Case study:Fluvial restoration in River Carrión: Difference between revisions
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|Approval status= | |Approval status=Approved | ||
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{{Location | {{Location | ||
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{{Project overview | {{Project overview | ||
|Status=Complete | |Status=Complete | ||
|Themes=Environmental flows and water resources, Habitat and biodiversity, Hydromorphology | |||
|Country=Spain | |Country=Spain | ||
|Main contact forename=AEMS | |Main contact forename=AEMS | ||
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|Contact organisation url=riosconvida.es/ | |Contact organisation url=riosconvida.es/ | ||
|Multi-site=No | |Multi-site=No | ||
|Project picture=010 Rio Carrion.jpg | |||
|Project summary=The Carrión river restoration located in Fresno del Río and Pino del Río (Palencia) covered a river reach with maximum flows between 218 and 527 m3/s, which is regulated by Camporredondo and Compuerto dams. The minimum flow is about 2 m3/s, set by the Confederación Hidrográfica del Duero. The concern about this reach was due to shore erosion and the lack of refuge for trout. | |Project summary=The Carrión river restoration located in Fresno del Río and Pino del Río (Palencia) covered a river reach with maximum flows between 218 and 527 m3/s, which is regulated by Camporredondo and Compuerto dams. The minimum flow is about 2 m3/s, set by the Confederación Hidrográfica del Duero. The concern about this reach was due to shore erosion and the lack of refuge for trout. | ||
In order to mitigate the impact of flow regulation and to improve the aquatic habitat for fish, several actions took place both instream and at the riparian zone: Boulders (limestone) were placed in the riverbed for improve the instream structure and habitat diversity; reforestation of the margins with four live fences; reforestation with single stakes; plantation of 170 stakes (75 % Salix fragilis and 25% of Salix purpurea and Salix atrocinerea); construction of a wing deflector consisting of stones, logs, and branch cuttings of willow and aquatic plants for its stabilization; plantation of branch cuttings and stakes of willow at stable margins to give shading and shelter for the trouts. | In order to mitigate the impact of flow regulation and to improve the aquatic habitat for fish, several actions took place both instream and at the riparian zone: Boulders (limestone) were placed in the riverbed for improve the instream structure and habitat diversity; reforestation of the margins with four live fences; reforestation with single stakes; plantation of 170 stakes (75 % Salix fragilis and 25% of Salix purpurea and Salix atrocinerea); construction of a wing deflector consisting of stones, logs, and branch cuttings of willow and aquatic plants for its stabilization; plantation of branch cuttings and stakes of willow at stable margins to give shading and shelter for the trouts. | ||
The effectiveness of the project was monitored by the Junta de Castilla y León almost until 1999. The evolution of trout population was measured with periodic samplings (electrofishing). | The effectiveness of the project was monitored by the Junta de Castilla y León almost until 1999. The evolution of trout population was measured with periodic samplings (electrofishing). | ||
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|File name=011 Rio Carrion CHDUERO 003.jpg | |||
|Caption=Aerial view of Carrion River between Pino del Río and Fresno del Río | |||
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|File name=011 Rio Carrion CHDUERO 003 I.jpg | |||
|Caption=Aerial view of Carrion River between Pino del Río and Fresno del Río in 2010 | |||
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|File name=011 Rio Carrion CHDUERO 003 II.jpg | |||
|Caption=Carrión River before works | |||
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|File name=011 Rio Carrion CHDUERO 003 III.jpg | |||
|Caption=Carrion River during works, in 1997 | |||
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|File name=011 Rio Carrion CHDUERO 003 IV.jpg | |||
|Caption=Carrion River after works, in 1998 | |||
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|File name=011 Rio Carrion CHDUERO 003 V.jpg | |||
|Caption=Carrion River after works, in 1999 | |||
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|File name=011 Rio Carrion CHDUERO 003 VI.jpg | |||
|Caption=Riverbanks before works, in 1994 | |||
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|File name=011 Rio Carrion CHDUERO 003 VII.jpg | |||
|Caption=Riverbanks after works, in 1998 | |||
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{{Measures | {{Measures | ||
|Bank and bed modifications measure= | |Bank and bed modifications measure=New bioengineering elements in order to stabilize slope banks, Deflectors, Creation of wooden deflectors, Creation of gravel deflectors, Bed load addition, Bank reprofiling, | ||
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{{Monitoring_documents}} | {{Monitoring_documents}} | ||
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{{Additional Documents}} | {{Additional Documents}} | ||
{{Case study documents | {{Case study documents | ||
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Latest revision as of 16:08, 2 January 2019
Project overview
Status | Complete |
---|---|
Project web site | |
Themes | Environmental flows and water resources, Habitat and biodiversity, Hydromorphology |
Country | Spain |
Main contact forename | AEMS |
Main contact surname | AEMS |
Main contact user ID | |
Contact organisation | AEMS - Ríos con Vida |
Contact organisation web site | http://riosconvida.es/ |
Partner organisations | |
Parent multi-site project | |
This is a parent project encompassing the following projects |
No |
Project summary
The Carrión river restoration located in Fresno del Río and Pino del Río (Palencia) covered a river reach with maximum flows between 218 and 527 m3/s, which is regulated by Camporredondo and Compuerto dams. The minimum flow is about 2 m3/s, set by the Confederación Hidrográfica del Duero. The concern about this reach was due to shore erosion and the lack of refuge for trout.
In order to mitigate the impact of flow regulation and to improve the aquatic habitat for fish, several actions took place both instream and at the riparian zone: Boulders (limestone) were placed in the riverbed for improve the instream structure and habitat diversity; reforestation of the margins with four live fences; reforestation with single stakes; plantation of 170 stakes (75 % Salix fragilis and 25% of Salix purpurea and Salix atrocinerea); construction of a wing deflector consisting of stones, logs, and branch cuttings of willow and aquatic plants for its stabilization; plantation of branch cuttings and stakes of willow at stable margins to give shading and shelter for the trouts.
The effectiveness of the project was monitored by the Junta de Castilla y León almost until 1999. The evolution of trout population was measured with periodic samplings (electrofishing).
Monitoring surveys and results
Lessons learnt
Image gallery
Catchment and subcatchmentSelect a catchment/subcatchment
Catchment
Subcatchment
Site
Project background
Cost for project phases
Reasons for river restoration
Measures
MonitoringHydromorphological quality elements
Biological quality elements
Physico-chemical quality elements
Any other monitoring, e.g. social, economic
Monitoring documents
Additional documents and videos
Additional links and references
Supplementary InformationEdit Supplementary Information
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