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Membrane and Desalination Technologies - TCE Moodle Website

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Potable Water Biotechnology, <strong>Membrane</strong> Filtration <strong>and</strong> Biofiltration 479<br />

Size (µm) 0.0001 0.001 0.01 0.1 1.0 10 100<br />

Molecular weight<br />

(Daltons)<br />

200 20,000 200,000<br />

Drinking water<br />

Bacteria<br />

pathogens<br />

Giardia<br />

Cryptosporidium<br />

Viruses<br />

<strong>Membrane</strong> filtration<br />

process<br />

MCF<br />

MF<br />

Fig. 11.1. Comparison of membrane filtration applications in drinking water treatment process<br />

(adapted from (2)).<br />

2.2. <strong>Desalination</strong><br />

<strong>Desalination</strong> is the area of growth for membrane technology. Various types of membranes<br />

used for desalination include reverse osmosis, nanofiltration, <strong>and</strong> electrodialysis. Other<br />

techniques such as the distillation process, ion exchange, freezing, <strong>and</strong> other miscellaneous<br />

processes are also widely employed. Approximately 60% of the worldwide desalting capacity<br />

is attributable to distillation technologies (3). However, the percent of worldwide desalting<br />

capacity by membrane processes has been steadily increasing (4).<br />

To obtain drinking water from brackish water or seawater, the membrane system is a good<br />

alternative treatment method. A combination of ultrafiltration followed by reverse osmosis<br />

can be very cost effective. Ultrafiltration cartridges used as pretreatment can considerably<br />

extend the useful life of reverse osmosis elements. When treating brackish water with<br />

relatively low total dissolved solids (TDS), ultrafiltration can be used as pretreatment to<br />

reverse osmosis <strong>and</strong> to produce permeate for blending with reverse osmosis product water.<br />

The result is water for distribution that not only tastes good, but is less expensive to produce.<br />

2.3. Control of Disinfection By-Products<br />

Recently there has been a growing interest in employing membrane processes for removal<br />

of precursors to DBPs. The major precursor of DBPs is natural organic matter (NOM). NOM<br />

is normally derived from plant or microbial residues, or is produced in situ in water by life<br />

cycles <strong>and</strong> by a variety of decomposition pathways (5). NOM can be categorized into humic,<br />

microbial by-products, <strong>and</strong> colloidal natural organic matter, depending on their source <strong>and</strong><br />

characteristics. Microbial by-products are composed of acids, with a relatively high charge<br />

density, polysaccharides, amino sugars, <strong>and</strong> proteins. Humic material, normally found in<br />

surface water, consists of fulvic acid <strong>and</strong> humic acid. Fulvic acid has an average molar mass<br />

RO<br />

NF<br />

UF

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