Eumetopias jubatus

(Schreber, 1776)

Steller Sea Lion

G3Vulnerable Found in 65 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
Near threatenedIUCN
HighThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.104433
Element CodeAMAJC03010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNNear threatened
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderCarnivora
FamilyOtariidae
GenusEumetopias
Synonyms
Phoca jubata
Other Common Names
Northern Sea Lion (EN) Otarie de Steller (FR) Steller Sea-lion (EN)
Concept Reference
Wilson, D. E., and D. M. Reeder (editors). 1993. Mammal species of the world: a taxonomic and geographic reference. Second edition. Smithsonian Institution Press, Washington, DC. xviii + 1206 pp. Available online at: http://www.nmnh.si.edu/msw/.
Taxonomic Comments
The English name for sea lions has been inconsistently rendered as sea lion, sealion, and sea-lion (Rice 1998, Wozencraft, in Wilson and Reeder 2005).
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-04-04
Change Date1996-11-18
Edition Date2011-07-25
Edition AuthorsHammerson, G., and E. W. West
Threat ImpactHigh
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences21 - 80
Rank Reasons
Fairly large breeding range around the edge of the North Pacific; abundance declined greatly in the 1970s and 1980s, then declined at a lower rate in the 1990s, especially in the western segment of the range; subsequently the decline greatly decreased or ceased; population fluctuations may be related to competition with fisheries, environmental variability, toxic substances, predation by orcas (killer whales), or other factors, but further study is needed.
Range Extent Comments
Range includes coastal waters of the North Pacific Ocean from California and northern Honshu, Japan, and Korea, north to the Bering Strait (Kenyon and Rice 1961, Calkins and Pitcher 1983, Loughlin et al. 1984, Bigg 1988, Perlov 1991, Sea Lion Recovery Plan Team 1991, NMFS 2008). NMFS (2008) divides the population into eastern and western distinct population segments at 144° west longitude (Cape Suckling, Alaska).

Breeding rookeries extend from the central Kuril Islands and the Okhotsk Sea in the west to Año Nuevo Island and (formerly) San Miguel Island, California, in the east (Loughlin et al. 1987; NMFS 1993, 2008). Most of the largest rookeries formerly were in the Gulf of Alaska and the Aleutian Islands (Loughlin et al. 1984), but with the decline in the western distinct population segment the largest rookeries are now in Southeast Alaska and British Columbia (NMFS 2008). Breeding colonies occur in Oregon and British Columbia but not in Washington (nonbreeding occurrences only, mainly October to April).
Occurrences Comments
NMFS (2008) mapped approximately 65 breeding rookeries (sites where greater than 50 pups were born); 13 of these are in the eastern distinct population segment. There are several hundred haul-out sites (NMFS 1993).
Threat Impact Comments
Western distinct population segment (DPS): A threats assessment concluded that the following threats are relatively minor: (1) Alaska Native subsistence harvest, (2) illegal shooting, (3) entanglement in marine debris, (4) disease, and (5) disturbance from vessel traffic and scientific research. Considerable uncertainty remains about the following potential threats to the recovery of the western DPS (relative impacts in parenthesis): competition with fisheries (potentially high), environmental variability (potentially high), incidental take by fisheries (low), toxic substances (medium) and predation by killer whales (potentially high). Considerable uncertainty, controversy, and disagreement exist within the scientific and stakeholder communities with regard to the potential threat posed by killer whale predation. [Source: NMFS 2008]

Eastern DPS: No threats to continued recovery were identified by NMFS (2008) for the eastern DPS. Although several factors affecting the western DPS also affect the eastern DPS (e.g., environmental variability, killer whale predation, toxic substances, disturbance, shooting), these threats do not appear to be at a level sufficient to keep this population from continuing to recover, given the long term sustained growth of the population as a whole. However, concerns exist regarding global climate change and the potential for the southern part of the range (i.e., California) to be adversely affected. [Source: NMFS 2008]
Ecology & Habitat

Description

Pelage, which lacks underfur, is tawny, yellowish brown, or reddish brown in adults (may appear to be darker when fur is wet), dark brown to blackish in pups; small external ears are present; all limbs are flipperlike, and the hind limbs can be turned forward and used in terrestrial locomotion. Adult males have long, coarse hair on the chest, shoulders, and back; the chest and neck are massive and muscular (Hall 1981, Nowak 1991). Newborn pups have a thick, dark-brown coat that molts to lighter brown after 6 months (Daniel 2003).

