Hostname: page-component-586b7cd67f-dsjbd Total loading time: 0 Render date: 2024-11-22T17:49:35.187Z Has data issue: false hasContentIssue false

Imposex of Mauritia arabica on the south-eastern coast of China

Published online by Cambridge University Press:  29 October 2008

Changjiang Huang
Affiliation:
School of Environmental Sciences and Public Health, Wenzhou Medical College, Wenzhou, Zhejiang 325035, People's Republic of China Institute of Marine Biology, Shantou University, Shantou 515063, People's Republic of China
Shixi Zhu
Affiliation:
Institute of Marine Biology, Shantou University, Shantou 515063, People's Republic of China
Junda Lin
Affiliation:
Department of Biological Sciences, Florida Institute of Technology, Melbourne, FL 32901, USA
Qiaoxiang Dong*
Affiliation:
School of Environmental Sciences and Public Health, Wenzhou Medical College, Wenzhou, Zhejiang 325035, People's Republic of China
*
Correspondence should be addressed to: Qiaoxiang Dong, School of Environmental Sciences and Public Health, Wenzhou Medical College, University Town Chashan Gaojiao Yuanqu, Wenzhou, Zhejiang 325035, People's Republic of China email: [email protected]

Abstract

Imposex, the development of male sexual organs in female gastropods, is mainly induced by organotin compounds used as biocides in antifouling paints. As part of our continued efforts to report the occurrence of imposex gastropods along the coast of mainland China, this study investigates the imposex prevalence in Mauritia arabica (Mesogastropod: Cypraeidae). A total of 529 adults were collected from 11 sites in south-eastern China between March 2001 and June 2005. Of these, 303 were females and 226 were males. Imposex is classified into six stages representing the sequence from the initial appearance of the seminal groove or small penis (S1) to the point when this duct blocks the pallial oviduct and aborted egg capsules appear (S6). All six stages of imposex were found in M. arabica with three different types (a, b and c) of expression in stages 1 and 3, two types (a and b) in stage 2, and one type in stages 4, 5, and 6. Imposex development was also measured by various indices such as the vas deferens sequence index (VDS), female penis length (FPL), percentage of affected females (%I), the relative penis length (RPL), and relative penis size (RPS—the cubed form of RPL). Imposex individuals were found in all 11 sites with %I ranged from 26% to 100%. Excluding the data from site 3 (with only one female and one male), VDS scores ranged from 1.05 to 4.07, with an average of 2.86, and the RPL ranged from 0.9 to 56.8. High correlations were observed among VDS, FPL, %I, RPL, and the RPS. Our findings suggest that M. arabica is an ideal bioindicator for organotin pollution along the south-eastern coast of China, and can be used in conjunction with the rock shell, Thais clavigera, a well-established bioindicator of tributyltin and triphenyltin contamination. To our knowledge, this is the first detailed report of imposex in M. arabica.

Type
Research Article
Copyright
Copyright © Marine Biological Association of the United Kingdom 2008

