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Advances in Water Treatment and Enviromental Management

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146 WATER TREATMENT2.4 Experimental FacilityThe measurements were conducted <strong>in</strong> a closed-circuit system with a volume V of 2m 3 of water (see Fig. 3). The flow is driven by two pumps with variable discharges Q wup to 0.070 m 3 /s, which is equivalent to a Reynolds number of 2.0.10 5 . The work<strong>in</strong>gcross-section, made of plexiglass, measured 2 m high with a diameter of 0.44 m. Auniform velocity distribution was obta<strong>in</strong>ed by an arrangement of screens <strong>in</strong> a diffuser.Freestream turbulence was found to be lower than 5% (= type T0). A variation <strong>in</strong>turbulence <strong>in</strong>tensity could be achieved by grids at the entrance of the cross-section.The size of the selected grid mesh is M=5 cm <strong>and</strong> the quadraticsl bars are b=1,5 cmper side (=grid type T1).Gas (Air) is <strong>in</strong>jected through 25 nozzles, positioned at each cross of the turbulencegrid (see Fig. 4). The gas flow rate <strong>in</strong> each nozzle can be controlled <strong>in</strong>dividually. Themass-transfer measurements have been carried out <strong>in</strong> co-current flow with anaverage volumetric void fraction,ß, <strong>in</strong> the range of 0 < ß < 10%.The cont<strong>in</strong>ous measurements of dissolved oxygen <strong>in</strong> the fluid were performed bymeans of membrane electrodes <strong>in</strong> accordance to the ASCE-St<strong>and</strong>ards [1].Determ<strong>in</strong>ation due to this dynamical method is permissible because of the relativeshort length of the column <strong>and</strong> the small f<strong>in</strong>eness ratio. The assumption of completemix<strong>in</strong>g is then justified. The air was analyzed before <strong>and</strong> after pass<strong>in</strong>g the bubblecolumn <strong>in</strong> an oxygen detector. Because of this method it is possible to carry out amass-balance of the system.Fig. 3: Cross-Section of the Bubble Column

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