Case study:Upper Cringle Floodplain Restoration Project: Difference between revisions

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{{Case study status
|Approval status=Draft
|Approval status=Approved
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{{Location
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{{Project overview
{{Project overview
|Project title=Upper Cringle Floodplain Restoration Project
|Status=Complete
|Status=Complete
|Project web site url=lincsrivers.org.uk/upper-cringle-brook-gets-a-makeover/?msclkid=6925b300d11011ecbd85ed27680329e8
|Themes=Environmental flows and water resources, Flood risk management, Habitat and biodiversity, Hydromorphology, Water quality
|Themes=Environmental flows and water resources, Flood risk management, Habitat and biodiversity, Hydromorphology, Water quality
|Country=England
|Country=England
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|Contact organisation=Lincolnshire Rivers Trust
|Contact organisation=Lincolnshire Rivers Trust
|Contact organisation url=lincsrivers.org.uk
|Contact organisation url=lincsrivers.org.uk
|Name of parent multi-site project=Case_study:Upper Witham Restoration
|Multi-site=No
|Multi-site=No
|Project picture=Before and After Collage.png
|Picture description=Upper Cringle Brook Before and After Collagee
|Project summary=The Limestone Becks are located over a 3,000km2 limestone ridge in the west of Lincolnshire and are supplied by consistent flows of high-quality groundwater. They are isolated and unique, and if in good condition, have potential to support a rich aquatic flora and fauna, rarely found in Eastern England.
Cringle Brook is a 12km limestone beck exemplifying both good and poor river habitat.  The lower sections of the Brook remain relatively natural whilst the Upper Cringle Brook, historically straightened and deepened, faces a range of pressures including deterioration in habitat quality through changing management practices and diffuse pollution from the wider catchment, damaging it to such an extent it is substantially poorer ecologically.
The current overall WFD status is moderate with invertebrates and macrophytes at moderate (2019 classification).
Cringle Brook is also a catchment for supply of public drinking water, currently closed due to elevated pesticide concentrations.  The site is also downstream of Skillington village waste-water treatment plant where phosphate treatment options are limited. A separate project is being undertaken in the wider catchment to address diffuse pollution however, it is anticipated that the new wetland areas created by this project will help provide some degree of natural attenuation.
The project location at the top of the Witham catchment was deemed ideal as natural processes could be used to make space for water and help trap sediment.  This project included 1km of the Upper Cringle Brook, which was un-farmed, dry floodplain, with the deepened and straightened channel running along the Southern edge. The channel and floodplain were completely disconnected, and the channel habitat was very poor.
Previous experience in the Upper Witham Catchment has shown that the only effective option for restoration is to provide the river with a floodplain. In-channel measures alone would not make a worthwhile improvement. This is why other options were not considered. 
1 ha (the maximum area agreed by the landowner) of inset floodplain was excavated along the 1km stretch with secondary channels, back channels and ponds added and some trees from the site were pulled across the new floodplain, enabling natural processes to be restarted, creating diversity and sinuosity in the channel. Without this action, the habitat will not be improved and a WFD reason for failure will not be addressed.  Spoil generated from the excavations was used on the same site to create a 1.7 ha wildflower area adjacent to the floodplain.
|Monitoring surveys and results=A Morph River Condition assessment survey was carried out before with a follow up survey later in the summer and a further one in a year.  Ecological surveys also carried out prior to project will be compared to surveys to be carried out next year to assess ecological impact. Results are expected to show a significant improvement in habitat and ecology along the restored 1km stretch. Drone video footage was recorded before and afterwards showing the extent of the works and the increased water storage capacity of the newly instated inset floodplains. Fixed point photography of the floodplain over time will be used to study sediment deposition.  Phosphate levels will also be measured upstream between water treatment works and project site and compared with downstream of site to monitor ‘polishing’ effect of floodplain reconnection along the stretch. Baseline data from EA gauging stations should provide evidence of  the volume of water storage made available by the and the possible reduction of peak flows in Upper Witham system.
|Lessons learn=Head waters should not be discounted as a place to look to restore even when restoration seems unfeasible due to current condition. The benefits can be significant.
When lowering floodplains, considering how the material can be landscaped on site and used for other benefits e.g., wildflower habitats but understanding that the site to look a bit stark whilst this establishes.
The value of an experienced site supervisor and a skilled contractor cannot be underestimated.
Confidence in the contractor's experience enabled them free reign to be creative within the constraints of the given inset floodplain parameters, and to observe and work with the river gives a more organic approach (regular site checks ensure all going to plan and landowner completely happy). 
Concise and transparent communication with landowner to build trust is key, enabling a more flexible approach on the broader principles of work as they were set out, facilitating a more natural approach from the contractors on the ground.
|Project title=Upper Cringle Floodplain Restoration Project
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|File name=Before restoration pic early Feb 22.jpg
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|File name=Post restoration pic late Feb 22.jpg
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|Subcatchment=Upper Witham
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{{Site
{{Site
|Name=Upper Cringle Brook
|Name=Upper Cringle Brook
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{{Biological quality elements header}}
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{{Biological quality element table row
|Element=Invertebrates: Diversity
|Monitored before=No
|Monitored after=Yes
|Qualitative monitoring=Yes
|Quantitative monitoring=Yes
|Control site used=Yes
|Result=Awaiting results
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{{Physico-chemical quality elements header}}
{{Physico-chemical quality element table row
|Element=Nutrient concentrations
|Monitored before=No
|Monitored after=Yes
|Qualitative monitoring=No
|Quantitative monitoring=Yes
|Control site used=Yes
|Result=Awaiting results
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|File name=Upper Cringle Brook Restoration Case Study 2024 Update.pdf
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{{Additional links and references
|Link=lincsrivers.org.uk/upper-cringle-brook-gets-a-makeover/
|Description=Press Release
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Latest revision as of 12:02, 27 February 2024

