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New Zealand Mudsnail

Potamopyrgus antipodarum (Gray 1843)

Behavior

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Perception in New Zealand mudsnails is mainly via chemical cues. In their native range, the chemical odor of predatory fish causes the snails to hide under rocks in an attempt to evade predation. They are also able to sense light.

Perception Channels: visual ; chemical

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Associations

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Predation on New Zealand mudsnails in North America is unknown. They are known to survive passage through the digestive tracts of some birds and fish, including mountain whitefish and rainbow trout.

However, in their native range, the snails are consumed by several species of fish and waterfowl and are infected by as many as 14 parasitic trematodes of the genus Microphallus. Levri and Lively (1996) observed the foraging behaviors of grey ducks (Anas superciliosa), mallard ducks (Anas platyrhynchos), black swans (Cygnus atratus), Canada geese (Branta canadensis), and scaups (Aythya novaeseelandiae), and they reported that grey ducks and mallard ducks are the most likely predators of NZMS.

New Zealand mudsnails that experience predation may have spines on their shells for defense against predators and may forage less frequently in the presence of predators, especially during the morning when waterfowl predators are most active.

Known Predators:

  • grey ducks (Anas superciliosa)
  • mallard ducks (Anas platyrhynchos)
  • black swans (Cygnus atratus)
  • Canada geese (Branta canadensis)
  • New Zealand scaup, aka black teal (Aythya novaeseelandiae)
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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Morphology

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New Zealand mudsnails are shelled organisms that are either gray in color or some shade of light to dark brown. Male and female New Zealand mudsnails are very similar in physical appearance, but females are distinguished from males by the presence of developing embryos in their reproductive systems. In the western United States, the average length of the shell of the New Zealand mudsnail is 4 to 5 mm, with a maximum length of 6 to 7 mm. In their native range, the maximum length of the shell is 12 mm. The surface of the shell is characterized by right-handed coiling of 5 to 6 whorls demarcated by sulci. The shells of some individuals have a keel in the middle of each whorl and/or spines for defense against predators. A terminal oval aperture covered by a thin operculum is also present. New Zealand mudsnails may resemble snails native to the United States, but they are distinguished by their longer, narrower shells that have a greater number of whorls.

Range length: 4 to 12 mm.

Sexual Dimorphism: sexes alike

Other Physical Features: ectothermic ; bilateral symmetry

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Life Expectancy

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Under laboratory conditions, marked individuals were observed to survive over one year. The lifespan of New Zealand mudsnails in natural conditions is unknown.

Range lifespan
Status: captivity:
1 (high) years.

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Habitat

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New Zealand mudsnails prefer to live in streams and the littoral zones of lakes. They prefer shallow areas but can be found up to 60 m deep. They can be found in aquatic habitats of varying substrate types, including silt, sand, gravel, cobble, and macrophyte/vegetation. Densities are highest in macrophyte habitats and lowest in silt/sand habitats. Individuals of this species live in both eutrophic and clear waters, but they thrive in disturbed or degraded waters. New Zealand mudsnails can tolerate a wide range of temperatures, from near freezing to 34ºC. The optimal salinity of the water for the snails is near 5%, but they can tolerate brackish waters and even survive salinities as high as 30 to 35% for short periods of time. New Zealand mudsnails prefer low water velocities but can be found in high velocity areas buried in the sediment or underneath cobbles and boulders.

Range depth: 60 (high) m.

Habitat Regions: temperate ; freshwater

Aquatic Biomes: lakes and ponds; rivers and streams; brackish water

Other Habitat Features: intertidal or littoral

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Distribution

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New Zealand mudsnails (Potamopyrgus antipodarum) are native to freshwater streams and lakes of New Zealand and small, neighboring islands. However, by several speculated means of human introduction, they have become an invasive species in Australia, Europe, and North America. Occurrences of the species in North America, most of which are in the western United States, have been carefully documented since it was first discovered in Idaho. The snails are known to be established in Oregon, California, northern Arizona, New York, and Canada, affecting major freshwater systems such as Lake Ontario, Lake Erie, and Lake Superior. They also have been recently introduced in Japan.

Biogeographic Regions: nearctic (Introduced ); palearctic (Introduced ); australian (Introduced ); oceanic islands (Native )

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Trophic Strategy

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New Zealand mudsnails are considered scrapers/grazers. Their diet consists of diatoms, epiphytic and periphytic algae, and animal and plant detritus. Therefore, they can be considered planktivores, algivores, and detrivores.

