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Artykuły w czasopismach na temat "Tributyltin"
Stefanizzi, Valeria, Antonella Minutolo, Elena Valletta, Martina Carlini, Franca M. Cordero, Anna Ranzenigo, Salvatore Pasquale Prete i in. "Biological Evaluation of Triorganotin Derivatives as Potential Anticancer Agents". Molecules 28, nr 9 (2.05.2023): 3856. http://dx.doi.org/10.3390/molecules28093856.
Pełny tekst źródłaAlzieu, Claude. "Tributyltin". Ocean & Coastal Management 40, nr 1 (lipiec 1998): 23–36. http://dx.doi.org/10.1016/s0964-5691(98)00036-2.
Pełny tekst źródłaMaguire, R. J. "Environmental Assessment of Tributyltin in Canada". Water Science and Technology 25, nr 11 (1.06.1992): 125–32. http://dx.doi.org/10.2166/wst.1992.0283.
Pełny tekst źródłaMaguire, R. James, i Richard J. Tkacz. "Concentration of Tributyltin in the Surface Microlayer of Natural Waters". Water Quality Research Journal 22, nr 2 (1.05.1987): 227–33. http://dx.doi.org/10.2166/wqrj.1987.017.
Pełny tekst źródłaNISHIKIMI, Akihiko, Yukimi KIRA, Emiko KASAHARA, Eisuke F. SATO, Tomoko KANNO, Kozo UTSUMI i Masayasu INOUE. "Tributyltin interacts with mitochondria and induces cytochrome c release". Biochemical Journal 356, nr 2 (24.05.2001): 621–26. http://dx.doi.org/10.1042/bj3560621.
Pełny tekst źródłaAmbrosini, Annarina, Enrico Bertoli, Giovanna Zolese i Fabio Tanfani. "Interaction of tributylin acetate and tributyltin chloride with dipalmitoyl phosphatidylcholine model membrane". Chemistry and Physics of Lipids 58, nr 1-2 (maj 1991): 73–80. http://dx.doi.org/10.1016/0009-3084(91)90113-p.
Pełny tekst źródłaJayanthi, Arumugam. "Tributyltin Hydride (Bu3SnH)". Synlett 2007, nr 1 (styczeń 2007): 0173–74. http://dx.doi.org/10.1055/s-2006-958426.
Pełny tekst źródłaSimmonds, Mark. "Tributyltin—new legislation". Oryx 21, nr 2 (kwiecień 1987): 113. http://dx.doi.org/10.1017/s0030605300026685.
Pełny tekst źródłaDarwish, Alla, i J. Michael Chong. "Synthesis of Hexabutylditin from Tributyltin Hydride and bis(Tributyltin)oxide". Synthetic Communications 34, nr 10 (31.12.2004): 1885–90. http://dx.doi.org/10.1081/scc-120034172.
Pełny tekst źródłaMimura, Haruo, Ryusei Sato, Yuichi Furuyama, Akira Taniike, Masahiro Yagi, Kazutoshi Yoshida i Akira Kitamura. "Adsorption of tributyltin by tributyltin resistant marine Pseudoalteromonas sp. cells". Marine Pollution Bulletin 57, nr 6-12 (styczeń 2008): 877–82. http://dx.doi.org/10.1016/j.marpolbul.2008.03.029.
Pełny tekst źródłaRozprawy doktorskie na temat "Tributyltin"
Miller, Cynthia Elizabeth. "Tributyltin resistance among freshwater sediment bacteria". The Ohio State University, 1993. http://rave.ohiolink.edu/etdc/view?acc_num=osu1346092511.
Pełny tekst źródłaUnger, Michael A. "Investigation of tributyltin: Water/sediment interactions". W&M ScholarWorks, 1988. https://scholarworks.wm.edu/etd/1539616885.
Pełny tekst źródłaBriscoe, Scott F. "Tributyltin : molecular approaches to an environmental problem". Thesis, McGill University, 2004. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=85133.
