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Special Issue Survey of Cetaceans in Captive Care

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6. Life Support Systems 357from coal, granulometry 0.8 to 1.6 mm) can helpremove additional dead organic matter and reduceturbidity. These filters are backwashed regularly toremove accumulated particles and ma<strong>in</strong>ta<strong>in</strong> filtrationcapacity. This is done after empty<strong>in</strong>g the tank<strong>of</strong> its water and revers<strong>in</strong>g the flow <strong>in</strong>side the tank.To <strong>in</strong>crease clean<strong>in</strong>g efficiency, the substrate canbe decompressed and agitated by air scour throughthe <strong>in</strong>jection <strong>of</strong> air from below. High-rate pressuresand filters do not susta<strong>in</strong> a stable microbial populationthat can act as a biological filter, althoughsome microorganisms might survive backwashesand help to break down dissolved substances <strong>in</strong> am<strong>in</strong>imal way. This is why a sterilisation processhas to be added to the mechanical filtration.Flocculation—Flocculation is a useful additionalprocess used <strong>in</strong> substrate filtration. A flocculantis used to coagulate small particles <strong>in</strong>tobigger ones—the flocs—which will be moreefficiently trapped <strong>in</strong> the filter<strong>in</strong>g substrate and,thus, reduce oxidant demand (Anonymous, 1999;Gregory, 1989; Spotte, 1991). The flocculant mostcommonly used is alum<strong>in</strong>ium sulphate or alum,but polyalum<strong>in</strong>ium chloride and ferric chlorideare also used. The flocculent and water should bemixed properly; thus, a mix<strong>in</strong>g chamber is recommended(Boness, 1996).Figure 6.4. Filters for large whale poolsProte<strong>in</strong> Skimmers/Foam Fractionators—Anothermechanical system to remove organic matter andreduce nitrogen compounds (e.g., ammonia, nitrite,nitrate)—a prote<strong>in</strong> skimmer or foam fractionator—is now commonly <strong>in</strong>stalled <strong>in</strong> mar<strong>in</strong>e mammalfacilities. This dispersed-air flotation system usuallyis comb<strong>in</strong>ed with an oxidis<strong>in</strong>g system; thus, italso could be presented <strong>in</strong> the “Chemical Filtration”section. The polluted water is mixed with an air/ozone mixture through an <strong>in</strong>jector and pumped <strong>in</strong>tothe reaction chamber. Here, vortex<strong>in</strong>g causes turbulenceand <strong>in</strong>timate mix<strong>in</strong>g <strong>of</strong> the water and airbubbles. Prote<strong>in</strong>s with a lower specific weight thanwater are the first to flow upwards through the <strong>in</strong>ternalriser. Solids become attached to gas bubblesalready loaded with prote<strong>in</strong>s and also flow upward.Pollutants are concentrated <strong>in</strong>to foam, which thenis skimmed, leav<strong>in</strong>g clean water to flow througha different outlet (Shuran Sea Water Equipment:Aquaflotor Technical Guide; van der Toorn, 1987).This system usually is <strong>in</strong>stalled as a complementto sand filters and is comb<strong>in</strong>ed with ozone asan alternative to other means <strong>of</strong> dis<strong>in</strong>fection orsterilisation.Figure 6.2. Steel tower sand filters (Photograph from I. Smit)Figure 6.3. Horizontal steel filtersFigure 6.5. Prote<strong>in</strong> skimmers with ozone <strong>in</strong>jection(Photograph from I. Smit)

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