Oregon (Hodder et al. 1998). Largest breeding colony is on Guadalupe Island off Baja. Has strayed to Midway Island, Hawaii (Tomich 1986) and to a small island near Japan.
Northern elephant seals are generally brown in color, however there are variations to this coloration. Males are usually a darker brown, while females are a light tan color. Hair is reduced on adult males and females and is completely absent for a short time after moulting. Newborns have hair that is black in color until successfully weaned, when they shed their black coat and it is replaced by a lighter one. Countershading is a feature to all adults and newly weaned youngsters, displaying a darker color dorsally and a lighter color ventrally. They possess two, lobed hind flippers. Pinnae are absent, giving the ear the appearance of being flush with the skin. The most conspicuous feature to the male body is the inflated proboscis that adorns his face. This feature is absent in females and is larger than that of their slightly larger close relatives, southern elephant seals. Young males begin development of the proboscis at 2 years of age, but it is not fully developed until the animal reaches its 8th year of maturity. These mammals are among the largest of the group comprising aquatic carnivores in the Northern Hemisphere. Females typically weigh 600 to 900 kg and males, which outweigh females by 3 to 10 times, can top out at 2300 kg. Females reach a length of 3.1 m on average and males usually extend from 4.0 m to 5.0 m. Newborns typically weigh about 47 kg at birth. They weigh about 147 kg and measure about 1.5 m between 24 and 28 days old, when they are weaned. Teeth are dimorphic in the sexes with males having considerably enlarged canines that are used in fighting.
Range mass: 600 to 2300 kg.
Range length: 3.0 to 5.0 m.
Other Physical Features: endothermic ; homoiothermic; bilateral symmetry
Sexual Dimorphism: male larger; sexes shaped differently; ornamentation
- Ingles, L. 1965. Mammals of the Pacific States. Stanford, California: Stanford University Press.
Length: 650 cm
Weight: 3500000 grams
Size in North America
Average: 3.8 m males; 2.5 m females
Range: 3.6-4.2 m males; 2.2-3 m females
Average: 1,800 kg males; 650 kg females
Range: 1,500-2,300 kg males; 400-800 kg females
Catalog Number: USNM A4704
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Mammals
Sex/Stage: Female; Immature
Collector(s): W. Ayres
Year Collected: 1857
Locality: Saint Bartholomews Bay [= Puerto San Bartolome], Baja California Sur, Mexico, North America, North Pacific Ocean
- Lectotype: Gill, T. 7 Apr 1866 . Proceedings of the Essex Institute. 5: 13.
Northern elephant seals reside terrestrially on the sandy, rocky or muddy shores of the coastline, particularly on offshore islands. They typically aggregate in large groups while on land. These animals spend only 10% of their time on land, during reproduction and moulting. The other 90% is spent in the water, diving and foraging for food, and only 11% of this time in the water is spent at the surface. This means that an extraordinary 85-90% of their time is spent at sea and under water. These mammals can dive exceptionally deep, to 500 to 600 meters (almost 1 mile) on average and to record depths of over 1500 meters for extended periods of time (20 to 70 minutes).
Range depth: 1000 (high) m.
Average depth: 500-700 m.
Habitat Regions: temperate ; terrestrial ; saltwater or marine
Terrestrial Biomes: desert or dune
Aquatic Biomes: pelagic ; coastal
Other Habitat Features: intertidal or littoral
- Andrews, R., D. Costa, B. Le Boeuf, D. Jones. 2000. Breathing frequencies of northern elephant seals at sea and on land revealed by heart rate spectral analysis. Respiration Physiology, 123: 71-85.
- Bonner, W. 1990. The Natural History of Seals. New York, NY: Facts On File, Inc..
- Davis, R., L. Fuiman, T. Williams, B. Le Boeuf. 2001. Three-dimensional movements and swimming activity of a northern elephant seal. Comparative Biochemistry and Physiology Part A, 129: 759-770.
- Delong, R., B. Stewart. 1991. Diving patterns of northern elephant seal bulls. Marine Mammal Science, 7 (4): 369-384.
- Lawlor, T. 1979. Handbook to the Orders and Families of Living Mammals. Eureka, California: Mad River Press.
Habitat and Ecology
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. 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 gray above and silver gray below.
Body weight of adults fluctuates dramatically due to the demands of fasting during the breeding season. 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 2 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 above 14 years for males and 21 years for females (Reijnders et al 1993).
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. 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.
Females give birth within a few days of coming ashore, from late December to March. Females have a throaty sputtering growl, made with the mouth wide open, which is used as threat gesture. Females and pups have a warbling scream call that they use to call to each other, and in the case of the pup, to notify its mother when it is disturbed. 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. 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.
Northern elephant seals hold the record as the deepest-diving pinniped. Time-depth recording devices have documented dives to an astounding 1580 m by an adult male. They also have extreme breath holding ability and have been recorded to dive for as long as 77 minutes. Rest intervals at the surface are usually short, lasting only several minutes between routine dives that last 20-30 minutes and reach 300 to 800 m in depth. After leaving the rookeries, most of these seals spend 80-90% of their time underwater, helping explain why they are infrequently seen at sea.
During migration, females travel further west, but males travel further north. Most of the males go all the way up to the coast of Alaska and the Aleutians, while females move into the deep waters of the Pacific.
