Case study:River Ecclesbourne Restoration Project: Difference between revisions

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{{Location
|Location=53.015, -1.54275
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{{Measures
|Bank and bed modifications measure=Barrier removal, Creation of fish pass, Erosion Repair, Introducing sediment
|Floodplain / River corridor=Floodplain reconnection
|Planform / Channel pattern=Channel realignment, Creation of new channel
|Management interventions=Removal of invasive species, Riparian tree planting, Livestock exclusion
|Social measures=Environmental education activities with local schools, Community Education, Interpretation boards, interacting with farmers
}}
{{Motivations
|Hydromorphological quality elements=Continuity for organisms
|Biological quality elements=Fish
|Physico-chemical quality elements=Nutrient concentrations
}}
{{Project background
{{Project background
|Reach length directly affected=16000
|Reach length directly affected=16000
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|Approval status=Draft
|Approval status=Draft
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{{Location
 
|Location=53.015, -1.54275
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Latest revision as of 14:24, 25 February 2026

Location: 53° 0' 54.00" N, 1° 32' 33.90" W
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Measures

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Structural measures
Bank/bed modifications Barrier removal, Creation of fish pass, Erosion Repair, Introducing sediment
Floodplain / River corridor Floodplain reconnection
Planform / Channel pattern Channel realignment, Creation of new channel
Other
Non-structural measures
Management interventions Removal of invasive species, Riparian tree planting, Livestock exclusion
Social measures (incl. engagement) Environmental education activities with local schools, Community Education, Interpretation boards, interacting with farmers
Other


Reasons for river restoration

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Mitigation of a pressure
Hydromorphology Continuity for organisms
Biology Fish
Physico-chemical Nutrient concentrations
Other reasons for the project


Project background

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Reach length directly affected (m) 1600016,000 m <br />16 km <br />1,600,000 cm <br />
Project started 2018-12-06
Works started 2022-08-01
Works completed 2024-07-01
Project completed 2025-03-31
Total cost category 1000 - 5000 k€
Total cost (k€)
Benefit to cost ratio
Funding sources Government Grant in Aid, Private Company, Charitable Funds

Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design
Stakeholder engagement and communication
Works and works supervision
Post-project management and maintenance
Monitoring



Site

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Name River Ecclesbourne
WFD water body codes GB104028052720
WFD (national) typology River
WFD water body name Ecclesbourne Catchment
Pre-project morphology Impounded, Straightened, Over deepened
Reference morphology
Desired post project morphology Actively meandering, Pool-riffle, Run-glide
Heavily modified water body No
National/international site designation
Local/regional site designations
Protected species present Yes
Invasive species present Yes
Species of interest Atlantic salmon (Salmo salar), Brown trout (Salmo trutta), grayling (Thymallus thymallus), Brook lamprey
Dominant hydrology Quick run-off
Dominant substrate Gravel
River corridor land use Improved/semi-improved grassland/pasture, Urban
Average bankfull channel width category
Average bankfull channel width (m)
Average bankfull channel depth category
Average bankfull channel depth (m)
Mean discharge category
Mean annual discharge (m3/s)
Average channel gradient category
Average channel gradient
Average unit stream power (W/m2)


Catchment and subcatchment

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(affects all case studies in this subcatchment)

Catchment

River basin district Humber
River basin Derbyshire Derwent

Subcatchment

River name River Ecclesborne catchment (trib of R Derwent)
Area category 10 - 100 km²
Area (km2)
Maximum altitude category 200 - 500 m
Maximum altitude (m) 355355 m <br />0.355 km <br />35,500 cm <br />
Dominant geology Siliceous
Ecoregion Great Britain
Dominant land cover Improved grassland
Waterbody ID GB104028052720



Other case studies in this subcatchment: Ecclesbourne Farm project



Project overview

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Status Complete
Project web site
Themes Environmental flows and water resources, Fisheries, Habitat and biodiversity, Hydromorphology, Land use management - agriculture, Monitoring, Social benefits, Spatial planning, Urban, Water quality
Country England
Main contact forename Jennifer
Main contact surname Kril
Main contact user ID
Contact organisation Derbyshire Wildlife Trust
Contact organisation web site
Partner organisations Wild Trout Trust, Environment Agency, Nestle Waters & Premium Beverages, Chatsworth Estate
Parent multi-site project
This is a parent project
encompassing the following
projects
No
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Project summary