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Location: 52° 49' 29.40" N, 0° 38' 55.40" W
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Project overview

Edit project overview
Status Complete
Project web site http://lincsrivers.org.uk/upper-cringle-brook-gets-a-makeover/?msclkid=6925b300d11011ecbd85ed27680329e8
Themes Environmental flows and water resources, Flood risk management, Habitat and biodiversity, Hydromorphology, Water quality
Country England
Main contact forename Gail
Main contact surname Talton
Main contact user ID User:LincsRivers
Contact organisation Lincolnshire Rivers Trust
Contact organisation web site http://lincsrivers.org.uk
Partner organisations
Parent multi-site project

Case_study:Upper Witham Restoration

This is a parent project
encompassing the following
projects
No
Upper Cringle Brook Before and After Collagee

Project summary

Edit project overview to modify the project summary.


The Limestone Becks are located over a 3,000km2 limestone ridge in the west of Lincolnshire and are supplied by consistent flows of high-quality groundwater. They are isolated and unique, and if in good condition, have potential to support a rich aquatic flora and fauna, rarely found in Eastern England. Cringle Brook is a 12km limestone beck exemplifying both good and poor river habitat. The lower sections of the Brook remain relatively natural whilst the Upper Cringle Brook, historically straightened and deepened, faces a range of pressures including deterioration in habitat quality through changing management practices and diffuse pollution from the wider catchment, damaging it to such an extent it is substantially poorer ecologically.

The current overall WFD status is moderate with invertebrates and macrophytes at moderate (2019 classification).

Cringle Brook is also a catchment for supply of public drinking water, currently closed due to elevated pesticide concentrations. The site is also downstream of Skillington village waste-water treatment plant where phosphate treatment options are limited. A separate project is being undertaken in the wider catchment to address diffuse pollution however, it is anticipated that the new wetland areas created by this project will help provide some degree of natural attenuation.

The project location at the top of the Witham catchment was deemed ideal as natural processes could be used to make space for water and help trap sediment. This project included 1km of the Upper Cringle Brook, which was un-farmed, dry floodplain, with the deepened and straightened channel running along the Southern edge. The channel and floodplain were completely disconnected, and the channel habitat was very poor.

Previous experience in the Upper Witham Catchment has shown that the only effective option for restoration is to provide the river with a floodplain. In-channel measures alone would not make a worthwhile improvement. This is why other options were not considered.

1 ha (the maximum area agreed by the landowner) of inset floodplain was excavated along the 1km stretch with secondary channels, back channels and ponds added and some trees from the site were pulled across the new floodplain, enabling natural processes to be restarted, creating diversity and sinuosity in the channel. Without this action, the habitat will not be improved and a WFD reason for failure will not be addressed. Spoil generated from the excavations was used on the same site to create a 1.7 ha wildflower area adjacent to the floodplain.

Monitoring surveys and results

Edit project overview to modify the Monitoring survey and results.


A Morph River Condition assessment survey was carried out before with a follow up survey later in the summer and a further one in a year. Ecological surveys also carried out prior to project will be compared to surveys to be carried out next year to assess ecological impact. Results are expected to show a significant improvement in habitat and ecology along the restored 1km stretch. Drone video footage was recorded before and afterwards showing the extent of the works and the increased water storage capacity of the newly instated inset floodplains. Fixed point photography of the floodplain over time will be used to study sediment deposition. Phosphate levels will also be measured upstream between water treatment works and project site and compared with downstream of site to monitor ‘polishing’ effect of floodplain reconnection along the stretch. Baseline data from EA gauging stations should provide evidence of the volume of water storage made available by the and the possible reduction of peak flows in Upper Witham system.