Fifty-three species of prey have been identified in the diet of northern elephant seals. More than half of these species are squid. Other prey includes various fishes, such as Pacific whiting, several species of rock fish, and a variety of small sharks and rays. They have also been reported to feed on pelagic red crabs. Approximately 70% of their prey comes from mid and deep water zones in open ocean habitat far offshore.
Great white sharks and killer whales are predators on northern elephant seals. Recent work at the Farallon Islands off of central California has revealed that large great white sharks aggregate around the islands in the fall when juvenile elephant seals return for their annual moult. 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 seven to ten meters deep.
Habitat Type: Marine
Comments: Northern elephant seals feed at sea (temperate and subtropical) and use beaches for breeding and molting.
In California, elephants seals occupy beaches of continental islands and the mainland during breeding (winter) and molting (spring, summer) periods; also a peak in abundance on shore occurs in October when resting females, pups of the year, and some juveniles haul out briefly. When at sea, elephant seals spend little time at the surface; commonly they are at depths of several hundred meters. Young are born on beaches of continental islands and mainland (Ano Nuevo, Point Reyes). Young stay ashore 2-3 months after weaning, leave beaches by end of April. Females generally return to natal area to breed, but some emigrate to other sites hundreds of kilometers away.
Water temperature and chemistry ranges based on 1310 samples.
Depth range (m): 0 - 0
Temperature range (°C): 5.161 - 22.648
Nitrate (umol/L): 0.025 - 17.622
Salinity (PPS): 30.381 - 34.431
Oxygen (ml/l): 4.855 - 7.455
Phosphate (umol/l): 0.152 - 1.777
Silicate (umol/l): 1.436 - 38.397
Temperature range (°C): 5.161 - 22.648
Nitrate (umol/L): 0.025 - 17.622
Salinity (PPS): 30.381 - 34.431
Oxygen (ml/l): 4.855 - 7.455
Phosphate (umol/l): 0.152 - 1.777
Silicate (umol/l): 1.436 - 38.397
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
Non-Migrant: No. All populations of this species make significant seasonal migrations.
Locally Migrant: Yes. At least some populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).
Locally Migrant: Yes. At least some populations of this species make annual migrations of over 200 km.
Elephant seals make protracted migrations between breeding/molting areas and feeding grounds; over a period of 12 months, they migrate from breeding areas to feeding areas then back to breeding areas (to molt) then back to feeding areas and finally back to breeding areas (to breed); over a year, the distance traveled is about 20,000 km (Stewart and DeLong 1995). From San Miguel Island, adult females move to feeding areas at latitudes of but far away from Oregon and Washington; adult males move north to Alaska when not breeding or molting (Stewart and DeLong 1995). Many weaned pups leave breeding grounds in April, diperse north as far as Vancouver Island, return to central California coast in September. Young from southern California rookeries may move north to central California, return to island of birth to molt in spring of next year.
Northern elephant seals spend 90% of their lives in the water in order to feed. During their foraging migrations, they dive into the water repeatedly and continuously to find food, never stopping to rest or sleep for months at a time. Females and males feed separately from each other. Males travel north, remain closer to land, and tend to return to the same locations to feed year after year. Females migrate away from the land, west to the open ocean, and are less accurate in returning to the same places each year. Male foraging behavior is characterized by benthic dives to the sea floor. By contrast, females exhibit pelagic diving while foraging which is defined by a trip to the floor, a partial ascent, another trip to the floor, a partial ascent, etc. There is some speculation as to the reason why male size is so extreme in relation to female size and some suggestions indicate that food type may be a contributing factor. Males are more likely to eat food sources that are dense in mass such as sharks and skates, while females eat foods that are less dense such as squid. These differences in foods is a likely occurence to the different locales in which they are foraging. This resource partitioning is likely to be the result of differences in body size. Males are less vulnerable to predators and are thus safer foraging in areas with more predators. Females are more vulnerable to predators and thus must forage in areas with fewer predators.
While elephant seals are on land they are fasting. They go for extended periods of time without food while they are reproducing and moulting. During this time, all nutrition and energy is broken down from fat that is stored on their bodies as blubber. It is believed that these animals never drink water. Their source of water comes from food sources and broken down fats. In addition they have developed physiological methods to retain water, such as producing a concentrated urine. Another interesting phenomenon about these mammals is the behavior of eating stones before coming ashore. The true purpose of this behavior is not known. The stones are eliminated when they re-enter the water for migration, so it has been suggested that this phenomenon is in response to the long period of fasting.
Foods eaten include: cephalopods, skates, small sharks, and fish.
Animal Foods: fish; mollusks
Primary Diet: carnivore (Piscivore , Molluscivore )
Comments: Eats cephalopods, Pacific hake and other teleosts, various cartilaginous fishes, and jawless fishes (Condit and Le Boeuf 1984). Preys mostly on mesopelagic squid; also apparently feeds commonly on bottom in deep water; commonly dives to several hundred meters. Males do not feed during breeding season.
Northern elephant seals are exceptional divers. When foraging on fishes and squid, they sometimes dive deeper than 1,500 meters and can remain submerged for 1-2 hours. After weaning her pup, a female goes to sea and spends 83-90% of her time underwater.
Northern elephant seals are important as predators on octopus, squid, small sharks, skates, and fish. In this way they impact the populations of these animals. They are also important as food for animals which prey on them, such as great white sharks and orcas.
