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Overview
Brief Summary
Description
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Mammal Species of the World
- Original description: Linnaeus, C., 1758. Systema Naturae per regna tria naturae, secundum classis, ordines, genera, species cum characteribus, differentiis, synonymis, locis. Tenth Edition, Laurentii Salvii, Stockholm, 1:77, 824 pp.
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Biology
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Comprehensive Description
Description
Male slightly smaller than female. Slender, streamlined dolphin with long, narrow beak and distinct forehead. Dorsal fin varies from erect to slightly sickle-shaped. Pectoral fins are rather long and slender. Coloration variable but distinctive. Above, uniform slate-gray including dorsal fin and flippers. Underside much paler. Diagnostic 'hourglass' pattern along the flanks said to be tan to ocher, but generally appears pale gray in the water. At closer quarters, a dark line running from the flipper to the center of the lower jaw and from the eye to the base of the beak is visible. 33-67 teeth in each side of each jaw (average 40 to 50).
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Description
Delphinus delphis is listed in the UK Biodiversity Action Plan list of Species of Conservation Concern (Biodiversity Steering Group, 1995; Anon, 1999 (e) ). All species of cetaceans are given protection under the Wildlife and Countryside Act 1981 and the Wildlife (Northern Ireland) Order 1985. All cetacean species are listed on Annex A of EU Council Regulation 338/97 and therefore treated by the EU as if they are on CITES Appendix I thus prohibiting their commercial trade. The common dolphin is listed in Annex II and IV (Animal and Plant Species of Community Interest in Need of Strict Protection) of the EC Habitats Directive. Under Annex IV the keeping, sale or exchange of the species is banned, as well as deliberate capture, killing or disturbance. The Directive requires that member states monitor the incidental capture and killing of all dolphins. An 'Agreement on the Conservation of Small Cetaceans in the Baltic and North Seas' (ASCOBANS), formulated in 1992, has now been signed by seven European countries, including the UK. The Agreement makes provision for protection of specific areas, monitoring, research, information exchange, pollution control and heightening public awareness. The Bonn Convention includes North and Baltic Sea populations of common dolphin on Appendix II.
A report on dolphins in the south west of England (Marine Connection & Wildlife Trusts, 2007) informs of large increases in sightings of Delphinus delphis since 2000, with a peak from December to February.Trusted
Description
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Distribution
Range Description
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Range Description
The case for regarding Mediterranean Common Dolphins as a distinct subpopulation is not perfect, and admittedly rests upon a somewhat complicated chain of inference. Genetic studies indicate a significant level of divergence between Mediterranean and Atlantic populations (Natoli et al. in press). Differences in contaminant levels between dolphins from the Alboràn Sea (northwestern Mediterranean) and Atlantic Ocean also suggest a certain degree of isolation. Organochlorine concentrations in Alboràn Sea dolphins were about double those typical of dolphins in neighboring North Atlantic waters and showed a completely different profile (proportions between PCB congeners, the DDE/tDDT ratio, etc.) (Borrell et al. 2001). Genetic exchange between Common Dolphins from the Mediterranean Sea and Atlantic Ocean, to the extent that it occurs, appears to involve only animals from the Alboràn Sea (Natoli et al. in press), possibly due to oceanographic features such as the Almería-Orán thermohaline front.
At the eastern end of the Mediterranean, there is little indication of movement by Common Dolphins through the narrow Dardanelles Strait between the Aegean and the Marmara and Black Seas, where Common Dolphins are known to occur (Öztürk and Öztürk 1997, Frantzis et al. submitted). A preliminary study of skull morphometrics (Amaha 1994) suggested differences between Black Sea and Mediterranean Common Dolphins. In contrast, a genetic comparison of relatively small samples (8 Black Sea, 20 central Mediterranean) revealed no significant differences (Natoli et al. in press). Clearly, further work based on larger samples is needed to assess and characterize the relationship between Black Sea and Mediterranean Common Dolphins. It is acknowledged that some genetic exchange might occur in portions of the Aegean Sea where favorable habitat still exists (e.g., in the Thracian Sea; Frantzis et al. submitted). However, what remains between the Aegean and Alboràn sectors of the Mediterranean seems to be only isolated, remnant groups (possibly indicative of further population substructure). The once-large aggregate Mediterranean subpopulation is now a small fraction of what it was as recently as the middle of the twentieth century (Bearzi et al. 2003). One note of caution is that there has been relatively little survey coverage of waters along the North African coast.
