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Sinotaia aeruginosa

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Sinotaia aeruginosa
Shell
Scientific classification
Kingdom:
Animalia
Phylum:
Mollusca
Class:
Gastropoda
(unranked):
clade Caenogastropoda
informal group Architaenioglossa
Superfamily:
Viviparoidea
Family:
Viviparidae
Subfamily:
Bellamyinae
Genus:
Sinotaia
Species:
S. aeruginosa
Binomial name
Sinotaia aeruginosa
(Reeve, 1863)[2]
Distribution map showing known records (actual range may be larger).[1]
Synonyms

Paludina aeruginosa Reeve, 1863
Paludina quadrata var. aeruginosa Reeve, 1863
Bellamya aeruginosa (Reeve, 1863)

Sinotaia aeruginosa (synonym: Bellamya aeruginosa) is a species of freshwater snail with a gill and an operculum, an aquatic gastropod mollusk in the family Viviparidae. It is widely distributed and common species in China and in northern Vietnam inhabiting various shallow freshwater habitats, where it can reach high densities. It is a keystone species in its habitat and can significantly affect water quality and phytoplankton communities. It is commonly used in Chinese cuisine.

Taxonomy

This species was described under the name Paludina aeruginosa by English conchologist Lovell Augustus Reeve in 1863. He noted that it he thought it "very closely allied to Paludina quadrata".[2] Reeve's original text (the type description) reads as follows:

The Bronze Paludina Shell rather narrowly pyramidally conical, dark blue-green, whorls slopingly convex, sometimes obtusely keeled towards the base, everywhere obliquely plicately striated, beneath the lens spirally obsoletely very minutely punctured; aperture pyriformly ovate.

Hab. China.
Very closely allied to P. quadrata, from the same locality, the specimens are uniformly lighter, and of a peculiar

bronze blue-green colour.

The specific name aeruginosa derives from Latin aerūgō ("copper rust" or "bronze rust"), referring to the green color of the shell.

Later authors considered this taxon as a subspecies[3] or form[4] of Bellamya quadrata.[1] It is generally classified as a species Sinotaia aeruginosa within the genus Sinotaia,[1] although Chinese malacologists use the name Bellamya aeruginosa within the genus Bellamya.

Distribution

The species is found throughout China and Vietnam;[1] indeed, S. aeruginosa is one of the most common species in China.[5] It is common in the Yangtze River and Yellow River basins.[6] The distribution of S. aeruginosa includes East China (Anhui, Fujian, Jiangsu, Jiangxi, Shandong, Shanghai, Zhejiang), Northeast China (Heilongjiang, Jilin, Liaoning), North China (Beijing, Hebei, Inner Mongolia, Shanxi, Tianjin), Northwest China (Ningxia, Shaanxi), Central China (Henan, Hubei, Hunan), Southwest China (Chongqing, Guizhou, Sichuan, Yunnan) and South China (Guangdong, Guangxi, Hainan).[1] In Vietnam it is also common, but rarely reaches very high population densities.[7] The type locality is "China".[2] The species' distribution appears to have shrunk from the Middle Pleistocene to the Late Pleistocene, while a range expansion occurred in the Holocene.[6]

Description

The height of the shell is 20–30 mm (0.79–1.18 in), with both sexes having identical shell dimensions. Adults snails have shell of greater height than width. The shells of newborn snails are 2.93–3.70 mm (0.115–0.146 in) long, and differ from those of adults in being wider than high.[8] The snail including the shell has a weight of about 2.8 g.[9]

Drawing from the type description, apertural view.
Drawing from the type description, abapertural view.
Drawing of an apertural view with operculum.
 
Drawing of an abapertural view of a shell.

