Section 3: Mechanisms of toxicity and cell injuryUptake and transformation of 14C-labelled tributyltin chloride by the dog-whelk, nucella lapillus: Importance of absorption from the diet
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Modified, optimized method of determination of Tributyltin (TBT) contamination in coastal water, sediment and biota in Sri Lanka
2021, Marine Pollution BulletinCitation Excerpt :No information about TBT contamination in the coastal environment in Sri Lanka is documented to date. The most obvious routes of organotin exposure to biota and consequently to the food chain is through the diet and accumulation from surroundings (Kucuksezgin et al., 2011; Lee et al., 2006; Strand and Jacobsen, 2005; Bryan et al., 1989). However, with the rapid economic progress in Sri Lanka as a developing country, a set of restrictive environment quality standards for chemical pollutants is a timely requirement.
Extended imposex monitoring in N Atlantic Spain confirms punctual attainment of European environmental objectives for TBT
2018, Marine Pollution BulletinDeclines in TBT contamination in Irish coastal waters 1987-2011, using the dogwhelk (Nucella lapillus) as a biological indicator
2015, Marine Pollution BulletinCitation Excerpt :Spence et al. (1990) noted that at RPSI levels of < 5%, sterile females were absent generally, whilst at RPSI > 40% most, and sometimes all, females were sterile. Bryan et al. (1989) suggested there was a RPSI limit of 20–25% above which the reproduction of the female would be affected. This investigation documents imposex data compiled from 1987 to 2010/2011 and reports on temporal trends at selected locations, establishing the current imposex status around the Irish coast.
Tributyltin pollution biomonitoring under the Water Framework Directive: Proposal of a multi-species tool to assess the ecological quality status of EU water bodies
2015, Ecological IndicatorsCitation Excerpt :Possible changes may be due to differences in TBT bioavailability in several environmental compartments. For instance, while the dog-whelk seems to accumulate TBT mostly from water, with an estimated interference of less than 50% from its feeding habits (Bryan et al., 1989), other TBT exposure routes seem to be more relevant on the netted-whelk, with food uptake accounting for more than 50% of TBT body burden (Stroben et al., 1992a,b) and with contamination also possibly arising from the direct contact with TBT in interstitial water, subjected to adsorption/desorption processes from the sediments. As a result, different TBT accumulation may eventually occur between pre- and post-ban periods producing biased intercalibrations of VDSI/ISI.