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Geographic Range
Common dolphins can be found throughout the Atlantic and Pacific Oceans. They are abundant in the Mediterranean Sea, as well as in the Black Sea, the Gulf of Mexico, and the Red Sea. At times, these dolphins follow the Gulf Stream up to Norwegian waters. In addition, scattered populations have been found in the Indian Ocean and waters near Japan. They seldom venture into the Arctic.
(Baker, 1987;
http://whales.ot.com/).
Biogeographic Regions: indian ocean (Native ); atlantic ocean (Native ); pacific ocean (Native )
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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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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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Müller, Y. (2004). Faune et flore du littoral du Nord, du Pas-de-Calais et de la Belgique: inventaire. [Coastal fauna and flora of the Nord, Pas-de-Calais and Belgium: inventory]. Commission Régionale de Biologie Région Nord Pas-de-Calais: France. 307 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9269
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Koninklijk Belgisch Instituut voor Natuurwetenschappen: Beheerseenheid Mathematisch Model Noordzee en Schelde-estuarium: Oostende
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1122
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Camphuysen, Kees
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1119
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Jan Haelters
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=141792
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Gordon, D. (Ed.) (2009). New Zealand Inventory of Biodiversity. Volume One: Kingdom Animalia. 584 pp
http://www.marinespecies.org/porifera/porifera.php?p=sourcedetails&id=145244
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van der Land, J. (2001). Tetrapoda, in: Costello, M.J. et al. (Ed.) (2001). European register of marine species: a check-list of the marine species in Europe and a bibliography of guides to their identification. Collection Patrimoines Naturels, 50: pp. 375-376
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1406
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Slijper, E.J. (1938). Die Sammlung rezenter Cetacea des Musée Royal d'Histoire Naturelle de Belgique [The collection of recent Cetacea of the Musée Royal d'Histoire Naturelle de Belgique]. Bull. Mus. royal d'Hist. Nat. Belg./Med. Kon. Natuurhist. Mus. Belg. 14(10): 1-33
http://www.marinespecies.org/cetacea/aphia.php?p=sourcedetails&id=1619
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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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Koukouras, Athanasios. (2010). Check-list of marine species from Greece. Aristotle University of Thessaloniki. Assembled in the framework of the EU FP7 PESI project.
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=142068
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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: Transient
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Global Range: (>2,500,000 square km (greater than 1,000,000 square miles)) Worldwide in subtropical and warm temperate oceans, including the Mediterranean Sea and Black Sea. In the Pacific Ocean, ranges from British Columbia south to Chile and out to 135 degrees west longitude; there are few records from the Gulf of California; documented from New Caledonia, New Zealand, and Japanese waters in the western Pacific, and there are records from north of Hawaii; range may extend entirely across the tropical and temperate North Pacific; records from the western Atlantic range from at least Florida to Newfoundland and in the eastern Atlantic from northern Europe to the west coast of Africa (Heyning and Perrin 1994). Abundant in waters of eastern North America, ranging north in large numbers to near Nova Scotia and Newfoundland in summer; otherwise, generally ranges from Gulf of Maine to Chesapeake Bay area (Gaskin 1992). Penetrates tropical zone where relatively cool waters keep surface temperature between about 15 to 26 C (Mead and Brownell, in Wilson and Reeder 1993, Gaskin 1992).
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Range
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Physical Description
Morphology
Physical Description
The common dolphin is one of the smallest dolphins. Overall length can vary from 5 feet to a maximum of 8 feet. Females are slightly smaller than males. The common dolphin has a dorsal fin that is almost triangular, in addition to small flippers and flukes. The beak is sharply divided from the lower forehead by a deep groove. The beak is elongated and pointed more than any other species of the same genus. The jaws on each side of the beak are lined with 20 or more small, sharp, recurved teeth, perfect for catching slippery fish. Common dolphins are a colorful dolphin species. The back is either black or dark brown, and they have a white or cream-colored underside. A dark streak stretches from the the lower jaw to the flipper. The flippers and flukes are the same color as the back, black or dark brown, and the eyes are encirled with black markings that extend to the beak. The most distinctive feature is a crisscross pattern which runs across the dolphin's side. It resembles an hourglass and divides the top and bottom colors. This band is a buffy tan in front and gray towards the tail. This characteristic has given this species the nickname "crisscross dolphin".
(Allen, 1979; Baker, 1987; Flower, 1866).
Range mass: 100 to 136 kg.