S. aeruginosa breathes with gills. The right tentacle is thickened in the male but not the female.[8] The dry weight of composition of this species is as follows: 28.6% foot, 23.06% intestine, 9.78% gonad, 8.58% hepatopancreas, 29.98% other tissue.[10] The diploid chromosome number of Sinotaia aeruginosa is 2n=16.[11]

Ecology

Habitat

S. aeruginosa inhabits rice paddies, lakes, pools, slow flowing rivers, streams, ditches, ponds, and canals called khlongs in Vietnam.[1][8] It has a benthic lifestyle and lives mainly in shallow littoral areas,[12] usually in soft mud rich in organic matter.[8] It can actively glide over the sediment or bury into it.[13] This species is not actively migrating, rather its dispersal appears to be caused passively by floods, animals (zoochory), and accidentally by humans.[6] The species prefers water temperatures typical of subtropical habitats, e.g., 6 to 30.1 °C (42.8 to 86.2 °F) in Lake Tai.[13]

Populations can reach densities of up to 400 snails/m2.[8] In Chao Lake, it is the dominant gastropod species with an abundance 2-128 snails/m2 and an average biomass of 87.5 g/m2.[14] It is similarly dominant in Lake Tai.[15]

S. aeruginosa has been found to respond well to laboratory conditions with a water temperature of 24 °C, pH 8 and a 1:4 ratio of sediment to water.[8]

Populations of S. aeruginosa at high densities are able to alter the physicochemical features of water. They decrease the concentration of chlorophyll a and thus directly increase water transparency. This indirectly decreases the concentration of dissolved oxygen through consumption of oxygen-producing algae.[12] The species affects the composition of the phytoplankton community by decreasing the biomass of mostly toxic cyanobacteria and flagellates and promoting the biomass of mostly colonial green algae.[9][12] Nitrogen concentrations may also be decreased.[9] Its pronounced effect on water chemistry and community composition makes S. aeruginosa a keystone species in its habitat.[5]

Feeding habits

S. aeruginosa is a herbivorous deposit feeder.[8][16] It consumes mainly epiphytic algae,[17] but its diet also includes detritus, bacteria,[8] aquatic plants,[16] sand grains, diatoms, green algae,[18] and cyanobacteria such as Microcystis.[19] Its consumption of cyanobacteria during algal blooms may result in bioaccumulation of toxic microcystins (microcystin-LR, microcystin-RR) from Microcystis in the gonads, the hepatopancreas and the digestive tract.[19] Adult snails feeding ad libitum under ideal laboratory conditions eat 16.0 mg of fish food daily.[8]

Life cycle

S. aeruginosa is gonochoristic, which means that each individual animal is distinctly male or female.[6] The species is ovoviviparous.[16] Newborn snails attach to non-sediment substrates (shells of adults or other material) in their the first 2–3 days.[8]

The shell length of juvenile snails starts at about 3 mm and grows rapidly by about 190 μm daily. Juveniles become adults at the age of nine weeks, when they reach a shell height of 12.15–16.09 mm; from then on, they grow more slowly at about 30 μm daily. Snails can be reliably sexed at this age.[8]

Individuals start mating and reproducing in at water temperatures of 16–18 °C, although a temperature of 24–26 °C is optimal. Females start to give birth to the first newborn snails at the age of 18 weeks, when they reach a shell height of 15–16 mm and a body weight of 0.81–0.94 g.[8][16] Gravidity of adult females lasts the entire year.[8] The average number of newborn snails in the wild is 0.24 snails per day (50 per year)[8][16] or up to 0.55 snails per day in the laboratory.[8] Each gravid female carries 19–21 embryos inside her.[8]

Generation time is quite short at about four months.[6][8] The species can have three generations per year in the aquarium.[8] The reproductive cycle is about six months.[16]

Environmental sensitivity

S. aeruginosa has been the subject of various aquatic toxicology studies into the effects of copper,[8][20] cadmium,[21] lead,[22] ethylbenzene,[23] 2,2',4,4'- tetrabromodiphenyl ether,[21][24] tributyltin,[25] microcystin,[26] multi-walled carbon nanotubes,[27] and 17β-estradiol.[28] The species has a high sensitivity to copper exposure and could thus be used for monitoring of sediment toxicity caused by environmental copper pollution.[8]

Sinotaia aeruginosa snails from West Lake in Hanoi, Vietnam were found to be contaminated with copper, lead and zinc.[29] The concentration of these elements in these snails exceeded standards of Food and Drug Administration and of Food Standards Australia New Zealand.[29]

Distribution of rare earth elements was studied in a labolatory. Results shown bioaccumulation of lanthanum, samarium, gadolinium and yttrium in Sinotaia aeruginosa and there was found no bioaccumulation of cerium in this snail.[30]