Northern elephant seals try to feed by diving deep when in the water because the animals that view them as prey typically feed near the surface. Females migrate to the open ocean to feed in order to avoid predators as much as possible.
This list may not be complete but is based on published studies.
Known prey organisms
This list may not be complete but is based on published studies.
10,000 to >1,000,000 individuals
Comments: Total population in the early 1990s was about 127,000.
Dominance hierarchy forms among males on breeding grounds. Highly gregarious when ashore, during breeding season and when molting. Adult females and juveniles come ashore to molt in spring, males in summer, nonpregnant females and young in fall. Preweaning mortality varies greatly among different colonies, from a few percent to sometimes 76% (see Stewart and Huber 1993 for additional survivorship data).
Life History and Behavior
Perception Channels: tactile ; chemical
Comments: Adult females and juveniles return to shore to molt in April-May. Males return to beaches to molt in late spring and summer. After molting, seals go to sea again to feed before returning once again to the breeding beaches.
Because these animals spend such an extraordinary amount of time in the water, there are many gaps in how much we know about them. It is difficult to discern lifespans of these animals and what might be defined as a "natural" cause of death. Estimates of survival of reproductive females is represented in percentages with the probability of survival decreasing with each year of life. In the first year of life, a female's chances of survival are 35%, at 2 years, 30%, and at 3 years, 20%. Adult males live an average of 11 to 13 years old. Young pups are quite vulnerable to death, particularly by predation and trampling. Trampling usually happens as a result of a large male defending its females, crushing the pup under his weight as he tries to quickly move toward an intruder. By some estimates as many as 10% of the young pup population may perish this way annually.
Status: wild: 18 (high) years.
Status: wild: 9 years.
Status: wild: 13 (high) years.
Status: wild: 6.5 years.
Status: captivity: 15.0 years.
- Klimley, A., B. Le Boeuf, K. Cantara, J. Richert, S. Davis. 2001. Radio-acoustic positioning as a tool for studying sit-specific behavior of the white shark and other large marine species. Marine Biology, 138: 429-446.
Lifespan, longevity, and ageing
There is a definitive hierarchy structure to the mating system of these animals because they are polygynous and they aggregate in colonies on land during the breeding season. Each dominant male controls access to mating opportunities with a group of females. Bonner (1990) calls this mating system "female defence polygyny". Less dominant males are restricted to the fringes of a colony and continually try to gain access to females, resulting in battles between males and aggressive charges by the dominant male. Sub-dominant males usually run away but occasionally a male will challenge the dominant male in an attempt to take over the harem. Females release an audible "bawling" sound when a non-dominant male tries to mate with her. This results in a defense attempt by the dominant bull, who chases the less dominant male away. Occasionally the less dominant male becomes defiant and this can result in spectacular displays of threats and sometimes violent fighting. When a male wants to mate, he throws a flipper over the side of a female, grips her neck in his teeth and begins copulation. Resistance by a female only results in the male moving his large and heavy body on top of the female so she is unable to move. Aggressive interactions among males often result in elephant seal pups being killed by trampling. (Bonner 1990)
Mating System: polygynous
Northern elephant seals haul out for birthing and breeding from December to March. The females come into heat only 19 days after giving birth. They remain receptive for about four days, during which mating occurs. Females become sexually mature at 2 years of age, but usually begin giving birth in the 4th year of life. Males are sexually mature at the age of 6 or 7, but only occasionally are allowed to mate before they reach the age of 9 or 10 because of the hierarchy system of mating exhibited by these animals. (Reeves, et al. 1992; Bonner 1990) These animals display a phenomenon in their development cycle called delayed implantation. Delayed implantation lasts for about 3 months, resulting in a total gestation time of nearly one year. This allows both birthing and mating to occur in the same time frame, during the short period of the year when these animals are aggregated in terrestrial colonies. Interestingly, the embryo is never actually implanted, by definition of most mammals. Instead, it attaches only outwardly to the uterine wall throughout its development. (Bonner 1990; Mathews 1952)
Breeding interval: Females may breed as often as once yearly.
Breeding season: Breeding and birthing occurs from December to March.
Range number of offspring: 1 to 2.
Average number of offspring: 1.
Range gestation period: 10 to 12 months.
Range weaning age: 23 to 27 days.
Range age at sexual or reproductive maturity (female): 2 to 10 years.
Average age at sexual or reproductive maturity (female): 9 years.
Range age at sexual or reproductive maturity (male): 2 to 10 years.
Average age at sexual or reproductive maturity (male): 9 years.
Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; viviparous ; delayed implantation
Average birth mass: 37500 g.
Average number of offspring: 1.
The pregnancy will ultimately last just under one year, as a result of delayed implantation. Parturition, which results in one offspring per year (although there have been occurrences of twins), will occur the following winter and lactation will follow for about 27 days before the pup is weaned. Pup weight gain during the period of lactation is phenomenal, the milk is extremely high in fat. During weaning the pup remains close to the mother until such a time that the mother leaves the pup behind to return to sea. Young pups left alone form groups or "pods", which remain on shore for up to 12 weeks without parental care. They learn to swim in the surf and eventually swim further out to sea for a short time to feed. An interesting phenomenon displayed by young male pups left to fend for themselves is that of "milk stealing". An attempt to nurse from lactating females still on the beach raising their young can give the successful pup a significant advantage in survival and higher ranking later on in his life by increasing his weight and overall health.
