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Integrated catchment management: from
rhetoric to reality in a Scottish HELP basin
     Alan Werritty 1, Chris Spray1, Tom Ball 1 Mike Bonell 1,
   Josselin Rouillard 1, Alan MacDonald 2, Luke Comins 3 and
                         Roy Richardson 4
      1 UNESCO   Centre for Water Law, Policy and Science,
                       University of Dundee
                    2 British Geological Survey

                           3 Tweed Forum

           4 Scottish Environment Protection Agency
Outline

•   UNESCO HELP programme: promoting ‘healthy rivers’
•   Policy drivers for river restoration: Eddleston Water
•   Characterisation and current status
•   Proposed measures
•   Opportunities, constraints and barriers
•   Conclusions
UNESCO HELP programme
• Hydrology for the Environment, Life and Policy
  (HELP) established by UNESCO in 1999
• Global network of c. 90 basins “delivering social,
  economic and environmental benefits to stakeholders
  through research towards sustainable and
  appropriate use of water”
• Articulation between stakeholders and scientists
  means breaking the paradigm lock yielding rapid and
  agreed solutions and, if needed, resetting policy.
• River Tweed designated a HELP basin in 2008 –
  Eddleston Water proposed for river restoration 2009
Paradigm lock in integrated catchment management
Policy drivers for river restoration: Eddleston Water
 Two main policy drivers:
 • EC Water Framework Directive => Water Environment
 and Water Services (Scotland) Act 2003: Eddleston Water
 characterised as having “poor” ecological status
 • EC Directive on the Assessment and Management of
 Floods => Flood Risk Management (Scotland) Act 2009:
 section 20 requires SEPA to assess whether the
 “alteration ... or restoration of natural features and
 characteristics ... could contribute to management of
 flood risk” often referred to as natural flood
 management
Characterisation and current status: topography
                     Eddleston Water a south-flowing
                     tributary of Tweed draining 69 km2
                     • fractured greywackes mantled with
                     highly variable covers of till, fluvio-
                     glacial outwash and peat
                     • annual precipitation: 850 mm (valley
                     floor)-1500 mm (summits)
                     • steeper slopes east of main stem =>
                     flashy runoff: gentler slopes west of
                     main stem => delayed flow.
                     QMED c. 23 m3s-1 , Q10 c. 38 m3s-1
                     • ideal exemplar of “source-pathway-
                     receptor” flood risk management
                     model
Characterisation and current status: land cover

                            Land cover
                            • improved grassland
                            dominate valley floor and
                            lower slopes
                            • extensive Forestry
                            Commission woodland
                            west side of catchment
                            • small areas of fen and
                            incipient wetlands
                            adjacent to main stem


         Km
Characterisation and current status: landscapes
                                          Sources




                                          Pathways
Characterisation and current status: channelisation
                                               Roy Map




                          Main stem sinuous c.1750: but
                          extensively channelised by 1811
                          Minimal recovery since and main
                          reason for ‘poor’ WFD status
                          because of current
                          hydromorphology
Characterisation and current status: habitat




Bad     Poor    Moderate   Satisfactory   Good   Very good
Characterisation and current status: fisheries
Characterisation and current status: hydrometry

                          Poor current hydrometry:
                          2 stage only gauging stations
                          and 1 raingauge.

                          Estimates of bankfull
                          discharge on tributaries (blue)
                          and main stem (yellow)

                          Waterheads: c. 3 m3s-1

                          Eddleston Village c. 10 m3s-1

                          Peebles c. 19 m3s-1
Characterisation and current status: flood risk
                       Annual flood            Return             Discharge
                       risk probability        period (yrs)      (m3s-1)
                       QMED                    2                  22.8
                       0.2                     15                 31.7
                       0.1                     10                 38.1
                       0.05                    20                 47.1
                       0.02                    50                 54.8
                       0.01                    100                63.5
                       0.005                   200                73.2
                     Source: JBA Consulting 2008

                                                              Peebles
                                                              flooded
                                                              every 5-10
                                                              years.

                                                              Currently no
                                                              structural
                       Scottish Borders                       defences,
                       Council identifies 589                 only flood
                       properties within                      warning
                       SEPA’s 1:200 year flood                scheme.
                       envelope.
Characterisation and current status: summary
      • fails to achieve WFD ‘good’ status –
      because of ‘poor’ hydromorphology
      • channelised reaches of main stem poor
      habitat (poor mix of channel types, lack of
      riparian vegetation)
      • highest runoff from eastern tributaries and
      rapid increase in downstream bankfull
      discharge
      • catchment ideal exemplar for flood risk
      management measures (source-pathway-
      receptor) no structural defences
Proposed measures: overall aim

