Over 200,000 kilometers of free-flowing river habitat in Europe is altered due to impoundments

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作者
Piotr Parasiewicz
Kamila Belka
Małgorzata Łapińska
Karol Ławniczak
Paweł Prus
Mikołaj Adamczyk
Paweł Buras
Jacek Szlakowski
Zbigniew Kaczkowski
Kinga Krauze
Joanna O’Keeffe
Katarzyna Suska
Janusz Ligięza
Andreas Melcher
Jesse O’Hanley
Kim Birnie-Gauvin
Kim Aarestrup
Peter E. Jones
Joshua Jones
Carlos Garcia de Leaniz
Jeroen S. Tummers
Sofia Consuegra
Paul Kemp
Hannah Schwedhelm
Zbigniew Popek
Gilles Segura
Sergio Vallesi
Maciej Zalewski
Wiesław Wiśniewolski
机构
[1] National Inland Fisheries Research Institute,
[2] European Regional Centre for Ecohydrology of the Polish Academy of Sciences,undefined
[3] University of Lodz,undefined
[4] University of Natural Resources and Life Sciences,undefined
[5] University of Kent,undefined
[6] Technical University of Denmark,undefined
[7] Swansea University,undefined
[8] Durham University,undefined
[9] RAVON,undefined
[10] University of Southampton,undefined
[11] Technical University of Munich,undefined
[12] Warsaw University of Life Sciences,undefined
[13] IS Environnement,undefined
[14] Hydronexus,undefined
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摘要
European rivers are disconnected by more than one million man-made barriers that physically limit aquatic species migration and contribute to modification of freshwater habitats. Here, a Conceptual Habitat Alteration Model for Ponding is developed to aid in evaluating the effects of impoundments on fish habitats. Fish communities present in rivers with low human impact and their broad environmental settings enable classification of European rivers into 15 macrohabitat types. These classifications, together with the estimated fish sensitivity to alteration of their habitat are used for assessing the impacts of six main barrier types (dams, weirs, sluices, culverts, fords, and ramps). Our results indicate that over 200,000 km or 10% of previously free-flowing river habitat has been altered due to impoundments. Although they appear less frequently, dams, weirs and sluices cause much more habitat alteration than the other types. Their impact is regionally diverse, which is a function of barrier height, type and density, as well as biogeographical location. This work allows us to foresee what potential environmental gain or loss can be expected with planned barrier management actions in rivers, and to prioritize management actions.
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