Case study:Little Don Catchment Case Study: Difference between revisions

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{{Project overview
|Project title=Little Don Catchment Case Study
|Status=Complete
|Status=Complete
|Themes=Environmental flows and water resources
|Themes=Environmental flows and water resources
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|Contact organisation=Environment Agency
|Contact organisation=Environment Agency
|Contact organisation url=https://www.catchmentbasedapproach.org/index.php?option=com_k2&view=item&layout=item&id=29&Itemid=244
|Contact organisation url=https://www.catchmentbasedapproach.org/index.php?option=com_k2&view=item&layout=item&id=29&Itemid=244
|Partner organisations=Yorkshire Water;
|Name of parent multi-site project=
|Multi-site=No
|Multi-site=No
|Project picture=River Don map.png
|Project summary=1. Brief Outline of Scheme
The Little Don rises in the Peak District National Park and joins the River Don just south of Stocksbridge town, a river length of about 20km. Flow in the watercourses are heavily regulated and managed by three reservoirs and several smaller impounding weirs. The reservoirs are operated by Yorkshire Water, with Langsett and Midhope reservoirs being operated for water storage, and Underbank reservoir for a compensation flow release.
Langsett and Midhope reservoirs modify the downstream flow regimes by buffering the range and magnitude of flows. As a result the baseflow is lower than would be expected naturally and the timing and magnitude of autumn/winter high flows is dependent on the levels in the reservoirs during this time. A compensating flow is released from Underbank reservoir (the bottom reservoir of the group), although analysis of catchment inflows and rainfall patterns has shown this to be too high, a legacy of the industrial use of the Don catchment. Other Yorkshire Water reservoir compensation flow release trials have demonstrated that modifying flows to more naturally flow regimes can improve the quantity and diversity of the ecological community. The Little Don is defined as a Heavily Modified Water Body (HMWB) under the Water Framework Directive and assessed at moderate ecological potential, with an objective to improve to good ecological potential by 2027;
this WFD objective is the main driver for the scheme.
Barriers along the Little Don have been observed to significantly reduce ecological connectivity with large proportions of the watercourses under-used by trout and other fish. Whilst the barriers restrict the movement of coarse sediment, studies were inconclusive on the extent of the problem. Additional pressures within the catchment include water pollution (including minewater discharges) and invasive non-native species (such as the New Zealand mud snail).
2. How the scheme was developed
The Don Network plan originally included wide consultation, the outcomes of which included an action on the Environment Agency and Yorkshire Water to investigate these pressures further. Funding has been sourced through the water industry National Environment Programme for action by Yorkshire Water to reduce the environmental pressures caused by the operation of the reservoirs, particularly to the flow regime of the Little Don.
A working group composed of representatives from the Environment Agency and Yorkshire Water developed a range of options, focusing on confirmed pressures and those directly linked to the reservoirs and impoundments; flow regulation and barriers.
The Coal Authority led on plans for the construction of a minewater treatment plant.
The Environment Agency’s Yorkshire and North East regional fish pass prioritisation project identified a number of priority actions to improve fish passage. For example, installation of a fish pass on a weir used for industrial water supply would double the length of the Little Don accessible to fish from the River Don.
3. What the scheme will deliver
Action to improve flow regulation: These aim for the best possible flow regime downstream of the reservoirs without impacting on water supply. Yorkshire Water are appraising the costs and benefits of a range of options to provide more natural flows downstream of Langsett, Midhope and Underbank reservoirs.
Action to reduce barriers: Flow changes alone would not solve the problem as barriers would continue to limit the migration of fish and modify the flow character of impounded reaches along the Little Don. The working group developed a range of barrier mitigation measures to either remove the weirs or install fish passes where this was not possible. Fish passes for the reservoir dams have not been progressed as costs are significantly higher than benefits.
Action to improve water quality: Water pollution from minewater discharge between Langsett and Underbank reservoirs has been reduced through the construction of a minewater treatment plant by the Coal Authority. The Environment Agency, Yorkshire Water, and Highways England are to trial a solution to deal with the small residual minewater discharge not currently being pumped through the Coal Authority’s treatment plant.
It is also expected that Yorkshire Water’s work with ‘Moor for the Future’ on grip blocking will further improve water quality.
The Don Network has actions in place to promote water quality solutions downstream of Underbank reservoir:
*  Collaborative working with polluters and adoption of new techniques
*  Raising awareness of Sustainable Urban Drainage Systems (SUDs) and encouraging local authorities and developers to incorporate SUDs more consistently in new developments
4. Costs and benefits
The expected benefits of a more natural flow regime would be:
*An increase in the level of diversity and variability in both physical habitat and ecology.
*An increase in fish densities, growth rates, spawning and resilience.
*Improvement in longitudinal connectivity along a watercourse allowing fish to access areas that may have previously been under-used.
*Enhancement of physical processes along a watercourse, increasing scour, flushing deposited sediments downstream, and re-oxygenating gravels.
Mitigating the barriers is expected to have a range of benefits:
*Direct benefits to fish and other aquatic organisms by allowing free movement of populations
*Indirect benefits to plants and other aquatic organisms by naturalising in-channel habitats
*Improvements to flow patterns and a reduction in impoundment
*Improvements in the transport of sediment and a reduction in sediment accumulation upstream of the structure
*Restoration of natural processes, including erosion and deposition
Options appraisal identified that building a fish pass upstream of Langsett reservoir, was cost beneficial. Whilst quite a modest option compared to the range of measures assessed, this option was favourable since the fish pass would allow about 5 km of under-used habitat to be accessible to brown trout and other fish currently living in Langsett reservoir. This measure will be in place by 2020.
|Monitoring surveys and results=5. Monitoring
Fish monitoring is taking place upstream and downstream of the new fish pass at Langsett. Yorkshire Water have also tagged fish to see if they approach the weir and what time of year. Walkover survey has been carried out with Yorkshire Water, Don Catchment Rivers Trust and the Environment Agency between Langsett and Underbank to identify issues and possible solutions. Monitoring will also be done before and after actions in the next water industry National Environment Programme.
|Project title=Little Don Catchment Case Study
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|Subcatchment=Little Don from Source to River Don
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{{Case study monitoring documents
|Monitoring document=Appendix 2 CaBA Case Studies - River Don final.pdf
|Description=River Don case study file
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{{Additional Documents}}
{{Additional Documents}}

