Overview
Distribution
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Bogutskaya, N.G. and A.M. Naseka 2004 Catalogue of agnathans and fishes of fresh and brackish waters of Russia with comments on nomenclature and taxonomy. KMK Scientific Press Ltd. Moscow. 389 p. (Ref. 53210)
http://www.fishbase.org/references/FBRefSummary.php?id=53210&speccode=62234
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Physical Description
Morphology
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Chyung, M.-K. 1977 The fishes of Korea. Il Ji Sa Publishing Co. Seoul, Korea. 727 p. (Ref. 12218)
http://www.fishbase.org/references/FBRefSummary.php?id=12218&speccode=8737
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Size
Max. size
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Chyung, M.-K. 1977 The fishes of Korea. Il Ji Sa Publishing Co. Seoul, Korea. 727 p. (Ref. 12218)
http://www.fishbase.org/references/FBRefSummary.php?id=12218&speccode=8737
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Ecology
Habitat
Amur River Benthopelagic Habitat
The persistence of mercury contamination in Amur River bottom sediments is a major issue, arising from historic cinnabar mining in the basin and poor waste management practises, especially in the communist Soviet era, where industrial development was placed ahead of sound conservation practises.
Other large benthopelagic river fish of the Amur Basin is the 200 cm yellowcheek (Elopichthys bambusa) and the 122 cm Mongolian redfin (Chanodichthys mongolicus)
- C.Michael Hogan. 2012. ''Amur River. Encyclopedia of Earth, National Council for Science and the Environment, Washington DC ed. Peter Saundry; ed.in-chief Cutler J.Cleveland
- Fishbase. 2010. Species in Amur
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Yangtze River Benthopelagic Habitat
The upper Yangtze basin consists chiefly of Paleozoic limestone and terrigenous sedimentary rock, with some granitic material. The most downstream element of the upper Yangtze basin is often termed the Sichuan Basin; here the Yangtze cuts through Triassic and Permian material before entering the Three Gorges. The Three Gorges area is a stretch of the Yangtze that runs approximately 660 kilometers, terminating at the site of the Three Gorges Dam. Prior to construction of the dam, the Three Gorges area was a site of exceptional natural beauty; after dam construction the gorge areas were filled with approximately 100 meters in depth of Yangtze water, and considerable amounts of the watershed were graded.
The lower Yangtze basin consists of anabranching river structures and Pleistocene coastal terraces. Prior to development of the Three Gorges Dam, the Yangtze Delta was replenished with a copious sediment load reaching the river mouth; however, the dam has now severely limited the natural flow and deposition of sediment to the delta region. Consequently, the integrity of the delta is been compromised, with scouring exceeding deposition, and the very stability of the delta is endangered.
Lower and middle basins of the Yangtze carry heavy pollutant loads. In the lower Yangtze basin nitrate levels are high, measuring at about 1000 tons per day at Datong; these levels accrue from high applications of chemical fertilizer applied and also considerable loadings of untreated sewage due to the large human population of the basin, with correspondingly little infrastructure for sewage treatment.
Heavy metal concentrations are also high in the lower Yangtze, with measurements of dissolved lead at 0.078 microgram/liter; cadmium (0.024 microgram/liter), chromium (0.57 microgram/liter), copper (1.9 microgram/liter), and nickel (0.50 microgram/liter). Levels of dissolved arsenic have been measured at 3.3 microgram/liter) and zinc at 1.5 microgram/liter), both notably higher by factors of 5.5 and 2.5 respectively than other typical large world rivers. In Yangtze River suspended sediment, arsenic comprises 31 microgram/gram, lead comprises 83 microgram/gram, and nickel comprises 52 micrograms/gram of sediment content
A number of other benthopelagic associates are found in the Yangtze, including: Anabarilius polylepis, Bangana rendahli, Pseudogyrinocheilus prochilus, Sinocyclocheilus grahami and Siniperca roulei. The demersal fish Silurus meridionalis also is found as a Yangtze River endemic species.
- C.Michael Hogan. 2012. ''Yangtze River. Encyclopedia of Earth, National Council for Science and the Environment, Washington DC ed. Mark McGinley; ed.in-chief Cutler J.Cleveland
- Fishbase. 2010. Species in Yangtze. http://www.fishbase.org/trophiceco/FishEcoList.php?ve_code=14
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Environment
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Life History and Behavior
Life Cycle
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Kottelat, M. 2001 Fishes of Laos. WHT Publications Ltd., Colombo 5, Sri Lanka. 198 p. (Ref. 43281)
http://www.fishbase.org/references/FBRefSummary.php?id=43281&speccode=6261
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Molecular Biology and Genetics
Molecular Biology
Statistics of barcoding coverage: Acheilognathus chankaensis
Public Records: 0
Species: 1
Species With Barcodes: 1
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Conservation
Threats
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IUCN 2006 2006 IUCN red list of threatened species. www.iucnredlist.org. Downloaded July 2006.
http://www.fishbase.org/references/FBRefSummary.php?id=57073
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Relevance to Humans and Ecosystems
Benefits
Importance
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Baensch, H.A. and R. Riehl 1985 Aquarien atlas. Band 2. Mergus, Verlag für Natur- und Heimtierkunde GmbH, Melle, Germany. 1216 p. (Ref. 2060)
http://www.fishbase.org/references/FBRefSummary.php?id=2060&speccode=13123
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Wikipedia
Khanka spiny bitterling
The Khanka spiny bitterling (Acanthorhodeus chankaensis) is a temperate freshwater fish belonging to the Acheilognathinae subfamily of the Cyprinidae family. It originates in the inland rivers in Asia, and is found in China, Korea, and Russia. It was originally described as Devario chankaensis by Benedykt Dybowski in 1872.
The fish will grow in length up to 12 centimetres (5 in). It lives in a temperate climate in water with a pH of 7.0, a hardness of 15 DH, and a temperature range of 18 to 22°C (64 to 72°F). It is of commercial importance for fisheries and public aquariums.
When spawning, the female deposits the eggs inside bivalves. The young hatch and remain within the bivalve until they can swim.
References
- Froese, Rainer, and Daniel Pauly, eds. (2011). "Acanthorhodeus chankaensis" in FishBase. August 2011 version.
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