How Do Biota Respond to Additional Physical Restoration of Restored Streams?

Springer Science and Business Media LLC - Tập 20 - Trang 144-162 - 2016
Christer Nilsson1, Judith M. Sarneel1,2, Daniel Palm3, Johanna Gardeström1, Francesca Pilotto1, Lina E. Polvi1, Lovisa Lind1, Daniel Holmqvist4, Hans Lundqvist3
1Landscape Ecology Group, Department of Ecology and Environmental Science, Umeå University, Umeå, Sweden
2Ecology & Biodiversity Group and Plant Ecophysiology Group, Utrecht University, Utrecht, The Netherlands
3Department of Wildlife, Fish, and Environmental Studies, Swedish University of Agricultural Sciences, Umeå, Sweden
4Ume/Vindel River Fishery Advisory Board, Lycksele, Sweden

Tóm tắt

Restoration of channelized streams by returning coarse sediment from stream edges to the wetted channel has become a common practice in Sweden. Yet, restoration activities do not always result in the return of desired biota. This study evaluated a restoration project in the Vindel River in northern Sweden in which practitioners further increased channel complexity of previously restored stream reaches by placing very large boulders (>1 m), trees (>8 m), and salmonid spawning gravel from adjacent upland areas into the channels. One reach restored with basic methods and another with enhanced methods were selected in each of ten different tributaries to the main channel. Geomorphic and hydraulic complexity was enhanced but the chemical composition of riparian soils and the communities of riparian plants and fish did not exhibit any clear responses to the enhanced restoration measures during the first 5 years compared to reaches restored with basic restoration methods. The variation in the collected data was among streams instead of between types of restored reaches. We conclude that restoration is a disturbance in itself, that immigration potential varies across landscapes, and that biotic recovery processes in boreal river systems are slow. We suggest that enhanced restoration has to apply a catchment-scale approach accounting for connectivity and availability of source populations, and that low-intensity monitoring has to be performed over several decades to evaluate restoration outcomes.

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