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Size
Size in North America
Length:
Range: 1.7-2.2 m males; 1.6-2.2 m females
Weight:
Range: up to 110 kg
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Type Information
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Mammals
Sex/Stage: Male;
Preparation: Skull
Collector(s): Collector Unknown
Year Collected: 1848
Locality: Locality Unknown, Chile, South America, South Pacific Ocean
- Type: Peale. 1848. U.S. Explor. Exped., 8. 33.
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Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Mammals
Sex/Stage: Female;
Preparation: Skull
Collector(s): J. Wallace
Year Collected: 1876
Locality: New York, New York Bay, New York, United States, North America, North Atlantic Ocean
- Syntype: Cope, E. D. 1876. Proc. Acad. Nat. Sci. Philadelphia. 28: 134.
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Ecology
Habitat
Habitat and Ecology
Mediterranean common dolphins frequent coastal and upper slope waters (Bearzi et al. 2003). In the Black Sea, common dolphins are distributed mainly offshore and visit shallow coastal waters following seasonal aggregations and regular mass migrations of small pelagic fishes such as anchovy and sprat (Birkun 2006). Black Sea common dolphins avoid waters with low salinity, and this may explain why they do not occur in the Sea of Azov and in the Kerch Strait.
Associations with other marine mammal species are common. Schools in the Eastern Tropical Pacific (ETP) are sometimes associated with yellowfin tuna, and have thus been involved in tuna purse-seine fishing operations (Gerrodette 2002). Mixed-species groups of common, striped and Risso’s dolphins (Grampus griseus) have been observed frequently in the pelagic waters of the Gulf of Corinth, Greece (Frantzis and Herzing 2002). The prey of common dolphins consists largely of small schooling fishes and squids (Perrin 2002).
Systems
- Marine
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Habitat and Ecology
Systems
- Marine
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Habitat
Common dolphins are fond of coastal waters, but are also found well out to sea. Generally, they prefer surface temperatures greater than 10 degrees Celsius. These dolphins normally travel at 5 to 7 miles per hour (although they are known to reach speeds of 29 miles per hour when pursuing food), and can move up to 150 to 200 miles in a 48 hour period. When swimming, schools follow and dive over prominent features of the ocean bottom. Also, herd movements correlate with the seasonal shifts in population of certain fish.
(Alpers, 1961; Baker, 1987; Schevill, 1974;
http://whales.ot.com/).
Aquatic Biomes: benthic ; reef ; coastal
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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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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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Water temperature and chemistry ranges based on 4409 samples.
Environmental ranges
Depth range (m): 0 - 2150
Temperature range (°C): 2.217 - 29.261
Nitrate (umol/L): 0.000 - 17.224
Salinity (PPS): 30.701 - 39.945
Oxygen (ml/l): 4.117 - 7.897
Phosphate (umol/l): 0.033 - 1.095
Silicate (umol/l): 0.494 - 12.030
Graphical representation
Depth range (m): 0 - 2150
Temperature range (°C): 2.217 - 29.261
Nitrate (umol/L): 0.000 - 17.224
Salinity (PPS): 30.701 - 39.945
Oxygen (ml/l): 4.117 - 7.897
Phosphate (umol/l): 0.033 - 1.095
Silicate (umol/l): 0.494 - 12.030
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Habitat
A pelagic species more likely to be encountered from boats offshore going to or from dive sites rather than by the reefs themselves.
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Habitat Type: Marine
Comments: Primarily pelagic, in waters of about 10-28 C; usually along or seaward of the 100 fathom contour. 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: No. No populations of this species make annual migrations of over 200 km.
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Trophic Strategy
Food Habits
Delphinus delphis feed on small fish as well as squid and octopus. Small fish include young herring, pilchard, anchovies, nocturnal hake, sardines, small bonito, as well as sauries. Individual dolphins eat up to 18 to 20 pounds of fish per day. Groups of common dolphins all feed at the same time during the night or day. They are sometimes joined by bands of bottlenose or white-sided dolphins. These feeding forays can last up to an hour. During these, each dolphin rushes to the center of the school the group has been pursuing and tries to seize as many fish as possible, which it swallows whole. Common dolphins have also been known to dive below schools and drive them to the surface. They push their prey completely out of the water and catch them in midair.
(Allen, 1979; Alpers, 1961; Baker, 1987;
http://whales.ot.com/).
