Aluminum slurry coatings to replace cadmium for aeronautic applications

Cadmium has been widely used as a coating to provide protection against galvanic corrosion for steels and for its natural lubricity on threaded applications. However, it is a toxic metal and a known carcinogenic agent, which is plated from an aqueous bath containing cyanide salts. For these reasons, the use of cadmium has been banned in Europe for most industrial applications. However, the aerospace industry is still exempt due to the stringent technical and safety requirements associated with aeronautical applications, as an acceptable replacement is yet to be found. Al slurry coatings have been developed as an alternative to replace cadmium coatings. The coatings were deposited on AISI 4340 steel and have been characterized by optical and electron microscopy. Testing included salt fog corrosion exposure, fluid corrosion exposure (immersion), humidity resistance, coating-substrate and paint-coating adhesion, electric conductivity, galvanic corrosion, embrittlement and fatigue. The results indicated that Al slurry coatings are an excellent alternative for Cd replacement.

Inorganic hydrophobic coatings: Surfaces mimicking the nature

Added value products are being developed in ceramic industry. Different optical effects as bright metallic shine or new functionalities as hydrophobicity or bactericide characteristics are the new properties searched on the tiles. In this study, we prepare glassy coatings for tiles based on copper pigment by a conventional industrial process. The obtained coatings present different aesthetical aspects, including bright metallic aspect which confers a high decorative value to the tile. Furthermore, these metallic coatings present hydrophobic properties with contact angles with water as high as 115 degrees and also bactericide characteristics. Superficial microstructure and nanoparticles were found in the bactericide-hydrophobic samples, resembling the surface of hydrophobic leaf surfaces. This structure was formed by the crystallization of CuO nanoparticles as Tenorite due to the copper saturation of the glassy matrix at the surface of the coatings.

Highly conductive coatings of carbon black/silica composites obtained by a sol-gel process

Conductive submicronic coatings of carbon black (CB)/silica composites have been prepared by a sol-gel process and deposited by spray-coating on glazed porcelain tiles. Stable CB dispersions with surfactant were rheologically characterized to determine the optimum CB-surfactant ratio. The composites were analyzed by Differential Thermal and Thermogravimetric Analysis and Hg-Porosimetry. Thin coatings were thermally treated in the temperature range of 300-500degC in air atmosphere. The microstructure of the coatings was determined by scanning electron microscopy and the structure evaluated by confocal Raman spectroscopy. The electrical characterization of the samples was carried out using dc intensity-voltage curves. The coatings exhibit good adhesion, high density and homogeneous distribution of the conductive filler (CB) in the insulate matrix (silica) that protects against the thermal degradation of the CB nanoparticles during the sintering process. As consequence, the composite coatings show the lowest resistivity values for CB-based films reported in the literature, with values of ~7times10 -5Omegam.

Quinine doped hybrid sol-gel coatings for wave guiding and optical applications

Pure and quinine doped silica coatings have been prepared over sodalime glasses. The coatings were consolidated at low temperature (range 60-180 A degrees C) preserving optical activity of quinine molecule. We designed a device to test the guiding properties of the coatings. We confirmed with this device that light injected in pure silica coatings is guided over distances of meters while quinine presence induces isotropic photoluminescence. With the combined use of both type of coatings, it is possible to design light guiding devices and illuminate regions in glass elements without electronic circuits.

Evaluación de efectos de biocidas contenidos en recubrimientos “antifouling “(AF coatings) en ecosistemas marinos

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.