Parental Investment: no parental involvement; precocial ; pre-fertilization (Protecting: Female); pre-hatching/birth (Provisioning: Female, Protecting: Female); pre-weaning/fledging (Provisioning: Female, Protecting: Female)
- Bonner, W. 1990. The Natural History of Seals. New York, NY: Facts On File, Inc..
- Matthews, L. 1952. Sea Elephant: The Life and Death of the Elephant Seal. London: MacGibbon & Kee.
- Reeves, R., B. Stewart, S. Leatherwood. 1992. The Sierra Club Handbook of Seals and Sirenians. San Francisco: Sierra Club Books.
Single pup is born late December-February (rarely March), mainly in February. Pups are weaned in 4 weeks. Mating occurs a few days before the pups are weaned, then females go to sea to feed. Most adults vacate the breeding areas by the end of February. Young go to sea at 11-16 weeks, after fasting on beach for several weeks. Relatively few males (mainly 9-11 years old, or younger in newly established colonies) inseminate most of the females. Females produce their first pup usually at 3-5 years. Most females breed annually. Reproductive success increases between maternal ages of 3-7 years, then levels off; however, females breeding at a young age may experience lowered reproductive success later in life (Sydeman et al. 1991). Males live up to 15-16 years; oldest known female was 18 years old.
Evolution and Systematics
The nasal turbinates of the northern elephant seal reduce water loss via countercurrent heat exchange.
"Elephant seals fast completely from food and water for 1-3 months during terrestrial breeding. Temporal countercurrent heat exchange in the nasal passage reduces expired air temperature (Te) below body temperature (Tb). At a mean ambient temperature of 13.7 degrees C, Te is 20.9 degrees C. This results in the recovery of 71.5% of the water added to inspired air. The amount of cooling of the expired air (Tb - Te) and the percentage of water recovery varies inversely with ambient temperature. Total nasal surface area available for heat and water exchange, located in the highly convoluted nasal turbinates, is estimated to be 720 cm² in weaned pups and 3140 cm² in an adult male. Nasal temporal countercurrent heat exchange reduces total water loss sufficiently to allow maintenance of water balance using metabolic water production alone." (Huntley et al. 1984:447)
Learn more about this functional adaptation.
- Huntley, A. C.; Costa, D. P.; Rubin, R. D. 1984. The contribution of nasal countercurrent heat exchange to water balance in the northern elephant seal, Mirounga angustirostris. 447-454 p.
Molecular Biology and Genetics
Barcode data: Mirounga angustirostris
Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species.
See the BOLD taxonomy browser for more complete information about this specimen and other sequences.
-- end --
Download FASTA File
Statistics of barcoding coverage: Mirounga angustirostris
Public Records: 2
Specimens with Barcodes: 2
Species With Barcodes: 1
Northern elephant seals are not presently endangered. At one time, however, this species was thought to have been hunted to extinction. They were presume extinct by the 1880's, after being exploited by hunters and whalers seeking to use the animals' thick layer of blubber as an oil source. A few animals were then discovered in 1892 which were captured and killed for scientific study. Eventually, it was discovered that a population of about 20 to 100 individuals had survived. Studies have shown that all individuals of the current population, which has grown to over 175,000, are relatives of these few survivors. The population bottleneck that occurred during this time is of concern because genetic variation is reduced, creating the possibility for the population to be vulnerable to disease or reproductive failure.
US Migratory Bird Act: no special status
US Federal List: no special status
CITES: no special status
IUCN Red List of Threatened Species: least concern
- Weber, D., B. Stewart, J. Garza, N. Lehman. 2000. An empirical genetic assessment of the severity of the northern elephant seal population bottleneck. Current Biology, 10: 1287-1290.
IUCN Red List Assessment
Red List Category
Red List Criteria
IUCN Evaluation of the Northern Elephant Seal, Mirounga angustirostris
Prepared by the Pinniped Specialist Group
A. Population reduction Declines measured over the longer of 10 years or 3 generations
A1 CR > 90%; EN > 70%; VU > 50%
Al. Population reduction observed, estimated, inferred, or suspected in the past where the causes of the reduction are clearly reversible AND understood AND have ceased, based on and specifying any of the following:
(a) direct observation
(b) an index of abundance appropriate to the taxon
(c) a decline in area of occupancy (AOO), extent of occurrence (EOO) and/or habitat quality
(d) actual or potential levels of exploitation
(e) effects of introduced taxa, hybridization, pathogens, pollutants, competitors or parasites.
The current population is ~170,000 and growing. The population is renowned for its remarkable growth during the 20th century, following virtual annihilation by sealers in the 19th century. In 2005, 42,589 pups were counted, an increase of 14,699 (53%) over the number observed in 1991. Total population size increased at a rate of 3% from 1991 to 2005.
A2, A3 & A4 CR > 80%; EN > 50%; VU > 30%
A2. Population reduction observed, estimated, inferred, or suspected in the past where the causes of reduction may not have ceased OR may not be understood OR may not be reversible, based on (a) to (e) under A1.
The total population of this species is probably expanding.
A3. Population reduction projected or suspected to be met in the future (up to a maximum of 100 years) based on (b) to (e) under Al.
A population reduction is not suspected, although the species is susceptible to El Niño and climate warming may increase its effects.