Latest revision as of 09:54, 27 March 2018

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Location: 53° 29' 58.91" N, 1° 40' 10.60" W
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Project overview

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Status Complete
Project web site
Themes Environmental flows and water resources
Country England
Main contact forename sarah
Main contact surname Hyde
Main contact user ID
Contact organisation Environment Agency
Contact organisation web site http://https://www.catchmentbasedapproach.org/index.php?option=com k2&view=item&layout=item&id=29&Itemid=244
Partner organisations Yorkshire Water;
Parent multi-site project
This is a parent project
encompassing the following
projects
No
Project picture

Project summary

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1. Brief Outline of Scheme

The Little Don rises in the Peak District National Park and joins the River Don just south of Stocksbridge town, a river length of about 20km. Flow in the watercourses are heavily regulated and managed by three reservoirs and several smaller impounding weirs. The reservoirs are operated by Yorkshire Water, with Langsett and Midhope reservoirs being operated for water storage, and Underbank reservoir for a compensation flow release.

Langsett and Midhope reservoirs modify the downstream flow regimes by buffering the range and magnitude of flows. As a result the baseflow is lower than would be expected naturally and the timing and magnitude of autumn/winter high flows is dependent on the levels in the reservoirs during this time. A compensating flow is released from Underbank reservoir (the bottom reservoir of the group), although analysis of catchment inflows and rainfall patterns has shown this to be too high, a legacy of the industrial use of the Don catchment. Other Yorkshire Water reservoir compensation flow release trials have demonstrated that modifying flows to more naturally flow regimes can improve the quantity and diversity of the ecological community. The Little Don is defined as a Heavily Modified Water Body (HMWB) under the Water Framework Directive and assessed at moderate ecological potential, with an objective to improve to good ecological potential by 2027; this WFD objective is the main driver for the scheme.

Barriers along the Little Don have been observed to significantly reduce ecological connectivity with large proportions of the watercourses under-used by trout and other fish. Whilst the barriers restrict the movement of coarse sediment, studies were inconclusive on the extent of the problem. Additional pressures within the catchment include water pollution (including minewater discharges) and invasive non-native species (such as the New Zealand mud snail).

2. How the scheme was developed

The Don Network plan originally included wide consultation, the outcomes of which included an action on the Environment Agency and Yorkshire Water to investigate these pressures further. Funding has been sourced through the water industry National Environment Programme for action by Yorkshire Water to reduce the environmental pressures caused by the operation of the reservoirs, particularly to the flow regime of the Little Don.

A working group composed of representatives from the Environment Agency and Yorkshire Water developed a range of options, focusing on confirmed pressures and those directly linked to the reservoirs and impoundments; flow regulation and barriers. The Coal Authority led on plans for the construction of a minewater treatment plant.