Plant Foods: algae; phytoplankton

Other Foods: detritus

Primary Diet: herbivore (Algivore); planktivore ; detritivore

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Associations

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In their freshwater ecosystems, New Zealand mudsnails occupy the role of scrapers/grazers and are considered to be a link between primary producers and fish. They also play a vital role in the transmission of Microphallus to ducks by serving as intermediate hosts.

New Zealand mudsnails are known to exist in extremely high densities and may comprise more than 90% of the macroinvertebrate biomass in introduced habitats. Due to their abundance, they may out-compete native mollusks and grazers for resources such as food. The decrease in the availability of resources is a likely explanation for the decline in species diversity in the presence of NZMS, the negative correlation between the NZMS population and that of mayflies, caddisflies, stoneflies, and chironomids, and the listing of five species of mollusks as endangered species. New Zealand mudsnails may also alter nutrient (carbon and nitrogen) cycling, interrupting energy flow and potentially threatening many other members of their ecosystems.

Commensal/Parasitic Species:

  • parasitic flatworms in the genus Microphallus
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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Benefits

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Because New Zealand mudsnails thrive in disturbed and degraded waters, this species can be used as an indicator of ecosystem status.

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Benefits

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There are no direct, adverse effects of New Zealand mudsnails on humans, but control of the species is difficult and may be expensive in regions where it is not native.

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Life Cycle

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New Zealand mudsnails are ovoviviparous, meaning that the development of embryos in their eggs actually occurs within the female. After completing development, the eggs hatch within the female, and the female then gives birth to the young snails. New Zealand mudsnails have been observed to grow 0.1 mm/day at 21ºC under laboratory conditions, with growth rates depending on the size of the individual. Females reach maturity at 3 to 6 months of age.

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Conservation Status

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New Zealand mudsnails are not a protected species in their native range. Outside the native range, actions are being taken against the species to limit its spread as a pest.

US Federal List: no special status

CITES: no special status

State of Michigan List: no special status

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Untitled

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Several aspects of the ecology of New Zealand mudsnails have contributed to their success as an invasive species. First, their tolerance of a wide range of abiotic conditions, such as temperature and salinity, aids them in transport from their native range via the ballast water of ships. Second, their escape from natural predators and parasites and their high competitive ability at the early stages of succession contribute to their establishment in introduced habitats. Third, their high fecundity, fast reproductive rate, and active and passive means of dispersal aid in their spread. Finally, their great abundance allows them to impact the ecosystem by consuming most of the primary production, dominating nutrient cycles and secondary production and decreasing populations of other mollusks and grazers.

The potential and realized negative impacts of New Zealand mudsnails have been recognized, and measures are being taken to control their spread based on what is known about their ecology. New Zealand mudsnails experience mortality when exposed to freezing or high temperatures with low humidity. It is recommended that all equipment that could be harboring the snails be frozen for several hours or be exposed to temperatures of 29 to 30ºC and low humidity for a minimum of 24 hours or temperatures greater than 40ºC and low humidity for a minimum of two hours.

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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Keith Pecor, The College of New Jersey
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George Hammond, University of Michigan-Ann Arbor
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Reproduction

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New Zealand mudsnails are dioecious. Populations in New Zealand consist of sexual males and both sexual and asexual females, whereas introduced populations are comprised entirely of asexual females.

In their native range, individuals that reproduce sexually are promiscuous. During copulation, the male is found on top of the shell of a female, and the apertures of the two snails are in contact. Females can either maintain their position and proceed with mating or move in a manner that displaces the males. The duration of copulation is typically between 20 minutes and 1.5 hours. Males do not discriminate between sexual females and asexual or parasitically-castrated females, although their genes will not be passed to the offspring of the latter two types of females.

Populations found in the United States consist of triploid females that reproduce asexually by way of parthenogenesis. This type of asexual reproduction is also observed in their native range and leads to populations of genetically identical females or clones in both their native and introduced habitats.

Mating System: polygynandrous (promiscuous)

In New Zealand, reproduction typically occurs every three months. In the western United Staes, reproduction occurs throughout the year, with seasonal peaks during the months of March and October. Females reach sexual maturity at a shell length of 3 mm and produce approximately 230 young per year. Larger females produce more offspring than smaller females, and asexual females produce double the number of female offspring produced by sexual females. This species is ovoviviparous, carrying as many as 10 to 120 eggs at a time for development and giving birth to live snails. Developing embryos are sometimes present within the reproductive system of asexual females at the time of birth.

Breeding interval: In New Zealand, every 3 months.

Breeding season: Year-round

Range number of offspring: 10 to 120.

Average number of offspring: 21.6.

Range age at sexual or reproductive maturity (female): 3 to 6 months.

