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Overview
Brief Summary
Description
Links:
Mammal Species of the World
- Original description: Forster, 1770. In Kalm, Travels into North America, 1:18.
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Biology
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Comprehensive Description
Description
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Description
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Distribution
Range Description
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Geographic Range
The range of Hyperoodon ampullatus (the northern bottlenose whale) extends from the polar ice of the North Atlantic southwest to Long Island Sound and southeast to the Cape Verde Islands.
Biogeographic Regions: atlantic ocean (Native )
- MacDonald, D. 1987. The Encyclopedia of Mammals. New York, New York: Facts on File Publications.
- Minasian, S., K. Balcomb, L. Foster. 1984. The World's Whales. Washington, D.C.: Smithsonian Books.
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Distribution
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Distribution
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UNESCO-IOC Register of Marine Organisms
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1318
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Jan Haelters
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=141792
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MEDIN (2011). UK checklist of marine species derived from the applications Marine Recorder and UNICORN, version 1.0.
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=149081
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Guiry, M.D. & Guiry, G.M. (2011). Species.ie version 1.0 World-wide electronic publication, National University of Ireland, Galway (version of 15 March 2010).
http://www.marinespecies.org/ascidiacea/aphia.php?p=sourcedetails&id=149068
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Borges, P.A.V., Costa, A., Cunha, R., Gabriel, R., Gonçalves, V., Martins, A.F., Melo, I., Parente, M., Raposeiro, P., Rodrigues, P., Santos, R.S., Silva, L., Vieira, P. & Vieira, V. (Eds.) (2010). A list of the terrestrial and marine biota from the Azores. Princípia, Oeiras, 432 pp.
http://www.marinespecies.org/ascidiacea/aphia.php?p=sourcedetails&id=149079
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Ramos, M. (ed.). 2010. IBERFAUNA. The Iberian Fauna Databank
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149024
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Lesage, Veronique, Jean-Francois Gosselin, Mike Hammill, Michael C.S. Kingsley, Jack Lawson (2007). Ecologically and Biologically Significant Areas (EBSAs) in the Estuary and Gulf of St. Lawrence - A marine mammal perspective. DFO Can. Sci. Advis. Sec. Res. Doc. 2007/046: 1-96.
http://www.marinespecies.org/cetacea/aphia.php?p=sourcedetails&id=151497
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National Distribution
Canada
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
United States
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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Global Range: Deep arctic and cooler temperate waters of the North Atlantic, from Nova Scotia to about 70 degrees N in Davis Strait, along the east coast of Greenland to 77 degrees N, and from the United Kingdom to the west coast of Spitzbergen (IUCN 1991). Strandings have occurred south in the western Atlantic to Rhode Island. The Gully southeast of Sable Island and the northern Labrador Sea near the entrance to Hudson Strait are areas of known concentration (Leatherwood and Reeves 1983, Reeves and Mitchell 1993). Has strayed to the Mediterranean (Mead and Brownell, in Wilson and Reeder 1993), the White Sea, and the North Sea (IUCN 1991). Remains widely distributed and locally abundant in some areas (Reeves and Mitchell 1993).
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Range
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Physical Description
Morphology
Physical Description
Individuals of this species can reach up to 9.8m in length, but most are around 6.7-7.6m at the age of sexual maturity (7-14 years). They are sexually dimorphic, with males being up to 25% larger than females. The size of individuals in the Gully population (off Nova Scotia) is believed to be some 0.7m shorter than that of other Northern bottlenose whales. Individual whales may live up to 37 years (Herman 1980, MacDonald 1987, Whitehead et al. 1997a).
Northern bottlenose whales are varied in color, ranging from greenish-brown to chocolate and gray. Individuals may be blotted with patches of grayish-white and coloration is generally lighter on the flanks and underbelly, fading to a white or cream color. Young calves are generally chocolate colored in appearance (Evans 1987, Tinker 1988).
The body is long, robust and cylindrical and the beak is short, resembling a bottle in shape. Both sexes have large, protruding melons that are often vertical anteriorly in older animals and turn yellowish-white with age in males. The melon of the female is not as prominent as that of the male.The posteriorly-curved dorsal fin is 30-38cm in height and is located at a distance of 1/3 the total body length from the tail. The tail fluke lacks a medial notch and the flippers are small and pointed (Minasian et al. 1984, Tinker 1988).