Pełny tekst źródłaBailey, Susan K. "Tributyltin (TBT) contamination in Scottish coastal waters". Thesis, Edinburgh Napier University, 1991. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.292212.
Pełny tekst źródłaDingle, Pope Nicholas. "The bioavailability of sediment-bound tributyltin (TBT)". Thesis, University of Plymouth, 1998. http://hdl.handle.net/10026.1/2606.
Pełny tekst źródłaCruz, Andreia Sofia Henriques. "Tributyltin (TBT) resistance in Aeromonas molluscorum Av27". Doctoral thesis, Universidade de Aveiro, 2012. http://hdl.handle.net/10773/9545.
Pełny tekst źródłaO tributilestanho (TBT) é considerado um dos xenobióticos mais tóxicos, produzidos e deliberadamente introduzidos no meio ambiente pelo Homem. Tem sido usado numa variedade de processos industriais e subsequentemente descarregado no meio ambiente. O tempo de meia-vida do TBT em águas marinhas é de várias semanas, mas em condições de anóxia nos sedimentos, pode ser de vários anos, devido à sua degradação mais lenta. Embora o TBT tenha sido descrito como sendo tóxico para eucariotas e procariotas, muitas bactérias podem ser resistentes a este composto. O presente trabalho teve como objetivo principal elucidar o mecanismo de resistência ao TBT em bactérias. Para além disso, pretendeu-se desenvolver um biorepórter para detectar TBT no ambiente. Para atingir estes objetivos foram delineadas várias tarefas cujos principais resultados obtidos se apresentam a seguir. Várias bactérias resistentes ao TBT foram isoladas de sedimento e água do Porto de Pesca Longínqua (PPL) na Ria de Aveiro, Portugal. Entre estas, Aeromonas molluscorum Av27 foi selecionada devido à sua elevada resistência a este composto (concentrações até 3 mM), à sua capacidade de degradar o TBT em compostos menos tóxicos (dibutilestanho, DBT e monobutilestanho, MBT) e também por usar o TBT como fonte de carbono. A. molluscorum Av27 foi caracterizada genotipica e fenotipicamente. Os fatores de virulência estudados mostraram que esta estirpe i) possui atividade lipolítica; ii) não é citotóxica para células de mamíferos, nomeadamente para células Vero; iii) não possui integrões de classe I e II e iv) possui cinco plasmídeos com aproximadamente 4 kb, 7 kb, 10 kb, 100 kb e mais de 100 kb. Estes resultados mostraram que a estirpe Av27 não é tóxica, aumentando assim o interesse nesta bactéria para futuras aplicações, nomeadamente na bioremediação. Os testes de toxicidade ao TBT mostraram que este composto tem um impacto negativo no crescimento desta estirpe, bem como, na densidade, no tamanho e na atividade metabólica das células e é responsável pela formação de agregados celulares. Assim, o TBT mostrou ser bastante tóxico para as bactérias interferindo com a atividade celular geral. O gene Av27-sugE, que codifica a proteína SugE pertencente à família das “small multidrug resistance proteins” (SMR), foi identificado como estando envolvido na resistência ao TBT nesta estirpe. Este gene mostrou ser sobreexpresso quando as células crescem na presença de TBT. O promotor do gene Av27-sugE foi utilizado para construir um bioreporter para detetar TBT, contendo o gene da luciferase do pirilampo como gene repórter. O biorepórter obtido reúne as características mais importantes de um bom biorepórter: sensibilidade (intervalo de limite de detecção de 1-1000 nM), rapidez (3 h são suficientes para a deteção de sinal) e, possivelmente, não é invasivo (pois foi construído numa bactéria ambiental). Usando sedimento recolhido no Porto de Pesca Longínqua da Ria de Aveiro, foi preparada uma experiência de microcosmos com o intuito de avaliar a capacidade de Av27 para bioremediar o TBT, isoladamente ou em associação com a comunidade bacteriana indígena. A análise das amostras de microcosmos por PCR-DGGE e de bibliotecas de 16S rDNA revelaram que a comunidade bacteriana é relativamente estável ao longo do tempo, mesmo quando Av27 é inoculada no sedimento. Para além disso, o sedimento estuarino demonstrou ser dominado por bactérias pertencentes ao filo Proteobacteria (sendo mais abundante as Delta e Gammaproteobacteria) e Bacteroidetes. Ainda, cerca de 13% dos clones bacterianos não revelaram nenhuma semelhança com qualquer dos filos já definidos e quase 100% afiliou com bactérias não cultiváveis do sedimento. No momento da conclusão desta tese, os resultados da