Report on Harmonisation of freshwater biological methods
Report on Harmonisation of freshwater biological methods
Report on Harmonisation of freshwater biological methods
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103. For macrophytes <strong>on</strong>ly a few <strong>methods</strong> presented are WFD compliant. This isbecause the <strong>methods</strong> developed prior to the implementati<strong>on</strong> <strong>of</strong> the WFD are generallylacking in the definiti<strong>on</strong> <strong>of</strong> stream type-specific reference c<strong>on</strong>diti<strong>on</strong>s. This does nothold for schemes specifically designed for WFD m<strong>on</strong>itoring purposes (Austria,Germany, The Netherlands). Sweden and UK intend to implement a predictive habitatapproach (a RIVPACS-type system for aquatic plants) in the near future to modelmacrophyte reference communities.104. For benthic invertebrates, <strong>on</strong>ly a small number <strong>of</strong> <strong>methods</strong> included in thisoverview fulfill the WFD classificati<strong>on</strong> demands at least partially. In particular,recently developed <strong>methods</strong> <strong>of</strong> the categories predictive and multimetric assessment<strong>methods</strong> incude stream type-specific evaluati<strong>on</strong> based <strong>on</strong> reference c<strong>on</strong>diti<strong>on</strong>s. Somecountries have modified their traditi<strong>on</strong>al <strong>methods</strong> (e.g. Saprobic System) and/ orcombined them with new assessment <strong>methods</strong> (e.g. for morphological degradati<strong>on</strong>) tomeet the requirements <strong>of</strong> the WFD (Rolauffs et al., 2004). Furthermore, it is plannedto adjust the site-specific reference <strong>of</strong> the UK RIVPACS system by c<strong>on</strong>siderati<strong>on</strong> <strong>of</strong>stream morphology (Nix<strong>on</strong> et al., 1997).105. Integrated assessment <strong>of</strong> all indicative parameters <strong>of</strong> macrozoobenthoscommunities is d<strong>on</strong>e by multimetric indices. Besides the overall appraisal <strong>of</strong>ecological quality, their modular structure enables indicati<strong>on</strong> <strong>of</strong> the cause <strong>of</strong>degradati<strong>on</strong> by providing individual metric values. Full ecological evaluati<strong>on</strong>accounting for several biota is carried out by the ecosystem comp<strong>on</strong>ent’s assessmentsystems described above.106. More than 50 percent <strong>of</strong> the <strong>methods</strong> present results in five classes <strong>of</strong> quality.Some <strong>of</strong> these banding schemes represent recent amendments with respect to thedemands <strong>of</strong> the WFD. In this c<strong>on</strong>text it has to be noted that the numbering <strong>of</strong> qualityclasses is performed c<strong>on</strong>versely. Some schemes label the highest class with ‘1’ andincrement the number according to increasing deteriorati<strong>on</strong>. Other classificati<strong>on</strong>sdenote high quality levels with ‘5’ and count down. This anomaly has to bec<strong>on</strong>sidered and resolved in c<strong>on</strong>necti<strong>on</strong> with the exchange and comparis<strong>on</strong> <strong>of</strong> qualityresults derived by different <strong>methods</strong>.107. Another 12 percent <strong>of</strong> the <strong>methods</strong> use seven classes <strong>of</strong> water qualityoriginating from the classificati<strong>on</strong> <strong>of</strong> saprobity introduced by Liebmann (1962).26