Filtre à eau

Résumé

Un filtre à eau est composé d'un système de filtration qui vise à séparer l'eau des particules solides (résidus) en la faisant passer à travers un milieu poreux, ce qui ne laisse passer que les liquides et les particules solides plus fines que les trous du filtre (porosité). L'eau qui ressort de ce système de filtration est débarrassée des particules solides plus grosses que les pores du filtre. Certains filtres à eau sont prévus pour rendre l'eau potable (filtration très fine, inférieure à la taille d'un microbe). Certains filtres sont portables pour pouvoir être utilisés lors de randonnées pour produire de l'eau potable à partir du liquide prélevé dans les cours d'eau, ou pour adoucir l'eau (ex : carafe filtrante). Les différents types de filtres à eau existants sont nombreux et plus ou moins onéreux, les filtres à eau les plus performants sont les filtres à eau sous évier, qui filtre à l'aide de cartouche de filtration, qui sont souvent peu chère et facile d'utilisation. L'eau t

Source officielle

https://fr.wikipedia.org/wiki/Filtre_%C3%A0_eau

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Since a few decades our planet has been loaded with billion tons of synthetic polymer-based materials, commonly named plastics. The large scale of plastic production, associated with its limited recyclability, are the driving force for the accumulation of such materials into the environment. Garbage patches, i.e. islands of plastics in the ocean, are striking evidences of this issue. A sustainable handling, that is production and disposal, of synthetic polymer-based materials is one of the greatest challenges that humanity has to face.Proteins and nucleic acids are natural polymers. Arguably, Nature produces an amount of such polymers that is higher with respect to man-made polymers. However, these materials do not accumulate into the environment, that is the approach used by Nature to handle these polymers is sustainable. The secret for its sustainaibility lies on the circularity in the materialsâ use. Indeed, proteins and nucleic acids are sequence-defined polymers that undergo depolymerization to monomers, and recycling into new materials by reassembling the so obtained monomers into arbitrarily different sequences. Organisms digest proteins into amino acids. These monomers are in turn polymerized to produce the protein of need, at the time of the protein synthesis.In this thesis we show that this process is achievable outside living organisms. Indeed, we depolymerized structurally different short peptides, and peptides mixtures into their constitutive amino acids, and recycled such monomers into biotechnologically relevant proteins (green, and red fluorescent proteins), by using an amino acid-free cell-free transcription-translation system. We further applied our methodology to recycle proteins with high relevance in materials engineering such as Î²-lactoglobulin films, used for water filtration, or silk fibroin solutions into green fluorescent protein. We were also successful in recycling mixtures composed of short peptides, and technologically relevant proteins into fluorescent proteins, as well as into bioactive enzymes (catechol 2,3-dioxygenase). Finally, we achieved multiple cycles of recycling (two cycles), and we demonstrated that the strategy can be expanded beyond the set of the twenty proteinogenic amino acids.Presented herein is a nature-inspired approach to recycling of soft materials, where unknown mixtures of polymers are recycled into the polymer of need, by the local community, at the time of recycling. The materials are costantly transformed into different ones, without any external feed, and there is no way to distinguish a new polymer from a recycled one. The strength of this method lies in its compatibility with the principles of circular economy.

EPFL2021

Chargement

Surface modification of PES virus filtration membrane

Claire Roulin

Virus filtration by size exclusion is a robust means of eliminating viruses in blood or pharma products. Porous polymer membranes with a narrow size distribution are used to allow passage of the protein product but retain viruses. The chosen polymer must resist process-induced physical and chemical wear and is therefore generally inert and hydrophobic material. When filtrating potentially heterogeneous products such as IgG from pooled blood samples, protein adsorption on the polymer surface causes high fouling. This eventually blocks the filter and reduces total filtration volume. A solution to this adsorption problem is to graft a hydrophilic gel-like polymer layer on the membrane inner surface to reduce protein adsorption. The surface properties are thus changed while retaining the stability of the bulk polymer. The grafting was initiated with an electron beam, which creates free radicals by unspecific scission of the polymer backbone through electron irradiation. Two acrylate monomers were used for polymerization, a monofunctional monomer and a bifunctional one, used as a crosslinker to form the gel structure. Two different grafting method were tested. The first grafting method is simultaneous grafting, where the membrane is impregnated with the monomer solution then irradiated. Initiation and polymerization thus occur almost simultaneously. The grafted membrane properties were assessed using flow measurements, protein adsorption tests, FTIR absorbance measurements, virus retention tests and filter integrity tests. Comparing the various grafting approaches, it can be seen that simultaneous grafting lowers considerably protein adsorption, to the price of a highly reduced buffer flow. These filters therefore run slowly but can process more volume before fouling. The sequential grafting method using peroxides as initiators did not show significant filtration improvements compared to the reference membrane when the solution with monomer and crosslinker was used. However, when only monofunctional monomer was used for peroxidation grafting, the protein filtration capacity was increased with limited buffer flow loss. Generally, the sequential method is interesting for graft polymerization of porous membranes because it allows higher degree of grafting and the versatile grafting parameters involved give many development options depending on the application

2010

Chargement

A luminescent bacterial biosensor was used to quantify bioavailable arsenic in artificial groundwater. Its light production above the background emission was proportional to the arsenite concentration in the toxicologically relevant range of 0 to 0.5 mu M. Effects of the inorganic solutes phosphate, Fe(II) and silicate on the biosensor signal were studied. Phosphate at a concentration of 0.25 g L-1 phosphate slightly stimulated the light emission, but much less than toxicologically relevant concentrations of the much stronger inducer arsenite. No effect of phosphate was oberved in the presence of arsenite. Freshly prepared sodium silicate solution at a concentration of 10 g L-1 Si reduced the arsenite-induced light production by roughly 37%, which can be explained by transient polymerization leading to sequestration of some arsenic. After three days of incubation, silicate did not have this effect anymore, probably because depolymerization occurred. In the presence of 0.4 g L-1 Fe(II), the arsenite-induced light emission was reduced by up to 90%, probably due to iron oxidation followed by arsenite adsorption on the less soluble Fe(III) possibly along with some oxidation to the stronger adsorbing As(V). Addition of 100 mu M EDTA was capable of releasing all arsenic from the precipitate and to transform it into the biologically measurable, dissolved state. The biosensor also proved valuable for monitoring the effectiveness of an arsenic removal procedure based on water filtration through a mixture of sand and iron granules.

Springer Verlag2005

Chargement

EPFL2021

Surface modification of PES virus filtration membrane

Claire Roulin

2010