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Special Issue Survey of Cetaceans in Captive Care

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6. Life Support Systems 355al., 1999). Erysipelothrix rhusiopathiae is anotherpathogenic bacterium, which also is presumed to be<strong>in</strong> food. It causes erysipelas, which can be lethal <strong>in</strong>its septicemic form (Dunn, 1990; Sweeney, 1993).The ma<strong>in</strong> bacteria that is monitored is coliformbacteria, which can cause water contam<strong>in</strong>ation. Itcan be recognized, though, that pathogens could bepresent <strong>in</strong> mar<strong>in</strong>e mammal pools when coliformsare low <strong>in</strong> number or absent (Spotte, 1991). Faecalcoliform bacteria, Escherichia coli, is released <strong>in</strong>the water through dolph<strong>in</strong> faecal matter. A high concentration<strong>of</strong> E. coli can be harmful to animals and<strong>in</strong>dicates an unbalanced sterilisation system or waterexchange. Measurements are obta<strong>in</strong>ed by the MTF(Multiple Tube Fermentation) method. The concentrations<strong>of</strong> these bacteria is expressed <strong>in</strong> MPN (MostProbable Number). Another method called MF(Membrane Filtration) can be used and is expressed<strong>in</strong> number <strong>of</strong> colony-form<strong>in</strong>g units/100 ml <strong>of</strong> water(Spotte, 1991). Coliform count should be performedweekly (E. coli is the most significant <strong>of</strong> the familyEnterobacteriacae, which also <strong>in</strong>cludes most species<strong>of</strong> Citrobacter, Enterobacter, and Klebsiella)(Arkush, 2001; Spotte, 1991). Results above 100MPN require a correction <strong>of</strong> the sterilisation systemor an <strong>in</strong>crease <strong>in</strong> the chang<strong>in</strong>g <strong>of</strong> water (Sweeney &Samansky, 1995).A weekly count <strong>of</strong> total bacteria should beevaluated aga<strong>in</strong>st the historical norm <strong>of</strong> the location.If the tests <strong>in</strong>dicate a contam<strong>in</strong>ation, they willbe repeated and the source identified (Sweeney,1993).A water- and soil-borne bacterium, Burkholderiapseudomallei (formerly named Pseudomonaspseudomallei), endemic to Southeast Asia, but nowrecognized <strong>in</strong> humans and animals worldwide, canbe found <strong>in</strong> dolph<strong>in</strong>arium waters, especially afterheavy ra<strong>in</strong>s when soil is washed <strong>in</strong>to the pools. Itis responsible for a dangerous <strong>in</strong>fectious diseasecalled melioidosis, which is lethal <strong>in</strong> most cases(Liong et al., 1985; Reeves et al., 1994; Sweeney,1986). A vacc<strong>in</strong>e is now available for melioidosis(Kennedy-Stoskopf, 1990), but it is still recommendedthat the presence <strong>of</strong> this bacterium bemonitored closely <strong>in</strong> regions at risk.Where pools hold<strong>in</strong>g cetaceans have sandybottoms, regular <strong>in</strong>spections will be undertakento ensure that bottom sediments do not becomeanoxic (Anonymous, 1992b).AlgaeAlgae are s<strong>in</strong>gle-celled (e.g., phytoplankton) orsimple multi-celled (e.g., macrophyte or seaweed)organisms commonly found <strong>in</strong> surface water andproduce their own food through photosynthesis.Excessive algal growth may cause the water to haveundesirable odours or tastes, and decay <strong>of</strong> algaecan deplete the oxygen <strong>in</strong> the water (Anonymous,1999). Algal growth is favoured by warm temperatureand daylight Ultra-Violet (UV) rays (Sweeney& Samansky, 1995), and it occurs on all submergedsurfaces. It is not dangerous for the dolph<strong>in</strong>s, butit is unsightly—especially <strong>in</strong> concrete pools. Inpools and lagoons made <strong>of</strong> natural materials, thealgae only needs to be removed once <strong>in</strong> a while.Chlor<strong>in</strong>e, ozone, copper, biological filtration, andUV dis<strong>in</strong>fection can control algae.The follow<strong>in</strong>g table presents a summary <strong>of</strong>water tests that are carried out on a regular basisby many surveyed facilities. Sweeney (1993) recommendedkeep<strong>in</strong>g records on site for at leastthree years <strong>in</strong> a digital format.Table 6.2. Frequency and targeted range <strong>of</strong> water quality measurementsMeasurement Frequency RangeAir temperature 2 x day N/AWater temperature 2 x day see Cetacean Species Information TableSal<strong>in</strong>ity Daily 25-35 ‰pH Daily 8.2; if chlor<strong>in</strong>ation, 7.5-7.6Turbidity Daily £ 0.5 NTUDissolved oxygen Weekly 5.0-8.8 ppm DOColiform bacteria Weekly £ 100 MPN/100 ml; more frequent if > 200 MPN until level dropsbelow 100Total bacteria Weekly see historical norm <strong>of</strong> locationAmmonia Weekly £ 0.05 mg/l <strong>of</strong> waterNitriteNitrate Weekly £ 1 mg/l rapidly converted to nitrate£ 10 mg/lFree chlor<strong>in</strong>e 2-3 x day £ 0.2 ppmTotal chlor<strong>in</strong>e£ 0.5 ppmAlkal<strong>in</strong>ity Weekly 100-150 mg/l

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