Key Reproductive Features: seasonal breeding ; year-round breeding ; gonochoric/gonochoristic/dioecious (sexes separate); parthenogenic ; sexual ; asexual ; fertilization (Internal ); ovoviviparous

This author found no published information on parental investment by New Zealand mudsnails.

Although females retain their eggs until they hatch, it's not known whether the embryos are nourished in anyway other than via the yolk created when each egg is produced.

Parental Investment: female parental care ; pre-fertilization (Provisioning); pre-hatching/birth (Protecting: Female)

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Simeron, A. 2011. "Potamopyrgus antipodarum" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potamopyrgus_antipodarum.html
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Alexa-Jade Simeron, The College of New Jersey
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New Zealand mud snail

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The New Zealand mud snail (Potamopyrgus antipodarum) is a species of very small freshwater snail with a gill and an operculum. This aquatic gastropod mollusk is in the family Tateidae.

It is native to New Zealand, where it is found throughout the country,[3] but it has been introduced to many other countries, where it is often considered an invasive species because populations of the snail can reach very high densities.

Shell description

Shells of Potamopyrgus antipodarum f. carinata (left)
and Potamopyrgus antipodarum (right).
Scale bar is 0.5 cm.
Shell with the typical black earthy coat
A group of mudsnails of all growth sizes from juvenile to adults, compared to an American 10 cent coin, which is 18 mm in diameter.

The shell of Potamopyrgus antipodarum is elongated and has dextral coiling, with 7 to 8 whorls. Between whorls are deep grooves. Shell colors vary from gray and dark brown to light brown. The average height of the shell is approximately 5 mm ( 1 5 {displaystyle {egin{matrix}{frac {1}{5}}end{matrix}}} {egin{matrix}{frac {1}{5}}end{matrix}} in); maximum size is approximately 12 mm ( 1 2 {displaystyle {egin{matrix}{frac {1}{2}}end{matrix}}} {egin{matrix}{frac {1}{2}}end{matrix}} in). The snail is usually 4–6 mm in length in the Great Lakes, but grows to 12 mm in its native range.[4][5][6] It is an operculate snail, with a 'lid' that can seal the opening of its shell. The operculum is thin and corneus with an off-centre nucleus from which paucispiral markings (with few coils) radiate. The aperture is oval and its height is less than the height of the spire. Some morphs, including many from the Great Lakes, exhibit a keel in the middle of each whorl; others, excluding those from the Great Lakes, exhibit periostracal ornamentation such as spines for anti–predator defense.[4][7][5][6]

Taxonomy

This species was originally described as Amnicola antipodarum in 1843 by John Edward Gray:

Inhabits New Zealand, in fresh water. Shell ovate, acute, subperforated (generally covered with a black earthy coat); whorls rather rounded, mouth ovate, axis 3 lines; operculum horny and subspiral: variety, spire rather longer, whorls more rounded. This species is like Paludina nigra of Quoy and Gaimard, but the operculum is more spiral. Quoy described the operculum as concentric, but figured it subspiral. Paludina ventricosa of Quoy is evidently a Nematura.[2]

Forms

  • Potamopyrgus antipodarum f. carinata (J. T. Marshall, 1889)

Distribution

This species was originally endemic to New Zealand where it lives in freshwater streams and lakes in New Zealand and adjacent small islands.[8]

It has now spread widely and has become naturalised, and an invasive species in many areas including: Europe (since 1859 in England), Australia, Tasmania, Asia (Japan,[9] in Garmat Ali River in Iraq since 2008[10]), and North America (USA and Canada: Thunder Bay in Ontario since 2001, Washington State since 2002,[11] British Columbia since July 2007[9]), most likely due to inadvertent human intervention.

Invasion in Europe

Since being found in Ireland as early as 1837, Potamopyrgus antipodarum has now spread to nearly the whole of Europe. It is considered as about the 42nd worst alien species in Europe and the second worst alien gastropod in Europe.[12]

It does not occur in Iceland, Albania, Bulgaria or the former Yugoslavia.[13]

Countries where it is found include:

Distribution within the United States

Distribution of Potamopyrgus antipodarum within the USA in 2009.

First detected in the United States in Idaho's Snake River in 1987, the mudsnail has since spread to the Madison River, Firehole River, and other watercourses around Yellowstone National Park; samples have been discovered throughout the western United States.[6] Although the exact means of transmission is unknown, it is likely that it was introduced in water transferred with live game fish and has been spread by ship ballast or contaminated recreational equipment such as wading gear.[20]

The New Zealand mudsnail has no natural predators or parasites in the United States, and consequently has become an invasive species. Densities have reached greater than 300,000 individuals per m² in the Madison River. It can reach concentrations greater than 500,000 per m², endangering the food chain by outcompeting native snails and water insects for food, leading to sharp declines in native populations.[21] Fish populations then suffer because the native snails and insects are their main food source.

