- Nerita piscinalis O.F. Müller, 1774
- Cincinna piscinalis (Müller, 1774)
European Stream Valvata, European Valve Snail
No status defined
Value of species
The distribution of Valvata piscinalis is Palearctic.
Although this species is widely distributed in some areas in North America as an introduced species, Valvata piscinalis has declined in some parts of its native distribution, and in some areas it is endangered.
This species occurs in the British Isles and throughout Europe, to Asia Minor and all the way to Tibet.
The European valve snail is native to Europe, the Caucasus, western Siberia and Central Asia and is common in many freshwater environments therein. It is entirely absent from Iceland. Europe: Austria - endangered (3, gefährdet), Croatia, Czech Republic - near threatened (NT), in Bohemia and Moravia, Slovakia, Poland, Germany - (Arten der Vorwarnliste): critically endangered (2, stark gefährdet) in Saxony and in Thuringia, endangered (3, gefährdet) in Berlin, (4R, rückläufig) in Bavaria, species with limited distribution in Brandenburg, (Arten der Vorwarnliste) in Hesse and in North Rhine-Westphalia. In other federal states of Germany the species is common, the Netherlands, the British Isles: Great Britain and Ireland, Sweden - not in red list. Asia: India.
Valvata piscinalis is an introduced species in the United States. The European valve snail was originally introduced to Lake Ontario at the mouth of the Genesee River in 1897. In forty years it dispersed to Lake Erie and subsequently it expanded its range to the Saint Lawrence River, the Hudson River, Champlain Lake and Cayuga Lake. Valvata piscinalis was recorded in the 1990s and the first decade of the 21st century in Superior Bay in Lake Superior (Minnesota), Lake Michigan (Wisconsin) and Oneida Lake in the Lake Ontario watershed (New York State).
This small snail is found in freshwater streams, rivers, and lakes, preferring running water and tolerating water with low calcium levels.
In its native range, this species’ presence has been associated with oligotrophic nearshore zones, clear-water habitats more than turbid water, sparsely vegetated lakes or sites dominated by Chara spp. and Potamogeton spp., littoral habitats with high siltation rates, lentic and stagnant waters or slow streams, fine substrates (mud, silt and sand) – especially during hibernation, and aquatic macrophytes – for laying its egg masses.
The snail appears to be somewhat resistant to declines in macrophyte cover, because populations have been recorded to survive in ponds after vegetation cover almost completely disappeared. This species is found at depths anywhere from 0.5 m to 23 m in the Great Lakes. In Europe, it usually is found in depths of up to 10 m.
Valvata piscinalis tolerates varying calcium concentrations, and generally does not require very high temperatures to survive. Individuals can overwinter in mud, often experiencing growth during this cold period, although some populations may experience mortality in frozen littoral zones. This species can tolerate salinities up to 0.2% and is distributed in northern parts of the Curonian Lagoon, where it experiences periodic intrusions of saline water for a few hours or days at a time.
The species is an efficient feeder, grazing on epiphytic algae and detritus, and in more eutrophic environments is capable of filter feeding on suspended organic matter and algae. Valvata piscinalis can also rasp off pieces of aquatic vegetation.
Valvata piscinalis is known for its rapid growth and high fecundity. It reproduces as a hermaphrodite, one individual acting as the male and the other as the female, and has no free larval stage. It may spawn 2 or 3 times in a year, laying up to 150 eggs at a time which are deposited on vegetation. Hatching normally occurs in 15–30 days. Individuals breed around the age of 1 and usually die at 13–21 months. In Europe, breeding occurs from April to September, occurring later at more northerly latitudes. S. Myzyk (2007) described life cycle of Valvata piscinalis.
Valvata piscinalis is a common first intermediate host for the parasitic trematode Echinoparyphium recurvatum and has also been shown to act as the first and second intermediate hosts to Echinoparyphium mordwilokoi in native environments in Europe. As second intermediate host for Cyanthocotyle bushiensis. As intermediate host for Syngamus trachea.
- Гураль Р.І., Гураль-Сверлова Н.В. Каталог прісноводних молюсків України [Електронний ресурс]. – 2018. – 317с.
- Жирак Р.М. Видовий склад джмелів (Hymenoptera, Apidae, Bombus) в природних і антропогенних біотопах Рогатинського Опілля // Наукові записки Державного природознавчого музею. - Львів, 2004. - 19. - С.183-184.