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The River Ecclesbourne Restoration Project (Derbyshire, England) is a six‑plus year, partnership‑led programme to restore river health and reconnect migratory fish to upstream habitat. It targeted two major barriers: Snake Lane Weir (2.5 m) and Postern Mill Weir (2 m), delivering a phased approach, removal and rock‑ramp installation at Snake Lane (Phase 1, winter 2022) and a 400 m re-meander and paleochannel reconnection at Postern Mill (Phase 2, winter 2023 – spring 2024). The work was driven by long‑term evidence showing severe fragmentation (20+ years of Environment Agency surveys) and by the return of migratory salmon to the Derwent after earlier catchment improvements. Interventions emphasised working with natural processes: regrading channels, creating riffle–pool sequences, restoring sediment continuity, and reconnecting floodplain and paleochannel to allow dynamic morphological adjustment. Delivery combined technical design, regulatory oversight and blended funding from partners including Derbyshire Wildlife Trust (lead for Postern Mill), Wild Trout Trust (lead for Snake Lane), the Environment Agency, Nestlé Waters & Premium Beverages and Chatsworth Estate. Community engagement, volunteer habitat work and education were integral throughout. The project cost exceeded £1.1 million (Snake Lane ~£500k; Postern Mill ~£460k) and completed physical works in 2025, with complimentary wider catchment restoration (Invasive species control, tree planting and biodiversity enhancements, with monitoring funded through 2029. The scheme sits within a coordinated catchment strategy (Derbyshire Derwent Catchment Partnership, Humber River Basin Management Plan and Derbyshire Derwent Fish Passage Project) and contributes to wider ambitions to reopen the Derwent and Trent catchments to migratory fish. “The River Ecclesbourne Restoration Project is the result of more than six years of dedicated partnership work to improve river health and restore fish passage across the catchment."

Monitoring surveys and results

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Monitoring is multimethod and repeatable, designed to measure habitat change, species response and connectivity. Core elements are: annual electrofishing at six historic EA sites to track species composition, abundance, biomass and age structure; eDNA sampling for early detection of low‑density or cryptic species; redd counts each autumn/winter to map salmon spawning distribution; fixed‑point photography and drone surveys to document geomorphic evolution; trail cameras to record wildlife use; and UKHab assessments to classify habitat condition. Additional techniques included non‑EA electric fishing surveys, repeat visits to assess rust‑fungus biocontrol trials for invasive plants, and hydraulic/flow modelling used both in design and post‑event evaluation. These complementary methods provide quantitative and qualitative lines of evidence for adaptive management and are repeated on a defined schedule to allow before/after and upstream/downstream comparisons.

Results: The project reopened previously inaccessible habitat and produced clear biological responses: salmon recolonised upstream reaches within months of Snake Lane works (a spawned‑out hen found 1 km upstream), and by 2025 an Atlantic salmon parr plus several newly recorded coarse fish species were documented at Postern Mill, confirming reconnection. Electrofishing and eDNA confirm return and movement of species including Atlantic salmon, chub, grayling and gudgeon. Morphological monitoring shows active sediment transport, evolving riffles, pools and meanders; trail cameras and public reporting demonstrate increased wildlife use and strong community interest. The scheme gained national/international attention (Dam Removal Europe finalist; Natural History Museum case study).

Lessons learnt

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- Work with natural processes rather than over‑engineering: re-meandering and floodplain reconnection produced rapid geomorphic recovery and self‑sustaining habitat complexity. - Robust evidence and modelling matter, especially under extreme weather: detailed hydraulic modelling supported design decisions and proved accurate during Storm Babet, informing emergency responses and building public confidence. - Partnerships and blended funding accelerate delivery and broaden ownership; engaging landowners and tenant farmers early secured permissions and stewardship. - Community engagement and transparent communication (GIS storyboards, QR codes, videos, field visits) are essential for social licence and long‑term stewardship.

Overall, the Ecclesbourne project demonstrates that targeted, evidence‑led barrier removal and channel reconnection can rapidly restore connectivity and biodiversity while delivering multiple social and climate‑resilience benefits.

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Monitoring

Hydromorphological quality elements

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

Biological quality elements

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

Physico-chemical quality elements

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

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



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Supplementary Information

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