Mudsnails are impressively resilient. A snail can live for 24 hours without water. They can however survive for up to 50 days on a damp surface,[22] giving them ample time to be transferred from one body of water to another on fishing gear. The snails may even survive passing through the digestive systems of fish and birds.[23]

Mudsnails have now spread from Idaho to most western states of the U.S., including Wyoming, California, Nevada, Oregon, Montana, and Colorado. Environmental officials for these states have attempted to slow the spread of the snail by advising the public to keep an eye out for the snails, and bleach or heat any gear which may contain mudsnails. Rivers have also been temporarily closed to fishing to avoid anglers spreading the snails.[24][25]

The snails grow to a smaller size in the U.S. than in their native habitat, reaching 6 mm (¼ in) at most in parts of Idaho, but can be much smaller making them easy to overlook when cleaning fishing gear.

Clonal species like the New Zealand mudsnail can often develop clonal lines with quite diverse appearances, called morphs. Until 2005, all the snails found in the western states of the U.S. were believed to be from a single line. However a second morph has been identified in Idaho's Snake River. It grows to a similar size but has a distinctive appearance. (It has been nicknamed the salt-and-pepper mudsnail due to the final whorl being lighter than the rest of the shell.) This morph has apparently been present in the area for several years before being identified correctly as a distinct morph of Potamopyrgus antipodarum. It dominates the typical morph where they overlap, and has a much higher prevalence of males.[26]

In 1991, the New Zealand mudsnail was discovered in Lake Ontario,[27] and has now been found in four of the five Great Lakes. In 2005 and 2006, it was found to be widespread in Lake Erie.[28] By 2006 it had spread to Duluth-Superior Harbour and the freshwater estuary of the Saint Louis River.[29] It was found to be inhabiting Lake Michigan, after scientists took water samples in early summer of 2008.[30] The snails in the Great Lakes represent a different line from those found in western states, and were probably introduced indirectly through Europe.[26]

In 2002, the New Zealand mudsnail was discovered in the Columbia River Estuary. In 2009, the species was discovered in Capitol Lake in Olympia, Washington. The lake has been closed to all public use, including boating and other recreation, since 2009.[31] A heavy cold snap in 2013, combined with a drawdown in water level in preparation, was roughly estimated to have killed 40–60% of the mudsnail population.[32][33] Other known locations include the Long Beach peninsula, Kelsey Creek (King County), Thornton Creek (King County), and Lake Washington.

In 2010, the Los Angeles Times reported that the New Zealand mudsnail had infested watersheds in the Santa Monica Mountains, posing serious threats to native species and complicating efforts to improve stream-water quality for the endangered Southern California Distinct Population Segment of steelhead.[34] According to the article, the snails have expanded "from the first confirmed sample in Medea Creek in Agoura Hills to nearly 30 other stream sites in four years." Researchers at the Santa Monica Bay Restoration Commission believe that the snails' expansion may have been expedited after the mollusks traveled from stream to stream on the gear of contractors and volunteers.[35]

As of 21 September 2010 In Colorado, Boulder Creek and Dry Creek have infestations of New Zealand mudsnails. The snails have been present in Boulder Creek since 2004 and were discovered in Dry Creek in September 2010. Access to both creeks has been closed to help avoid spread of the snails. In the summer of 2015 an industrial-scale wetland rehabilitation project was undertaken in northeast Boulder to rid the area of a mud snail infestation.

Ecology

Habitat

The snail tolerates siltation, thrives in disturbed watersheds, and benefits from high nutrient flows allowing for filamentous green algae growth. It occurs amongst macrophytes and prefers littoral zones in lakes or slow streams with silt and organic matter substrates, but tolerates high flow environments where it can burrow into the sediment.[4][6][36][37][38][39][40][41][42][43][44]

In the Great Lakes, the snail reaches densities as high as 5,600 per m² and is found at depths of 4–45 m on a silt and sand substrate.[4][5][6]

This species is euryhaline, establishing populations in fresh and brackish water. The optimal salinity is probably near or below 5 ppt, but Potamopyrgus antipodarum is capable of feeding, growing, and reproducing at salinities of 0–15 ppt and can tolerate 30–35 ppt for short periods of time.[4][6][45][46][47][48]

It tolerates temperatures of 0–34 °C.[4][6][49]

Feeding habits

Potamopyrgus antipodarum is a nocturnal grazer-scraper, feeding on plant and animal detritus, epiphytic and periphytic algae, sediments and diatoms.[4][6][50][51][52][53]

