Case study:Greatham Managed Realignment Scheme: Difference between revisions

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Revision as of 11:57, 2 February 2024

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Project overview

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Status Complete
Project web site
Themes Flood risk management, Habitat and biodiversity, Water quality
Country England
Main contact forename environment
Main contact surname agency
Main contact user ID
Contact organisation Environment Agency
Contact organisation web site http://www.ecrr.org/Portals/27/Greatham%20North%20Managed%20Realignment%20Scheme.pdf
Partner organisations natural england; RSPB
Parent multi-site project
This is a parent project
encompassing the following
projects
No
Project picture

Project summary

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The Environment Agency identified that the implementation of the Tees Tidal Flood Risk Management strategy would result in in the loss of intertidal habitats which form part of the Teesmouth and Cleveland Coast Special Protection Area (SPA) and Ramsar site. In addition, the need for further coastal defence works necessary as part of the Redcar Flood Alleviation Scheme also has the potential to cause a loss of SPA habitats.

The Environment Agency therefore had a legal requirement to deliver at least 20 ha of intertidal habitat within the Tees Estuary as compensation for the impact predicted as part of its flood and coastal risk management projects. The Environment Agency purchased 77 ha of land alongside Greatham Creek (part of the Greatham North flood cell) in order to

implement a managed realignment scheme and create the required habitats. The Greatham Managed Realignment Scheme allows future work to the tidal flood defences of the Tees Estuary to continue whilst providing long-term environmental benefit through the conservation of the integrity of the Teesmouth and Cleveland Coast SPA and Ramsar site. The scheme aimed to create a range of complementary habitats of benefit to a variety of wildlife, and ensure better access to for the public was available

Monitoring surveys and results

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  • The scheme delivered 22 ha of intertidal habitat, comprising a mixture of saltmarsh and mudflats. In addition, other parts of the site delivered areas of saline and brackish water, rough grasslands and coastal and floodplain grassland.
  • The borrow pits were restored to provide a minimum of 12 ha of freshwater habitat for species such as great crested newt, common frog and aquatic invertebrates and species rich and meadow grassland.
  • No significant adverse impacts to the hydromorphology and sediment regime in the Tees Estuary are expected.
  • Features of historic significance, such as salterns (sites historically used for salt making), will be returned to their pre-reclamation situation, reducing current pressures from erosion by burrowing and grazing animals. The regrading of the relic drainage system on site and the location of the breaches were designed, in part, to reduce erosion of the salterns

Lessons learnt

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Cumulative benefits can be achieved through undertaking managed realignment schemes for habitat improvements which also form part of the local areas flood defence strategy.


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Catchment and subcatchment

Catchment

River basin district Northumbria
River basin Tees

Subcatchment

River name Greatham Creek Catchment (trib of Tidal Tees)
Area category 10 - 100 km²
Area (km2)
Maximum altitude category 100 - 200 m
Maximum altitude (m) 149149 m <br />0.149 km <br />14,900 cm <br />
Dominant geology Calcareous
Ecoregion Great Britain
Dominant land cover Arable and Horticulture
Waterbody ID GB103025076030



Other case studies in this subcatchment: Greatham Marsh Restoration


Site

Name
WFD water body codes
WFD (national) typology
WFD water body name
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Reference morphology
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Heavily modified water body
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Invasive species present
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Project background

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Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design
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Monitoring



Reasons for river restoration

Mitigation of a pressure
Hydromorphology
Biology
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Measures

Structural measures
Bank/bed modifications
Floodplain / River corridor
Planform / Channel pattern
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Non-structural measures
Management interventions
Social measures (incl. engagement)
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Monitoring

Hydromorphological quality elements

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Before measures After measures Qualitative Quantitative

Biological quality elements

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Any other monitoring, e.g. social, economic

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Monitoring documents



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Supplementary Information

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