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Membrane and Desalination Technologies - TCE Moodle Website

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<strong>Membrane</strong> Systems Planning <strong>and</strong> Design 337<br />

These types of questions should be considered as a part of the screening process before<br />

selecting any membrane filtration systems to pilot. An additional consideration for MF/UF<br />

systems is that because these systems are proprietary, the membrane modules vary in design<br />

<strong>and</strong> are not presently interchangeable. Thus, a utility is limited to obtaining replacement<br />

membranes from only one supplier after a system has been installed.<br />

In some cases, screening tools for MF/UF membranes may be limited to experience at<br />

other sites or chemical incompatibility. Therefore, pilot testing is an important consideration.<br />

For NF/RO, proprietary software programs that are available from the various membrane<br />

manufacturers can predict membrane system removal performance with a fairly good degree<br />

of accuracy for a particular membrane product. Small-scale module testing may be an option<br />

for screening some MF/UF membranes. Similarly, NF/RO membranes could be screened for<br />

some parameters using flat-sheet studies or single element tests.<br />

2.1.3. Scheduling<br />

Scheduling is another important aspect of pilot test planning. One factor to consider when<br />

scheduling a pilot test for surface waters is seasonal variations in water quality, since<br />

turbidity, temperature, algae content, taste <strong>and</strong> odor, <strong>and</strong> other parameters can potentially<br />

vary significantly throughout the year. A description of typical seasonal variation in surface<br />

water quality is summarized below (1). Note that not all of the seasonal variations described<br />

will be applicable for every site, or necessarily pertinent for all types of membrane filtration<br />

systems.<br />

Summer: Because user dem<strong>and</strong> is typically highest in the summer, the filtration system<br />

may also have to produce more water during this season. However, greater production is<br />

facilitated by warmer water temperature. The degree to which a membrane process is affected<br />

by a change in water temperature is related to the viscosity of the water. Since the viscosity of<br />

the water is lower at higher temperatures, the membrane flux will likely be at its peak in this<br />

season. Warmer water also facilitates enhanced algal growth that may be problematic for<br />

membrane system operation. Taste <strong>and</strong> odor events may also manifest during the summer<br />

months.<br />

Autumn: In areas with hardwood cover in the watershed, autumn months typically bring an<br />

increase in the organic content of surface water resulting from the decay of fallen leaves.<br />

Turbidity may sharply increase, as well. Furthermore, cooler air temperatures <strong>and</strong> wind cause<br />

surface waters in reservoirs to “turnover,” bringing deeper, more anaerobic water to the<br />

surface <strong>and</strong> thus creating the potential for both taste <strong>and</strong> odor, <strong>and</strong> iron <strong>and</strong> manganese<br />

problems.<br />

Winter: Although winter months yield the coldest water temperatures <strong>and</strong> thus typically<br />

the lowest membrane fluxes, the dem<strong>and</strong> for water is typically at its lowest, as well. Both the<br />

cold temperature <strong>and</strong> decrease in dem<strong>and</strong> are likely to minimize required membrane flux in<br />

this season. Most membrane manufacturers have membrane-specific temperature compensation<br />

factors for cold-water operations.<br />

Spring: Spring months usually yield increases in water temperature, as well as in the<br />

potential for turbidity spikes related to run-off caused from snow melt. There is also potential

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