análise química de compostos organoestânicos não estavam disponíveis, e por essa razão não foi possível tirar quaisquer conclusões sobre a capacidade desta bactéria remediar o TBT em sedimentos. Esses resultados irão ajudar a esclarecer o papel de A. molluscorum Av27 na remediação de TBT. Recentemente, a capacidade da estirpe Av27 remediar solo contaminado com TBT foi confirmada em bioensaios realizados com plantas, Brassica rapa e Triticum aestivum (Silva 2011a), e também com invertebrados Porcellionides pruinosus (Silva 2011B). Assim, poder-se-á esperar que a bioremediação do sedimento na experiência de microcosmos também tenha ocorrido. No entanto, só a análise química dos compostos organostânicos deverá ser conclusiva. Devido à dificuldade em realizar a análise analítica de organoestânicos, um método de bioensaio fácil, rápido e barato foi adaptado para avaliar a toxicidade do TBT em laboratório, antes de se proceder à análise química das amostras. O método provou a sua utilidade, embora tenha mostrado pouca sensibilidade quando se usam concentrações de TBT baixas. Em geral, os resultados obtidos contribuíram para um melhor entendimento do mecanismo de resistência ao TBT em bactérias e mostraram o potencial biotecnológico de A. molluscorum Av27, nomeadamente, no que refere à sua possível aplicação na descontaminação de TBT no ambiente e também no desenvolvimento de biorepórteres.
Tributyltin (TBT) is considered as one of the most toxic xenobiotics, ever produced and deliberately introduced into the environment by Man. It has been used in a variety of industrial processes and subsequently discharged into the environment. The typical half-life of TBT in marine waters is of several weeks, but in deeper anoxic sediments it may be of several years, due to its slower degradation. Although TBT has been reported to be toxic to both eukaryotes and prokaryotes, bacteria can be resistant to this compound. In the present work a major goal was outlined: to elucidate the TBT resistance mechanism in bacteria. Additionally, it was also an objective developing a bioreporter to detect TBT in the environment. For this purpose a number of tasks were delineated and the main results obtained are bellow described. Several resistant bacteria were isolated from sediment and water at Porto de Pesca Longínqua (PPL) site in Ria de Aveiro, Portugal. Among those, Aeromonas molluscorum Av27 was selected due to its high resistance to TBT (up to 3 mM), its ability to degrade this compound into less toxic compounds (dibutyltin, DBT and monobutyltin, MBT) and also because it uses TBT as carbon source. A. molluscorum Av27 was genotypically and phenotypically characterized. The virulence factors studied showed that Av27 strain: i) has lipolytic activity; ii) is not cytotoxic for mammal cells, namely Vero cells; iii) does not have class I and II integrons and iv) possesses five plasmids with approximately 4 kbp, 7 kbp, 10 kbp, 100 kbp and more than 100 kbp. These results demonstrated that Av27 strain is not toxic, increasing the interest on this bacterium for future applications, namely bioremediation. Different growth parameters were studied revealing that a temperature of 25°C, a salinity range from 1 to 4% and a pH between 6 and 9 were the optimal growth conditions to Av27 strain. Regarding the antibiotic resistance profile, A. molluscorum Av27 is resistant to penicillin (10 μg), amoxicillin/clavulanic acid (30 μg) and cephalothin (30 μg) and also to the vibriostatic agent O/129; moreover, Av27 strain uses various compounds as carbon and energy source. TBT toxicity tests showed that this compound has a negative impact on bacterial growth, cell density, cell size and metabolic activity and promoted the formation of cell aggregates. Thus, TBT was found to be very toxic for this bacterium interfering with general cell activity. A gene, Av27-sugE, encoding the SugE protein belonging to the small multidrug resistance (SMR) proteins family was identified to be involved in the TBT resistance in this strain. This gene showed to be over-expressed when cells grow in the presence of TBT. Based on the Av27-sugE putative promoter, a bioreporter for TBT was constructed, containing the firefly luciferase as the reporter gene. The obtained bioreporter gathers the most important characteristics of a good