Animal Foods: fish; mollusks
Primary Diet: carnivore (Piscivore )
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Comments: Feeds opportunistically on pelagic schooling fishes (e.g., smelt, herring, mackerel, mullet, lantern fish) and squid.
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Population Biology
Global Abundance
10,000 to >1,000,000 individuals
Comments: In the eastern tropical Pacific, northern stock population was estimated at around 500,000 in the 1980s; central stock evidently declined from around 500,000 in the late 1970s to about 250,000 in the 1980s; though data are weak, southern stock may have declined from 750,000 in 1976 to under 250,000 in 1982 (reanalysis yielded estimates that were a couple 100,000s lower) (see IUCN 1991). See IUCN (1991) for population estimates and trend information for other parts of the range (most data are difficult to interpret).
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General Ecology
Travels in groups of a few to several thousand; commonly in groups of several hundred in the Pacific.
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Life History and Behavior
Behavior
Behaviour
Forms schools of up to several hundred animals but also in much smaller groups. Swims fast, reportedly up to 40kmph. Joins ships and bow rides but seldom remains for extended periods of time. Crosses and recrosses the path of the boat seemingly effortlessly. Reportedly shy of divers. A good way to locate this species is to watch for flocks of Lesser Crested Terns Sterna bengalis or other tern species fishing in large flocks. This indicates a large school of fish and possibly dolphins. Omnivorous on small fish, krill, other crustacea and octopus. Observed feeding on squid at dusk. Gestation 11 months. Calves normally born in spring. Nursed for 19 months and lives 35 yrs or more.
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Cyclicity
Life Expectancy
Lifespan/Longevity
Average lifespan
Status: wild: 20.0 years.
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Lifespan, longevity, and ageing
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Reproduction
Reproduction
Common dolphins are viviparous, as are all mammals except monotremes. Females normally give birth to one baby at a time, but have been found to carry twins or triplets. Gestation usually lasts 10 to 12 months. When the calf is born (tail first) it is 3 feet long and usually weighs 25 to 35 pounds.
Common dolphins reach sexual maturity after 12 to 15 years. Courtship occurs in the spring and fall. Males and females court by stroking each other with their flippers, by vigorously rubbing their bodies together, and by swimming along side each other. The male often rushes towards the female as if he is about to bump into her before moving away. The female often swims away from the male's pursuits. After this playful courtship, these dolphins mate in the belly-to-belly position. The male enters the female with his hidden penis and gives a short series of pelvic thrusts. Females have also been observed thrusting. Other sexual activity includes beak-genital propulsion.
Common dolphins have an estimated life span of 35 to 40 years.
(Alpers, 1961; Baker, 1979; Cousteau, 1988; McIntyre, 1974;
http://whales.ot.com/).
Range number of offspring: 1 to 3.
Range gestation period: 10 to 12 months.
Range age at sexual or reproductive maturity (female): 12 to 15 years.
Range age at sexual or reproductive maturity (male): 12 to 15 years.
Key Reproductive Features: iteroparous ; gonochoric/gonochoristic/dioecious (sexes separate); viviparous
Average birth mass: 7000 g.
Average number of offspring: 1.
Babies immediately become a part of the family group. The calf stays close to its mother and never wanders more than a few feet away. The calf feeds on milk from the teats of its mother. Unlike human babies, however, dolphins do not have the lips needed to suck the teats. Also they could not breathe under water if they were able to suck. To solve these problems, the mother squirts milk into her offspring's mouth by contracting muscles. The young dolphin then goes up to the surface to breathe and then comes down for more. Dolphin milk has 6 times more protein and is much more fattening than human milk. It allows the baby dolphin to increase its weight 2 to 3 times faster than a human baby does during the first six months. Suckling goes on for about a year and a half. After six months, the baby occasionally takes solid food.
Parental Investment: pre-fertilization (Provisioning, Protecting: Female); pre-hatching/birth (Provisioning: Female, Protecting: Female); pre-weaning/fledging (Provisioning: Female, Protecting: Female); pre-independence (Protecting: Female); post-independence association with parents; extended period of juvenile learning
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Reproductive parameters vary significantly among different populations. Gestation lasts 10-11 months. Lactation lasts up to 19 months, though in at least some areas young may be weaned in 6 months or less. Sexually mature in 5-7 years or more (but apparently 2-4 years in Black Sea). Calving interval averages probably somewhat over 2 years.
