Zooplankton of the open Baltic: Extended Atlas - IOW
Zooplankton of the open Baltic: Extended Atlas - IOW
Zooplankton of the open Baltic: Extended Atlas - IOW
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procedure <strong>of</strong> sample preparation is described in Gifford and Caron (2000),<br />
Strüder-Kypke et al. (2003).<br />
All fixatives do not necessarily preserve <strong>the</strong> cell shape and size <strong>of</strong> live<br />
specimens, it is important to note that fixatives shrink cells. So, investigators<br />
will use a conversion factor (for aloricate ciliates, which are preserved with<br />
2% Lugol's - 190 fg C µm -3 ) (Putt & Stoecker, 1989). Biomass <strong>of</strong> planktonic<br />
ciliates can be determined by multiplying <strong>the</strong> species abundance by <strong>the</strong><br />
individual mass <strong>of</strong> ciliates. Calculation <strong>of</strong> <strong>the</strong> volume and mass <strong>of</strong> <strong>the</strong> cell<br />
may be performed by establishing <strong>the</strong> similarity <strong>of</strong> <strong>the</strong> ciliate cell to different<br />
geometric figures.<br />
Additional methodological information on ciliates can be obtained from<br />
manuals for microzooplankton sampling, fixation, and staining (e.g. Gifford<br />
& Caron, 2000; Strüder-Kypke et al., 2003; http://www.liv.ac.uk/ciliate/<br />
intro.htm).<br />
3.4. Identification and counting <strong>of</strong> meso- and macrozooplankton<br />
Species identification and counting are <strong>the</strong> basis <strong>of</strong> any community<br />
analysis. These procedures are time-consuming and require considerable<br />
pr<strong>of</strong>essional experience. This fact <strong>of</strong>ten restricts <strong>the</strong> number <strong>of</strong> samples that<br />
can be analysed with an acceptable effort within a reasonable time span.<br />
Attempts to overcome <strong>the</strong>se difficulties by <strong>the</strong> automatic counting methods<br />
may help to solve <strong>the</strong> problem <strong>of</strong> under-sampling (Wiebe & Benfield, 2003).<br />
However, application <strong>of</strong> <strong>the</strong> automatic methods is limited to uniform samples<br />
(e.g. cultures in laboratories), to certain size-class specific analyses, or to a<br />
coarse separation <strong>of</strong> organisms from larger taxonomic groups with significant<br />
differences in general body morphology. Coupling <strong>of</strong> such procedures with<br />
computerised image analysis may be helpful; however, it is still linked with<br />
sophisticated technical equipment and a need <strong>of</strong> special s<strong>of</strong>tware.<br />
Routinely, for monitoring purposes counting is performed for <strong>the</strong><br />
dominant organisms from easily identifiable taxonomic groups, and <strong>the</strong>ir<br />
developmental stages. More taxonomic skills are required for <strong>the</strong><br />
identification <strong>of</strong> certain species. The species names should be used according<br />
to <strong>the</strong> International Code <strong>of</strong> Zoological Nomenclature (http://www.iczn.org).<br />
Information on <strong>the</strong> validity <strong>of</strong> names and actual taxonomic classification can<br />
be given, for example, after <strong>the</strong> Integrated Taxonomic Information System<br />
(http://www.itis.gov) and The European Register <strong>of</strong> Marine Species<br />
(http://www.marbef.org/data/erms.php).<br />
The laboratory procedure <strong>of</strong> sorting mesozooplankton starts with<br />
removing <strong>the</strong> carcinogenic formalin from <strong>the</strong> sample by its filtration through<br />
meshes smaller than <strong>the</strong> mesh size <strong>of</strong> <strong>the</strong> sampling gear. The filtrated<br />
preservative is used again after <strong>the</strong> analysis for any fur<strong>the</strong>r storage. The<br />
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