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Membrane and Desalination Technologies - TCE Moodle Website

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282 J. Paul Chen et al.<br />

solutions are prevented from diffusing through the membrane, but anions will get through until<br />

equilibrium is reached. For a cation-selective membrane, cations will diffuse through the membrane<br />

while anions will be retained. Potential difference is the driving force behind these<br />

separation processes. It is created by the displacement of the system from the equilibrium ratios,<br />

which can be controlled by adjusting solution concentrations. The application for ion exchange<br />

includes:<br />

l pH control without adding acid or base<br />

l Recovery of acids <strong>and</strong> bases from salts<br />

l Water softening<br />

4. <strong>Membrane</strong> bioreactor. <strong>Membrane</strong> bioreactor (MBR) can be defined as integration of conventional<br />

biological degradation <strong>and</strong> membrane separation into a single process where microorganisms<br />

responsible for biodegradation <strong>and</strong> suspended solids are separated from biologically treated water<br />

by a membrane filtration unit. The entire biomass is confined within the system, providing both<br />

perfect control of the sludge retention time for the microorganism in the bioreactor <strong>and</strong> physical<br />

disinfection of the effluent (12, 29, 30).<br />

As the MBR process does not need the secondary clarifier for the solid–liquid separation,<br />

it can prevent these “inherited” problems that occur in the conventional processes for the<br />

wastewater reclamation (30). The resulting high-quality <strong>and</strong> completely disinfected effluent<br />

means that the MBR process can be used for many purposes, that is, industrial <strong>and</strong> municipal<br />

wastewater treatment <strong>and</strong> reuse. More important, the l<strong>and</strong> requirement of MBR is much less<br />

than that of conventional wastewater reclamation processes.<br />

2.3. Case Studies on <strong>Membrane</strong> Applications in Water Treatment<br />

2.3.1. Case 1: <strong>Desalination</strong> of Seawater by RO<br />

<strong>Desalination</strong> of seawater is one of the important applications of membrane processes.<br />

There are various ways to produce freshwater such as distillation, electrodialysismembrane<br />

distillation, freezing, membrane bioreactor <strong>and</strong> reverse osmosis. Among them, distillation is<br />

the most used technique, but RO is becoming more popular in the desalination industry. A<br />

flow diagram of a single-stage RO system is shown in Fig. 7.4.<br />

To reduce fouling <strong>and</strong> protect membrane, pre-treatment must be performed for seawater.<br />

A pre-treatment system removes suspended solids <strong>and</strong> other potential fouling materials.<br />

Flocculation agents such as iron chloride or polyelectrolytes are added in order to remove<br />

suspended solids. Chlorine is added to remove bacteria <strong>and</strong> algae.<br />

The water quality is determined by membrane materials <strong>and</strong> configurations. Cellulose<br />

acetate membranes can be degraded by the formation of biological slimes on the membrane<br />

surface, while polyamide membranes cannot tolerate chlorine. Thus, sodium hydrogen<br />

sulphite is normally needed to remove chlorine in the water. Operation at higher temperatures<br />

<strong>and</strong> pressures can cause the compaction of the membrane layer <strong>and</strong> thus reduce output. A<br />

stagnant boundary layer at the membrane surface can cause concentration polarization of<br />

salts, increasing the chance of precipitation <strong>and</strong> reducing output (26, 27). The operating brine<br />

concentration, pressure <strong>and</strong> water conversion factor need to be selected to limit both<br />

compaction <strong>and</strong> concentration polarization effects.

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