The harbour porpoise (Phocoena phocoena) is one of six species of porpoise. It is one of the smallest marine mammals. As its name implies, it stays close to coastal areas or river estuaries, and as such, is the most familiar porpoise to whale watchers. This porpoise often ventures up rivers, and has been seen hundreds of miles from the sea. The harbour porpoise may be polytypic, with geographically distinct populations representing distinct races: P. p. phocoena in the North Atlantic and West Africa, P. p. relicta in the Black Sea and Sea of Azov, an unnamed population in the northwest Pacific and P. p. vomerina in the northeast Pacific.
The English word porpoise comes from the French pourpois (old French porpais, 12th cent.), which is from Medieval Latin porcopiscus, which is a compound of porcus (pig) and piscus (fish). The old word is probably a loan-translation of a Germanic word, cf. Danish marsvin and Dutch mereswijn (sea swine). Classical Latin had a similar name, porculus marinus, and the notion behind the name is probably a fancied resemblance of the snout to that of a pig or the sound of a porpoise breathing resembling a pig snort. The species is sometimes known as the common porpoise in texts originating in the United Kingdom. It is also called a "puffer" or "puffing pig" by fishermen in New England and eastern Canada. The species' taxonomic name, Phocaena phocaena, is the Latinized form of the Greek φώκαινα, phōkaina, "big seal", as described by Aristotle; this from φώκη, phōkē, "seal".
The harbour porpoise is a little smaller than the other porpoises, at about 67–85 cm (26–33 in) long at birth, weighing 6.4-10 kg. Adults of both sexes grow to 1.4 m to 1.9 m (4.6-6.2 ft). The females are heavier, with a maximum weight of around 76 kg (167 pounds) compared with the males' 61 kg (134 pounds). The body is robust, and the animal is at its maximum girth just in front of its triangular dorsal fin. The beak is poorly demarcated. The flippers, dorsal fin, tail fin and back are a dark grey. The sides are a slightly speckled, lighter grey. The underside is much whiter, though there are usually grey stripes running along the throat from the underside of the body.
Populations and distribution
The harbour porpoise species is widespread in cooler coastal waters of the North Atlantic, North Pacific and the Black Sea. The populations in these regions are not continuous and are classified as separate subspecies with P. p. phocoena in the North Atlantic and West Africa, P. p. relicta in the Black Sea and Sea of Azov, an unnamed population in the northwest Pacific and P. p. vomerina in the northeast Pacific. Recent genetic evidence suggests the harbour porpoise population structure may be more complex, and they should be reclassified.
In the Atlantic, harbour porpoises may be present in a curved band of water running from the coast of West Africa to the coasts of Spain, France, the United Kingdom, Ireland, Scandinavia, Iceland, Greenland, Nova Scotia and Newfoundland and the eastern seaboard of the United States. There is another band in the Pacific Ocean running from Sea of Japan, Vladivostok, the Bering Strait, Alaska and California. The harbour porpoise has a global population of 700,000. Areas with sizable numbers include the North Sea, where porpoises number about 350,000; and well as the Gulf of Maine/Bay of Fundy area, the US west coast and Alaska.
Harbour porpoises prefer temperate and subarctic waters. They inhabit fjords, bays, estuaries and harbours, hence their name. They feed mostly on small pelagic schooling fish, particularly herring, capelin, and sprat. They will, however, eat squid and crustaceans in certain places. This species tends to feed close to the sea bottom, at least for waters less than 200 m deep. However, when hunting spat, porpoise may stay closer to the surface. When in deeper waters, porpoises may forage for mid-water fish, such as pearlsides. Harbour porpoises tend to be solitary foragers, but they do sometimes hunt in packs and herd fish together. Young porpoises need to consume about 7% to 8% of their body weight each day to survive, which is approximately 15 pounds or 7 kilograms of fish. Significant predators of harbour porpoises include white sharks and killer whales (orcas). Researchers at the University of Aberdeen in Scotland have also discovered that the local bottlenose dolphins attack and kill harbour porpoises without eating them due to competition for a decreasing food supply.
Behaviour and reproduction
Some studies suggest porpoises are relatively sedentary and usually don't leave a certain area for long. Nevertheless, they have been recorded to move from onshore to offshore waters along coast. Dives of 220m by harbour porpoises have been recorded. Dives can last five minutes but typically last one minute.
