5.1 Nanofiltration membrane characteristics and materials
3 min read•august 7, 2024
Nanofiltration membranes are key players in water treatment. They use size exclusion and charge interactions to remove dissolved solutes from liquids. With pore sizes between 0.5 to 2 nanometers, they can filter out smaller particles than other membrane types.
These membranes are made from various materials, with thin-film composites being the most common. Surface properties like are crucial for performance. Techniques like and can improve fouling resistance, making nanofiltration more effective for water purification.
Membrane Characteristics
Nanofiltration Membrane Properties
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Top images from around the web for Nanofiltration Membrane Properties
A durable thin-film nanofibrous composite nanofiltration membrane prepared by interfacial ... View original
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Performance and properties of coking nanofiltration concentrate treatment and membrane fouling ... View original
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Molecular engineering of high-performance nanofiltration membranes from intrinsically ... View original
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A durable thin-film nanofibrous composite nanofiltration membrane prepared by interfacial ... View original
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Performance and properties of coking nanofiltration concentrate treatment and membrane fouling ... View original
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Nanofiltration is a pressure-driven membrane separation process that removes dissolved solutes from water and other liquids
Pore size of nanofiltration membranes typically ranges from 0.5 to 2 nanometers (nm), allowing them to remove smaller particles and molecules compared to microfiltration and ultrafiltration membranes
Molecular weight cut-off (MWCO) is a measure of the smallest molecular weight solute that a membrane can reject with 90% efficiency, commonly ranging from 200 to 1000 Daltons (Da) for nanofiltration membranes
Charge enables nanofiltration membranes to preferentially remove ions based on their charge, with negatively charged membranes rejecting multivalent anions (sulfates, phosphates) and positively charged membranes rejecting multivalent cations (calcium, magnesium)
Rejection Mechanisms
Nanofiltration membranes combine size exclusion and charge interactions to achieve selective rejection of solutes
Size exclusion occurs when solutes larger than the membrane pores are physically prevented from passing through, while smaller solutes can permeate the membrane
is a charge-based rejection mechanism where the membrane repels similarly charged ions, enhancing the rejection of multivalent ions (calcium, magnesium, sulfates)
is another charge-based mechanism that arises from the interaction between ions and the polarization charges induced at the membrane-solution interface, further contributing to the rejection of charged solutes
Membrane Materials
Thin-Film Composite Membranes
Thin-film composite (TFC) membranes are the most widely used type of nanofiltration membranes, consisting of a thin selective layer on top of a porous support layer
The selective layer is typically made of , formed by interfacial polymerization of two monomers (m-phenylenediamine, trimesoyl chloride) on the surface of the porous support
The porous support layer provides mechanical stability and is usually made of or
TFC membranes offer high , selectivity, and stability, making them suitable for various nanofiltration applications (water softening, color removal, micropollutant removal)
Polymeric Materials
Polymeric materials are the primary choice for nanofiltration membranes due to their versatility, ease of fabrication, and cost-effectiveness
Polyamide is the most common selective layer material in TFC nanofiltration membranes, offering excellent salt rejection, chemical stability, and fouling resistance
is another polymeric material used in nanofiltration membranes, known for its hydrophilicity and chlorine tolerance
Other polymeric materials explored for nanofiltration membranes include polyethersulfone, , and , aiming to improve specific properties (permeability, selectivity, fouling resistance)
Surface Properties
Surface Modification Techniques
Surface modification techniques are employed to improve the performance and fouling resistance of nanofiltration membranes
Grafting involves covalently attaching functional groups or polymer chains onto the membrane surface to alter its properties (hydrophilicity, charge, fouling resistance)
Coating is another surface modification approach where a thin layer of material (polyvinyl alcohol, polyethylene glycol) is deposited onto the membrane surface to enhance its characteristics
uses ionized gas to modify the membrane surface chemistry and morphology, introducing functional groups and increasing surface roughness for improved fouling resistance
Hydrophilicity and Fouling Resistance
Hydrophilicity refers to the affinity of the membrane surface towards water, with more hydrophilic surfaces exhibiting better wettability and lower fouling propensity
Fouling resistance is a critical surface property that determines the membrane's ability to resist the accumulation of foulants (organic matter, inorganic scalants, microorganisms) on its surface
Increasing the surface hydrophilicity through surface modification techniques (grafting, coating, plasma treatment) can significantly enhance the fouling resistance of nanofiltration membranes
Hydrophilic surfaces form a hydration layer that prevents foulants from directly interacting with the membrane, reducing adsorption and facilitating foulant removal during cleaning processes