A4. An observed, estimated, inferred, projected or suspected population reduction (up to a maximum of 100 years) where the time period must include both the past and the future, and where the causes of reduction may not have ceased OR may not be understood OR may not be reversible, based on (a) to (e) under A1.
A population reduction to negligible numbers was observed in the past due to hunting by sealers. Hunting stopped and the population recovered, thus the criteria do not apply.
B. Geographic range in the form of either B1 (extent of occurrence) AND/OR B2 (area of occupancy)
B1. Extent of occurrence (EOO): CR < 100 km²; EN < 5,000 km²; VU < 20,000 km²
The EOO (distribution of colonies) is > 20,000 km². The EOO at sea of foraging individuals is much larger than that.
B2. Area of occupancy (AOO): CR < 10 km²; EN < 500 km²; VU < 2,000 km²
The AOO (distribution of colonies) is > 2,000 km². The AOO at sea of foraging individuals is much larger than that.
AND at least 2 of the following:
(a) Severely fragmented, OR number of locations: CR = 1; EN < 5; VU < 10
(b) Continuing decline in any of: (i) extent of occurrence; (ii) area of occupancy; (iii) area, extent and/or quality of habitat; (iv) number of locations or subpopulations; (v) number of mature individuals.
(c) Extreme fluctuations in any of: (i) extent of occurrence; (ii) area of occupancy; (iii) number of locations or subpopulations; (iv) number of mature individuals.
Does not apply for the species.
C. Small population size and decline
Number of mature individuals: CR < 250; EN < 2,500; VU < 10,000
Population size is larger than the criteria and is not declining.
AND either C1 or C2:
C1. An estimated continuing decline of at least: CR = 25% in 3 years or 1 generation; EN = 20% in 5 years or 2 generations; VU = 10% in 10 years or 3 generations (up to a max. of 100 years in future)
C2. A continuing decline AND (a) and/or (b):
(a i) Number of mature individuals in each subpopulation: CR < 50; EN < 250; VU < 1,000
(a ii) % individuals in one subpopulation: CR = 90–100%; EN = 95–100%; VU = 100%
(b) Extreme fluctuations in the number of mature individuals.
Does not apply to the species.
D. Very small or restricted population
Number of mature individuals: CR < 50; EN < 250; VU < 1,000 AND/OR restricted area of occupancy typically: AOO < 20 km² or number of locations < 5
Most populations are larger than the criteria and are widely distributed.
E. Quantitative analysis
Indicating the probability of extinction in the wild to be: Indicating the probability of extinction in the wild to be: CR > 50% in 10 years or 3 generations (100 years max.); EN > 20% in 20 years or 5 generations (100 years max.); VU > 10% in 100 years
There has been no quantitative analysis of the probability of extinction. Climate change may impact the population to the point that the probability of extinction may be important but the quantitative value is unknown.
Listing recommendation — The Northern Elephant Seal is increasing and currently expanding its range. Despite past population reductions, this species should now be classified as Least Concern.
National NatureServe Conservation Status
Rounded National Status Rank: NNA - Not Applicable
Rounded National Status Rank: N4 - Apparently Secure
NatureServe Conservation Status
Rounded Global Status Rank: G5 - Secure
Population growth was due primarily to growth at colonies in southern California. Three colonies accounted for 88.2% of the growth in pups produced: increases in pup production of 5,683 for San Nicolas Island, 4,096 for Santa Rosa Island and 3,459 for Piedras Blancas.
Global Short Term Trend: Increase of 10 to >25%
Comments: Nearly hunted to extinction; population has increased from no more than 100 in late 1800s to 80,000 in 1984 and 127,000 in 1991 (Stewart and Huber 1993). In 1991, more than 21,000 pups were born at California rookeries, about 85% of them on San Nicolas and San Miguel islands (Reeves et al. 1992). In the mid-1990s, the California population was increasing and the Mexican population was apparently stable or decreasing (NMFS, Federal Register, 15 March 1996). See Cooper and Stewart (1983), Bodkin et al. (1985), and Stewart and Huber (1993) for discussion of increase.
Incidental take in a variety of coastal net fisheries does occur, but at low levels. This is assumed to be because northern elephant seals move offshore rapidly after leaving colonies to minimize their risk of shark predation. Most of the prey of the northern elephant seal is either of low commercial value or minimally harvested in fisheries. 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.
Relevance to Humans and Ecosystems
Northern elephant seals may consume some fish and other prey that are important to the fishing industry. However, their impact is probably exaggerated.
Northern elephant seals are a huge attraction for tourists to the Año Nuevo State Reserve in California. Here visitors can watch these magnificent animals from a safe distance, during breeding season. Northern elephant seals were once hunted for their blubber, which was refined to use as oil.
Elephant seals are the only known animals capable of filling collapsed lungs. Their lungs collapse during dives. The surfactant/lubricant responsible for this ability is being researched at the Scripps Institute in San Diego for the potential benefit to premature humans with immature lungs.
Northern elephant seals have also been used in research related to the effect of weightlessness on bone density because they spend 90% of their time in a neutrally buoyant environment. NASA has used this research in their efforts to counteract the effect of weightlessnes on bone density in astronauts.
Because northern elephant seals can dive to extreme depths it has been suggested that they can greatly aid human efforts to explore and map the deep oceans once instruments that can withstand extreme pressures are developed.