The dentition of the species is highly reduced, with males possessing one or occasionally two pairs of short teeth in the tip of the lower jaw. These teeth never erupt in females, may never fully erupt in males, and often fall out with age (Minasian et al. 1984).
Range mass: 5800 to 7500 kg.
Range length: 9.8 (high) m.
Sexual Dimorphism: male larger
- Herman, L. 1980. Cetacean Behavior: Mechanisms and Functions. Malabar, Florida: Robert E. Krieger Publishing Company.
- Whitehead, H., A. Faucher, S. Gowans, S. McCarrey. 1997a. Status of the Northern Bottlenose Whale, Hyperoodon ampullatus, in The Gully, Nova Scotia. The Canadian Field-Naturalist, 111: 287-292.
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Size
Size in North America
Length:
Range: 9-9.5 m males; 8-8.5 m females
Weight:
Average: 10,000 kg males; 7,500 kg females
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Diagnostic Description
Morphology
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Ecology
Habitat
Habitat and Ecology
The species occupies a very narrow niche; the primary food source is squid of the genus Gonatus (Hooker et al. 2001; Whitehead et al. 2003). The whales may also occasionally eat fish (such as herring and redfish), sea cucumbers, starfish, and prawns. They do much of their feeding on or near the bottom in very deep water (> 800 m, and as deep as 1,400 m; Hooker and Baird 1999).
Systems
- Marine
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Habitat
H. ampullatus is most commonly found in waters at least 1000m deep and often forages at or near the north atlantic ice shelf in sheltered embayments during the spring and summer.
Habitat Regions: temperate ; polar ; saltwater or marine
Aquatic Biomes: pelagic ; coastal
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Habitat
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UNESCO-IOC Register of Marine Organisms
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1318
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Habitat
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Water temperature and chemistry ranges based on 62 samples.
Environmental ranges
Depth range (m): 0 - 0
Temperature range (°C): 1.580 - 22.450
Nitrate (umol/L): 0.303 - 9.648
Salinity (PPS): 31.475 - 36.512
Oxygen (ml/l): 5.034 - 7.861
Phosphate (umol/l): 0.051 - 0.736
Silicate (umol/l): 0.913 - 5.167
Graphical representation
Temperature range (°C): 1.580 - 22.450
Nitrate (umol/L): 0.303 - 9.648
Salinity (PPS): 31.475 - 36.512
Oxygen (ml/l): 5.034 - 7.861
Phosphate (umol/l): 0.051 - 0.736
Silicate (umol/l): 0.913 - 5.167
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Habitat Type: Marine
Comments: Cold temperate to arctic marine waters, often in water 1000 m or more in depth; ice edges and broken pack ice (Leatherwood and Reeves 1983). Cold, deep water along and seaward of the edge of the continental shelf (Reeves and Mitchell 1993, Reeves et al. 1993). Sometimes penetrates up to several miles into ice-covered areas but more frequently occurs in open ocean. Young are born in the water.
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Habitat
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Habitat
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Migration
Non-Migrant: No. All populations of this species make significant seasonal migrations.
Locally Migrant: No. No 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.
Moves northward to edge of pack ice in Davis Straight in spring and summer (Leatherwood and Reeves 1983). In the eastern Atlantic, moves northward April-July, southward July-September (see IUCN 1991). In general, migratory movements are poorly documented (Reeves and Mitchell 1993, Reeves et al. 1993).
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Trophic Strategy
Food Habits
Hyperoodon ampullatus feeds primarily on squid (e.g. Gonatus fabricii), although sea cucumbers (Holothuroidea), herring (Clupea harrengus), cuttlefish (Sepiidae), sea stars (Asteroidea), and other benthic invertebrates supplement the diet. Utilizing a feeding method similar to that of Physeter macrocephalus (the sperm whale), northern bottlenose whales make deep, sustained dives to capture prey. Dives last up to 70min and diving depths range from 80 to 800m with a maximum recorded dive depth of 1453m. Breathing intervals of 10min are common between deep dives and individuals frequently resurface in close proximity to where a dive began (Herman 1980, Hooker and Baird 1999, Minasian et al. 1984, Reeves 1993, Walker 1975).
