Difference between revisions of "TBT and intersex in periwinkles"

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<u>'''Main results of the study'''</u>
 
<u>'''Main results of the study'''</u>
  
The study showed that in all sampling regions, the occurrence of intersex characteristics in periwinkles decreased during the 3 year study period. Intersex characteristics were more abundant at former TBT hot spots, located near the harbor of Antwerp and Vlissingen. The percentage of sterile females decreased in all locations during the study period. These results show that the TBT ban has positive effects on the populations. The ban has also negative effects such as an increased fuel coast due to the attachment of organisms on the hull of ships, the use of less effective antifouling paints (copper based) which need to be applied more often. It should also be considered, that copper might also be toxic at high concentrations. (See also [[Effects_of_copper-based_antifouling_paints_on_brine_shrimp|here.]]) Therefore, using copper based antifouling paints instead of TBT might just replace one environmental problem by another.<ref name="pub">[http://www.vliz.be/imis/imis.php?module=ref&refid=70468 De Wolf, H.; Handa, C.; Backeljau, T.; Blust, R. (2004). A baseline survey of intersex in Littorina littorea along the Scheldt Estuary, The Netherlands. Mar. Pollut. Bull. 48(5-6): 592-596]</ref>
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The study showed that in all sampling regions, the occurrence of intersex characteristics in periwinkles decreased during the 3 year study period. Intersex characteristics were more abundant at former TBT hot spots, located near the harbor of Antwerp and Vlissingen. The percentage of sterile females decreased in all locations during the study period. These results show that the TBT ban has positive effects on the populations. The ban has also negative effects such as an increased fuel coast due to the attachment of organisms on the hull of ships, the use of less effective antifouling paints ([[copper]] based) which need to be applied more often. It should also be considered, that copper might also be toxic at high concentrations. (See also [[Effects_of_copper-based_antifouling_paints_on_brine_shrimp|here.]]) Therefore, using copper based antifouling paints instead of TBT might just replace one environmental problem by another.<ref name="pub">[http://www.vliz.be/imis/imis.php?module=ref&refid=70468 De Wolf, H.; Handa, C.; Backeljau, T.; Blust, R. (2004). A baseline survey of intersex in Littorina littorea along the Scheldt Estuary, The Netherlands. Mar. Pollut. Bull. 48(5-6): 592-596]</ref>
  
  
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{{author
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|AuthorID=19826
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|AuthorFullName=Daphnis De Pooter
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[[Category:North Sea]]
 
[[Category:North Sea]]
 
[[Category:Coastal and marine pollution]]
 
[[Category:Coastal and marine pollution]]

Latest revision as of 10:36, 13 March 2013

Context of the study

Organotin compounds (like TBT) used in antifouling paints can disrupt the endocrine system of many gastropod species. Concentrations of 1 ng tin / l sea water results in imposex; the development of non-functional male reproductive organs in females. In the periwinkle however, higher concentrations of TBT (> 10ng tin/l) can also cause intersex; the transformation of the oviduct into a non-functional prostate. Both conditions can lead to female sterility. After TBT was banned in 2003, many periwinkle populations stopped displaying imposex characteristics. It remains unknown whether they still display intersex characteristics. [1]

2 periwinkles © Decleer

Content of the study

The study investigated the occurrence of intersex in periwinkles sampled at 5 locations in the Western Scheldt estuary between 2000 and 2002.

Main results of the study

The study showed that in all sampling regions, the occurrence of intersex characteristics in periwinkles decreased during the 3 year study period. Intersex characteristics were more abundant at former TBT hot spots, located near the harbor of Antwerp and Vlissingen. The percentage of sterile females decreased in all locations during the study period. These results show that the TBT ban has positive effects on the populations. The ban has also negative effects such as an increased fuel coast due to the attachment of organisms on the hull of ships, the use of less effective antifouling paints (copper based) which need to be applied more often. It should also be considered, that copper might also be toxic at high concentrations. (See also here.) Therefore, using copper based antifouling paints instead of TBT might just replace one environmental problem by another.[1]


References

The main author of this article is Daphnis De Pooter
Please note that others may also have edited the contents of this article.

Citation: Daphnis De Pooter (2013): TBT and intersex in periwinkles. Available from http://www.coastalwiki.org/wiki/TBT_and_intersex_in_periwinkles [accessed on 29-03-2024]