Life cycle

Potamopyrgus antipodarum is ovoviviparous and parthenogenic. This means that they can reproduce asexually; females "are born with developing embryos in their reproductive system." Native populations in New Zealand consist of diploid sexual and triploid parthenogenically cloned females, as well as sexually functional males (less than 5% of the total population). All introduced populations in North America are clonal, consisting of genetically identical females.[6]

As the snails can reproduce both sexually and asexually, the snail has been used as a model organism for studying the costs and benefits of sexual reproduction. Asexual reproduction allows all members of a population to produce offspring and avoids the costs involved in finding mates. However, asexual offspring are clonal, so lack variation. This makes them susceptible to parasites, as the entire clonal population has the same resistance mechanisms. Once a strain of parasite has overcome these mechanisms, it is able to infect any member of the population. Sexual reproduction mixes up resistance genes through crossing over and the random assortment of gametes in meiosis, meaning the members of a sexual population will all have subtly different combinations of resistance genes. This variation in resistance genes means no one parasite strain is able to sweep through the whole population. New Zealand mudsnails are commonly infected with trematode parasites, which are particularly abundant in shallow water, but scarce in deeper water. As predicted, sexual reproduction dominates in shallow water, due to its advantages in parasite resistance. Asexual reproduction is dominant in the deeper water of lakes, as the scarcity of parasites means that the advantages of resistance are outweighed by the costs of sexual reproduction.[54]

Each female can produce between 20 and 120 embryos.[20] The snail produces approximately 230 young per year. Reproduction occurs in spring and summer, and the life cycle is annual.[4][6][8][48][55][56] The rapid reproduction rate of the snail has caused the numbers of individuals to increase rapidly in new environments. The highest concentration of New Zealand mudsnails ever reported was in Lake Zurich, Switzerland, where the species colonized the entire lake within seven years to a density of 800,000 per m².[6][57]

Parasites

The parasites of this species include at least 11 species of Trematoda.[6][58] Common parasites of this snail include trematodes of the genus Microphallus.[6][59][60]

In their native habitat, these parasites sterilize many snails, keeping the populations to a manageable size. However, elsewhere in the world in the absence of these parasites, they have become an invasive pest species.[6]

Other interspecific relationship

Potamopyrgus antipodarum can survive passage through the guts of fish and birds and may be transported by these animals.[23]

It can also float by itself or on mats of Cladophora spp., and move 60 m upstream in 3 months through positive rheotactic behavior.[4] It can respond to chemical stimuli in the water, including the odor of predatory fish, which causes it to migrate to the undersides of rocks to avoid predation.[6][61]