The Environment Agency’s Yorkshire and North East regional fish pass prioritisation project identified a number of priority actions to improve fish passage. For example, installation of a fish pass on a weir used for industrial water supply would double the length of the Little Don accessible to fish from the River Don.

3. What the scheme will deliver

Action to improve flow regulation: These aim for the best possible flow regime downstream of the reservoirs without impacting on water supply. Yorkshire Water are appraising the costs and benefits of a range of options to provide more natural flows downstream of Langsett, Midhope and Underbank reservoirs.

Action to reduce barriers: Flow changes alone would not solve the problem as barriers would continue to limit the migration of fish and modify the flow character of impounded reaches along the Little Don. The working group developed a range of barrier mitigation measures to either remove the weirs or install fish passes where this was not possible. Fish passes for the reservoir dams have not been progressed as costs are significantly higher than benefits. Action to improve water quality: Water pollution from minewater discharge between Langsett and Underbank reservoirs has been reduced through the construction of a minewater treatment plant by the Coal Authority. The Environment Agency, Yorkshire Water, and Highways England are to trial a solution to deal with the small residual minewater discharge not currently being pumped through the Coal Authority’s treatment plant.

It is also expected that Yorkshire Water’s work with ‘Moor for the Future’ on grip blocking will further improve water quality.

The Don Network has actions in place to promote water quality solutions downstream of Underbank reservoir:

  • Collaborative working with polluters and adoption of new techniques
  • Raising awareness of Sustainable Urban Drainage Systems (SUDs) and encouraging local authorities and developers to incorporate SUDs more consistently in new developments

4. Costs and benefits

The expected benefits of a more natural flow regime would be:

  • An increase in the level of diversity and variability in both physical habitat and ecology.
  • An increase in fish densities, growth rates, spawning and resilience.
  • Improvement in longitudinal connectivity along a watercourse allowing fish to access areas that may have previously been under-used.
  • Enhancement of physical processes along a watercourse, increasing scour, flushing deposited sediments downstream, and re-oxygenating gravels.

Mitigating the barriers is expected to have a range of benefits:

  • Direct benefits to fish and other aquatic organisms by allowing free movement of populations
  • Indirect benefits to plants and other aquatic organisms by naturalising in-channel habitats
  • Improvements to flow patterns and a reduction in impoundment
  • Improvements in the transport of sediment and a reduction in sediment accumulation upstream of the structure
  • Restoration of natural processes, including erosion and deposition

Options appraisal identified that building a fish pass upstream of Langsett reservoir, was cost beneficial. Whilst quite a modest option compared to the range of measures assessed, this option was favourable since the fish pass would allow about 5 km of under-used habitat to be accessible to brown trout and other fish currently living in Langsett reservoir. This measure will be in place by 2020.

Monitoring surveys and results

Edit project overview to modify the Monitoring survey and results.


5. Monitoring

Fish monitoring is taking place upstream and downstream of the new fish pass at Langsett. Yorkshire Water have also tagged fish to see if they approach the weir and what time of year. Walkover survey has been carried out with Yorkshire Water, Don Catchment Rivers Trust and the Environment Agency between Langsett and Underbank to identify issues and possible solutions. Monitoring will also be done before and after actions in the next water industry National Environment Programme.

Lessons learnt

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Catchment and subcatchment

Catchment

River basin district Humber
River basin Don and Rother

Subcatchment

River name Little Don from Source to River Don
Area category 10 - 100 km²
Area (km2)
Maximum altitude category 500 - 1000 m
Maximum altitude (m) 539539 m <br />0.539 km <br />53,900 cm <br />
Dominant geology Siliceous
Ecoregion Great Britain
Dominant land cover Bog
Waterbody ID GB104027057460



Other case studies in this subcatchment: Sheephouse Wood Mine Water Treatment Scheme


Site

Name
WFD water body codes
WFD (national) typology
WFD water body name
Pre-project morphology
Reference morphology
Desired post project morphology
Heavily modified water body
National/international site designation
Local/regional site designations
Protected species present
Invasive species present
Species of interest
Dominant hydrology
Dominant substrate
River corridor land use
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)
Project started
Works started
Works completed
Project completed
Total cost category
Total cost (k€)
Benefit to cost ratio
Funding sources

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



Reasons for river restoration

Mitigation of a pressure Abstraction
Hydromorphology
Biology
Physico-chemical
Other reasons for the project


Measures

Structural measures
Bank/bed modifications
Floodplain / River corridor
Planform / Channel pattern
Other
Non-structural measures
Management interventions
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

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




Additional documents and videos


Additional links and references

Link Description

Supplementary Information

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