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Membrane and Desalination Technologies - TCE Moodle Website

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Treatment of Food Industry Foods <strong>and</strong> Wastes by <strong>Membrane</strong> Filtration 243<br />

MF membranes are made of a wide range of inorganic materials (such as alumina,<br />

zirconia–carbon composites, carbon–carbon composites, ceramics, stainless steel, silica,<br />

etc.) <strong>and</strong> natural <strong>and</strong> synthetic polymers (such as polypropylene, polycarbonates, polysulfone,<br />

polyvinylchloride, PVC, copolymer – cellulose esters, cellulose acetate, etc.) (15–16).<br />

UF membranes are mainly made of polysulfone-type materials (such as polyether sulfone,<br />

polyphenylene sulfone, sulfonated polysulfone, etc.). This type of membranes is also available<br />

in a wide range of organic materials (such as PVC copolymer, cellulose acetate, etc.) <strong>and</strong><br />

inorganic materials (such as ceramic composites, stainless steel, etc.).<br />

Most NF membranes are multiple-layer thin-film composites of synthetic polymers. The<br />

active NF membrane layer usually consists of negatively charged chemical groups. NF<br />

membranes are of porous filter media with an average pore diameter of 2 nm. The nominal<br />

molecular weight cutoff ranges from 100 to 200. The active NF membrane layer can be made<br />

of polyamide, polyvinyl alcohol, sulfonated polysulfone, <strong>and</strong> sulfonated polyethersulfone.<br />

Salt rejection by NF membranes is mainly due to electrostatic interaction between the ions<br />

<strong>and</strong> the NF membrane. Rejection of neutral substances is by size (17).<br />

CA <strong>and</strong> derivatives are widely used as the RO membranes, despite their real <strong>and</strong> perceived<br />

limitations. Thin-film composite membranes containing a polyamide separating barrier on a<br />

polysulfone or polyethylene supporting layer, generally give better performance for RO<br />

applications with regard to temperature <strong>and</strong> pH stability <strong>and</strong> cleanability, but have almost<br />

zero chlorine resistance. In general, these thin-film composite membranes will be the material<br />

of choice for RO applications, unless there is a specific fouling problem with these membranes.<br />

The membranes of UF, NF, <strong>and</strong> RO have been tried for ED with various results. The use of<br />

ionic membranes (18) in ED <strong>and</strong> EDR processes has been applied as illustrated in Fig. 6.3.<br />

Table 6.2 shows the special features of four types of membrane systems: tubular membrane<br />

modules, hollow-fiber membrane modules, plate membrane modules <strong>and</strong> spiral-wound<br />

membrane modules (14). Each design has its own special applications, advantages, <strong>and</strong><br />

disadvantages.<br />

The large-bore tubular membrane modules (Fig. 6.4) are suitable for food streams with<br />

high concentration of suspended solids, such as citrus juices <strong>and</strong> animal waste streams, even<br />

Table 6.2<br />

Special features of membrane equipment<br />

Tubular Hollow fibers Plates Spiral<br />

Channel height (mm) >10

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