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Delphinus delphis
There are 4 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: Delphinus delphis
Public Records: 4
Species: 4
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
Contributor/s
Justification
History
- 1996Lower Risk/least concern
- 1994Insufficiently Known(Groombridge 1994)
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IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
Assessor/s
Reviewer/s
Justification
Consultation and peer review:
This assessment and the supporting documentation was drafted by Giovanni Bearzi in consultation with Ana Cañadas, Alexandros Frantzis, Giuseppe Notarbartolo di Sciara, Elena Politi, Randall Reeves, and Barbara Taylor. It was reviewed by the CSG membership prior to submission to IUCN.
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Conservation Status
Common dolphins face many obstacles at the hands of human beings. They face exploitation by man, entanglements in fishing nets, hunting, as well as other human disturbances. These, however, can be avoided if the dolphin is lucky. Unfortunately, common dolphins, as well as other aquatic life, cannot avoid the pollution that is overtaking their habitats. Many laws have been enacted to protect the dolphins and other marine life.
(Alpers, 1961;
http://whales.ot.com/).
IUCN Red List of Threatened Species: endangered
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National NatureServe Conservation Status
Canada
Rounded National Status Rank: N4 - Apparently Secure
United States
Rounded National Status Rank: NNA - Not Applicable
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NatureServe Conservation Status
Rounded Global Status Rank: G5 - Secure
Reasons: Abundant and widespread, with limited threats.
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Status
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Trends
Population
In the Atlantic, abundance in European continental shelf waters was estimated at 63,400 (95%CI=27,000-149,000) in 2005 (SCANS-II project; P. Hammond pers. comm.). Offshore, abundance in a block bounded by 53-57ºN and 18-29ºW was estimated at 273,000 (95%CI=153,000-435,000) in 1995 (Cañadas et al. in press). West of the Bay of Biscay, 62,000 common dolphins were estimated in the fishing grounds of the albacore tuna driftnet fishery in 1993 (Goujon 1996). In the western North Atlantic, 121,000 (CV=0.23) were estimated to occur (Waring et al. 2006).
In the western Mediterranean, abundance has been estimated at 19,400 (95%CI=15,300-22,800) in the northern Alborán Sea between 2000 and 2004 (Cañadas 2006). Once one of the most common species in the Mediterranean Sea, the short-beaked common dolphin has experienced a generalized and major decline during the last 30-40 years (Bearzi et al. 2003). Dramatic negative trends were recorded in portions of the central Mediterranean, particularly in the northern Adriatic Sea and in the eastern Ionian Sea (Bearzi et al. 2004; 2006). Recent genetic studies indicate that population structure within the Mediterranean reflects differences in distribution pattern and habitat use by short-beaked common dolphins in the eastern (where the species is predominantly coastal) and western (where it is predominantly pelagic) portions of the basin (Natoli 2004). Genetic exchange between short-beaked common dolphins from the Mediterranean Sea and the Atlantic Ocean, to the extent that it occurs, appears to involve predominantly animals from the Alborán Sea (Natoli 2004).
The population size in the Black Sea is unknown. Line transect surveys have been conducted recently to estimate common dolphin abundance in a few parts of the range. The survey areas are small relative to the total range of the subspecies. Results suggest that current population size is at least several 10,000s, and possibly 100,000 or more (Birkun 2006). By the mid 1960s, the Black Sea subpopulation collapsed due to long-running overexploitation, and a reduction of 70% was inferred. However, directed takes continued until 1983 when cetacean hunting finally ceased. The population has not recovered (Birkun 2006).
Population Trend
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Population
There is no basin-wide estimate of abundance for Common Dolphins in the Mediterranean Sea. Line-transect ship surveys of the Alboràn Sea in 1991?1992 produced an estimate of 14,736 (CV=0.38; 95% CI=6,923?31,366), with a density of 0.16 dolphins per km², but no estimates were made for this species elsewhere in the western Mediterranean due to the low number of sightings (Forcada and Hammond 1998). Vella (in press) combined data from ship and aerial surveys conducted between 1997?2002, and obtained a density estimate of 0.135 dolphins per km² (CV=0.28; 95% CI=0.066?0.290) in the area around the Maltese islands. Around the island of Kalamos in the eastern Ionian Sea, the mean sighting frequency was 0.016 groups per km (or 0.11 dolphins per km) in the years 1993?2000, but in 2001?2002 there was a significant decrease to 0.007 groups per km (or 0.04 dolphins per km) (Student?s t=4.88, p<0.001). The number of individuals encountered in this area has decreased continually, and many individuals that used to be seen regularly until 1996 have disappeared (Bearzi et al. 2003).