Conservation

The species' population trend is unknown,[1] but population sizes are mostly large.[6] Water pollution and sedimentation are threats to local populations,[1] while more general threats include habitat fragmentation by damming and habitat destruction.[6] The genetic diversity of this species was found to be high in China.[6] S. aeruginosa is currently classified as Least Concern by the IUCN.[1]

Parasites and predators

S. aeruginosa serves as an intermediate host for Angiostrongylus cantonensis[31][32] and for Echinochasmus fujianensis.[33]

Predators of the species include the black carp Mylopharyngodon piceus; S. aeruginosa is one of the main food sources for this fish, making it important in the freshwater food chain.[8]

Human use

Sinotaia aeruginosa
Chinese food from Guangxi with Sinotaia aeruginosa.
Nutritional value per 100 g (3.5 oz)
2.07 g[34]
 
Threonine3.416 g[34]
Isoleucine2.447 g
Leucine5.910 g
Lysine4.201 g
Methionine1.293 g
Cystine1.477 g
Phenylalanine2.401 g
Tyrosine3.232 g
Valine2.262 g
Arginine5.171 g
Histidine1.339 g
Alanine3.970 g
Aspartic acid7.387 g
Glutamic acid11.588 g
Glycine3.878 g
Proline2.170 g
Serine3.186 g
Vitamins and minerals
Other constituentsQuantity
Water78.34 g[34]
Crude fat0.78 g[34]
Crude protein14.43 g[34]
Crude ash4.38 g[34]
†Percentages estimated using US recommendations for adults,[35] except for potassium, which is estimated based on expert recommendation from the National Academies.[36]

S. aeruginosa is commonly sold in markets and restaurants in China[37] and constitutes one of the three predominant freshwater snails found in Chinese markets,[32] where it is considered a delicacy.[10] The species is also used as feed in crab culture[19] as well as fish, poultry and livestock raising.[1] The annual production of S. aeruginosa in Chao Lake in 2002 amounted to 28 084 t.[19] Although harvesting pressure in China is high, the high genetic diversity suggests that the species is currently not negatively affected by it.[6]

References

This article incorporates public domain text from the reference[2]

