Rainbow smelt

Rainbow smelt
Conservation status
Scientific classification
Kingdom: Animalia
Phylum: Chordata
Class: Actinopterygii
Order: Osmeriformes
Family: Osmeridae
Genus: Osmerus
Species: O. mordax
Binomial name
Osmerus mordax
(Mitchill, 1814)
Subspecies

Osmerus mordax mordax
Osmerus mordax dentex

The rainbow smelt, Osmerus mordax, is an anadromous species of fish of the family Osmeridae. The distribution of Osmerus mordax is circumpolar.[1] The rainbow smelt was introduced to the Great Lakes, and from there has made its way to various other places. Walleye, trout, and other larger fish prey on these smelt. The rainbow smelt prefer juvenile ciscoes and other small organisms such as zooplankton. They are spring spawners and prefer clean streams with light flow and light siltation. The rainbow smelt face several barriers. They are weak swimmers and cannot overcome most fish ladders. This prevents them from making it past the dams to the headwater streams where they need to spawn. The rise in erosion and dams help to decimate the smelt population in the 1980s. There are currently plans to try to reduce damming and to help control erosion. With current efforts to reduce the human impact on these and many other affected species the population is back on the rise.

Contents

Description

The body of the rainbow smelt is slender and cylindrical. It has a silvery, pale green back and is iridescent purple, blue, and pink on the sides, with a light underside. When full grown, the rainbow smelt is between 7 and 9 inches (18 and 23 cm) long and weighs about 3 ounces (85 g), and ones over 12 inches (30 cm) are known.[2]

Distribution and habitat

The rainbow smelt has been wide spread across North American watersheds.[3] The North American native range of the rainbow smelt extends through the Atlantic drainages between New Jersey and Labrador to Arctic and Pacific drainages of Vancouver Island. The rainbow smelt has been introduced into water bodies in the U.S. states of Colorado, Connecticut, Georgia, Idaho, Illinois, Indiana, Iowa, Kansas, Kentucky, Louisiana, Maine, Maryland, Massachusetts, Michigan, Minnesota, Missouri, Montana, Nebraska, New Hampshire, New York, North Carolina, North Dakota, Ohio, Pennsylvania, South Dakota, Tennessee, Vermont, Virginia, Wisconsin.[4] Landlocked populations were historically known in Maine, and fish from one of these populations were introduced to Crystal Lake, Michigan and then spread to the Great Lakes.

Rainbow smelt invaded the Great Lakes watershed through an intentional introduction of eggs to Crystal Lake in 1912.[5] This lake drains into Lake Michigan, from which fish escaped into Lake Michigan and spread quickly throughout the Great Lakes and their tributaries. Early records documenting the smelt's range expansion in the Great Lakes include Lake Michigan, Lake Erie, Lake Huron, Lake Ontario, and Lake Superior. [5] Rainbow smelt were first reported from Lake Ontario in 1929, and probably reached it by dispersal along natural waterways from the Finger Lakes, New York, where they were intentionally introduced in 1917. The ability of rainbow smelt to disperse is determined by the connectivity of lakes, the ability of smelt to move through connecting streams, and the suitability of connected lakes as habitat.[6] Rainbow smelt are weak swimmers so they cannot make it over fish ladders.[7] This has helped to prevent an even wider spread of their range.

Rainbow smelt occur in rivers, coastal areas and ponds. In their anadromous territories, they spend the summers along the coast, normally in waters no more than 20 feet (6.1 m) deep and no more than 1 mile (1.6 km) from shore. They overwinter under the ice in estuaries, producing an antifreeze protein and glycerol.[8] In the spring, they spawn at night in small streams, often ones that go dry in the summer.