Population Trend
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Global Short Term Trend: Relatively stable (=10% change)
Comments: See GABUNDCOM.
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Threats
Threats
Incidental capture of common dolphins in European Atlantic fisheries has been well studied in recent years, and as a result of recent EU legislation, on-board observer programs are being carried out in most of the fisheries considered to have a potentially significant bycatch of common dolphins. Northridge (2006) showed that bycatches of common dolphins in European pelagic trawl fisheries probably total around 800 animals per year in UK and French pelagic trawl fisheries for sea bass. Annual catch rates in the UK sector of this fishery have been falling in recent years and the annual average total mortality recently (2000-2006) has been 170 animals in this sector. Other bycatches in the same area are known to occur in gill nets, tangle nets and possibly other fisheries (ICES 2005; Northridge 2006).
In the western North Atlantic, 105 common dolphins are taken on average each year by sink gill nets and bottom trawls (Waring et al. 2006). By-catches have also been reported from other areas (Crespo et al. 2000; Bearzi et al. 2003).
The main factors thought to have contributed, singly or in synergy, to the decline of Mediterranean short-beaked common dolphins include: 1) incidental mortality in fishing gear, especially driftnets, 2) reduced availability of prey caused by overfishing and habitat degradation, 3) contamination by xenobiotic chemicals resulting in immunosuppression and reproductive impairment, and 4) environmental changes such as increased water temperatures affecting ecosystem dynamics (Bearzi et al. 2003, 2006). A recent survey focusing on the Moroccan driftnet fishing fleet estimated that about 12,000-15,000 dolphins are killed annually around the Strait of Gibraltar (Tudela et al. 2004).
At least 840,000 dolphins were taken from the Black Sea from 1946 until a ban of small cetacean hunting was declared in Turkey in 1983. The take was certainly much greater because that value did not incorporate catch statistics from Romania (whole period), Turkey (before 1976 and after 1981) and Bulgaria (before 1958) (Birkun 2006).
Reduced prey availability is considered to be a major threat to Black Sea common dolphins (Bushuyev 2000). Of two mass mortality events that killed an unknown but certainly large number of common dolphins in 1990 and 1994 (Krivokhizhin and Birkun 1999), the latter was recognised as the result of a morbillivirus epizootic. However, both die-offs coincided with a drastic (8 to 12 fold) decline in the abundance of the two main common dolphin prey species, anchovy and sprat. Such a reduction was caused by a combination of overfishing, eutrophication and the explosive increase of the introduced ctenophore Mnemiopsis leidyi. Correlation between large die-offs of Black Sea common dolphins and prey scarcity suggests that reduced prey availability increases susceptibility to viral infection (Birkun 2006). Prey depletion caused by overfishing was considered as a main cause for the decline of common dolphins in the eastern Ionian Sea (Bearzi et al. 2006).
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Threats
Fishery bycatch is a major threat to many cetacean populations, and it could well have played a role in the decline of Common Dolphins in at least some Mediterranean areas (IWC 1994). In the Alboràn Sea, for example, drift gillnets are known to have caught a few hundred Common Dolphins per year (Silvani et al. 1999). This fishery has stopped, but it operated for many years and undoubtedly had some impact on the population. If drift nets were taking Common Dolphins in the Alboràn Sea, it is reasonable to assume that they were (and are) doing so in other parts of the Mediterranean where drift net fishing and Common Dolphin occurrence overlap. Bearzi et al. (2003) suggest that bycatch alone is unlikely to be the factor most responsible for the decline of Common Dolphins in the Mediterranean, but it may have played a significant role at certain times and in certain areas.
The possibility that the Striped Dolphin has been increasing in the Mediterranean and has begun to occupy the ecological niche of the Common Dolphin has been discussed in the literature (Viale 1985, Aguilar 2000, Bearzi et al. 2003). Such a hypothesis is extremely difficult to prove or disprove, particularly if invoked as a causal factor in the Common Dolphin's decline. Even if it were true that Striped Dolphins have been extending their range to inshore waters traditionally inhabited by Common Dolphins, it would be unclear whether this process was being driven by competitive exclusion, or was instead a secondary outcome of the Common Dolphin's disappearance for some other reason. In any event, competition would not be an issue in areas such as the northern Adriatic Sea, where the Common Dolphin has disappeared while the Striped Dolphin rarely occurs.