See also

References

  1. ^ Van Damme, D. (2013). "Potamopyrgus antipodarum". IUCN Red List of Threatened Species. 2013: e.T155980A738398. doi:10.2305/IUCN.UK.2013-2.RLTS.T155980A738398.en. Retrieved 19 November 2021.
  2. ^ a b Dieffenbach, E. 1843. Travels in New Zealand; with contributions to the geography, geology, botany, and natural history of that country. In two volumes - Vol. II. - pp. i-iv [= 1-4], 1-396, pl. [1]. London. (Murray), page 241.
  3. ^ "Potamopyrgus antipodarum (Gray in Dieffenbach, 1843)". Retrieved 14 July 2019.
  4. ^ a b c d e f g h i Zaranko, D. T., D. G. Farara and F. G. Thompson. 1997. Another exotic mollusk in the Laurentian Great Lakes: the New Zealand native Potamopyrgus antipodarum (Gray 1843) (Gastropoda, Hydrobiidae).
  5. ^ a b c Levri, E.P., A.A. Kelly and E. Love. 2007. The invasive New Zealand mud snail (Potamopyrgus antipodarum) in Lake Erie. Journal of Great Lakes Research 33: 1–6.
  6. ^ a b c d e f g h i j k l m n o Benson, A.J.; Kipp, R.M.; Larson, J. & Fusaro, A. (2013). "Potamopyrgus antipodarum". USGS Nonindigenous Aquatic Species Database. U.S. Geological Survey. Retrieved 25 May 2013.
  7. ^ Holomuzki, J. R. and B. J. F. Biggs. 2006. Habitat–specific variation and performance trade–offs in shell armature of New Zealand mudsnails. Ecology 87(4):1038–1047.
  8. ^ a b Hall, R. O. Jr., J. L. Tank and M. F. Dybdahl. 2003. Exotic snails dominate nitrogen and carbon cycling in a highly productive stream. Frontiers in Ecology and the Environment 1(8):407–411.
  9. ^ a b Timothy M. Davidson, Valance E. F. Brenneis, Catherine de Rivera, Robyn Draheim & Graham E. Gillespie. Northern range expansion and coastal occurrences of the New Zealand mud snail Potamopyrgus antipodarum (Gray, 1843) in the northeast Pacific Archived 2011-07-21 at the Wayback Machine Aquatic Invasions (2008) Volume 3, Issue 3: 349-353.
  10. ^ Murtada D. Naser & Mikhail O. Son. 2009. First record of the New Zealand mud snail Potamopyrgus antipodarum (Gray 1843) from Iraq: the start of expansion to Western Asia? Archived 2011-07-21 at the Wayback Machine. Aquatic Invasions, Volume 4, Issue 2: 369-372, DOI 10.3391/ai.2009.4.2.11.
  11. ^ "Knapweeds, Invasive Species Council Priority Species". invasivespecies.wa.gov. Retrieved 2019-06-30.
  12. ^ Nentwig, Wolfgang; Bacher, Sven; Kumschick, Sabrina; Pyšek, Petr; Vilà, Montserrat (2017-12-18). "More than "100 worst" alien species in Europe". Biological Invasions. 20 (6): 1611–1621. doi:10.1007/s10530-017-1651-6. ISSN 1387-3547.
  13. ^ a b Mikhail O. Son. Rapid expansion of the New Zealand mud snail Potamopyrgus antipodarum (Gray, 1843) in the Azov-Black Sea Region Archived 2011-07-21 at the Wayback Machine. Aquatic Invasions (2008) Volume 3, Issue 3: 335-340.
  14. ^ Paludestrina jenkinsi in Lough Neagh and elsewhere. Irish Naturalists’ Journal 1: 174-175.
  15. ^ a b Čejka T., Dvořák L. & Košel V. 2008: Present distribution of Potamopyrgus antipodarum (Gray, 1843) (Mollusca: Gastropoda) in the Slovak Republic. - Malacologica Bohemoslovaca, 7: 21-25. Online serial at <http://mollusca.sav.sk&gt Archived 2018-12-25 at the Wayback Machine; 25-February-2008.
  16. ^ Dmitry P. Filippenko & Mikhail O. Son. The New Zealand mud snail Potamopyrgus antipodarum (Gray, 1843) is colonising the artificial lakes of Kaliningrad City, Russia (Baltic Sea Coast) Archived 2011-07-21 at the Wayback Machine. Aquatic Invasions (2008) Volume 3, Issue 3: 345-347.
  17. ^ Boris Alexandrov, Alexandr Boltachev, Taras Kharchenko, Artiom Lyashenko, Mikhail Son, Piotr Tsarenko & Valeriy Zhukinsky. Trends of aquatic alien species invasions in Ukraine Archived 2011-07-21 at the Wayback Machine. Aquatic Invasions (2007) Volume 2, Issue 3: 215-242.
  18. ^ a b c d e Canella Radea, Ioanna Louvrou and Athena Economou-Amilli First record of the New Zealand mud snail Potamopyrgus antipodarum J.E. Gray 1843 (Mollusca: Hydrobiidae) in Greece – Notes on its population structure and associated microalgae Archived 2011-07-21 at the Wayback Machine. Aquatic Invasions (2008) Volume 3, Issue 3: 341-344
  19. ^ Kuchař P. Potamopyrgus jenkinsi poprvé v Československu. Źiva, Prague, 31(1): page 23. (in Czech).
  20. ^ a b "Biology". New Zealand mudsnails in the Western USA. Montana State University. Archived from the original on 2006-05-04. Retrieved 2006-05-04.
  21. ^ Benson, Amy (2006). "New Zealand Mudsnail: Potamopyrgus antipodarum". Florida Integrated Science Center. Archived from the original on 2006-02-19. Retrieved 2006-05-04.
  22. ^ Davis, Ken W. (2004-02-24). "Select Research Findings on the New Zealand Mudsnail (Potamopyrgus antipodarum)" (PDF). Wildlife Survey & Photo Service. p. 1. Archived from the original (PDF) on 2006-05-26. Retrieved 2006-05-07.
  23. ^ a b Aamio, K. and E. Bornsdorff. 1997. Passing the gut of juvenile flounder Platichthys flesus (L.) – differential survival of zoobenthic prey species. Marine Biology 129: 11–14.
  24. ^ "Non-native snail turns up in Truckee River". Elko Daily Free Press. 20 May 2013. p. 4.
  25. ^ "News Release - Discovery of Invasive New Zealand Mud Snail Forces Temporary Closure of Putah Creek". California Department of Fish and Game. 2003-12-16. Archived from the original on 2004-02-02. Retrieved 2006-05-07.
  26. ^ a b "Western USA Potamopyrgus antipodarum morphs". Department of Ecology, Montana State University-Bozeman. 2006-02-22. Archived from the original on 2006-04-29. Retrieved 2006-05-07.
  27. ^ Levri, Edward P.; Dermott, Ron M.; Lunnen, Shane J.; Kelly, Ashley A.; Ladson, Thomas (2008). "The distribution of the invasive New Zealand mud snail (Potamopyrgus antipodarum) in Lake Ontario" (PDF). Aquatic Ecosystem Health and Management. 11 (4): 412–421. doi:10.1080/14634980802523140. S2CID 83841912. Archived (PDF) from the original on 2016-01-14.
  28. ^ New Zealand Mud Snails Invade Lake Erie!, International Association for Great Lakes Research, 26 March 2007.
