63 resultados para antifouling
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The bioassay guided purification of the octocoral Eunicea laciniata organic extract, collected at Santa Marta bay, Colombia, allowed the isolation of the new compound (-)-3β-pregna-5,20-dienyl-β-D-arabinopyranoside (1), along with the known compounds 1(S*),11(R*)-dolabell-3(E),7(E),12(18)-triene (2), 13-keto-1(S),11(R)-dolabell-3(E ),7(E),12(18)-triene (3), cholest- 5,22-dien-3β-ol (4), cholesterol (5), y brassicasterol (6). The structure and absolute configuration of 1 was determined on based spectroscopic analyses (NMR and CD). The extract showed antifouling activity against five strains of marine bacteria associated to heavy fouled surfaces. Also showed activity against the cypris of the cosmopolitan barnacle Balanus amphitrite, and low toxicity in Artemia salina test.
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The pollutants discharged into the estuaries are originate from two main sources-industrial and sewage. The former may be toxic which includes heavy metals, residues from antifouling paint particles and pesticides, while large discharges of sewage will contain pathogenic microorganisms. The contamination is enough to destroy the amenities of the waterfront, and the toxic substances may completely destroy the marine life and damage to birds, fishes and other marine organisms. Antifouling biocides are a type of chemical used in marine structure to prevent biofouling. These antifouling biocides gradually leach from the ships and other marine structures into water and finally settled in sediments. Once a saturation adsorption is reached they desorbed into overlying water and causes threat to marine organisms. Previous reports explained the imposex and shell thickening in bivalves owing to the effect of biocides. So bivalves are used as indicator organisms to understand the status of pollution. The nervous system is one of the best body part to understand the effect of toxicant. Acetylcholine esterase enzyme which is the main neurotransmitter in nervous was used to understand the effect of pollutants. Present study uses Acetylcholine esterase enzyme as pollution monitoring indicator
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Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
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De entre los diversos grupos de contaminantes que pueden ser dañinos para ecosistemas acuáticos, sobresalen en los últimos años los biocidas utilizados como principio activo en recubrimientos antifouling ó pinturas anti-incrustantes para cascos de barcos y todo tipo de equipamiento sumergido ó en contacto con agua. Estos recubrimientos se aplican como sistema de protección para combatir la formación y asentamiento de comunidades bioincrustantes (fouling) frente a superficies expuestas al agua, también tienen como finalidad proteger frente a la corrosión de tipo químico y biológico. Normalmente estas pinturas anti-incrustantes son aplicadas en embarcaciones comerciales y de recreo, plataformas petrolíferas, tuberías submarinas, compuertas de presas, instalaciones destinadas a acuicultura, entre otro equipamiento. La utilización de biocidas en la formulación de pinturas anti-incrustantes para barcos ha sido propuesta por muchos investigadores como la aplicación de más impacto para los ecosistemas marinos, debido al intenso tráfico marítimo mundial que provoca la difusión de biocidas contaminantes en los mares, sobre todo en zonas costeras, bahías y puertos que es donde se magnifica el problema. Los llamados recubrimientos antifouling de segunda generación fueron los primeros que emplearon el tributilestaño (TBT) como principio activo en su formulación, a pesar de su gran eficacia y amplia utilización, al cabo del tiempo se ha demostrado su alta toxicidad y persistencia; por lo que existe una gran actividad investigadora en la búsqueda de alternativas asimismo eficientes pero más respetuosas con el medio marino. En este trabajo se pretende comparar los efectos para ecosistemas marinos del TBT y cinco biocidas como son dibutilestaño dicloruro, diuron (diclorofenil dimetil urea), piritionato de Zn ó Zn omadine, óxido de cobre (I) y DCOIT (Dicloro-2-n-octil-4-isotiazol-3-ona). Estos biocidas se han seleccionado en función de su naturaleza química diferenciada, distintas solubilidades en agua, eficacia, ecotoxicidad, persistencia y bioacumulación fundamentalmente. Para proceder a la clasificación del riesgo para ecosistema marino de los biocidas mencionados, nos valdremos de dos metodologías, una será la evaluación de unos índices de riesgo de biocidas para ecosistemas acuáticos con el fin de realizar una clasificación prospectiva de los mismos, basada en criterios PBT (Persistencia, Bioacumulación y Toxicidad para organismos acuáticos) y otra será una evaluación de la razón de la EXPOSICIÓN, valorada como PEC (Predictive Environmental Concentration) con relación a los EFECTOS originados, valorados como PNEC (Predicted No-Effect Concentration). Para cuantificar PEC nos valdremos de modelizaciones para ecosistemas marinos como MAMPEC (Marine Antifoulant Model to Predict Environmental Concentrations). Para cuantificar PNEC se hace uso de bioensayos a corto o largo plazo en organismos acuáticos. De esta manera podremos agrupar los biocidas en diversas categorías de riesgo y así poder decidir cuando su impacto medioambiental es asumible ó no asumible, alternativas posibles y en todo caso que decisiones se deben tomar al respecto.