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Comments: Relatively heavily exploited in the yellowfin tuna industry of the eastern tropical Pacific (1987 kill was estimated at about 20,000; not subject to any particular threat in waters off North America (Gaskin 1992). Some are killed incidental to various fisheries in other parts of the world.
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Threats
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Management
Conservation Actions
Common dolphins, as with other species impacted by the ETP tuna purse-seine fishery, are managed both nationally by the coastal countries and internationally by the IATTC. The IATTC has imposed annual stock mortality limits on each purse seiner and has promulgated regulations regarding the safe release of dolphins (Bayliff 2001). In the eastern North Pacific, the U.S. drift gillnet fishery has been required to use acoustic warning devices since 1996 to reduce cetacean bycatch; however, some bycatch of Delphinus delphis has continued (Carretta et al. 2005).
The current ban on driftnet fishing in the Mediterranean should be implemented and enforced as a matter of priority.
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Conservation Actions
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Conservation
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Relevance to Humans and Ecosystems
Benefits
Economic Importance for Humans: Negative
Common dolphins feed on fish. This can be a problem for those trying to catch the fish on which these dolphins are preying. In fact, the United Nations reported that dolphins along the California coast eat an average of 300,000 tons of anchovies each year, whereas commercial fisherman take in only 110,000 tons. Because of this, many angry fisherman who catch these enemies in their nets often kill them.
(Allen, 1979;
http://whales.ot.com/).
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Economic Importance for Humans: Positive
Common dolphins are a very helpful and friendly species. They have been known to rescue humans. They also provide entertainment for sailors as they play along the sides of their ships. Furthermore, fisherman use common dolphins in trying to locate fish. In some cultures, such as on the Polynesian Gilbert Islands, dolphins are also eaten as food.
(Alpers, 1961).
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Economic Uses
Comments: Small numbers are taken directly, mainly for human consumption or animal feed, in many parts of the range (IUCN 1991).
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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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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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Wikipedia
Short-beaked common dolphin
The short-beaked common dolphin (Delphinus delphis) is a species of common dolphin. It has a larger range than the long-beaked common dolphin (D. capensis), occurring throughout warm-temperate and tropical oceans, with the possible exception of the Indian Ocean.[4] There are more short-beaked common dolphins than any other dolphin species in the warm-temperate portions of the Atlantic and Pacific Oceans.[5] It is also found in the Caribbean and Mediterranean Seas.
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Physical characteristics
The short-beaked common dolphin is a medium sized dolphin, smaller than the more widely-known bottlenose dolphin. Adults range between 1.6 and 2 metres (5.2 and 6.6 ft), long, and can weigh between 70 and 235 kilograms (150 and 520 lb), although a range between 70 and 110 kilograms (150 and 240 lb) is more common.[4] Males are generally longer and heavier.[4] The color pattern on the body is unusual. The back is dark and the belly is white, while on each side is an hourglass pattern colored light grey, yellow or gold in front and dirty grey in back.[6] It has a long, thin rostrum with 50–60 small, sharp, interlocking teeth on each side of each jaw.[7]
Taxonomy
The short-beaked common dolphin is a member of common dolphin genus, Delphinus within the dolphin family, Delphinidae. Until the mid-1990s, the different forms within Delphinus were not recognized as separate species, but were all considered members of the species D. delphis.[4][5] Currently, there are two recognized species of Delphinus: the short-beaked common dolphin and the long-beaked common dolphin (D. capensis).[1] The short-beaked common dolphin is generally smaller than the long-beaked common dolphin and has a shorter rostrum.
Behavior
Short-beaked common dolphins can live in aggregations of hundreds or even thousands of dolphins.[5] They sometimes associate with other dolphin species, such as pilot whales.[5] They have also been observed bow riding on baleen whales, and they also bow ride on boats.[5] It is a fast swimmer (up to 60 km/h), and breaching behavior and aerial acrobatics are common with this species.[4]
Diet
The short-beaked common dolphin has a varied diet consisting of many species of fish and squid that live less than 200 metres (660 ft) deep.[5]
Reproduction
The Short-beaked common dolphin has a gestation period of 10 to 11 months.[5] The newborn calf has a length of between 70 and 100 centimetres (2.3 and 3.3 ft) and weighs about 10 kilograms (22 lb).[4] For the Black Sea population, weaning occurs at between 5 and 6 months, but occurs later (up to about 19 months) in other areas.[4][5] Typical interbirth interval ranges from 1 year for the Black Sea population to 3 years for eastern Pacific Ocean populations.[5] Age of sexual maturity also varies by location, but can range between 2 and 7 years for females and 3 and 12 years for males.[4][5]
Maximum lifespan is 35 years, but has been estimated at 22 years for the Black Sea population.[4][5]
Conservation
The Mediterranean population of the short-beaked common dolphin Delphinus delphis is listed on Appendix I[8], while the North Sea, Baltic Sea, Mediterranean, Black Sea and eastern tropical Pacific populations are listed on Appendix II[8] of the Convention on the Conservation of Migratory Species of Wild Animals (CMS). The regional listing on Appendix I [8] means that this population has been categorized as being in danger of extinction and CMS Parties strive towards strictly protecting these animals, conserving or restoring the places where they live, mitigating obstacles to migration and controlling other factors that might endanger them. It was listed on Appendix II[8] as it has an unfavourable conservation status or would benefit significantly from international co-operation organised by tailored agreements.