bioreporter: sensitivity (detection limit range from 1-1000 nM), fastness (3 h for signal detection) and possibly non-invasive (it was constructed in an environmental bacterium). A microcosm experiment using estuarine sediment from PPL, Ria de Aveiro, was established to evaluate the ability of Av27 to bioremediate TBT, alone or in association with the indigenous bacterial community. PCR-DGGE and 16S rDNA libraries analysis of the microcosm samples revealed that the bacterial community is relatively stable over time, even when Av27 is inoculated in the sediment. Additionally, the estuarine sediment demonstrated to be dominated by bacteria belonging to the phyla Proteobacteria (among the most abundant Delta and Gammaproteobacteria) and Bacteroidetes. Moreover, about 13% of the bacterial clones showed no similarity to any of the phyla already defined and almost 100% affiliated with unculturable sediment bacteria. At the time of conclusion of this thesis, the results of organotin compounds chemical analysis were not available; therefore it was not possible to draw any conclusions about the TBT remediation in microcosm. Those results will help clarify the role of A. molluscorum Av27 in the remediation of TBT. Recently the ability of Av27 strain to remediate soil contaminated with TBT was confirmed in bioassays performed with plants, Brassica rapa and Triticum aestivum (Silva 2011a) and also invertebrates Porcellionides pruinosus (Silva 2011b). Thus it could also be expected that bioremediation of the sediment from the microcosm experiment has also occurred. Still only the organotin chemical analysis shall be conclusive. Due to the difficulty in performing analytical analysis, an easy, rapid, and inexpensive bioassay method was adapted to monitor TBT toxicity in the laboratory, prior to chemical analysis. The method proved its usefulness albeit showing low sensitivity when low TBT concentrations are used. Overall, the results obtained contributed to the elucidation of TBT resistance in bacteria and revealed the biotechnological potential of A. molluscorum Av27, namely in its possible application to decontaminating TBT in the natural environment and also in the development of bioreporters.
Barros, Ana Rodrigues. "Tributyltin (TBT) effects at a vascular level". Master's thesis, Universidade de Aveiro, 2016. http://hdl.handle.net/10773/16393.
Pełny tekst źródłaOrganotins are an important class man made organometallic compounds and tributyltin (TBT) is one of the most studied chemicals within this class. TBT is a potent endocrine disruptor being also considered as an obesogenic, immunotoxic and neurotoxic compound. Humans were exposed to this and other organotin compounds as a consequence of their widespread commercial applications including plastic stabilizers, catalytic agents and industrial biocides. Their utilization as catalytic agents in the production of silicones leads to the presence of these chemicals in silicone based products including those used in biomedical applications such as breast implants and cardiac valves which may constitute a potential source of exposure. According to the World Health Organization cardiovascular diseases are sharply increasing and constitute the prime cause of death globally. Taking this into account, regulatory agencies, recommend the study of organotin compounds toxicity. Considering the limited number of studies on the cardiovascular effects of organotins, the present thesis aims to elucidate the effects of TBT at the vascular level. The study of TBT effect on the contractility of rat artery (aorta) was performed by the organ bath technique and the L-type calcium channels in A7r5 (cell line derived from the smooth muscle of embryonic rat aorta) was measured by whole-cell configuration of the patch clamp technique. The obtained results demonstrated that TBT seems to relax the rat aorta without endothelium contracted by noradrenaline and potassium chloride but this effect is not significantly different from the respectively ethanol control. The electrophysiological experiments demonstrated that the inhibition of the calcium current by the L-type calcium channels in the A7r5 vascular smooth muscle cells was also not significantly different, which suggests that probably the mode of action of TBT is more complex and involves other pathways.