  1. ^ a b c d e f g h i j k "Sinotaia aeruginosa". IUCN Red List of Threatened Species. 2012. IUCN: e.T167038A1164990. 2012. doi:10.2305/IUCN.UK.2012-1.RLTS.T167038A1164990.en. Retrieved 9 February 2016. {{cite journal}}: Unknown parameter |authors= ignored (help)
  2. ^ a b c d Reeve L. A. (1863). "Paludina". Plate VII. In: Reeve L. A. (1864). Conchologia iconica, or, Illustrations of the shells of molluscous animals. London.
  3. ^ Template:Fr icon Dautzenberg P. & Fischer H. (1905). "Liste des mollusques recoltes par M. H. Mansuy en Indo Chine et au Yunnan et description d'especes nouvelles". Journal de Conchyliologie 53: 343-471, page 419.
  4. ^ Template:De icon Kobelt W. (1909). "Die Gattung Paludina Lam. (Vivipara Montfort): Neue Folge. In: Abbildungen Nach de Natur mit Beschreibungen". Systematisches Conchylien–Cabinet von Martini und Chemnitz 1(21a): 97-380, plates 15–77, pages 123-124, plate 21, figures 1–3, 10–11, 18.
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  6. ^ a b c d e f g h i Gu, Qian H.; Husemann, Martin; Ding, Baoqing; Luo, Zhi; Xiong, Bang X. (2015). "Population genetic structure of Bellamya aeruginosa(Mollusca: Gastropoda: Viviparidae) in China: Weak divergence across large geographic distances". Ecology and Evolution. 5 (21): 4906–4919. doi:10.1002/ece3.1673. PMC 4662307. PMID 26640670.
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  20. ^ Li, Zi-Cheng; An, Li-Hui; Fu, Qing; Liu, Ying; Zhang, Lei; Chen, Hao; Zhao, Xing-Ru; Wang, Li-Jing; Zheng, Bing-Hui; Zhang, Lin-Bo (2011). "Construction and characterization of a normalized cDNA library from the river snail Bellamya aeruginosa after exposure to copper". Ecotoxicology. 21 (1): 260–7. doi:10.1007/s10646-011-0786-y. PMID 21915736.
  21. ^ a b "铜锈环棱螺HSP70对Cd和BDE-47胁迫的响应敏感性" [Response Sensitivity of HSP70 in Bellamya aeruginosa Exposed to Cadmium and BDE-47]. Journal of Chongqing Normal University (in Chinese): 22–28. doi:10.11721/cqnuj20140605.
  22. ^ Template:Cn icon Ma T. W., Zhu C., Zhou K. et al. (2010). Cd Pb单一及复合污染沉积物对铜锈环棱螺肝胰脏SOD和MT的影响 "Effects of Cd, Pb, and combined contaminated sediments on hepatopancreatic SOD and MT in Bellamya aeruginosa". Journal of Agro-Environment Science 29(1): 30–37. abstract.
  23. ^ Zheng, Shimei; Zhou, Qixing; Gao, Jie; Xiong, Hongxia; Chen, Cuihong (2012). "Behavioral alteration and DNA damage of freshwater snail Bellamya aeruginosa stressed by ethylbenzene and its tissue residue". Ecotoxicology and Environmental Safety. 81: 43–48. doi:10.1016/j.ecoenv.2012.04.016. PMID 22591725.
  24. ^ Template:Cn icon Zhou K., Ma T. W., Zhu C. et al. (2010). 2,2',4,4'-四溴联苯醚(BDE-47)污染沉积物对铜锈环棱螺肝胰脏的SOD、CAT和EROD活性的影响 "Effect of 2,2',4,4'- tetrabromodiphenyl ether (BDE-47)-contaminated sediments on SOD, CAT, and EROD activities in the hepatopancreas of Bellamya aeruginosa". Acta Scientiae Circumstantiae 30(8): 1666–1673. abstract, PDF.
  25. ^ Template:Cn icon Peng J. Y., Liu J., Ma T. W. et al. (2012). "Effects of sediment associated tributyltin (TBT) on the hepatopancreatic antioxidant defense system of Bellamya aeruginosa". Shanghai Envinmental Sciences 31(3): 97–101. abstract.
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Further reading

  • Template:Cn icon Chen, Q (1987). "A preliminary study on the population dynamics and annual production of Bellamya aeruginosa (Reeve) in lake East Lake (Wuhan)–Dong Hu, Wuhan". Acta Hydrobiologica Sinica. 11 (2): 117–130.
  • Qu, M. Z.; Qu, Y. F.; Ren, W. W.; Wang, Y. X.; Wu, Q. H. (2010). "The mechanism of controlling Microcystis bloom by Bellamya aeruginosa". Journal of Fudan University. 49: 301–308.
  • Xiong, Y. Q.; You, W. H. (2002). "Preliminary study on effects of SOD and catalase of Bellamya aeruginosa raised in Suzhou Creek". Journal of East China Normal University. 4: 96–101.
  • Template:De icon Yen T.-C. (1939). "Die chinesischen Land- und Süßwasser-Gastropoden des Natur-Museums Senckenberg". Senckenbergische Naturforschende Gesellschaft, Frankfurt, Germany.
  • Yin, Hongbin; Cai, Yongjiu; Duan, Hongtao; Gao, Junfeng; Fan, Chengxin (2014). "Use of DGT and conventional methods to predict sediment metal bioavailability to a field inhabitant freshwater snail (Bellamya aeruginosa) from Chinese eutrophic lakes". Journal of Hazardous Materials. 264: 184–194. doi:10.1016/j.jhazmat.2013.11.030. PMID 24295770.
  • Yun-Jun, Yan; Yan-Ling, Liang; Hong-Zhu, Wang (2001). "Energy flow of Bellamya aeruginosa in a shallow algal lake, Houhu Lake (Wuhan, China)". Chinese Journal of Oceanology and Limnology. 19 (3): 243–248. doi:10.1007/BF02850661.
  • Template:De icon Zilch A. (1958). "Die Typen und Typoide des Natur-Museums Senckenberg, 21: Mollusca, Cyclophoridae, Craspedopominae-Cochlostominae". Archiv für Molluskenkunde 87: 53–76.
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