Positive Impacts: ecotourism ; research and education
- Hill, A. 1996. "Get Outside! the Bay Area...naturally" (On-line). Accessed November 11, 2001 at http://www.sfgate.com/getoutside/1996/feb96/elephantseals.html.
Comments: Nearly driven to extinction by commercial exploitation in the 1800s.
Northern elephant seal
The northern elephant seal (Mirounga angustirostris) is one of two species of elephant seal (the other is the southern elephant seal). It is a member of the family Phocidae ("true seals"). Elephant seals derive their name from their great size and from the male's large proboscis, which is used in making extraordinarily loud roaring noises, especially during the mating competition. Sexual dimorphism in size is great: The males can grow to 14 ft (4 m) and 5,000 lb (2,300 kg), while the females grow to 11 ft (3 m) and 1,400 lb (640 kg). Correspondingly, the mating system is highly polygynous; a successful male is able to impregnate up to 50 females in one season.
The huge male northern elephant seal typically weighs 1,500–2,300 kg (3,300–5,100 lbs) and measures 4–5 m (13.2–16.5 ft), although some males can weigh up to 3,700 kg (8,152 lbs). Females are much smaller and can range from 400 to 900 kg (990-2,000 lbs) in weight, or roughly a third of the male's bulk, and measure from 2.5 to 3.6 m (8.2–11.9 ft). The bull Southern Elephant Seals are, on average, larger than those in the Northern species but the females in both are around the same size, indicating the even higher level of sexual dimorphism in the Southern species. Both adult and juvenile elephant seals are bar-skinned and black before molting. After molting, they generally have a silver to dark gray coat that fades to brownish-yellow and tan. Adult males have hairless necks and chests speckled with pink, white and light brown. Pups are mostly black at birth and molt to a silver gray after weaning.
The eyes are large, round and black. The width of the eyes and a high concentration of low light pigments suggest sight plays an important role in the capture of prey. Like all seals, elephant seals have atrophied hind limbs whose underdeveloped ends form the tail and tail fin. Each of the "feet" can deploy five long, webbed fingers. This agile, dual palm is used to propel water. The pectoral fins are used little while swimming. While their hind limbs are unfit for locomotion on land, elephant seals use their fins as support to propel their bodies. They are able to propel themselves quickly (as fast as 8 km/h) in this way for short-distance travel, to return to water, catch up with a female or chase an intruder.
Like other seals, elephant seals' bloodstreams are adapted to the cold in which a mixture of small veins surrounds arteries capturing heat from them. This structure is present in extremities such as the hind legs.
A unique characteristic of the northern elephant seal is that it has developed the ability to store oxygenated red blood cells within its spleen. In a 2004 study researchers used MRI to observe physiological changes of the spleen of 5 seal pups during simulated dives. By 3 minutes, the spleens on average contracted to a fifth of their original size, indicating a dive-related sympathetic contraction of the spleen. Also, a delay was observed between contraction of the spleen and increased hematocrit within the circulating blood, and attributed to the hepatic sinus. This fluid-filled structure is initially expanded due to the rush of RBC from the spleen and slowly releases the red blood cells into the circulatory system via a muscular vena caval sphincter found on the cranial aspect of the diaphragm. This ability to slowly introduce RBC into the blood stream is likely to prevent any harmful effects caused by a rapid increase in hematocrit.
Range and ecology
The northern elephant seal lives in the eastern Pacific Ocean. Feeding grounds extend from northern Baja California to northern Vancouver Island. Males migrate as far north as Alaska and British Columbia, while females migrate as far west as Hawaii. They come ashore to breed, give birth and molt, mostly on offshore islands. While the pelagic range covers an enormous span, breeding is restricted to only about seven principal areas, four of which are on islands off the coast of California. Recently, increasing numbers have been observed in the Gulf of California. Breeding colonies exist at Channel Islands, Año Nuevo State Reserve, Piedras Blancas Light, Morro Bay State Park and the Farallon Islands in the US, and Isla Guadalupe, Isla Benito del Este and Isla Cedros in Mexico. Some breeding has been observed at Castle Rock in Northern California and Shell Island off Oregon and in January 2009, the first elephant seal births were recorded in British Columbia at Race Rocks. The California breeding population is now demographically isolated from the population in Baja California.
Historical occurrences of residential or occasional in western North Pacific are fairly unknown. There have been two records of vagrants visiting to Japanese coasts; a male on Niijima in 1989 (reference introducing a visit by a North Pacific Right Whale in 2011), and a young seal on beaches in Hasama, Tateyama in 2001 (where another right whale was seen in 2000). Some individuals have been observed on the coast of northeast Asia. Certain individuals established haul-out sites at the Commander Islands in the early 2000s; however, due to aggressive interactions with local Steller sea lions, long-term colonization is not expected.
The northern elephant seals are nocturnal deep feeders famous for the long time intervals they remain underwater. This species dives to great depths while feeding, typically between 300 m (1,000 ft) and 800 m (2,600 ft); moreover, the northern elephant seal will generally not feed in depths of less than 200 m (700 ft). Both sexes eat a variety of prey, including pelagic, deep-water squid, Pacific hake, sharks, rays, and ratfish. Octopoteuthis deletron squid are the most common prey item, found in the stomachs of 58% of individuals sampled off the coast of California. A female northern elephant seal was documented in 2013 by a deep sea camera at a depth of 894 m (2,933 ft), where it consumed a Pacific hagfish, slurping it up from the ocean floor. The event was reported by a Ukrainian boy named Kirill Dudko, who further reported the find to scientists in Canada. Elephant seals do not need to drink, as they get their water from food and metabolism of fats.
