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A Methods Manual for the Collection, Preparation and Analysis of ...

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depending on <strong>the</strong> period <strong>of</strong> exposure prior to sampling, <strong>the</strong> flora may not represent a‘climax’ community,<strong>the</strong> smooth surfaces <strong>of</strong> some artificial substrata <strong>of</strong>ten lead to ‘sloughing <strong>of</strong>f’ <strong>of</strong> <strong>the</strong> diatomfilm.substrata are <strong>of</strong>ten lost, removed or v<strong>and</strong>alised if <strong>the</strong> substratum is not fixed in position.An appropriate method <strong>and</strong> apparatus needs to be devised <strong>for</strong> each site.artificial substrata need to be immersed in <strong>the</strong> river <strong>for</strong> at least four weeks be<strong>for</strong>esampling (although this period is dependent on <strong>the</strong> trophic status <strong>of</strong> <strong>the</strong> water). Thiscauses a delay in <strong>the</strong> availability <strong>of</strong> data, as well as adding to <strong>the</strong> cost <strong>of</strong> <strong>the</strong> monitoringprogram as transport costs to <strong>and</strong> from <strong>the</strong> site in question are doubled.Fur<strong>the</strong>r in<strong>for</strong>mation about <strong>the</strong> use <strong>and</strong> application <strong>of</strong> artificial substrata can be found inCattaneo <strong>and</strong> Amireault (1992), Gold et al (2002) <strong>and</strong> Lane et al. (2003).2. Sampling <strong>for</strong> aquatic bio-diversity studiesAll <strong>the</strong> methods mentioned in this manual can be used <strong>for</strong> sampling diatoms from differenthabitats <strong>for</strong> biodiversity studies. However, certain techniques are less suitable when samplingdiatoms to infer water quality. Phytoplankton drifts downstream <strong>and</strong> thus is not as stable orreliable as <strong>the</strong> phytobenthos if an indication <strong>of</strong> a water quality impact at a specific point isrequired.2.1 Cobbles <strong>and</strong> small boulders (rocks)See section 1.1.2.2 Phytobenthos (“Floatation method” <strong>for</strong> epipsammon <strong>and</strong> epipelon)The epipsammon <strong>and</strong> epipelon are components <strong>of</strong> <strong>the</strong> phytobenthos <strong>and</strong> yield very diverseassemblages <strong>of</strong> usually motile diatoms. However, <strong>the</strong> “floatation method” discussed belowdoes not allow <strong>for</strong> <strong>the</strong> inclusion in <strong>the</strong> analysis <strong>of</strong> non-motile diatoms. The method has <strong>the</strong>considerable advantage <strong>of</strong> extracting <strong>the</strong> motile living fraction <strong>of</strong> <strong>the</strong> diatom community <strong>for</strong>subsequent analysis <strong>of</strong> <strong>the</strong> assemblage. Samples taken from <strong>the</strong> epilithon may contain manyattached <strong>and</strong> non-motile species which cannot be removed from <strong>the</strong> sample in <strong>the</strong> mannerbelow.2.3 Qualitative sampling <strong>of</strong> sedimentsThe common method, described by Round (1991) is to use 5 mm Ø glass tube about a meterlong or more attached (splinted) to a rod (e.g. a broomstick) <strong>for</strong> deeper water at <strong>the</strong> margin <strong>of</strong>a river.13

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