Os compostos orgânicos de estanho são uma importante classe de compostos organometálicos produzidos pelo homem, e o tributilestanho (TBT) é um dos químicos mais estudados dentro desta classe. O TBT atua como um potente disruptor endócrino, sendo também considerado como um composto obesogénico, imunotóxico e neurotóxico. A exposição humana a este e outros compostos orgânicos de estanho deve-se à sua vasta utilização em aplicações comerciais como estabilizadores de plásticos, agentes catalíticos e biocidas industriais. A sua utilização como agentes catalíticos na produção de silicones faz com que estes compostos estejam presentes em vários produtos à base de silicone, incluindo os usados em aplicações biomédicas como implantes mamários e válvulas cardíacas, o que pode constituir uma fonte potencial de exposição para os humanos. De acordo com a Organização Mundial de Saúde, as doenças cardiovasculares estão a aumentar e são consideradas como a principal causa de morte a nível mundial. Tendo isto em conta, as agências reguladoras recomendam o estudo da toxicidade dos compostos orgânicos de estanho. Considerando o número limitado de estudos sobre os efeitos cardiovasculares dos compostos orgânicos de estanho, o presente trabalho pretende elucidar os efeitos do TBT ao nível vascular. Os efeitos do TBT na contractilidade de artérias de rato (aorta) foram estudados pela técnica do banho de órgãos e a medição dos canais de cálcio tipo L foi realizada em A7r5 (linha celular de músculo liso vascular derivada de aorta embrionária de rato) através da técnica do patch clamp na configuração whole cell. Os resultados obtidos demonstram que o TBT parece induzir relaxamento nas artérias sem endotélio contraídas previamente com noradrenalina e com cloreto de potássio, mas esse efeito não é significativamente diferente do controlo de solvente usado. Nas experiências de eletrofisiologia a inibição das correntes de cálcio através dos canais de cálcio tipo L nas células A7r5 também não mostrou ser significativamente diferente do controlo, o que parece demonstrar que o modo de ação pelo qual o TBT induz efeito nas células vasculares é mais complexo e envolve outras vias.
Gkenakou, Evgenia-Varvara. "The remediation of tributyltin-contaminated dredgings and waters". Thesis, University of Southampton, 2008. https://eprints.soton.ac.uk/67188/.
Pełny tekst źródłaSutton, Benjamin Josiah. "Intramolecular radical additions to pyridines, quinolines and isoquinolines". Thesis, University of Southampton, 2003. https://eprints.soton.ac.uk/426728/.
Pełny tekst źródłaSakultantimetha, Arthit. "Enhancement of tributyltin biodegradation for sustainable remediation of the environment". Thesis, University of Strathclyde, 2010. http://oleg.lib.strath.ac.uk:80/R/?func=dbin-jump-full&object_id=14442.
Pełny tekst źródłaKsiążki na temat "Tributyltin"
Dr, Benson Robert, World Health Organization, International Program on Chemical Safety. i Inter-Organization Programme for the Sound Management of Chemicals., red. Tributyltin oxide. Geneva: World Health Organization, 1999.
Znajdź pełny tekst źródłaEbdon, L. The variation of tributyltin levels with time in selected estuaries prior to the introduction of regulations governing the use of tributyltin-based anti-fouling paints. Amsterdam: Elsevier Scientific Publsihing, 1988.
Znajdź pełny tekst źródłaJ, De Mora S., red. Tributyltin: Case study of an environmental contaminant. Cambridge: Cambridge University Press, 1996.
