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Report on Harmonisation of freshwater biological methods

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enthic algae in the reach, but results may not be sensitive to subtle water qualitychanges because <strong>of</strong> habitat variability between reaches. Species compositi<strong>on</strong> <strong>of</strong>assemblages from a single habitat potentially reflect water quality differences betweenstreams more precisely than multihabitat sampling, but impacts in other habitats in thereach may be missed (Barbour et al, 1999).16. The sampling frequency for phytobenthos m<strong>on</strong>itoring varies from annually inFrance, every 3 years in Austria and 4 years in Romania.17. Barbour et al. (1999) recommended that single habitat sampling should be usedwhen biomass <strong>of</strong> periphyt<strong>on</strong> is assessed. In other circumstances the use <strong>of</strong>multihabitat sampling may be more appropriated. The <strong>on</strong>ly references for biomassquantificati<strong>on</strong> relate to the assessment method developed by Norway, which isperformed in a single substratum, in riffle c<strong>on</strong>diti<strong>on</strong>s.18. The level <strong>of</strong> tax<strong>on</strong>omic resoluti<strong>on</strong> used in the assessment methodologies based inphytobenthos is the species or species groups. Only Slovenia uses a higher tax<strong>on</strong>omiclevel, which varies from species to family or higher tax<strong>on</strong>omic level. Forphytobenthos most <strong>of</strong> the indices require species-level identificati<strong>on</strong>, although somecan be used with genera, or a mixture <strong>of</strong> genera and species. Some taxa are difficult toidentify and in these cases the taxa have been pooled into “paired taxa”.19. Despite the complexity <strong>of</strong> diatoms identificati<strong>on</strong>, this is costly and timec<strong>on</strong>suming process and hence, the lowest tax<strong>on</strong>omic level is <strong>of</strong>ten preferable,providing a better ecological resoluti<strong>on</strong>, especially for definiti<strong>on</strong> <strong>of</strong> referencec<strong>on</strong>diti<strong>on</strong>s. This problem will be enhanced if the m<strong>on</strong>itoring programmes includediatoms and n<strong>on</strong>-diatoms groups.20. The identificati<strong>on</strong> process is based <strong>on</strong> a European Standard EN 14407 (2004)Water quality: Guidance standard for the identificati<strong>on</strong>, enumerati<strong>on</strong> andinterpretati<strong>on</strong> <strong>of</strong> benthic diatom samples from running water. This standardestablishes <strong>methods</strong> for identificati<strong>on</strong> and enumerati<strong>on</strong> <strong>of</strong> relative proporti<strong>on</strong>s <strong>of</strong>diatom taxa <strong>on</strong> prepared slides and <strong>of</strong> data interpretati<strong>on</strong> relevant to assessment <strong>of</strong>water quality in rivers and streams. It is suitable for use with indices and assessment<strong>methods</strong> based <strong>on</strong> the relative abundance <strong>of</strong> taxa.71

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