Occurrence and environmental fate of Irgarol 1051, a new antifouling agent

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). ^

Novel antifouling and antimicrobial compound from a marine-derived fungus Ampelomyces sp.

In this study, using a bioassay-guided isolation and purification procedure, we obtained 3-chloro-2,5-dihydroxybenzyl alcohol from a marine-derived Ampelomyces species that effectively inhibited larval settlement of the tubeworm Hydroides elegans and of cyprids of the barnacle Balanus amphitrite. The inhibitive effect on larval settlement was nontoxic and the EC50 of 3-chloro-2,5-dihydroxybenzyl alcohol ranged from 3.19 mu g ml(-1) to 3.81 mu g ml(-1) while the LC50 was 266.68 lambda g ml(-1) for B. amphitrite cyprids; EC50 ranged from 0.67 mu g ml(-1) to 0.78 mu g ml(-1), and LC50 was 2.64 mu g ml(-1) for competent larvae of H. elegans, indicating that inhibitive effect of this compound was nontoxic. At a concentration of 50 mu g per disc, this compound showed strong inhibitive effects on the growth of 13 out of 15 marine bacterial species tested in disc diffusion bioassay. Overall, the high inhibitory activities against bacteria and larval settlement as well as the non- or low-toxic nature of this compound to the barnacle and polychaete larvae suggest this compound could be a potent antifoulant and/or antibiotic.

The effect of organotin and copper sulfate on the late development and presettlement behavior of the hard clam Mercenaria mercenaria

The effect of organotin compounds and copper, commonly used as antifouling agent, were studied on Mercenaria mercernaria larvae. They were reared under usual hatchery conditions until they reached 190 um in diameter. The larvae were subjected to four compounds, tributylin chloride (TBT), monobutyltin chloride (MBT), trimethyltin chloride (TMT), cupric sulfate (CuSo4) plus control. Mortality was measured at 24, 48 h, and 96h. Behavioral and/or metamorphic changes were recorded in triplicate at 24-48 and 96 h. The appearance in swimming larvae of a functional foot was considered a sign of competence to set and was recorded as a "pediveliger". Swimming larvae were considered as larvae that have not yet reached their total development and they were recorded as "swimming". Larvae that did not show foot or swimming activity and were static but alive on the bottom were recorded as "bottom". TBT was found to completely inhibit swimming activity at sublethal concentrations throughout the period of observation. Copper and MBT inhibited swimming from 48 h, TMT did not inhibit swimming activity at any of the times recorded. The four compounds ranked in order of decreasing toxicity were TBT>TMT>CU>MBT.

Avaliação da exposição de botos-cinza (Sotalia guianensis Van Benédén, 1864) aos compostos orgânicos de estanho através das concentrações hepáticas de estanho total na costa sudeste e sul do Brasil

Durante as últimas décadas, observou-se um aumento da preocupação em relação aos ecossistemas marinhos devido à grande entrada de poluentes, resultando em efeitos deletérios em organismos aquáticos e seres humanos. Dentre as atividades humanas que podem introduzir compostos tóxicos persistentes e bioacumulativos (PBTs Persistent Bioaccumulative Toxicants) no ambiente marinho está o uso de tintas antiincrustrantes, aplicadas nos cascos de navios para evitar que algas, mexilhões e outros organismos se fixem às embarcações. Não raramente, compostos organoestânicos (OTs) como o Tributilestanho (TBT) ou o Trifenilestanho (TPT) constituíam o princípio ativo de tal preparado. Devido à alta toxicidade desses compostos, a IMO (Organização Marítima Internacional) baniu totalmente o uso dos mesmos. Como os OTs são prontamente bioacumulados, elevadas concentrações de estanho total (SnT) vêm sendo encontradas em cetáceos (Mammalia, Cetacea). Os botos-cinza (Sotalia guianensis Van Beneden, 1864) ocupam elevados níveis tróficos e bioacumulam os PBTs aos quais estão expostos. Alguns autores relataram que o estanho hepático em cetáceos se encontra predominantemente na forma orgânica, visto que, na forma inorgânica tal metal é pobremente absorvido pela mucosa gastrintestinal, de forma que as concentrações hepáticas de SnT refletem o input antrópico de OTs. O presente estudo teve como principal objetivo, avaliar a exposição de botos-cinza aos OTs, através determinação das concentrações hepáticas de estanho total (SnT = orgânico + inorgânico), por Espectrometria de Absorção Atômica com Atomização em Forno de Grafite (GFAAS Graphite Furnace Atomic Absorption Spectrometry). Para tal, amostras de botos-cinza de diferentes áreas do litoral brasileiro, compreendendo a Região da Grande Vitória (GV), Baía de Guanabara (BG), Baía de Sepetiba (B.Sep), a Baía de Paranaguá (PR) e a Baía da Babitonga (SC), foram analisadas, visando comparar ambientes distintamente contaminados com OTs. Sendo assim, as concentrações hepáticas de SnT (em ng/g, peso seco) de botos-cinza variaram de <312 (limite de detecção) a 8.250, para a GV (n=22); de <312 a 14.100, para B.Sep (n = 38); <312 a 5.147, para PR (n= 22), bem como de 626 a 24.780 (ng/g, peso seco) para os botos de SC (n=10). As maiores concentrações foram verificadas nos botos da BG (n=11), variando de 1.265 a 24.882 (ng/g, peso seco). As concentrações encontradas na Baía de Guanabara (BG) estão entre as mais elevadas detectadas em cetáceos.

Eletroanálise e oxidação fotoeletrocatalítica dos disruptores endócrinos bisfenol A e nonilfenol sobre eletrodo de nanotubos de 'TI'/'TI''O IND.2' auto-organizados

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

IMPOSEX AS AN INDICATOR OF ORGANOTIN POLLUTION AT RIO DE JANEIRO SOUTH COAST: SEPETIBA AND ILHA GRANDE BAYS

Imposex is the development of male sexual characteristics, i.e., penis and/or vas deferens in females of dioecious gastropods. This phenomenon has been associated to the use of the organotin based marine antifouling paints and used worldwide as a bioindicator of pollution by the TBT (antifouling agent) as well as to evaluate the related ecological impact. This study reports imposex in Stramonita haemastoma at south coast of Rio de Janeiro State (Brazil), specifically at Sepetiba and Ilha Grande Bays. All the stations where snails were found have shown imposex. Ilha Grande Bay presented the highest values of imposex indices when compared to Sepetiba Bay. The results suggest that high concentration of shipping activities and coastal morphology are the principal causes at the most polluted sites.

Polyaniline as marine antifouling and corrosion-prevention agent

Conductive polyaniline was found to have special marine antifouling property. The coating from conducting polyaniline and epoxy resin(or polyurethane) can last 6-9 months in Southern China sea, i.e., less than 10% of the coating surface was fouled during this period. The conducting polyaniline has special synergetic antifouling effect on other antifouling agents like cuprous oxide or 4, 4'-dichlorodiphenyltrichloroethane. The conductivity of the polyaniline was found to be extremely important for its antifouling effect. Moreover, employing aliphatic polyamine as solvent of emeraldine base and curing agent of epoxy resin, a new technique to process corrosion prevention coating containing emeraldine base was developed, therefrom the emeraldine base and epoxy resin was in molecular level blending. This technique was solvent free and extremely effective, i.e., only 1wt% of emeraldine base in the coating can have good corrosion prevention property.