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Titlebook: Biological Effects by Organotins; Toshihiro Horiguchi Book 2017 Springer Japan 2017 Organotin.Gastropod imposex.Molluscan endocrinology.Nu

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31#
發(fā)表于 2025-3-26 22:02:54 | 只看該作者
32#
發(fā)表于 2025-3-27 04:36:49 | 只看該作者
Organotins and Imposex in Europe: A Pre-ban and Post-ban Perspectiveated under the light of the 2003 European ban (Directive 2002/62/EC and Regulation 782/2003) and the AFS Convention (entered into force in 2008). The reduction of TBT pollution is addressed under the same light. Overall, we conclude that significant reductions in imposex levels started to emerge aft
33#
發(fā)表于 2025-3-27 08:06:32 | 只看該作者
34#
發(fā)表于 2025-3-27 09:33:05 | 只看該作者
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發(fā)表于 2025-3-27 15:00:40 | 只看該作者
36#
發(fā)表于 2025-3-27 20:23:53 | 只看該作者
Mode of Action of Organotins to Induce the Development of Imposex in Gastropods, Focusing on SteroidT interference with the release of penis morphogenetic/retrogressive factor from the pedal/cerebropleural ganglia; (5) an increase in the level of an alanine-proline-glycine-tryptophan amide (APGWamide) neuropeptide in response to TBT; and (6) activation of the retinoid X receptor (RXR). The latest
37#
發(fā)表于 2025-3-28 00:14:48 | 只看該作者
Reproductive Organ Development in the Ivory Shell , and the Rock Shell ,lia in imposex-exhibiting female rock shells, . (Muricidae), using specimens from a wild population and tributyltin (TBT)-exposed females in the laboratory, allowed observation of a variety of vas deferens morphogenesis patterns. Taking into consideration observed results both from wild female speci
38#
發(fā)表于 2025-3-28 05:25:04 | 只看該作者
Kinetics of Interface Reactionsn the environment. Decreasing the detection limit of methods without greatly compromising their sensitivity was a profound topic of environmental research for organotin analysis. In the case of analytical technique, from the late 1970s, the usage of titrometric and spectrophotometric methods were su
39#
發(fā)表于 2025-3-28 07:44:05 | 只看該作者
40#
發(fā)表于 2025-3-28 12:21:26 | 只看該作者
T. E. Madey,C. Benndorf,S. Semancik, <0.02–1,350?μg/kg dry, <0.04–150?μg/kg dry, <0.01–46.5?μg/kg dry, <0.1–688.2?μg/kg dry, <8–420?μg/kg dry, respectively. Irgarol 1051 was detected in the range of <0.1–35?μg/kg in clam, mussel, and oyster from Vietnam, Thailand, and Japan. The concentrations of diuron and sea nine 211 in bivalves w
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