Animal Foods: fish; mollusks; aquatic crustaceans; other marine invertebrates
Primary Diet: carnivore (Molluscivore )
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Comments: Easts mainly squid, also sometimes herring, sea stars, and other bottom invertebrates and deep water fishes.
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General Ecology
Frequently found traveling in groups of 5-15, also in pairs or singly. According to IUCN (1991), occurs most frequently in groups of 2-4. Approaches ships, may remain with wounded companions.
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Life History and Behavior
Cyclicity
Life Expectancy
Lifespan/Longevity
Average lifespan
Status: wild: 37.0 years.
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Lifespan, longevity, and ageing
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Reproduction
Reproduction
The mating system of Hyperoodon ampullatus is believed to be polygynous, with a single mature male associating with a group of females during the mating season.
Mating System: polygynous
Females become sexually mature at a length of 6.7-7m (8-14 years) and males reach maturity at 7.3-7.6m (7-9 years) (Evans 1987, MacDonald 1987, Minasian et al. 1984).
Mating occurs in spring and early summer and calves are born from April to June. Data from the Gully population near Nova Scotia indicates that the mating and calving period for this population may be from June to August. The gestation period for all Northern bottlenose whales is around twelve months and females exhibit a calving interval of two to three years. (Whitehead et al. 1997a, MacDonald 1987, Reeves et al. 1993, Tinker 1988).
Breeding interval: Females exhibit a calving interval of two to three years
Breeding season: Mating occurs in spring and early summer
Average gestation period: 12 months.
Average weaning age: 12 months.
Range age at sexual or reproductive maturity (female): 8 to 14 years.
Range age at sexual or reproductive maturity (male): 7 to 9 years.
Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); viviparous
Average gestation period: 365 days.
Average number of offspring: 1.
Calves are around 3.5m in length at birth and weaning occurs at around one year of age.
Parental Investment: pre-fertilization (Provisioning, Protecting: Female); pre-hatching/birth (Provisioning: Female, Protecting: Female); pre-weaning/fledging (Provisioning: Female, Protecting: Female)
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Breeding and parturition occur in spring. Gestation lasts about 1 year. Litter size is 1. Calves are weaned after a year or more. Interval between pregnancies probably is 2-3 years (mean probably 2). Minimum age at sexual maturity is 7-11 years. Maximum known longevity apparently is 27 years in females, 37 years in males.
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Hyperoodon ampullatus
There are 2 barcode sequences available from BOLD and GenBank. 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.
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Download FASTA File
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Statistics of barcoding coverage: Hyperoodon ampullatus
Public Records: 2
Species: 2
Species With Barcodes: 1
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Conservation
Conservation Status
IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
Assessor/s
Reviewer/s
Justification
History
- 1996Lower Risk/conservation dependent(Baillie and Groombridge 1996)
- 1994Insufficiently Known(Groombridge 1994)
- 1990Vulnerable(IUCN 1990)
- 1988Vulnerable(IUCN Conservation Monitoring Centre 1988)
- 1986Vulnerable(IUCN Conservation Monitoring Centre 1986)
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Conservation Status
The IUCN relieved Hyperoodon ampullatus of its "vulnerable" listing in 1991, an currently lists it as "Lower Risk, subjec to continued conservation." COSEWIC (Committee on the Status of Endangered Wildlife in Canada) assigned the species to its "vulnerable" category in 1996. Though not listed under the U.S. Endangered Species Act, trade in northern bottlenose whales is restricted by CITES, the species is included in Appendix I. These whales have not been hunted commercially since 1973.
US Federal List: no special status
CITES: appendix i
IUCN Red List of Threatened Species: data deficient
- Simmonds, M., J. Hutchinson. 1996. The Conservation of Whales and Dolphins. New York, New York: John Wiley & Sons.
- Elderkin, M. August 20,1998. "Nova Scotia species at risk with official COSEWIC status" (On-line). Accessed October 13,1999 at http://www.gov.ns.ca/NATR/wildlife/endngrd/specie98.htm.
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National NatureServe Conservation Status
Canada
Rounded National Status Rank: N3 - Vulnerable
United States
Rounded National Status Rank: NU - Unrankable
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Status
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Trends
Population
A study by Christensen and Ugland (1983) resulted in an estimated initial (pre-whaling) population size of about 90,000 whales, reduced to some 30,000 by 1914. The population size by the mid-1980s was said to be about 54,000, roughly 60% of the initial stock size.