While hunting in the dark depths, elephant seals seem to locate their prey at least partly by vision; the bioluminescence of some prey animals can facilitate their capture. Elephant seals do not have a developed a system of echolocation in the manner of cetaceans, but their vibrissae, which are sensitive to vibrations, are assumed to play a role in search of food. Males and females differ in diving behavior. Males tend to hug the continental shelf while making deep dives and forage along the bottom, while females have more jagged routes and forage in the open ocean. Males return to the same feeding ground every year, while females have less predictable feeding migrations. Elephant seals are prey for killer whales and white sharks. Both are most likely to hunt pups, and seldom hunt large bull elephant seals, but have taken seals of all ages. The shark, when hunting adults, is most likely to ambush a seal with a damaging bite and wait until it is weakened by blood loss to finish the kill.
Social behavior and reproduction
Northern elephant seals return to their terrestrial breeding ground in December and January, with the bulls arriving first. The bulls haul out on isolated or otherwise protected beaches, typically on islands or very remote mainland locations. It is important that these beach areas offer protection from the winter storms and high surf wave action. The bulls engage in fights of supremacy to determine which few bulls will achieve a harem.
After the males have arrived the beach, the females arrive to give birth. Females fast for five weeks and nurse their single pup for four weeks; in the last few days of lactation, females come into estrus and mate. In this polygynous society, a high-ranking bull can have a harem of 30–100 cows, depending on his size and strength. Males unable to establish harems will wait on the periphery, and will try to mount nearby females. Dominant bulls will disrupt copulations of lower-ranking bulls. They can mount females without interference, but commonly break off to chase off rivals. While fights are not usually to the death, they are brutal and often with significant bloodshed and injury; however, in many cases of mismatched opponents, the younger, less capable males are simply chased away, often to upland dunes. In a lifetime, a successful bull could easily sire over 500 pups. Most copulations in a breeding colony are done by only a small number of males and the rest may never be able to mate with a female. Pups are sometimes crushed during battles between bulls.
After arrival on shore, males fast for three months, and females fast for five weeks during mating and when nursing their pups. The gestation period is about 11 months. Sometimes, a female can become very aggressive after giving birth and will defend her pup from other females. Such aggression is more common in crowded beaches. While most females nurse their own pups and reject nursings from alien pups, some do accept alien pups with their own. An orphaned pup may try to find another female to suckle and some are adopted, at least on Año Nuevo Island. Pups nurse about four weeks and are weaned abruptly approximately two months before being abandoned by their mother. Left alone, weaned pups will gather into groups and stay on shore for 12 more weeks. The pups learn how to swim in the surf and eventually swim farther to forage. Thus, their first long journey at sea begins.
Elephant seals communicate though various means. Males will threaten each other with the snort, a sound caused by expelling air though their probosces, and the clap-trap, a loud, clapping sound comparable to the sound of a diesel engine. Pups will vocalize when stressed or when prodding their mothers to allow them to suckle. Females make an unpulsed attraction call when responding to their young, and a harsh, pulsed call when threatened by other females, males or alien pups. Elephant seals produce low-frequency sounds, both substrate-borne and air-borne. These sounds help maintain social hierarchy in crowded or noisy environments and reduce energy consumption when fasting.
History and status
Beginning in the 18th century, northern elephant seals were hunted extensively, almost to extinction by the end of the 19th century, being prized for oil made from their blubber, and the population may have fallen as low as 20. In 1874, Charles Melville Scammon recorded in Marine Mammals of the Northwestern Coast of America, that an 18-ft-long bull caught on Santa Barbara Island yielded 210 gallons of oil. They were thought to be extinct in 1884 until a remnant population of eight individuals was discovered on Guadalupe Island in 1892 by a Smithsonian expedition, who promptly killed seven of the eight for their collections. The elephant seals managed to survive, and were finally protected by the Mexican government in 1922. Since the early 20th century, they have been protected by law in both Mexico and in the United States. Subsequently, the U.S. protection was strengthened after passage of the Marine Mammal Protection Act of 1972, and numbers have now recovered to over 100,000.
Nevertheless, a genetic bottleneck exists in the existing population, which could make it more susceptible to disease and pollution. In California, the population is continuing to grow at around 25% per year, and new colonies are being established; they are now probably limited mostly by the availability of haul-out space. Their breeding was probably restricted to islands, before large carnivores were exterminated or prevented from reaching the side of the ocean. Numbers can be adversely affected by El Niño events and the resultant weather conditions, and the 1997–98 El Niño may have caused the loss of about 80% of that year's pups. Presently, the northern elephant seal is protected under the federal Marine Mammal Protection Act and has a fully protected status under California law.
Populations of rookery sites in California have increased during the past century. At Año Nuevo State Park, for example, no individuals were observed whatsoever until the 1950s; the first pup born there was observed in the early 1960s. Currently, thousands of pups are born every year at Año Nuevo, on both the island and mainland. The growth of the site near San Simeon has proved even more spectacular; no animals were there prior to 1990. Currently, the San Simeon site hosts more breeding animals than Año Nuevo State Park during winter season.
