Case study:Manthorpe Floodplain Reconnection: Difference between revisions
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|Subcatchment=Upper Witham | |Subcatchment=Upper Witham | ||
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{{Site}} | {{Site | ||
|Name=Manthorpe Floodplain Reconnection | |||
|WFD water body code=GB105030056780 | |||
|WFD water body name=Witham - confluence of Cringle Brook to confluence Brant | |||
|Heavily modified water body=No | |||
|Protected species present=Yes | |||
|Invasive species present=No | |||
|Species=Native Crayfish / Brown Trout, | |||
}} | |||
{{Project background}} | {{Project background}} | ||
{{Motivations}} | {{Motivations}} |
Revision as of 16:10, 8 February 2024
This case study is pending approval by a RiverWiki administrator.
Project overview
Status | Complete |
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Project web site | |
Themes | Flood risk management, Habitat and biodiversity |
Country | England |
Main contact forename | Matt |
Main contact surname | Parr |
Main contact user ID | |
Contact organisation | Enviroment Agency |
Contact organisation web site | http://www.gov.uk/government/organisations/environment-agency |
Partner organisations | Wild Trout Trust, Lincolnshire Wildlife Trust. |
Parent multi-site project | |
This is a parent project encompassing the following projects |
No |
Project summary
There were five components to the scheme:
• Removal of redundant flood bank, and lowering of the floodplain to create a terraced floodplain with a lower more frequently connected floodplain and a higher terrace of un-lowered floodplain. This gives maximum benefit to the river and natural processes whilst providing some variation in flood event storage and habitat evolution and variety.
• Addition of riffles and gravel supply in the form of point bars and islands and splitting of channel into multiple threads creating a more natural form and allowing the river space to adjust to changes in flow but also allow natural processes like silt deposition, channel evolution, less intensive management, woody material to be retained in channel and on flood plain. The gravel raises the bed helping to connect the river into the floodplain reducing the amount of spoil generated to lower floodplain as well as providing rich habitats for riverine wildlife.
• Creation of floodplain ponds and terrestrial habitat features like habitat piles, stone piles for hibernacular, and woody material on the floodplain to encourage further hydraulic roughness in high flow events
• Spreading of spoil over the top of the valley sides outside of the floodplain, this was then reseeded with appropriate wildflower grassland mix and provides pollinator benefits.
Monitoring surveys and results
Brown trout have already been observed spawning on the new limestone gravels. Crayfish monitoring was carried out pre works and showed a very low baseline population with only 6 individuals caught, repeat monitoring of this will be carried out along with repeat bird surveys of the site.
Lessons learnt
4200 m3 of earth was removed from the floodplain during the lowering and removal of embankments. Reconnecting the floodplain has created 19,500m3 of space for water which now reconnects to the lower floodplain frequently after intense rainfall events at a 1 in 2 event magnitude.
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Subcatchment
Other case studies in this subcatchment: Aubourn Rock Ramp and Habitat Works, Belton Floodplain Reconnection and River Restoration, Dysart Park, Grantham Habitat Improvement, Grantham Blue Green - Urban Reach, Little Ponton, Papermill Weir Section in-channel restoration, River Witham Great Ponton, Stainby Road, Colsterworth, Syston and Barkston Restoration, Upper Cringle Floodplain Restoration Project... further results
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
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Supplementary InformationEdit Supplementary Information
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