Lessepsian migration

The Suez Canal across which marine species migrate, the so-called Lessepsian migration
Fistularia commersonii, a Lessepsian migrant[1]

Lessepsian migration (also called Erythrean invasion) is the ongoing migration of marine species across the Suez Canal, usually from the Red Sea to the Mediterranean Sea, more rarely in the opposite direction. It is named after Ferdinand de Lesseps, the French diplomat in charge of the canal's construction.

In a wider context, the term "Lessepsian migration" is used to describe any animal migration over man-made structures, i.e. that which would not have occurred had it not been for the presence of an artificial structure.

Red Sea to Mediterranean

The opening of the Suez Canal in 1869 created the first salt-water passage between the Mediterranean and Red Seas. The Red Sea is slightly higher than the Eastern Mediterranean, so the canal serves as a tidal strait that pours Red Sea water into the Mediterranean. The Bitter Lakes, which are hypersaline natural lakes that form part of the canal, blocked the migration of Red Sea species into the Mediterranean for many decades, but as the salinity of the lakes gradually equalized with that of the Red Sea, the barrier to migration was removed, and plants and animals from the Red Sea have begun to colonize the eastern Mediterranean.[2]

The Red Sea is generally saltier and more nutrient-poor than the Atlantic, so the Red Sea species have advantages over Atlantic species in the less salty and nutrient-rich Eastern Mediterranean. Accordingly, most invasions are of Red Sea species into the Mediterranean, and only few in the opposite direction. The construction of the Aswan High Dam across the Nile River in the 1960s reduced the inflow of freshwater and nutrient-rich silt from the Nile into the eastern Mediterranean, making conditions in the eastern Mediterranean even more like the Red Sea thus increasing the impact of the invasions and facilitating the occurrence of new ones.[2]

Invasive species originating from the Red Sea and introduced into the Mediterranean by the construction of the canal have become a major component of the Mediterranean ecosystem, and have had serious impacts on the Mediterranean ecology, endangering many local and endemic Mediterranean species. To this day, about 300 species native to the Red Sea have been identified in the Mediterranean Sea, and probably others are as yet unidentified. In recent years, the Egyptian government's announcement of its intentions to deepen and widen the canal have raised concerns from marine biologists, fearing this will worsen the invasion of Red Sea species into the Mediterranean, facilitating the crossing of the canal for additional species.[3]

Parasite invaders

The invasion of new Red Sea species into the Mediterranean has also facilitated the invasion of their associated parasites, for example the copepod Eudactylera aspera was found on a spinner shark Carcharhinus brevipinna taken off Tunisia, the copepod had originally been described from specimens taken from C. brevipinna off Madagascar and its finding in the Mediterranean has arguably confirmed the previously disputed status of C. brevipinna as a Lessepsian migrant. In addition the parasites originating in the Red Sea have shown an ability to use related native Mediterranean fish species as alternative hosts; e.g. the copepod Nipergasilus bora was known to parasitise the grey mullets Mugil cephalus and Planiliza carinata in the Red Sea, both taxa having been recorded as Lesepsian migrants, and was subsequently found parasitizing the native Mediterranean mullets Chelon aurata and Chelon labrosus.[4]

The invasion of these parasites may have the effect of reducing the competitive advantages that the Red Sea invaders have in the Mediterranean. For example the Indo-Pacific swimming crab Charybdis longicollis was first recorded in the Mediterranean in the mid 1950s and became dominant in silt and sandy substrates off the coast of Israel, making up to 70% of the total biomass in these habitats. Up until 1992 none of the specimens collected were infected with the parasite Heterosaccus dollfusi but in that year a few infected crabs were collected. The parasite is a barnacle which de-sexes its host and within three years the parasite had spread to southern Turkey and 77% of the crabs collected in Haifa Bay were infected. This rapid increase and high infection rate is attributed to the extremely high population density of the host and the year round reproduction of the parasite. One effect of this was that the population of the Mediterranean native swimming crab Liocarcinus vernalis recovered somewhat.[5]

Anti-Lessepsian migration

Only a comparatively few species have colonised the Red Sea from the Mediterranean, and these are referred to as anti-Lessepsian migrants. As the predominant flow of the canal is from south to north, this acts against the southward movement of Mediterranean species, and, as stated above, the Red Sea has higher salinity, fewer nutrients and a much more diverse biota than the eastern Mediterranean. Some of the anti-Lessepsian migrants such as the sea star Sphaerodiscus placenta are found only in specialised habitats such as the lagoon of El Bilaiyim, which lies 180 kilometres (110 mi) south of the southern entrance to the Suez Canal but is much more saline than the surrounding waters of the Gulf of Suez.[2]