Znajdź pełny tekst źródłaLund, M. A. The disposal of tributyltin wastes to landfill. [London]: Department of the Environment, Wastes Technical Division, 1991.
Znajdź pełny tekst źródłaUnited States. Congress. Senate. Committee on Environment and Public Works. Subcommittee on Environmental Protection. The effects of the chemical tributyltin (TBT) on the marine environment: Hearing before the Subcommittee on Environmental Protection of the Committee on Environment and Public Works, United States Senate, One hundredth Congress, first session, April 29, 1987. Washington: U.S. G.P.O., 1987.
Znajdź pełny tekst źródłaWisconsin--Superior, University of, United States. Environmental Protection Agency. Health and Ecological Criteria Division, Environmental Research Laboratory (Duluth, Minn.), Environmental Research Laboratory (Narragansett, R.I.), United States. Environmental Protection Agency. Office of Water i Great Lakes Environmental Center (Traverse City, Mich.), red. Ambient aquatic life water quality criteria for tributyltin: Draft. [Washington, D.C.]: U.S. Environmental Protection Agency, Office of Water, 1997.
Znajdź pełny tekst źródłaWisconsin--Superior, University of, Great Lakes Environmental Center, United States. Environmental Protection Agency. Health and Ecological Criteria Division., Environmental Research Laboratory (Duluth, Minn.), Environmental Research Laboratory (Narragansett, R.I.) i United States. Environmental Protection Agency. Office of Water., red. Ambient aquatic life water quality criteria for tributyltin: Draft. [Washington, D.C.]: U.S. Environmental Protection Agency, Office of Water, 1997.
Znajdź pełny tekst źródłaW, Hall Lenwood, i Maryland. Chesapeake Bay Research and Monitoring Division., red. Butyltin and copper monitoring in a northern Chesapeake Bay marina and river system in 1989: An assessment of tributyltin legislation. Queenstown, Md: University of Maryland, Agricultural Experiment Station, Wye Research and Education Center, 1990.
Znajdź pełny tekst źródłaMeador, James Parnell. Determination of a tissue and sediment threshold for tributyltin (TBT) to protect prey species of juvenile salmonids listed under the Endangered Species Act. [Seattle, Wash.]: U.S. Dept. of Commerce, National Oceanic and Atmospheric Administration, National Marine Fisheries Service, 2001.
Znajdź pełny tekst źródłaIrish, J. M. Industrial uses of tributyltin oxide and the resultant water quality implications. Birmingham: Tame Division, Severn-Trent Water Authority, 1986.
Znajdź pełny tekst źródłaCzęści książek na temat "Tributyltin"
Treichel, Paul M., Marvin H. Tegen i Stephen A. Koch. "(Benzenethiolato) Tributyltin". W Inorganic Syntheses, 114–15. Hoboken, NJ, USA: John Wiley & Sons, Inc., 2007. http://dx.doi.org/10.1002/9780470132562.ch25.
Pełny tekst źródłaUnger, M. A., R. J. Huggett i W. G. MacIntyre. "Sorption Behavior of Tributyltin". W Organotin, 475–83. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_23.
Pełny tekst źródłaMaguire, R. James. "Tributyltin in Canadian Waters". W Organotin, 535–51. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_26.
Pełny tekst źródłaLee, Richard F. "Metabolism of Tributyltin by Aquatic Organisms". W Organotin, 369–82. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_18.
Pełny tekst źródłaLaughlin, Roy B., John Thain, Brad Davidson, Aldis O. Valkirs i Frederick C. Newton. "Experimental Studies of Chronic Toxicity of Tributyltin Compounds". W Organotin, 191–217. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_10.
Pełny tekst źródłaSeligman, P. F., R. J. Maguire, R. F. Lee, K. R. Hinga, A. O. Valkirs i P. M. Stang. "Persistence and Fate of Tributyltin in Aquatic Ecosystems". W Organotin, 429–57. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_21.