- Campagna, C. (2008). Mirounga angustirostris. In: IUCN 2008. IUCN Red List of Threatened Species. Retrieved 28 January 2009.
- Beer, Encyclopedia of North American Mammals: An Essential Guide to Mammals of North America. Thunder Bay Press (2004), ISBN 978-1-59223-191-1.
- Mirounga angustirostris. Northern Elephant Seal. Smithonian National Museum of Natural History
- Novak, R. M. (1999). Walker's Mammals of the World. 6th edition. Johns Hopkins University Press, Baltimore. ISBN 0-8018-5789-9
- Thornton SJ and Hochachka PW (2004). "Oxygen and the diving seal". Undersea Hyperb Med. 31 (1): 81–95. PMID 15233163.
- Le Boeuf, B., D. Crocker, D. Costa, S. Blackwell, P. Webb (2000). "Foraging ecology of northern elephant seals". Ecological Monographs 70 (3): 353–382. JSTOR 2657207.
- Condit, R. and Le Boeuf, B.J. (1984). "Feeding Habits and Feeding Grounds of the Northern Elephant Seal". J. Mammal 65 (2): 281–290. doi:10.2307/1381167.
- U.S. Pacific Marine Mammal Stock Assessments: 2007 (NMFS-SWFSC-414). (PDF) . Retrieved on 2011-09-15.
- Stewart BS, Yochem PK, Huber HR, DeLong RL, Jameson RJ, Sydeman WJ, Allen SG, Le Boeuf BJ (1994) "History and present status of the Northern elephant seal population". In: Le Boeuf BJ, Laws RM (eds) Elephant Seals: Population Ecology, Behavior, and Physiology. University of California Press, Berkeley, CA, pp. 29–48, ISBN 0520083644.
- Hodder J, Brown RF, Cziesla C (1998). "The northern elephant seal in Oregon: A pupping range extension and onshore occurrence". Marine Mammal Science 14: 873–881. doi:10.1111/j.1748-7692.1998.tb00772.
- Elephant Seal birth of baby ninene. Racerocks.com. Retrieved on 2011-09-15.
- http://www9.ocn.ne.jp/~dorsals/honyu/azarasi.htm. retrieved on 14-05-2015
- Kuznetsov V.B. (2004). "Marine Mammals of the Holarctic".
- Morejohn, G.V. and Beltz, D.M. (1970). "Contents of the stomach of an elephant seal". Journal of Mammalogy 51 (1): 173–174. doi:10.2307/1378554.
- Le Beouf, Burney J.; Richard M. Laws (1994). Elephant Seals: Population ecology, behavior, and physiology. University of California Press. pp. 213–214. ISBN 978-0-520-08364-6.
- Outdoor. GrindTV. Retrieved on 2014-03-18.
- White Sharks – Carcharodon carcharias. Pelagic Shark Research Foundation.
- Riedman, M.L. and Le Boeuf, B.J. (1982). "Mother-pup separation and adoption in northern elephant seals". Behav. Ecol. Sociobiol 11 (3): 203–213. doi:10.1007/BF00300063. JSTOR 4599535.
- Le Boeuf BJ (1972). "Sexual behavior in the Northern Elephant seal Mirounga angustirostris". Behaviour 41 (1): 1–26. doi:10.1163/156853972X00167. JSTOR 4533425. PMID 5062032.
- Le Boeuf BJ (1974). "Male-male competition and reproductive success in elephant seals". Amer. Zool. 14: 163–176. doi:10.1093/icb/14.1.163.
- Le Boeuf BJ; Whiting, R. J.; Gantt, R. F. (1972). "Perinatal behavior of northern elephant seal females and their young". Behaviour 43 (1): 121–156. doi:10.1163/156853973x00508. JSTOR 4533472. PMID 4656181.
- Christenson, T. E. and Le Boeuf, B. J. (1978). "Aggression in the Female Northern Elephant Seal, Mirounga angustirostris". Behaviour 64 (1/2): 158–172. doi:10.1163/156853978X00495. JSTOR 4533866.
- Steward, B. S.; Huber, H. R. (1993). "Mirounga angustirostris". Mammalian Species 449: 1–10. doi:10.2307/3504174.
- Scammon, Charles Melville (2007). The marine mammals of the northwestern coast of North America: together with an account of the American whale-fishery. Heyday Books. p. 132. ISBN 978-1-59714-061-4. Retrieved 2011-09-05.
- Busch, Briton Cooper (1987). The War Against the Seals: A History of the North American Seal Fishery. McGill-Queen's Press. p. 187. ISBN 978-0-7735-0610-7.
- Hoelzel, A. R., Fleischer, R. C., Campagna, C., Le Boeuf, B. J. and Alvord, G. (2002). "Impact of a population bottleneck on symmetry and genetic diversity in the northern elephant seal". Journal of Evolutionary Biology 15 (4): 567–575. doi:10.1046/j.1420-9101.2002.00419.x.
- Weber, D. S., Stewart, B. S., Garza, J. C. & Lehman, N. (2000). "An empirical genetic assessment of the severity of the northern elephant seal population bottleneck". Current Biology 10 (20): 1287–1290. doi:10.1016/S0960-9822(00)00759-4. PMID 11069110.
- Le Boeuf, Burney J. and Kaza, Stephanie, ed. (1981). "Ch. 7 "Mammals"". The Natural History of Ano Nuevo. Boxwood Press. ISBN 0910286779.