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Report on Harmonisation of freshwater biological methods

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Table 1. European <strong>methods</strong> for m<strong>on</strong>itoring and assessment <strong>of</strong> macrophytes in watercourses.Method Country ReferenceWFD method for macrophytes Austria no referenceMacrophyte m<strong>on</strong>itoring Denmark Skriver 1999Macrophyte m<strong>on</strong>itoring Est<strong>on</strong>ia no referenceIndice Biologique Macrophytes en RivièreAFNOR (Associati<strong>on</strong> FrançaiseFrance(I.B.M.R.)de Normalisati<strong>on</strong>) 2002PHYLIB Germany Schaumburg et al. 2004Method for the survey <strong>of</strong> aquaticmacrophytes in running watersLatvia Cimdins et al. 1995KRW-Maatlatten for Aquatic FloraTheNetherlandsMolen et al. 2004Macrophyte assessment Norway no referenceMacrophyte m<strong>on</strong>itoringMean Trophic Ranking (MTR)SwedenUnitedKingdomSwedish Envir<strong>on</strong>mentalProtecti<strong>on</strong> Agency 2000Holmes et al. 199932. Compositi<strong>on</strong> and abundance <strong>of</strong> in-stream macrophytes are recorded in the field byvisual inspecti<strong>on</strong> from the banks or by wading in the stream. Larger watercourses areinvestigated by boat or diving. In some countries aqua-scopes are employed, whichare specifically designed tools to survey the plant growth underneath the watersurface. Rakes or grapnels are used to remove macrophytes for abundance estimati<strong>on</strong>or further tax<strong>on</strong>omic identificati<strong>on</strong>.33. Sampling area differs between individual <strong>methods</strong>. In the Nordic countriesseparate transects <strong>of</strong> 0.25 * 0.25 m² are sampled. The French and Latvian <strong>methods</strong>specify to survey an area <strong>of</strong> at least 100 m². Other schemes prescribe the investigati<strong>on</strong><strong>of</strong> stream reaches <strong>of</strong> 100 m or 500 m.34. Latvia and Norway follow the standard EN 14184:2003 Water quality: Guidancestandard for the surveying <strong>of</strong> aquatic macrophytes in running waters.35. Most comm<strong>on</strong>ly macrophytes are identified to species level, which is usually d<strong>on</strong>ein the field. Uncertain identificati<strong>on</strong>s are verified in the laboratory by referring toherbarium species.36. Two different schemes to record macrophyte abundance are in use. In mostcountries the relative coverage <strong>of</strong> the macrophyte community is measured. Methodsapplied in Austria and Germany specify the ‘plant mass estimate’ which accounts forthe three-dimensi<strong>on</strong>al extensi<strong>on</strong> <strong>of</strong> the plant stand. In both opti<strong>on</strong>s abundance is74

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