European seabass: one of the few anti-Lessepsian migrants
Chelidonura fulvipunctata

The sea slug Chelidonura fulvipunctata was originally described from waters around Japan and is widespread in the eastern Indian Ocean and western Pacific. It was first identified in the Mediterranean in 1961 and was seen in the Red Sea in 2005, most likely as a result of anti-Lessepsian migration.[6] In addition, a survey of polychaete worms in the southern Suez Canal found six species that were regarded as anti-Lessepsian migrants.[7] Among the fish species that have been confirmed as anti-Lessepsian migrants are Solea aegyptiaca, Mediterranean moray Murea helena, comber Serranus cabrilla, European seabass Dicentrarchus labrax, and spotted seabass Dicentrarchus punctatus.[8]

Other examples

Welland Canal and the Great Lakes

The sea lamprey reached Lake Ontario from the Atlantic Ocean through shipping canals and was recorded for the first time in Lake Ontario in the 1830s, but Niagara Falls was a barrier to their further spread. The deepening of the Welland Canal in 1919 allowed the sea lamprey to bypass the barrier created by the falls, and by 1938 sea lampreys had been recorded in all of the Great Lakes.[9]

The alewife (Alosa pseudoharengus), a species of shad from the western Atlantic also invaded the Great Lakes by using the Welland Canal to bypass Niagara Falls. They colonised the Great Lakes and became abundant mostly in Lake Huron and Lake Michigan, reaching their peak abundance by the 1950s and 1980s.[10]

See also

References

  1. Psomadakis, P.N.; Scacco, U.; Consalvo, I.; Bottaro, M.; Leone, F.; Vacchi, M. (2 February 2008). "New records of the lessepsian fish Fistularia commersonii (Osteichthyes: Fistulariidae) from the central Tyrrhenian Sea: signs of an incoming colonization?" (PDF). JMBA2 Biodiversity Records. Marine Biological Association of the United Kingdom. Archived from the original (PDF) on 2011-07-21.
  2. 1 2 3 "Essay about the phenomenon of Lessepsian Migration". Colloquial Meeting of Marine Biology I. Pierre Madl. Retrieved 29 December 2016.
  3. Galil, B. S. and Zenetos, A. (2002). A sea change: exotics in the eastern Mediterranean Sea, in: Leppäkoski, E. et al. (2002). Invasive aquatic species of Europe: distribution, impacts and management. pp. 325–36.
  4. C. Maillard; A. Raibaut (2012). "18. Human activities and modifications of ichtyofauna of the Mediterranean Sea: effects on parasitosis". In F. di Castri; A.J. Hansen; M Debussche. Biological Invasions in Europe and the Mediterranean Basin Volume 65 of Monographiae Biologicae. Springer Science & Business Media. p. 300. ISBN 9400918763.
  5. Bella S. Galil (2000). "Lessepsian immigration: Human impact on Leventine Biogeography". In J. Carel von Vaupel Klein. The Biodiversity Crisis and Crustacea - Proceedings of the Fourth International Crustacean Congress Crustacean Issues. CRC Press. pp. 50–51.
  6. Manuel António E. Malaquias; Andrea Zamora-Silva; Dyana Vitale; Andrea Spinelli; Sergio De Matteo; Salvatore Giacobbe; Deneb Ortigosa; Juan L. Cervera (2017). "The Suez Canal as a revolving door for marine species: a reply to Galil et al. (2016)(in press - Published online: 22 November 2016)" (PDF). Aquatic Invasions. 12.
  7. Faiza A. Abd-Elnaby (2009). "New Records of Polychaetes from the South Part of Suez Canal, Egypt" (PDF). World Journal of Fish and Marine Sciences. 1 (1): 7–19.
  8. Bruno Chanet; Martine Desoutter-Meniger; Sergey V. Bogorodsky (2012). "Range extension of Egyptian sole Solea aegyptiaca (Soleidae: Pleuronectiformes), in the Red Sea" (PDF). Cymbium. 36 (4): 581–584.
  9. "Sea Lamprey: The Battle Continues". Regents of the University of Minnesota. Retrieved 29 December 2016.
  10. Crispina B. Binohlan; Nicolas Baily (2016). R. Froese; D. Pauly, eds. "Alosa pseudoharengus (Wilson, 1811)". Fishbase. Retrieved 17 February 2017.
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