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Membrane and Desalination Technologies - TCE Moodle Website

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580 J.P. Chen et al.<br />

l up to 40% humic substances,<br />

l low inorganic content, <strong>and</strong><br />

l high microbiological counts including bacteria <strong>and</strong> fungi.<br />

Biofouling is perhaps the most difficult fouling threat to overcome. No system operator can<br />

afford to ignore the potential for biofouling. Biological organisms include bacteria, algae, <strong>and</strong><br />

fungi. Of these, bacteria cause the majority of problems in membrane treatment systems for a<br />

variety of reasons. Many bacteria can easily adapt to the environment inside the membrane<br />

treatment system. With the organic compounds concentrated on the membrane surface, the<br />

bacteria multiply rapidly <strong>and</strong> are rejected by the membrane. These bacteria have a number of<br />

defense mechanisms. For example, some have fimbriae, which stick out from all sides of the<br />

cell. These allow the bacteria to attach themselves, <strong>and</strong> remain attached, to the surface of the<br />

membrane or feed space. In addition, bacteria may secrete a mucous capsule, or slime, which<br />

coats the cell <strong>and</strong> protects them from any harsh elements entering their environment.<br />

The susceptibility of membranes to biological fouling is significantly dependent on the<br />

membrane composition. CA membranes are easily attacked by bacteria. Disinfection of feed<br />

water is required for such membranes. PA membranes are also susceptible to bacterial attack,<br />

but TFC membranes are generally quite resistant. Chlorination can be used for CA membranes,<br />

but must be followed by dechlorination for PA <strong>and</strong> other membranes, usually by the<br />

addition of sodium metabisulfate. In ultrapure water production, sterility is often maintained<br />

by ultraviolet (UV) sterilizers (41).<br />

A recent study has shown that some RO membranes are more prone to biofouling than<br />

others. The study involved a bioadhesion assay which utilizes a model bacterium, SW 8,<br />

known to adhere to membranes. Examination of the bacteria adhered to the membranes using<br />

optical microscopy revealed that membranes that are less susceptible to bioadhesion are<br />

hydrophilic in nature (39). Further investigation carried out on RO simulators that consisted<br />

of flat sheet membranes to simulate spiral-wound module revealed biofilm characteristics<br />

under field emission scanning electron microscope. Microorganisms covered the surface of<br />

all types of RO membranes used in the experiment to a density of about 2.25 10 8 cells/cm 2<br />

(39). Bacteria of different shapes (mostly rod shaped) with dimensions between 1 <strong>and</strong> 3 mm<br />

were observed. The organisms appeared to excrete extracellular polymeric substances (EPS).<br />

Underst<strong>and</strong>ing membrane fouling creates the foundation for researchers to devise an<br />

approach to counter or minimize fouling in order to maintain high RO performance. One<br />

strategy to alleviate membrane fouling is feed pretreatment to reduce or remove fouling<br />

constituents in the feed. A proper membrane cleaning <strong>and</strong> regeneration protocol to remove<br />

foulants periodically from the membrane surface is also essential in maximizing RO<br />

efficiency.<br />

4.2. Feed Pretreatment<br />

The success of RO process is highly dependent on appropriate feed pretreatment. Pretreatment<br />

must be effective in reducing RO fouling potential in a reliable <strong>and</strong> consistent manner.<br />

Feed pretreatment continues to be extensively studied. In the development of a pretreatment<br />

program, the focus is on removing as many fouling constituents in the feed water as possible

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