The social life of harbour porpoises is not well understood. They are generally seen as a solitary species. Most of the time, porpoise are either alone or in groups of no more than five animals. Porpoises mate promiscuously. Males produce large amounts of sperm, perhaps for sperm competition. Females, become sexual mature at by their third or fourth year and can calve each year for several consecutive years, being pregnant and lactating at the same time. The gestation of the porpoise is typically 10–11 months. Most births occur in late spring and summer. Calves are weaned after 8–12 months.
Harbour porpoises were traditionally hunted for food, as well as for their blubber, which was used for lighting fuel. The drive hunt in the Little Belt strait, Denmark, is the best known example. Thousands of porpoises were caught there until the end of the 19th century and again in smaller scale during the world wars. Currently, however, this species is not subject to commercial hunting, but it is hunted for food and sold locally in Greenland. In prehistoric times, this animal was hunted by the Alby People of the east coast of Oland, Sweden.
The Harbour porpoise populations of the North Sea, Baltic Sea, western North Atlantic, Black Sea and North West Africa are listed on Appendix II of the Convention on the Conservation of Migratory Species of Wild Animals (CMS). This listing means that these populations have an unfavourable conservation status or would benefit significantly from international co-operation organised by tailored agreements.
In addition, the Harbour porpoise is covered by the Agreement on the Conservation of Small Cetaceans of the Baltic, North East Atlantic, Irish and North Seas (ASCOBANS), the Agreement on the Conservation of Cetaceans in the Black Sea, Mediterranean Sea and Contiguous Atlantic Area (ACCOBAMS) and the Memorandum of Understanding Concerning the Conservation of the Manatee and Small Cetaceans of Western Africa and Macaronesia (Western African Aquatic Mammals MoU).
Currently, the total population is in the hundreds of thousands and the harbour porpoise is not under threat of extinction. There are, however, a number of threats that impact population distribution and numbers.
Interactions with fisheries
The main threat to porpoises is static fishing techniques such as gill and tangle nets. Bycatch in bottom-set gill nets is considered the main anthropogenic mortality factor for harbour porpoises worldwide. Bycatch is reported from the Black Sea, the Baltic Sea, the North Sea and the east coast of the United States and Canada. Bottom-set gill nets are anchored to the sea floor and are up to 12.5 miles (20 km) in length. It is unknown why porpoises become entangled in gill nets, since several studies indicate they are able to detect these nets using their echolocation. Porpoise-scaring devices, so-called pingers, have been developed to keep porpoises out of nets and numerous studies have demonstrated they are very effective at reducing entanglement. However, concern has been raised over the noise pollution created by the pingers and whether their efficiency will diminish over time due to porpoises habituating to the sounds.
Mortality resulting from trawling bycatch seems to be less of an issue, probably because porpoises are not inclined to feed inside trawls, as dolphins are known to do.
An increase in the temperature of the sea water is likely to affect the distribution of porpoises and their prey, but has not been shown to occur. Reduced stocks of sand eel along the east coast of Scotland seems to have been the main reason for the malnutrition in porpoises in the area.
Overfishing may reduce preferred prey availability for porpoises. Overfishing resulting in the collapse of herring in the North Sea caused porpoises to hunt for other prey species. Reduction of prey may result from climate change, or overfishing, or both.
Noise from ship traffic and oil platforms is thought to affect the distribution of toothed whales, like the harbour porpoise, that use echolocation for communication and prey detection. The construction of thousands of offshore wind turbines,planned in different areas of North Sea, is known to cause displacement of porpoises from the construction site, particularly if steel monopile foundations are installed by percussive piling, where reactions can occur at distances of more than 20 km. Noise levels from operating wind turbines are low and unlikely to affect porpoises, even at close range.
Marine top predators like porpoises and seals accumulate pollutants such as heavy metals, PCBs and pesticides in their fat tissue. Porpoises have a coastal distribution that potentially brings them close to sources of pollution. Porpoises may not experience any toxic effects until they draw on their fat reserves, such as in periods of food shortage, migration or reproduction.
- Mead, J. G.; Brownell, R. L., Jr. (2005). "Order Cetacea". In Wilson, D. E.; Reeder, D. M. Mammal Species of the World (3rd ed.). Johns Hopkins University Press. pp. 723–743. ISBN 978-0-8018-8221-0. OCLC 62265494. http://www.bucknell.edu/msw3/browse.asp?id=14300116.