  29. ^ "Invasive snail found in Minn. harbor". NBC News. Associated Press. 2006-05-03. Archived from the original on 2019-05-23. Retrieved 2019-05-23.
  30. ^ "Worrying invasive snail found in Lake Michigan". CTV News. The Associated Press. 2008-08-16. Archived from the original on 2008-09-02.
  31. ^ Dodge, John (2010-10-19). "Snail seclusion successful". The Olympian. Archived from the original on 2012-09-13. Retrieved 2011-03-31.
  32. ^ Shannon, Brad (4 December 2013). "Freeze could help kill Capitol Lake's mudsnail population". The News Tribune. Archived from the original on 27 December 2013.
  33. ^ Shannon, Brad (26 December 2013). "Cold estimated to have killed half of snails in Capitol Lake". The Olympian. Archived from the original on 27 December 2013.
  34. ^ "South-Central/Southern California Coast Steelhead Recovery Planning Domain 5-Year Review: Summary and Evaluation of Southern California Coast Steelhead Distinct Population Segment" (PDF). National Oceanic and Atmospheric Administration. 2011. Retrieved 2013-12-03.
  35. ^ Leovy, Jill (March 30, 2010). "Hard-to-kill snails infest Santa Monica Mountain watersheds". Los Angeles Times. Archived from the original on 2019-05-23. Retrieved 20 July 2018.
  36. ^ Collier, K. J., R. J. Wilcock and A. S. Meredith. 1998. Influence of substrate type and physico–chemical conditions on macroinvertebrate faunas and biotic indices in some lowland Waikato, New Zealand, streams. New Zealand Journal of Marine and Freshwater Research 32(1):1–19.
  37. ^ Holomuzki, J. R. and B. J. F. Biggs. 1999. Distributional responses to flow disturbance by a stream–dwelling snail. Oikos 87(1):36–47.
  38. ^ Holomuzki, J. R. and B. J. F. Biggs. 2000. Taxon–specific responses to high–flow disturbances in streams: implications for population persistence. Journal of the North American Benthological Society 19(4):670–679.
  39. ^ Negovetic, S. and J. Jokela. 2000. Food choice behaviour may promote habitat specificity in mixed populations of clonal and sexual Potamopyrgus antipodarum. Experimental Ecology 60(4):435–441.
  40. ^ Richards, D. C., L. D. Cazier and G. T. Lester. 2001. Spatial distribution of three snail species, including the invader Potamopyrgus antipodarum, in a freshwater spring. Western North American Naturalist 61(3):375–380.
  41. ^ Weatherhead, M. A. and M. R. James. 2001. Distribution of macroinvertebrates in relation to physical and biological variables in the littoral zone of nine New Zealand lakes. Hydrobiologia 462(1–3):115–129.
  42. ^ Death, R. G., B. Baillie and P. Fransen. 2003. Effect of Pinus radiata logging on stream invertebrate communities in Hawke’s Bay, New Zealand. New Zealand Journal of Marine and Freshwater Research 37(3):507–520.
  43. ^ Schreiber, E. S. G., G. P. Quinn and P. S. Lake. 2003. Distribution of an alien aquatic snail in relation to flow variability, human activities and water quality. Freshwater Biology 48(6):951–961.
  44. ^ Suren, A. M. 2005. Effects of deposited sediment on patch selection by two grazing stream invertebrates. Hydrobiologia 549(1):205–218.
  45. ^ Jacobsen, R. and V. E. Forbes. 1997. Clonal variation in life–history traits and feeding rates in the gastropod, Potamopyrgus antipodarum: performance across a salinity gradient. Functional Ecology 11(2):260–267.
  46. ^ Leppäkoski, E. and S. Olenin. 2000. Non–native species and rates of spread: lessons from the brackish Baltic Sea. Biological Invasions 2(2):151–163.
  47. ^ Costil, K., G.B. J. Dussart and J. Daquzan. 2001. Biodiversity of aquatic gastropods in the Mont St–Michel basin (France) in relation to salinity and drying of habitats. Biodiversity and Conservation 10(1):1–18.
  48. ^ a b Gerard, C., A. Blanc and K. Costil. 2003. Potamopyrgus antipodarum (Mollusca: Hydrobiidae) in continental aquatic gastropod communities: impact of salinity and trematode parasitism. Hydrobiologia 493(1–3):167–172.
  49. ^ Cox, T. J. and J. C. Rutherford. 2000. Thermal tolerances of two stream invertebrates exposed to diurnally varying temperature. New Zealand Journal of Marine and Freshwater Research 34(2):203–208.
  50. ^ Broekhuizen, N., S. Parkyn and D. Miller. 2001. Fine sediment effects on feeding and growth in the invertebrate grazer Potamopyrgus antipodarum (Gastropoda, Hydrobiidae) and Deleatidium sp. (Ephemeroptera, Letpophlebiidae). Hydrobiologia 457(1–3):125–132.
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  52. ^ Kelly, D. J. and I. Hawes. 2005. Effects of invasive macrophytes on littoral–zone productivity and foodweb dynamics in a New Zealand high–country lake. Journal of the North American Benthological Society 24(2):300–320.
  53. ^ Parkyn, S. M., J. M. Quinn, T. J. Cox and N. Broekhuizen. 2005. Pathways of N and C uptake and transfer in stream food webs: an isotope enrichment experiment. Journal of the North American Benthological Society 24(4):955–975.
  54. ^ Fox J., Dybdahl M., Jokela J., Lively C. (1996). Genetic structure of coexisting sexual and clonal subpopulations in a freshwater snail (Potamopyrgus antipodarum). Evolution. 50 (4): 1541-1548
  55. ^ Schreiber, E. S. G., A. Glaister, G. P. Quinn and P. S. Lake. 1998. Life history and population dynamics of the exotic snail Potamopyrgus antipodarum (Prosobranchia: Hydrobiidae) in Lake Purrumbete, Victoria, Australia. Marine and Freshwater Research 49(1):73–78.
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  57. ^ "New Zealand mudsnail (Potamopyrgus antipodarum)". Kansas Department of Wildlife and Parks. 2006. Retrieved 2006-05-04.
  58. ^ Larval Trematoda: Winterbourne
  59. ^ Dybdahl, M. F. and A. C. Krist. 2004. Genotypic vs. condition effects on parasite–driven rare advantage. Journal of Evolutionary Biology 17(5):967–973.
  60. ^ About Microphallus
  61. ^ Levri, E. P. 1998. Perceived predation risk, parasitism, and the foraging behavior of a freshwater snail (Potamopyrgus antipodarum). Canadian Journal of Zoology 76(10):1878–1884.
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New Zealand mud snail: Brief Summary