Pełny tekst źródłaHuggett, R. J., D. A. Evan, W. G. MacIntyre, M. A. Unger, P. F. Seligman i L. W. Hall. "Tributyltin Concentration in Waters of the Chesapeake Bay". W Organotin, 485–501. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_24.
Pełny tekst źródłaHuggett, R. J., F. A. Espourteille, C. D. Rice, M. A. Unger, C. A. Dooley i S. Y. Cola. "Analytical Methods for Tributyltin in Sediments and Tissues". W Organotin, 135–41. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_7.
Pełny tekst źródłaSchatzberg, Paul. "Measurement and Significance of the Release Rate for Tributyltin". W Organotin, 383–403. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_19.
Pełny tekst źródłaSeligman, P. F., C. M. Adema, J. Grovhoug, R. L. Fransham, A. O. Valkirs, M. O. Stallard i P. M. Stang. "Environmental Loading of Tributyltin from Drydocks and Ship Hulls". W Organotin, 405–27. Dordrecht: Springer Netherlands, 1996. http://dx.doi.org/10.1007/978-94-009-1507-7_20.
Pełny tekst źródłaStreszczenia konferencji na temat "Tributyltin"
Lee, R., A. Valkirs i P. Seligman. "Fate of Tributyltin in Estuarine Waters". W OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160625.
Pełny tekst źródłaSalazar, M., i S. Salazar. "Tributyltin Effects on Juvenile Mussel Growth". W OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160641.
Pełny tekst źródłaChamp, M., i W. Pugh. "Tributyltin Antifouling Paints: Introduction and Overview". W OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160644.
Pełny tekst źródłaOlson, G., i F. Brinckman. "Biodegradation of Tributyltin by Chesapeake Bay Microorganisms". W OCEANS '86. IEEE, 1986. http://dx.doi.org/10.1109/oceans.1986.1160369.
Pełny tekst źródłaLee, R. "Metabolism of Bis(Tributyltin)Oxide by Estuarine Animals". W OCEANS '86. IEEE, 1986. http://dx.doi.org/10.1109/oceans.1986.1160361.
Pełny tekst źródłaSeligman, P., A. Valkirs i R. Lee. "Degradation of Tributyltin in Marine and Estuarine Waters". W OCEANS '86. IEEE, 1986. http://dx.doi.org/10.1109/oceans.1986.1160366.
Pełny tekst źródłaBushong, S., W. Hall, W. Johnson i L. Hall. "Toxicity of Tributyltin to Selected Chesapeake Bay Biota". W OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160658.
Pełny tekst źródłaLaughlin, R. "Bioaccumulation of Tributyltin: The Link Between Environment and Organism". W OCEANS '86. IEEE, 1986. http://dx.doi.org/10.1109/oceans.1986.1160346.
Pełny tekst źródłaDavies, I., J. Drinkwater, J. McKie i P. Balls. "Effects of the Use of Tributyltin Antifoulants in Mariculture". W OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160629.
Pełny tekst źródłaUnger, M., W. Maclntyre i R. Huggett. "Equilibrium Sorption of Tributyltin Chloride by Chesapeake Bay Sediments". W OCEANS '87. IEEE, 1987. http://dx.doi.org/10.1109/oceans.1987.1160653.
Pełny tekst źródłaRaporty organizacyjne na temat "Tributyltin"
Blair, W. R., G. J. Olson, T. K. Trout, K. L. Jewett i F. E. Brinckman. Accumulation and fate of tributyltin species in microbial biofilms. Gaithersburg, MD: National Bureau of Standards, 1988. http://dx.doi.org/10.6028/nist.ir.88-3852.
Pełny tekst źródłaKotterman, M. J. J. Waterbodem immobilisatieonderzoek Noordzeekanaal: fase 2 : Binding van dioxines, tributyltin en PAKs aan actief kool. IJmuiden: Wageningen Marine Research, 2021. http://dx.doi.org/10.18174/543912.
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