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

REFERENCES

Blackmore, G. (2000) Imposex in Thais clavigera (Neogastropoda) as an indicator of TBT (tributyltin) bioavailability in coastal waters of Hong Kong. Journal of Molluscan Studies 66, 18.CrossRefGoogle Scholar
Bryan, G.W., Burt, G.R., Gibbs, P.E. and Pascoe, P.L. (1993) Nassarius reticulatus (Nassariidae: Gastropoda) as an indicator of tributyltin pollution before and after TBT restrictions. Journal of the Marine Biological Association of the United Kingdom 73, 913929.CrossRefGoogle Scholar
de Mora, S.J. and Pelletier, E. (1997) Environmental tributyltin research; past, present, future. Environmental Technology 18, 11691177.CrossRefGoogle Scholar
Dowson, P.H., Bubb, J.M. and Lester, J.N. (1993) Temporal distribution of organotins in the aquatic environment: five years after the 1987 UK retail ban on TBT-based anti-fouling paints. Marine Pollution Bulletin 26, 487494.CrossRefGoogle Scholar
Fioroni, P., Oehlmann, J. and Stroben, E. (1991) The pseudohermaphroditism of prosobranchs, morphological aspects. Zoologischer Anzeiger 226, 126.Google Scholar
Fretter, V. (1941) The genital ducts of some British stenoglossan prosobranchs. Journal of the Marine Biological Association of the United Kingdom 25, 173211.CrossRefGoogle Scholar
Gibbs, P.E. (1993) A male genital defect in the dog-whelk, Nucella lapillus (Neogastropoda), favouring the survival of a population in a TBT-polluted area. Journal of the Marine Biological Association of the United Kingdom 73, 667678.CrossRefGoogle Scholar
Gibbs, P.E. and Bryan, G.W. (1996) TBT-induced imposex in neogastropod snails: masculinization to mass extinction. In de Mora, S.J. (ed.) Tributyltin: case study of an environmental contaminant. Cambridge: Cambridge University Press, pp. 212236.CrossRefGoogle Scholar
Gibbs, P.E., Pascoe, P.L. and Burt, G.R. (1988) Sex change in the female dog-whelk Nucella lapillus, induced by TBT from anti-fouling paints. Journal of the Marine Biological Association of the United Kingdom 68, 715731.CrossRefGoogle Scholar
Horiguchi, T., Hyeon-Seo, C., Shiraishi, H., Shibata, Y., Soma, M., Morita, M. and Shimizu, M. (1998) Field studies on imposex and organotin accumulation in the rock shell, Thais clavigera, from the Seto Inland Sea and the Sanriku region, Japan. The Science of the Total Environment 214, 6570.CrossRefGoogle ScholarPubMed
Hung, T.C., Hsu, W.K., Mang, P.J. and Chuang, A. (2001) Organotins and imposex in the rock shell, Thais clavigera, from oyster mariculture areas in Taiwan. Environmental Pollution 112, 145152.CrossRefGoogle ScholarPubMed
Kay, A. (1960) Generic revision of the Cypraeinae. Proceedings of the Malacological Society of London 33, 278287.Google Scholar
Len, S. (1991) Invertebrate biology. Beijing: Beijing University Press.Google Scholar
Oehlmann, J., Stroben, E. and Fioroni, P. (1991) The morphological expression of imposex in Nucella lapillus (Linnaeus) (Gastropoda: Muricidae). Journal of Molluscan Studies 57, 375390.CrossRefGoogle Scholar
Oehlmann, J., Stroben, E. and Fioroni, P. (1992) The rough tingle Ocenebra erinacea (Neogastropoda: Muricidae): an exhibitor of imposex in comparison to Nucella lapillus. Helgoland Marine Research 46, 311328.Google Scholar
Oehlmann, J., Stroben, E., Schulte-Oehlmann, U. and Bauer, B. (1998) Imposex development in response to TBT pollution in Hinia incrassata (Strom, 1768) (Prosobranchia, Stenoglossa). Aquatic Toxicology 43, 239260.CrossRefGoogle Scholar
Omae, I. (2003) Organotin antifouling paints and their alternatives. Applied Organometallic Chemistry 17, 81105.CrossRefGoogle Scholar
Shi, H., Huang, C. and Lei, Z. (2003) Organotin compound pollution in coastal water as indicated by imposex in Babylonia formosae habei. Ocean Technology 22, 8286. [In Chinese with English abstract.]Google Scholar
Shi, H., Huang, C., Yu, X. and Zhu, S. (2004a) Imposex and female reproductive failure of Chicoreus brunneus and C. asianus. Journal of Tropical Oceanography 23, 8287. [In Chinese with English abstract.]Google Scholar
Shi, H., Huang, C., Yu, X., Zhu, S. and Zhang, Y. (2004b) Development of imposex and structural effect on males in three Nassarius spp. Marine Sciences 28, 3641. [In Chinese with English abstract.]Google Scholar
Shi, H., Huang, C., Yu, X. and Zhu, S. (2005a) An updated scheme of imposex for Cantharus cecillei (Gastropoda: Buccinidae) and a new mechanism leading to the sterilization of imposex-affected females. Marine Biology 146, 717723.CrossRefGoogle Scholar
Shi, H., Huang, C., Zhu, S., Yu, X. and Xie, W. (2005b) Generalized system of imposex and reproductive failure in female gastropods of coastal waters of mainland China. Marine Ecology Progress Series 304, 179189.CrossRefGoogle Scholar
Shim, W.J., Kahng, S.H., Hong, S.H., Kim, N.S., Kim, S.K. and Shim, J.H. (2000) Imposex in the rock shell, Thais clavigera, as evidence of organotin contamination in the marine environment of Korea. Marine Environmental Research 49, 435451.CrossRefGoogle ScholarPubMed
Smith, B.S. (1971) Sexuality in the American mud snail, Nassarius obsoletus Say. Proceedings of the Malacological Society of London 39, 377378.Google Scholar
Stroben, E., Oehlmann, J. and Fioroni, P. (1992) The morphological expression of imposex in Hinia reticulata (Gastropoda: Buccinidae): a potential biological indicator of tributyltin pollution. Marine Biology 113, 625636.CrossRefGoogle Scholar
Stroben, E., Oehlmann, J., Schulte-Oehlmann, U. and Fioroni, P. (1996) Seasonal variations in the genital ducts of normal and imposex-affected prosobranchs and its influence on biomonitoring indices. Malacological Review Suppl. 6, 173184.Google Scholar
Tan, K.S. (1997) Imposex in three species of Thais from Singapore, with additional observations on T. clavigera (Kuster) from Japan. Marine Pollution Bulletin 34, 577581.CrossRefGoogle Scholar
Vishwa kiran, Y. and Anil, A.C. (1999) Record of imposex in Cronia konkanensis (Gastropoda, Muricidae) from Indian waters. Marine Environmental Research 48, 123130.CrossRefGoogle Scholar
Wei, A. and Hu, J. (2006) Effects of endocrine disrupting chemicals on China's rivers and coastal waters. Frontiers in Ecology and Environment 4, 378386.Google Scholar
Yu, X., Huang, C., Zhu, S., Shen, J. and Dong, Q. (2004) Anatomical and histological studies on imposex of Thais clavigera. Oceanologia et Limnologia Sinica 35, 149155. [In Chinese with English abstract.]Google Scholar
Zhu, S. (2005) A large-scale investigation on imposex in the coastal waters of mainland China. Masters thesis. Shantou University, China [In Chinese with English abstract.]Google Scholar
Zhu, S., Dong, Q., Shen, J., Yu, X., Du, H. and Huang, C. (2005) Imposex of Conus betulinus and Conus vexillum. Acta Ecologica Sinica 25, 289297. [In Chinese with English abstract.]Google Scholar