Ecology

In 1885 Stedman and Argyle found that Osmerus mordax consumed bloaters (Coregonus hoyi) and alewives (Alosa pseudoharengus) however they also stated that this predator had not impacted the population of bloaters but that impact could be a possibility.[5] A 2003 study by Horppila et al. shows that smelt densities can exceed 40,000 individuals per hectare and may create a large predation pressure on the lake.[6] Horppila et al. also states that a single smelt can consume between .12 grams and .14 grams.[6] Another study showed that in Lake Ontario the primary food sources for rainbow smelt were slimy sculpins (Cottus cognatus) and opossum shrimp (Mysis relicta), but nothing was said on whether this predation had significant impact on the populations.[5] In 1973 Havey reported that there was increased growth in landlocked Atlantic salmon populations after the introduction of the smelt. It was also shown by Brandt and Madon in 1986 that adult lake trout (Salvalinus namaycush) could be a keystone predator species for the smelt.[5] Hrabik et al. (1998) found evidence of competition for food between introduced rainbow smelt and native yellow perch (Perca flavescens) in Wisconsin lake habitats, and smelt may be partially responsible for the decline of Great Lakes whitefish (Coregonus spp.).[5] The U.S. EPA stated in 2008 that they believe the smelt contributed to the extinction of the blue pike (Stizostedion vitreum glaucum) by outcompeting for food.[5] Acidity may alter smelt distributions because they were not found in small lakes with pH less than 6.0 in several surveys. Because of snowmelt, rainbow smelt eggs might be exposed to lethal pH decreases in poorly buffered lakes.[6]

Life history

Rainbow smelt are anadromous, ascending from saltwater to freshwater to spawn. Smelt are also capable of completing their life history exclusively in freshwater. Landlocked adult rainbow smelt spawn shortly after ice-off at night in the lower reaches of streams.[6] Shaw found in his research that no shoreline spawning had ever occurred.[9] McKenzie states that the number of eggs extruded by a female is positively related to its size and Nellbring stated in his 1989 research that the eggs are adhesive and attach to substrates such as gravel, sand, mud, or submerged vegetation.[6] Eggs are left unattended and hatch in 1–4 weeks, depending on water temperature. The time to sexual maturity is dependent on food supply and water temperature and abundant food and warmer temperatures encourage faster growth.[6] Crossman and Scott state that in optimal conditions and large lakes, rainbow smelt may reach 35.6 centimetres (14.0 in) and can live for over seven years.[6]

Fishing

Rainbow smelt are fished both commercially and for sport. Commercial harvests are down from historic levels; for example around 1850 an annual harvest from the Charles River alone was around 9 million fish. They are commonly processed into animal feed, but are also eaten by humans. They are a popular winter game fish and the spring smelt run is a tradition in many parts of their distribution. Fishing for rainbow smelt using a gill net is a popular activity along the city of Chicago's lakefront.

Management

The populations of the rainbow smelt in areas where it has been introduced, such as the Great Lakes, have been increasing in many regions, even with efforts to control its spread.[10] Several things are being done to manage this species. Massive fish removal by over-fishing reduced the rainbow smelt populations in some lakes by the 1980s.[6] Some people are taking a chemical approach to this growing problem, using Rotenone. Extoxnet describes Rotenone as "a slow-acting poison which interferes with the electron-transport system in the mitochondria. It acts as both a contact and stomach poison".[11] While this is effective, it also harms other organisms and is unpopular with the public. Cox and Kitchell state that declines in smelt numbers following natural recovery or stocking of grown predator fish have been reported from lakes ranging in size from Lake Superior and Hessen found similar results in a small pond near Lillehammer, Norway in 1983. This research shows that the reintroduction of large piscivores such as walleye can help lead to the reduction of chemicals and poison needing to be used.