provided by wikipedia EN

The New Zealand mud snail (Potamopyrgus antipodarum) is a species of very small freshwater snail with a gill and an operculum. This aquatic gastropod mollusk is in the family Tateidae.

It is native to New Zealand, where it is found throughout the country, but it has been introduced to many other countries, where it is often considered an invasive species because populations of the snail can reach very high densities.

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Alien species

provided by World Register of Marine Species
The natural area of distribution of the New-Zealand mudsnail Potamopyrgus antipodarum is situated around New-Zealand, but around 1859 the species was introduced to Europe with barrels of drinking water. The little snails must have entered these barrels while they were beeing washed or refilled. In 1927 the first Belgian specimens of the snails were found in the river Scheldt around Antwerp. In Belgium the species inhabits fresh- to slightly brackish waters. This species can reproduce very fast, though parthenogenesis. These snails prey on young oysters, and are therefore not very popular among oyster farmers.

Reference

VLIZ Alien Species Consortium. (2010).

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Alien species

provided by World Register of Marine Species
Jenkins’ waterhoren Potamopyrgus antipodarum kwam oorspronkelijk enkel voor rond Nieuw-Zeeland, maar werd omstreeks 1859 naar Europa gebracht in vaten met drinkwater. Bij het wassen of hervullen van deze vaten moeten de kleine slakjes erin geslopen zijn. In 1927 werden in de Schelde ter hoogte van Antwerpen de eerste exemplaren van Jenkin’s waterhoren in België gevonden. De soort komt voor in zoet tot lichtbrak water. Jenkins’ waterhoren kan zich zeer snel door parthenogenese ongeslachtelijk voortplanten. De soort voedt zich op jonge oesters en maakt zich daardoor niet echt geliefd bij oesterkwekers.
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