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Membrane and Desalination Technologies - TCE Moodle Website

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<strong>Membrane</strong> Systems Planning <strong>and</strong> Design 347<br />

3. OPERATIONAL UNIT PROCESSES<br />

All membrane filtration systems have associated operational unit processes that are<br />

essential for maintaining <strong>and</strong> optimizing system performance <strong>and</strong> therefore critical to the<br />

successful implementation of the technology. These operational processes include:<br />

1. Pretreatment<br />

2. Backwashing<br />

3. Chemical cleaning<br />

4. Integrity testing<br />

5. Post-treatment<br />

3.1. Pretreatment<br />

Pretreatment is typically applied to the feed water prior to entering the membrane system<br />

in order to minimize membrane fouling, but in some cases may be used to address other water<br />

quality concerns or treatment objectives. Pretreatment is most often utilized to remove<br />

foulants, optimize recovery <strong>and</strong> system productivity, <strong>and</strong> extend membrane life. Pretreatment<br />

may also be used to prevent physical damage to the membranes. Different types of pretreatment<br />

can be used in conjunction with any given membrane filtration system, as determined by<br />

site-specific conditions <strong>and</strong> treatment objectives. Pilot testing can be used to compare various<br />

pretreatment options, optimize pretreatment, <strong>and</strong>/or demonstrate pretreatment performance.<br />

Several different types of commonly used pretreatment for membrane filtration systems are<br />

discussed in the following subsections.<br />

3.1.1. Prefiltration<br />

Prefiltration, including screening or coarse filtration, is a common means of pretreatment for<br />

membrane filtration systems that is designed to remove large particles <strong>and</strong> debris. Prefiltration<br />

can either be applied to the membrane filtration system as a whole or to each membrane unit<br />

separately. The particular pore size associated with the prefiltration process varies depending<br />

on the type of membrane filtration system <strong>and</strong> the feed water quality. For example, although<br />

hollow-fiber MF <strong>and</strong> UF systems are designed specifically to remove suspended solids, large<br />

particulate matter can damage or plug the membranes fibers. For these types of systems the<br />

pore size of the selected prefiltration process may range from as small as 100 mm to as large as<br />

3,000 mm orhigher(11, 12), depending on the influent water quality <strong>and</strong> manufacturer<br />

specifications. Generally, hollow-fiber MF/UF systems that are operated in an inside-out<br />

mode are more susceptible to fiber plugging <strong>and</strong> thus may require finer prefiltration.<br />

Because NF <strong>and</strong> RO utilize non-porous semipermeable membranes that cannot be backwashed<br />

<strong>and</strong> are almost exclusively designed in a spiral-wound configuration for municipal<br />

water treatment, these systems must utilize much finer prefiltration in order to minimize<br />

exposure of the membranes to particulate matter of any size. Spiral-wound modules are<br />

highly susceptible to particulate fouling, which can reduce system productivity, create<br />

operational problems, reduce membrane life, or in some cases damage or destroy the<br />

membranes. If the feed water has turbidity less than approximately 1 NTU or a silt density<br />

index (SDI) less than approximately 5, cartridge filters with a pore size range from about

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