This species should continue to be heavily monitored and managed. Random samples as well as plotted samples should be preformed to help gather a good estimation of population size and density, and should be done very widely. Boat shocking and gill netting would be two good ways to perform the sampling. In smaller areas backpack shockers and seines may be used. In Robinson's research seines were used successfully in collecting samples for research.[12] Since these fish tend to heavily populate the Great Lakes boat shocking/gill netting would be the most productive way to gather information in a timely fashion. These fish have proven that given the right vector, whether human introductions or overflow into non-native streams, they can go almost anywhere. The heaviest amount of sampling should most likely occur in the Great Lakes and other northern reservoirs because this is where the largest populations tend to occur. This species should not be completely removed but it should be heavily managed. This is a good prey species for prized game fish but once the population gets out of control they can have a large impact on other important organisms. Introduction of large piscivores, such as walleye, seems to be working, and this method allows the reduction of poison and toxin use in the water.

References

  1. ^ Kovpak, N. E.; Skurikhina, L. A.; Kukhlevsky, A. D.; Oleinik, A. G.; Sendek, D. S. (2011). "Genetic divergence and relationships among smelts of the genus Osmerus from the Russian water". Russian journal of Genetics 47 (8): 958–972. doi:10.1134/S1022795411080102. 
  2. ^ Froese, Rainer, and Daniel Pauly, eds. (2006). "Osmerus mordax" in FishBase. June 2006 version.
  3. ^ Bentzen, P.; Taylor, E. B. (1993). "Evidence for multiple origins and sympatric divergence of trophic ecotypes of smelt (Osmerus) in Northeastern North America". Evolution 47 (3): 813–832. JSTOR 2410186. 
  4. ^ [Fuller P., E. Maynard. 2011. Osmerus mordax. USGS Nonindiginous Aquatic Species Database. nas.er.usgs.gov.]
  5. ^ a b c d e f g [Fuller P., E. Maynard. 2011. Osmerus Mordax. USGS Nonindiginous Aquatic Species Database. nas.er.usgs.gov.]
  6. ^ a b c d e f g h i Rooney, R. C.; Paterson, M. J. (2009). "Ecosystem effects of rainbow smelt (Osmerus mordax) invasions in inland lakes". Can. Tech. Rep. Fish. Aquat. Sci. 4: 1–20. 
  7. ^ Wyatt, L. H.; Baker, A. L.; Berlinsky, D. L. (2010). "Effects of sedimentation and periphyton communities on embryonic rainbow smelt, Osmerus mordax". Aquatic Sciences 72 (3): 361–369. doi:10.1007/s00027-010-0129-8. 
  8. ^ Treberg, J. R.; Wilson, C. E.; Richards, R. C.; Ewart, K. V.; Driedzic, W. R. (2002). "The freeze-avoidance response of smelt Osmerus mordax: initiation and subsequent suppression of glycerol, trimethylamine oxide and urea accumulation". The Journal of Experimental Biology 205 (Pt 10): 1419–1427. PMID 11976353. 
  9. ^ Shaw, J. L.; Curry, R. A. (2011). "Ontogenetic divergence of growth among rainbow smelt morphotypes". Environmental Biology of Fishes 92 (2): 217–227. doi:10.1007/s10641-011-9835-x. 
  10. ^ Roth, B.M.; T. R. Hrabik, C. T. Solomon, N. Mercado-Silva, T. F. Kitchell (2010). "A simulation of food-web interactions leading to rainbow smelt Osmerus mordax domance in Sparkling Lake, Wisconsin". Journal of Fish Biology 77 (6): 1379–1405. doi:10.1111/j.1095-8649.2010.02764.x. PMID 21039511. 
  11. ^ [Extoxnet. 1996. Rotenone. Extoxnet. extoxnet.orst.edu]
  12. ^ Robinson, J. L.; J. R. Hall, M. Charman, K.V. Ewart, W.R. Driedzic (2011). "Molecular Analysis, Tissue Profiles, and Seasonal Patterns of Cystolic and Mitochondrial GPDH in Freeze-Resistant Rainbow Smelt (Osmerus mordax)". Physiological and Biochemical Zoology 84 (4): 363–376. doi:10.1086/660162. PMID 21743250. 

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