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The purpose of this study is to characterize the degradation products of Irgarol 1051(2-methylthio-4-tertbutylamino-6-cyclopropylamino- s-triazine), a compound recently developed for use as an antifouling agent on boat hulls. The photolytic fate of this compound in different natural waters will be used in the development of a monitoring program designed to survey the occurrence of this compound and its degradation products in South Florida marinas, the Miami River and surrounding coastal areas. ^ The transformation of Irgarol 1051 and degradation rate constants were characterized in a photo-reactor under simulated natural conditions. The degradation pathway in the UVB-UVA region (300nm to 350nm) closely resembled the transformations under natural conditions in the pond, showing that both direct photolysis and the presence of natural sensitizers play an important role in the abiotic transformation of this compound. Irgarol 1051 has an average environmental half-life of 10 days in surface waters. Average concentrations from samples around Biscayne Bay and the Miami River increased from 1–5 ng/L during 1999 and increased to between 28 and 38 ng/L in 2001, respectively. Irgarol concentrations showed a strong correlation with concentrations of its major transformation product, M1, from samples collected as part of the study ([M1]/[Irgarol] = 0.247, R2 = 0.9165, n = 125). ^
Natural antifouling compound production by microbes associated with marine macroorganisms — A review
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In the marine environment, all hard surfaces including marine macroorganims are colonized by microorganisms mainly from the surrounding environment. The microorganisms associated with marine macroorganisms offer tremendous potential for exploitation of bioactive metabolites. Biofouling is a continuous problem in marine sectors which needs huge economy for control and cleaning processes. Biotechnological way for searching natural product antifouling compounds gained momentum in recent years because of the environmental pollution associated with the use of toxic chemicals to control biofouling. While, natural product based antifoulants from marine organisms particularly sponges and corals attained significance due to their activities in field assays, collection of larger amount of organisms from the sea is not a viable one. The microorganisms associated with sponges, corals, ascidians, seaweeds and seagrasses showed strong antimicrobial and also antifouling activities. This review highlights the advances in natural product antifoulants research from microbes associated with marine organisms.
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In the present study, embryotoxicity experiments using the sea urchin Lytechinus variegatus were carried out to better clarify the ecotoxicological effects of tributyltin (TBT) and triphenyltin (TPT) (the recently banned antifouling agents), and Irgarol and Diuron (two of the new commonly used booster biocides). Organisms were individually examined to evaluate the intensity and type of effects on embryo-larval development, this procedure has not been commonly used, however it showed to be a potentially suitable approach for toxicity assessment. NOEC and LOEC were similar for compounds of same chemical class, and IC10 values were very close and showed overlapping of confidence intervals between TBT and TPT, and between Diuron and Irgarol. In addition, IC10 were similar to NOEC values. Regardless of this, the observed effects were different. Embryo development was interrupted at the gastrula and blastula stages at 1.25 and 2.5 mu g l(-1) of TBT, respectively, whereas pluteus stage was reached with the corresponding concentrations of TPT. Furthermore, embryos reached the prism and morula stages at 5 mu g l(-1) of TPT and TBT, respectively. The effects induced by Irgarol were also more pronounced than those caused by Diuron. Pluteus stage was always reached at any tested Diuron concentration, while embryogenesis was interrupted at blastula/gastrula stages at the highest concentrations of Irgarol. Therefore, this study proposes a complementary approach for interpreting embryo-larval responses that may be employed together with the traditional way of analysis. Consequently, this application leads to a more powerful ecotoxicological assessment tool focused on embryotoxicity.