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Team:Imperial/Water Filtration
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| - | These properties contribute to the filter’s flow rate, measured in units of fluid filtered per unit surface area of the filter per unit time (e.g. Ga m | + | These properties contribute to the filter’s flow rate, measured in units of fluid filtered per unit surface area of the filter per unit time (e.g. Ga m<sup>-2</sup> h<sup>-1</sup>). Altering the filter’s flow rate generally affects the filter’s efficiency at removing its targets, as increasing the flow rate typically involves increasing the pore size or reducing the surface area of the filter in contact with the fluid. This trade-off is the main hurdle in industrial water filtration, where demands for high-quality filtration require very low flow rates. Industrial processes are further complicated by blockage of the pores, fouling of the filter by organisms and the lack of a complete set of materials that will exhaustively filter all contaminants - heavy metal ions, small organic molecules and non-polar compounds remain difficult to filter without prior chemical treatments that themselves need to be filtered out. </p> |
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Revision as of 00:07, 18 October 2014
Water Filtration
Overview
By attaching functional proteins to cellulose we can expand it's properties and selectivity capture specific contaminants in water. We used five different cellulose binding domains and fused them to different metal binding proteins, and sfGFP. We performed assays to test the binding of the CBD fusions to our cellulose.
Key Achievements
- Made cellulose binding domains
Introduction
Water is typically purified by passing it through layers of porous materials, each specially selected for its ability to remove specific forms of contamination. All porous materials can filter particles by size, many have extra capabilities thanks to their chemical properties. For example, charcoal - or activated carbon - is a porous component of household and industrial water filters that can also bind large or electron-rich molecules via the van der Waals forces, and catalyse the breakdown of other chemicals such as molecular chlorine. While there are many different types of filters, we can categorise and compare them using their measurable physical and chemical properties. The key physical properties are:
- Pore size - average or maximum size of pores in the material
- Porosity - volume of the filter not occupied by solid material
- Tortuosity - length of paths through the filter compared with a straight line
- Adhesion - the strength of hydrogen bond interactions between the fluid and filter
- Kinetic rate constants - parameters defining how the filter material affects chemical reactions in the fluid
These properties contribute to the filter’s flow rate, measured in units of fluid filtered per unit surface area of the filter per unit time (e.g. Ga m-2 h-1). Altering the filter’s flow rate generally affects the filter’s efficiency at removing its targets, as increasing the flow rate typically involves increasing the pore size or reducing the surface area of the filter in contact with the fluid. This trade-off is the main hurdle in industrial water filtration, where demands for high-quality filtration require very low flow rates. Industrial processes are further complicated by blockage of the pores, fouling of the filter by organisms and the lack of a complete set of materials that will exhaustively filter all contaminants - heavy metal ions, small organic molecules and non-polar compounds remain difficult to filter without prior chemical treatments that themselves need to be filtered out.
Turbidity
Phytochelatin-dCBD metal binding assay
Nickel filtration assay