Steller sea lions are the largest otariid. Males grow larger than females. The average standard length is 282 cm in adult males and 228 cm in adult females (maximum of about 325 cm and 290 cm, respectively); weight of males averages 566 kg and females 263 kg (maximum of about 1,120 kg and 350 kg) (Fiscus 1961, Calkins and Pitcher 1982, Loughlin and Nelson 1986, Winship et al. 2001). Newborn pups are about 1 meter long and weigh 16-23 kg (Daniel 2003).

Diagnostic Characteristics

This species differs from the California sea lion in larger adult size (average male Stellar sea lion is about 282 cm and 566 kg; average male California sea lion is about 250 cm and 400 kg), paler pelage, absence of a protruding crest on the forehead of adult males, and presence of a large diastema between the fourth and fifth upper postcanine teeth.

Habitat

Marine habitats include coastal waters near shore and over the continental slope; sometimes rivers are ascended in pursuit of prey. When not on land, the sea lions may congregate at nearshore traditional rafting sites, or move out to the edge of the continental shelf (Kajimura and Loughlin 1988, Sea Lion Recovery Plan Team 1991). While offshore, the sea lions are most often found within 35 km of shore (Kenyon and Rice 1961, Fiscus and Baines 1966, Fiscus et al. 1976, Bonnell et al. 1983) but may range out to several hundred kilometers offshore. The distance sea lions move offshore varies seasonally, with fewer animals being sighted at sea during the summer (Fiscus et al. 1976, Bonnell et al. 1983). Waters extending 0.9 km from rookeries (and major haulouts) were determined to be essential habitat by the Recovery Team (see NMFS 1993); these waters, plus an air zone extending 0.9 km above a rookery/major haulout and (in Alaska) a land zone extending 0.9 km landward from a rookery/major haulout are included in critical habitat designations.

The most commonly used terrestrial habitat types are rookeries and haulouts. Rookeries are areas where adults congregate for breeding and pupping. These habitats generally occur on beaches of remote islands with difficult access for humans and other mammalian predators (Sea Lion Recovery Plan Team 1991). The beaches can be sand, gravel, cobble, boulder, or bedrock. Female sea lions tend to select locations for pupping that are gently sloping and protected from waves (Sandegren 1970). Females often use the same pupping site in successive years and tend to breed in or near their natal colony (Calkins and Pitcher 1982). Rookery sites may be used as haulout sites during the nonbreeding season. Independent juveniles usually avoid rookeries (Gentry 1970, Sandegren 1970, Calkins and Pitcher 1983, Hoover 1988). From about two weeks after birth, the pups begin to spend increasing amounts of time in the intertidal areas and swimming near shore. Haulouts are areas used by adult sea lions during the nonbreeding season and by nonbreeding adults and subadults throughout the year (Sea Lion Recovery Plan Team 1991). Haulout locations include exposed rocks, reefs, beaches, jetties, breakwaters, navigational aids, floating docks, and sea ice. Selection of both rookery and haulout sites appears to depend on a number of factors including substrate type, degree of exposure to wind and waves, proximity to food resources, tradition of use, season, and the degree of human disturbance (Gentry 1970, Sandegren 1970, Calkins and Pitcher 1983, Hoover 1988, Johnson et al. 1989).

Ecology

Predators include orcas (killer whales) and sharks.

Reproduction

The life cycle includes several basic stages, minimally including recently born pups, dependent juveniles, independent juveniles, subadults, and adults.