Lessons learnt

Edit project overview to modify the lessons learnt.


Head waters should not be discounted as a place to look to restore even when restoration seems unfeasible due to current condition. The benefits can be significant.

When lowering floodplains, considering how the material can be landscaped on site and used for other benefits e.g., wildflower habitats but understanding that the site to look a bit stark whilst this establishes.

The value of an experienced site supervisor and a skilled contractor cannot be underestimated. Confidence in the contractor's experience enabled them free reign to be creative within the constraints of the given inset floodplain parameters, and to observe and work with the river gives a more organic approach (regular site checks ensure all going to plan and landowner completely happy).

Concise and transparent communication with landowner to build trust is key, enabling a more flexible approach on the broader principles of work as they were set out, facilitating a more natural approach from the contractors on the ground.


Image gallery


Before restoration pic early Feb 22.jpg
Post restoration pic late Feb 22.jpg
Before Photo.jpeg
After photo.JPG
ShowHideAdditionalImage.png


Catchment and subcatchment

Catchment

River basin district Anglian
River basin Witham

Subcatchment

River name Upper Witham
Area category 10 - 100 km²
Area (km2)
Maximum altitude category Less than 100 m
Maximum altitude (m) 4646 m <br />0.046 km <br />4,600 cm <br />
Dominant geology Calcareous
Ecoregion Great Britain
Dominant land cover Arable and Horticulture
Waterbody ID GB105030056760



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, Manthorpe Floodplain Reconnection, Papermill Weir Section in-channel restoration, River Witham Great Ponton, Stainby Road, Colsterworth, Syston and Barkston Restoration... further results


Site

Name Upper Cringle Brook
WFD water body codes GB105030051560
WFD (national) typology limestone river
WFD water body name Cringle Brook - Upper
Pre-project morphology Straightened, Over deepened
Reference morphology Anastomosing
Desired post project morphology Anastomosing
Heavily modified water body Yes
National/international site designation
Local/regional site designations
Protected species present Yes
Invasive species present No
Species of interest
Dominant hydrology Groundwater
Dominant substrate Clay, Gravel
River corridor land use Grassland
Average bankfull channel width category Less than 2 m
Average bankfull channel width (m)
Average bankfull channel depth category Less than 0.5 m
Average bankfull channel depth (m)
Mean discharge category Less than 0.1 m³/s
Mean annual discharge (m3/s)
Average channel gradient category 0.001 - 0.01
Average channel gradient
Average unit stream power (W/m2)


Project background

Reach length directly affected (m) 10001,000 m <br />1 km <br />100,000 cm <br />
Project started 03/02/2022
Works started 2022/02/03
Works completed 2022/04/30
Project completed 2022/04/30
Total cost category 50 - 100 k€
Total cost (k€) 9898 k€ <br />98,000 € <br />
Benefit to cost ratio 2.97
Funding sources Environment Agency

Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design 10 - 50 k€ 1414 k€ <br />14,000 € <br /> Lincolnshire Rivers Trust Gail Talton
Stakeholder engagement and communication Less than 1 k€ Lincolnshire Rivers Trust Gail Talton
Works and works supervision 50 - 100 k€ 8484 k€ <br />84,000 € <br /> Lincolnshire Rivers Trust Gail Talton
Post-project management and maintenance Less than 1 k€ Lincolnshire Rivers Trust Gail Talton
Monitoring Less than 1 k€ Lincolnshire Rivers Trust Gail Talton

Supplementary funding information

Works were paid for by a Water Environment Improvement Fund Grant and land was contributed to the project by the landowner.



Reasons for river restoration

Mitigation of a pressure Land drainage
Hydromorphology Channel pattern/planform
Biology Invertebrates, Macrophytes and/or phytobenthos: Average abundance
Physico-chemical Nutrient concentrations, Oxygen balance
Other reasons for the project Landscape enhancement


Measures

Structural measures
Bank/bed modifications Introducing large woody debris
Floodplain / River corridor Lowering of floodplain, Wildflower meadows
Planform / Channel pattern Back channel created, Channel naturalisation, Creation of an island, Creation of pond, Creation of backwater, Habitat creation
Other
Non-structural measures
Management interventions Associated terrestrial habitat improvements
Social measures (incl. engagement)
Other


Monitoring

Hydromorphological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative
Channel pattern/planform Yes Yes No Yes No Awaiting results

Biological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative
Invertebrates: Diversity No Yes Yes Yes Yes Awaiting results

Physico-chemical quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative
Nutrient concentrations No Yes No Yes Yes Awaiting results

Any other monitoring, e.g. social, economic

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative


Monitoring documents



Additional documents and videos


Additional links and references

Link Description
http://lincsrivers.org.uk/upper-cringle-brook-gets-a-makeover/ Press Release

Supplementary Information

Edit Supplementary Information