- 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). Phocoena phocoena. In: IUCN 2008. IUCN Red List of Threatened Species. Retrieved 7 October 2008.
- Shirihai, Hadoram and Jarrett, Brett (2006). Whales, Dolphins and Seals - A Field Guide to the Marine Mammals of the World. A&C Black Publishers. ISBN 0-7136-7037-1.
- Randall R. Reeves, Brent S. Stewart, Phillip J. Clapham and James A. Powell (2002). National Audubon Society Guide to Marine Mammals of the World. Alfred A. Knopf, Inc. ISBN 0375411410.
- Arne Bjorge, Krystal. A Tolley, "Harbor porpoise Phocoena phocoena" pgs. 530-532 of Encyclopedia of Marine Mammals (edited by William F. Perrin, Bernd Wursig, and J. G.M. Thewissen). Academic Press; 2nd edition. 2008.
- Harbour porpoises (Phocoena phocoena) in the North Atlantic: Distribution and genetic population structure. NAMMCO Sci. Pub 5: 11-29.
- Hammond, P. S., et al. (2002). "Abundance of harbour porpoise and other cetaceans in the North Sea and adjacent waters," Journal of Applied Ecology 39: 361-376.
- A Bjorge and GP Donovan (eds.) (1995). Biology of Phocoenids. AN INTERNATIONAL WHALING COMMISSION SPECIAL. Issue 16.
- Read, Andrew (1999). Porpoises. Stillwater, MN, USA: Voyageur Press. ISBN 0-89658-420-8.
- Westgate AJ, Read AJ, Berggren P, Koopman HN, Gaskin DE (1995). Diving behaviour of harbour porpoises, Phocoena phocoena. Can. J. Fish Aquat. Sci. 52, 1064-1073.
- Aage Petersen (1969). Porpoises and porpoise hunters. Middelfart, Denmark (in Danish).
- "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.
- R. Kastelein, W. W. L. Au, and D. de Haan (2000). Detection distances of bottom-set gill nets by harbour porpoises (Phocoena phocoena) and bottlenose dolphins (Tursiops truncatus). Mar.Environm.Res. 49:359-375.
- A. Villadsgaard, M. Wahlberg, and J. Tougaard (2007). Echolocation signals of free-ranging harbour porpoises, Phocoena phocoena. J.Exp.Biol. 210 (1):56-64.
- S. D. Kraus, A. J. Read, A. Solow, K. Baldwin, T. Spradlin, E. Anderson, and J. Williamson (1997). Acoustic alarms reduce porpoise mortality. Nature 388:525
- Larsen, F (1999). The effect of acoustic alarms on the by-catch of harbour porpoises in the Danish North Sea gill net fishery. Paper SC/51/SM41 presented to the IWC Scientific Committee
- T. M. Cox, A. J. Read, A. Solow, and N. Tregenza (2001). Will harbour porpoises (Phocoena phocoena) habituate to pingers? J.Cetacean.Res.Manage. 3 (1):81-86
- J. Carstensen, O. D. Henriksen, and J. Teilmann (2006). Impacts on harbour porpoises from offshore wind farm construction: Acoustic monitoring of echolocation activity using porpoise detectors (T-PODs). Mar.Ecol.Prog.Ser. 321:295-308
- J. Tougaard, J. Carstensen, J. Teilmann, H. Skov, and P. Rasmussen (2009). Pile driving zone of responsiveness extends beyond 20 km for harbour porpoises (Phocoena phocoena, (L.)). J.Acoust.Soc.Am. 126 (1):11-14
- P. T. Madsen, M. Wahlberg, J. Tougaard, K. Lucke, and P. L. Tyack (2006). Wind turbine underwater noise and marine mammals: Implications of current knowledge and data needs. Mar.Ecol.Prog.Ser. 309:279-295.
- J. Tougaard, O. D. Henriksen, and L. A. Miller (2009). Underwater noise from three offshore wind turbines: estimation of impact zones for harbor porpoises and harbor seals. J.Acoust.Soc.Am. 125 (6):3766-3773
- "Phocoena phocoena". Integrated Taxonomic Information System. http://www.itis.gov/servlet/SingleRpt/SingleRpt?search_topic=TSN&search_value=180473. Retrieved 18 March 2006.
- Friel, D. and Sleeman, D.P. 2010. A neonate harbour porpoise (Phocoena phocoena (L.)) with damaged skin. Ir Nat. J. 31: 55.