Historic catch distributions indicated the existence of at least six centers of abundance, each potentially representing a separate stock (Benjaminsen 1972): i) the Gully; ii) northern Labrador-Davis Strait; iii) northern Iceland; iv) and v), off Andenes and Møre, Norway, and vi) around Svalbard, Spitzbergen. Anecdotal reports from whalers suggest a north/south seasonal migration could occur in some regions but there is little strong evidence for this and whales are reported in the Gully year round. They inhabit the most northerly waters of the Barents and Greenland seas in summer (May to August).
The small resident population in the Gully is largely isolated from populations to the north (Labrador) and northwest (northern Iceland); the whales there are smaller and appear to breed at a different time of year (Whitehead et al. 1997b and are genetically distinct at both mitochondrial and nuclear markers, refuting the hypothesis of seasonal migrations between these regions (Dalebout et al. 2006). Little is known about populations in central and western North Atlantic (Reyes et al. 1993). For statistical consideration, Christensen (1975) assumed that all the bottlenose whales caught east of Greenland belonged to a single subpopulation, while Mitchell (1977) defined Cape Farewell (Greenland) to divide west and east North Atlantic catches (Culik 2004).
Population Trend
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Threats
Threats
By far the major bottlenose whaling nation has been Norway, though some hunting was also done by the UK, Canada and Denmark (Faroes). The northern bottlenose was sought after for its oil (including a form of spermaceti oil in the head) and later for pet food. No hunting of this species has been conducted by Norway since 1973 (Jefferson et al. 1993, Reyes, 1991. The species has been essentially unexploited for almost 30 years, with only a few animals taken in some years in the Faroe Islands (on average 2.2 whales per year in the period 1709-2002). The aggregate population was certainly reduced by whaling, and the extent of recovery is uncertain (Reeves et al. 2003). Mitchell (1977) considered that the population was severely depleted in both the early and modern whaling periods. Few incidental catches have been reported (Reyes 1991).
There are no major fisheries for squid in the Northeast Atlantic, but future developments could represent some threat. This species, like other beaked whales, is likely to be vulnerable to loud anthropogenic sounds, such as those generated by navy sonar and seismic exploration (Cox et al. 2006).
Predicted impacts of global climate change on the marine environment may affect this species of whale, although the nature of impacts is unclear (Learmonth et al. 2006).
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Comments: Currently there are no known major range-wide threats. Populations in the eastern North Atlantic may be depleted as a result of former whaling (Leatherwood and Reeves 1983). Population in the "Gully" off Nova Scotia is potentially threatened by oil and gas development, commercial shipping traffic, and fishing activities (Whitehead et al. 1997).
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Threats
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Management
Conservation Actions
The species was included in the International Whaling Commission schedule in 1977, with recommendations that northern bottlenose whales be granted Protected Stock status with zero catch limit (Klinowska 1991). Populations or stocks are not defined; this, together with estimates of present abundance), should be the focus of future studies (Culik 2004; Dalebout et al. 2006).
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Conservation
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Relevance to Humans and Ecosystems
Benefits
Economic Importance for Humans: Positive
The Northen bottlenose whale was hunted for centuries for the spermaceti oil contained in its head and as a souce of food for native peoples. Scottish, English, and Norwegian whalers hunted H. ampullatus commercially from the mid-1800's until 1973. Because of its behavior of approaching large vessels and defending injured group members, whalers found Northern bottlenose whales easy to hunt. This whale's behavior and the fact that the spermaceti oil contained in its head was of almost equal quality to that of the Sperm whale resulted in overhunting and gross reductions in Northern bottlenosed whale populations around the turn of the century (Bloch et al. 1996, Reeves et al. 1993).
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Economic Uses
Comments: Significant numbers were harvested by commercial whalers in the late 1800s-early 1900s and in the mid-1900s (through the early 1970s); used for head oil and for food for pets and fur-farm animals (IUCN 1991). No longer hunted regularly anywhere in range (Reeves and Mitchell 1993).
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Risks
IUCN Red List Category
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IUCN (2008) Cetacean update of the 2008 IUCN Red List of Threatened Species.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=125373
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