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Combining submerged membrane technology with anaerobic and ...

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Introductionof water. Energy savings can be achieved by injecting air into the base of the vertical<strong>membrane</strong> modules, obtaining an airlift effect <strong>and</strong> avoiding the use of a pump (reaching1.2 kWh·m -3 of purified water).The first systems developed were small-scale <strong>and</strong> industrial scale applications,treating small volumes of wastewater streams <strong>with</strong> high organic loads. In any case,operational costs remained high, <strong>with</strong> special emphasis on the modules <strong>and</strong> the powerconsumption, limiting the competitiveness of the <strong>technology</strong> compared to conventionalprocesses.In the eighties started the development of filtration <strong>membrane</strong>s on a larger scale,especially on three fronts: North America, Japan <strong>and</strong> Europe. Many types of <strong>membrane</strong>swere then developed specifically for the food industry. Nevertheless, the ease <strong>with</strong> whichthe modules rupture occurred generated distrust <strong>and</strong> uncertainty.In the early nineties, the <strong>membrane</strong> modules were optimized, developing newmodels more robust <strong>and</strong> reliable. The Japanese government launched an ambitious R&Dproject which led to the most important technological <strong>and</strong> industrial advance of the MBRprocess, <strong>with</strong> the development of <strong>submerged</strong> <strong>membrane</strong> modules, resulting in the<strong>submerged</strong> MBR <strong>membrane</strong> (figure 1.5B). In these systems the <strong>membrane</strong> module is<strong>submerged</strong> in the aeration tank, in contact <strong>with</strong> the mixed liquor. Therefore it was possibleto suppress the pump that was used to drive the sludge <strong>and</strong> replace it for another pumpthat suck the filtered effluent or permeate from the <strong>membrane</strong> module. Thus there was asignificant reduction in investment <strong>and</strong> operation costs due to the reduction <strong>and</strong>simplification of equipment <strong>and</strong> energy saving was needed to pump the sludge. Energyconsumption associated <strong>with</strong> water treatment by <strong>submerged</strong> MBR is between 0.55-1.5kWh·m -3 depending on configuration <strong>and</strong> <strong>membrane</strong> <strong>technology</strong> (Judd, 2011) <strong>and</strong> is higherthan that observed in well operated CAS reactors (0.38 to 0.48 kWh·m -3 , Evans <strong>and</strong>Laughton, 1994). Similarly, the costs <strong>and</strong> the operational problems decreased, emergingnew markets as well as pharmaceutical <strong>and</strong> food industries.In most of the first <strong>submerged</strong> MBR <strong>membrane</strong> modules were installed in the sametank where the influent was received. However there is a tendency today to remove the<strong>membrane</strong> from the influent inlet using an additional chamber to immerse <strong>membrane</strong>modules. This external <strong>submerged</strong> MBR configuration (figure 1.5C) significantly reduces<strong>membrane</strong> fouling.35

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