Females give birth to single pups a few days after arriving at the rookery, late May to early July (mainly late June). Females mate with territorial males within 2 weeks of parturition; mating occurs June to mid-July. Implantation is delayed 3-4 months; total gestation period is about 1 year. Female stays with her pup for 3-13 days, then begins a series of 1-2-day feeding trips that extend over a period of several weeks, during which time the pup is left ashore. Young are weaned usually within 1 year in California; lactation usually lasts more than 1 year in Alaska. Females are sexually mature in 3-4 years (or up to 8 years); may breed into their early 20s (Mathisen et al. 1962, Pitcher and Calkins 1981); most adult females breed annually, though a high rate of reproductive failure results in a lower than 100 percent birth rate among adult females (estimated at 55-63 percent by Pitcher and Calkins 1981 and Calkins and Goodwin 1988). Males attain sexual maturity at 3-7 years old (Pitcher and Calkins 1981), but breeding (territorial) males typically are at least 7-8 years old (most often 9-13 years old in Alaska) (Thorsteinson and Lensink 1962, Loughlin et al. 1987, Raum-Suryan et al. 2002). Males may live up to around 20 years and females to around 30 years.
Terrestrial Habitats
Bare rock/talus/scree
Other Nations (2)
United StatesN3
ProvinceRankNative
CaliforniaS2Yes
AlaskaS3Yes
WashingtonS3NYes
OregonS3Yes
CanadaN3
ProvinceRankNative
British ColumbiaS3B,S4NYes
Threat Assessments
ThreatScopeSeverityTiming
5 - Biological resource usePervasive - largeUnknownHigh (continuing)
5.4 - Fishing & harvesting aquatic resourcesPervasive - largeUnknownHigh (continuing)
7 - Natural system modificationsPervasive - largeUnknownHigh (continuing)
7.3 - Other ecosystem modificationsPervasive - largeUnknownHigh (continuing)
9 - PollutionPervasive - restrictedUnknownHigh (continuing)
9.2 - Industrial & military effluentsPervasive - restrictedUnknownHigh (continuing)

Roadless Areas (65)
Alaska (61)
AreaForestAcres
Behm IslandsTongass National Forest4,777
Brabazon AdditionTongass National Forest498,819
ChichagofTongass National Forest555,858
Chilkat-West Lynn CanalTongass National Forest199,772
Chugach-12Chugach National Forest8,116
Chugach-13Chugach National Forest13,337
ClevelandTongass National Forest189,447
College FiordChugach National Forest1,130,818
Copper River WetlandsChugach National Forest85,972
CrystalTongass National Forest18,972
Dall IslandTongass National Forest105,780
Douglas IslandTongass National Forest28,065
DukeTongass National Forest45,091
East KuiuTongass National Forest27,611
EudoraTongass National Forest195,022
Fidalgo-GravinaChugach National Forest257,968
Freshwater BayTongass National Forest44,933
Game CreekTongass National Forest54,469
GravinaTongass National Forest37,381
Hoonah SoundTongass National Forest79,764
Juneau UrbanTongass National Forest101,581
Juneau-Skagway IcefieldTongass National Forest1,187,268
KadinTongass National Forest2,035
KartaTongass National Forest52,117
Kashevarof IslandsTongass National Forest4,747
Kenai MountainsChugach National Forest306,600
KosciuskoTongass National Forest64,134
LindenbergTongass National Forest25,855
MadanTongass National Forest68,553
Mansfield PeninsulaTongass National Forest54,991
MontagueChugach National Forest204,875
MosmanTongass National Forest53,492
Nellie JuanChugach National Forest713,697
North BaranofTongass National Forest314,089
North EtolinTongass National Forest40,993
North KruzofTongass National Forest33,146
North RevillaTongass National Forest215,430
Outer IslandsTongass National Forest99,862
Port AlexanderTongass National Forest120,681
Prince William Sound Is.Chugach National Forest118,698
RedoubtTongass National Forest68,347
RevillaTongass National Forest29,298
RhineTongass National Forest23,010
Salmon BayTongass National Forest22,793
Sheridan GlacierChugach National Forest224,683
Sitka SoundTongass National Forest13,459
Sitka UrbanTongass National Forest112,003
Soda BayTongass National Forest78,091
South KruzofTongass National Forest55,193
South RevillaTongass National Forest52,105
South ZaremboTongass National Forest36,285
Suemez IslandTongass National Forest19,903
SullivanTongass National Forest67,323
Taku-SnettishamTongass National Forest664,928
Tenakee RidgeTongass National Forest20,527
Twenty MileChugach National Forest198,775
Upper SitukTongass National Forest16,789
Windham-Port HoughtonTongass National Forest161,952
WoewodskiTongass National Forest10,136
WoronkofskiTongass National Forest11,114
Yakutat ForelandsTongass National Forest323,648
Oregon (4)
AreaForestAcres
EagleMt. Hood National Forest16,841
TenmileSiuslaw National Forest10,818
Umpqua SpitSiuslaw National Forest2,090
WoahinkSiuslaw National Forest5,309
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