Case study:Barking Creekmouth
Project overview
Status | Complete |
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Project web site | |
Themes | Fisheries, Habitat and biodiversity, Social benefits |
Country | England |
Main contact forename | Scarr |
Main contact surname | Toni |
Main contact user ID | User:Ascarr |
Contact organisation | Environment Agency |
Contact organisation web site | http://www.environment-agency.gov.uk |
Partner organisations | |
Parent multi-site project | |
This is a parent project encompassing the following projects |
No |
Project summary
Previous site use/issues
• underused and undervalued area of greenspace, owned by the Environment Agency, adjacent to the Barking Barrier.
• The terrestrial habitat consisted of species poor grassland with patches of scrub and Japanese knotweed. Areas which would have supported saltmarsh species were encased in riprap covered in bitumen and had be historically land raised.
• The foreshore in this area is important for overwintering birds such as teal, shelduck, tufted duck, wigeon, gadwell, shoveler, pintail, little grebe. Common whitethroat, sandmartins and linnet has been seen breeding in the area a pair of oyster catchers were also recorded breeding in 2000. Saltmarsh and mudflat UK BAP habitat is very important for these types of fauna and also flora.
• Barking Creek is recognised as a valuable feeding and refuge area for a variety of fish species, flounder, eel, smelt, sea bass in both their adults and juveniles life stages. These utilise the full range of sub, intertidal and saltmarsh habitats for foraging and refuge.
• There was limited amenity use, lack of seating areas, views from site obstructed by flood defences and no wheelchair access to site.
• Failing flood defences.
Enhancements • Breach of existing defence and creation of tidal backwater providing increased flood storage and wildlife habitat. • The backwater area and new reedbeds represent a new, highly valuable feeding and refuge area for fish. Recent studies have shown that both juvenile and adult fish move into these areas as soon as they are inundated. They feed extensively on the invertebrates present within the reedbeds. Such habitats are increasingly thought to significantly enhance the juvenile survival of commercially important fish such as bass. The Thames Estuary is now recognised as an important nursery area for this species.
• Retreat and renewal of flood defences to provide current standards of flood risk allowing for changes due to climate change.
• New site entrance and access route through site.
• Creation of new seating and viewing areas.
• Interpretation boards installed with the aid of Lee Rivers Trust and local school children helped design the boards
Monitoring surveys and results
Lessons learnt
Catchment and subcatchment
Edit the catchment and subcatchment details
(affects all case studies in this subcatchment)
Site
Name | Barking Creekmouth |
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WFD water body codes | |
WFD (national) typology | Intertidal |
WFD water body name | |
Pre-project morphology | Estuary (tidal) |
Reference morphology | |
Desired post project morphology | |
Heavily modified water body | Yes |
National/international site designation | |
Local/regional site designations | saltmarsh and mudflat BAP habitat |
Protected species present | No |
Invasive species present | Yes |
Species of interest | Japanese knotweed (Fallopia japonica), sea bass (Dicentrarchus labrax), European eel (Anguilla anguilla), flounder (Platichthys flesus), Thin lipped mullet (Liza ramada), Sand goby (Pomatoschistus minutes), teal, shelduck, wigeon, gadwell, shoveler, pintail, duck (Anas sp.), oyster catchers, peregrine falcon, sand smelt (Atherina presbyter) |
Dominant hydrology | Tidal |
Dominant substrate | Estuarine mud |
River corridor land use | 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) |
Project background
Reach length directly affected (m) | 100100 m <br />0.1 km <br />10,000 cm <br /> |
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Project started | |
Works started | |
Works completed | |
Project completed | 2006/03/31 |
Total cost category | 100 - 500 k€ |
Total cost (k€) | 284284 k€ <br />284,000 € <br /> |
Benefit to cost ratio | |
Funding sources | Environment Agency, Office of the Deputy Prime Minister’s (now DCLG) Sustainable Communities Fund |
Cost for project phases
Phase | cost category | cost exact (k€) | Lead organisation | Contact forename | Contact surname |
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Investigation and design | |||||
Stakeholder engagement and communication | |||||
Works and works supervision | |||||
Post-project management and maintenance | |||||
Monitoring |
Reasons for river restoration
Measures
Structural measures
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Bank/bed modifications | |
Floodplain / River corridor | |
Planform / Channel pattern | |
Other | |
Non-structural measures
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Management interventions | |
Social measures (incl. engagement) | |
Other |
Monitoring
Hydromorphological quality elements
Element | When monitored | Type of monitoring | Control site used | Result | ||
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Before measures | After measures | Qualitative | Quantitative |
Biological quality elements
Element | When monitored | Type of monitoring | Control site used | Result | ||
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Before measures | After measures | Qualitative | Quantitative | |||
Fish | Yes | Yes | No | No | No | Improvement |
Physico-chemical quality elements
Element | When monitored | Type of monitoring | Control site used | Result | ||
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Before measures | After measures | Qualitative | Quantitative |
Any other monitoring, e.g. social, economic
Element | When monitored | Type of monitoring | Control site used | Result | ||
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Before measures | After measures | Qualitative | Quantitative |
Monitoring documents
Image gallery
Additional documents and videos
Additional links and references
Link | Description |
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Supplementary Information
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