In addition, the species is also covered by the Agreement on the Conservation of Small Cetaceans of the Baltic, North East Atlantic, Irish and North Seas (ASCOBANS) and the Agreement on the Conservation of Cetaceans in the Black Sea, Mediterranean Sea and Contiguous Atlantic Area (ACCOBAMS). The species is further included in the Memorandum of Understanding Concerning the Conservation of the Manatee and Small Cetaceans of Western Africa and Macaronesia (Western African Aquatic Mammals MoU) and the Memorandum of Understanding for the Conservation of Cetaceans and Their Habitats in the Pacific Islands Region (Pacific Cetaceans MoU)
References
- ^ a b Mead, James G.; Brownell, Robert L., Jr. (16 November 2005). "Order Cetacea (pp. 723-743)". In Wilson, Don E., and Reeder, DeeAnn M., eds. Mammal Species of the World: A Taxonomic and Geographic Reference (3rd ed.). Baltimore: Johns Hopkins University Press, 2 vols. (2142 pp.). ISBN 978-0-8018-8221-0. OCLC 62265494. http://www.bucknell.edu/msw3/browse.asp?id=14300045.
- ^ Hammond, P.S., Bearzi, G., Bjørge, A., Forney, K., Karczmarski, L., Kasuya, T., Perrin, W.F., Scott, M.D., Wang, J.Y., Wells, R.S. & Wilson, B. (2008). Delphinus delphis. In: IUCN 2008. IUCN Red List of Threatened Species. Downloaded on 7 October 2008.
- ^ Perrin, W. (2009). Delphinus delphis Linnaeus, 1758. In: Perrin, W.F. World Cetacea Database. Accessed through: World Register of Marine Species at http://www.marinespecies.org/aphia.php?p=taxdetails&id=137094 on 2010-06-26
- ^ a b c d e f g h i Shirihai, H. & Jarrett, B. (2006). Whales, Dolphins and Other Marine Mammals of the World. pp. 171–174. ISBN 0-691-12757-3.
- ^ a b c d e f g h i j k Perrin, W. (2002). "Common Dolphins". In Perrin, W.; Wursig, B. and Thewissen, J.. Encyclopedia of Marine Mammals. Academic Press. pp. 245–248. ISBN 0-12-551340-2.
- ^ Reeves, Stewart, Clapham, Powell. Guide to Marine Mammals of the World. p. 388. ISBN 0-375-41141-0.
- ^ "The Common Dolphin". http://library.thinkquest.org/17963/genus-Delphinus.html. Retrieved 2008-07-03.
- ^ a b c d "Appendix I and Appendix II" of the Convention on the Conservation of Migratory Species of Wild Animals (CMS). As amended by the Conference of the Parties in 1985, 1988, 1991, 1994, 1997, 1999, 2002, 2005 and 2008. Effective: 5th March 2009.
Unreviewed
Names and Taxonomy
Taxonomy
Comments: Mead and Brownell (in Wilson and Reeder 1993) included D. bairdii, D. capensis, and D. tropicalis in D. delphis. Heyning and Perrin (1994) examined variation in Delphinus in the eastern North Pacific and found two distinct forms, a short-beaked form that they recognized as D. capensis (D. bairdii is a junior synonym), and a long-beaked form regarded as D. delphis. They noted that the status of D. tropicalis needs to be examined to determine if it is an extremely long-beaked form along a cline of D. capensis or a third species of Delphinus. Mead and Brownell (in Wilson and Reeder 2005) recognized D. capensis and D. delphis (but not D. tropicalis) as distinct species.
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