2005
DOI: 10.1016/j.watres.2005.06.008
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Developing an optimal river typology for biological elements within the Water Framework Directive

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Cited by 50 publications
(46 citation statements)
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“…Reference conditions are best described at the scale of a river-type (Nijboer et al, 2004) and the comparison of conditions at a current site with those of a reference site belonging to the same stream-type allows an ecological quality evaluation. In short, a typology should be simple, intuitively understandable, with a minimum number of river types, whilst reducing natural variation of reference conditions within river-types (Dodkins et al, 2005). Reference sites should be viewed as the least disturbed sites within a river-type, rather than actual pristine conditions, as they rarely exist in most European countries.…”
Section: Mots-clésmentioning
confidence: 99%
“…Reference conditions are best described at the scale of a river-type (Nijboer et al, 2004) and the comparison of conditions at a current site with those of a reference site belonging to the same stream-type allows an ecological quality evaluation. In short, a typology should be simple, intuitively understandable, with a minimum number of river types, whilst reducing natural variation of reference conditions within river-types (Dodkins et al, 2005). Reference sites should be viewed as the least disturbed sites within a river-type, rather than actual pristine conditions, as they rarely exist in most European countries.…”
Section: Mots-clésmentioning
confidence: 99%
“…1], Brinson andRheinhardt 1996, Shaffer et al 1999). The mandate of the European Union Water Framework Directive (WFD) that ecological assessments must be comparable across member nations prompted several studies that assessed the effectiveness of different typologies in bioassessment (e.g., Lorenz et al 2004, Verdonschot and Nijboer 2004, Dodkins et al 2005, Ferréol et al 2005, Aroviita et al 2008, Turak and Koop 2008, especially regarding how to develop optimal typologies based on only those catchment and waterbody features that most strongly influence biota (e.g., Snelder et al 2004b, Dodkins et al 2005, Snelder and Hughey 2005, Heino and Mykrä 2006, Sánchez-Montoya et al 2007, Aroviita et al 2008. However, tests of the effectiveness of the typological approach in partitioning natural ecological variation have not produced encouraging results (Davy-Bowker et al 2006, Inglis et al 2008.…”
Section: A Brief History Of Approaches Used To Estimate Ecological Bementioning
confidence: 99%
“…Since catchment geomorphology and climate-related variables are often strong predictors of macroinvertebrate assemblages (Richards et al, 1996;Hawkins et al, 2000;Verdonschot and Nijboer, 2004;Chaves et al, 2005), sites within the same WFD type that were based on these factors are expected to represent relatively distinct ecological units for invertebrate communities (Verdonschot, 2006a;Sa´nchez-Montoya et al, 2007). Alternatively, in bottomup approaches, aquatic biological data are used to group similar stream sites (e.g., Wright et al, 1984;Parsons and Norris, 1996;Marchant et al, 1997;Ehlert et al, 2002;Heino et al, 2003;Lorenz et al, 2004;Dodkins et al, 2005;Sa´nchez-Montoya et al, 2007). To accomplish this purpose biotic data should be collected in reference sites since anthropogenic stress reduces natural differences between communities (Verdonschot, 2006a).…”
Section: Introductionmentioning
confidence: 99%
“…To accomplish this purpose biotic data should be collected in reference sites since anthropogenic stress reduces natural differences between communities (Verdonschot, 2006a). Additionally, there is a third combined option that consists of testing and refining physically derived classes with a subsequent or simultaneous analysis of biological data from undisturbed sites within those classes Dodkins et al, 2005).…”
Section: Introductionmentioning
confidence: 99%
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