... “to restore river and its whole catchment
whilst at the same time promoting
livelihoods of those who derive income
from the sustainable management of
farms, forests and fishery”:
• improved physical habitat;
• reduction in flood risk;
whilst promoting sustainable management of
farms, fisheries and forestry and recreational
opportunities for tourists.
Proposed measures: typology
Groups of 15 measures:
1 and 2 designed to improve habitat (planting riparian vegetation
and restricting stock access to the channel);
 3, 4 and 5 create more natural channel morphology (increased
sinuosity with decreased plane beds and greater differentiation into
pools, riffles and glides)
 6, 7 and 8 (breaching/removing embankments, planting floodplain
forests, introducing large woody debris) to provide temporary flood
storage, increase roughness and enhance riparian habitat
9 to 15 to reduce flood risk by decreasing the rate at which runoff is
generated in source areas:
• by increasing infiltration and storage of surface and soil water
(9, 10, 11, 12 and 13)
• by slowing rate at which runoff is conveyed via tributaries to
main stem (14, 15).
Proposed measures: location

            Selected groups of measures:
            A: breach/set back embankments,
            new fence margins, riparian
            woodland, wet woodland, large
            woody debris
            C: re-meander channel, riparian
            woodland
            L: Reduced stocking density, tributary
            woodland, floodplain forest
            N: create ponds, wetlands, riparian
            woodland block ditches, large woody
            debris
Proposed measures: flood storage Site A
Opportunities, constraints and barriers
                  • Interviews with key
                    stakeholders: Scottish Govt,
                    SEPA, Tweed Forum, Scottish
                    Borders Council, SNH, Tweed
                    Foundation, Scottish Water,
                    NFU(Scotland), Scottish Wildlife
                    Trust, Country Landowners
                    Business Association.
                  • Interviews with five landowners
                    (three floodplain and two
                    upland famers) middle-aged,
                    male, long-term landowners in
                    the valley (>30 years) with
                    several sources of income.
Opportunities, constraints and barriers: institutional

   • Legal constraints: EC Environmental regulation (Water
   Framework Directive and Habitats Directives) operation of
   statutory duties by SEPA and SNH;
   • Land use policy: high quality agricultural land on floodplains
   for food or flood control? Delivery of agri-environmental
   schemes over longer timespans (eg planting woodlands);
   • Land tenure: contrasting planning horizons for tenant
   farmers, owner-occupiers and large estates – value of multiple
   benefit measures (eg Coed Cymru project in Central Wales);
   • Quality of science: nature of science evidence base crucial in
   persuading land managers;
Opportunities, constraints and barriers: farmers

• understand aspirations and
land tenure systems of the
farming community – a real
opportunity and a threat;
• develop trust and a common
vision for aims of the restoration
programme;
• role of intermediary,
stakeholder-led organisation, via
technical and social support
networks (Tweed Forum highly
valued);
Opportunities, constraints and barriers: farmers


                        • local expert knowledge must be
                        factored in to any planning;
                        • financial incentives must be set
                        at the right level – to sustain farm
                        units and to attract engagement;
                        • long-term, guaranteed
                        contractual arrangements to
                        deliver focused outcomes;
                        • simplicity in any contractual
                        arrangements.
Conclusions
• Scientists lose some professional autonomy and deliver to
agendas set by the stakeholders – this a challenging change;
• Significant time and effort to engage with the local
community and landowners in framing project prior to
implementation – building up trust key to success;
• “Politics is the art of the possible”. Insights in terms of
potential legal, organisational, socio-economic, cultural and
scientific barriers should facilitate next phase and increase
chances of success;
• Crucial to work ‘with nature’ in ways that sustainably
maintain livelihoods of those who derive their living from
the river basin.

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Integrated catchment management: from rhetoric to reality in a Scottish HELP basin

  • 1. Integrated catchment management: from rhetoric to reality in a Scottish HELP basin Alan Werritty 1, Chris Spray1, Tom Ball 1 Mike Bonell 1, Josselin Rouillard 1, Alan MacDonald 2, Luke Comins 3 and Roy Richardson 4 1 UNESCO Centre for Water Law, Policy and Science, University of Dundee 2 British Geological Survey 3 Tweed Forum 4 Scottish Environment Protection Agency
  • 2. Outline • UNESCO HELP programme: promoting ‘healthy rivers’ • Policy drivers for river restoration: Eddleston Water • Characterisation and current status • Proposed measures • Opportunities, constraints and barriers • Conclusions
  • 3. UNESCO HELP programme • Hydrology for the Environment, Life and Policy (HELP) established by UNESCO in 1999 • Global network of c. 90 basins “delivering social, economic and environmental benefits to stakeholders through research towards sustainable and appropriate use of water” • Articulation between stakeholders and scientists means breaking the paradigm lock yielding rapid and agreed solutions and, if needed, resetting policy. • River Tweed designated a HELP basin in 2008 – Eddleston Water proposed for river restoration 2009
  • 4. Paradigm lock in integrated catchment management
  • 5. Policy drivers for river restoration: Eddleston Water Two main policy drivers: • EC Water Framework Directive => Water Environment and Water Services (Scotland) Act 2003: Eddleston Water characterised as having “poor” ecological status • EC Directive on the Assessment and Management of Floods => Flood Risk Management (Scotland) Act 2009: section 20 requires SEPA to assess whether the “alteration ... or restoration of natural features and characteristics ... could contribute to management of flood risk” often referred to as natural flood management
  • 6. Characterisation and current status: topography Eddleston Water a south-flowing tributary of Tweed draining 69 km2 • fractured greywackes mantled with highly variable covers of till, fluvio- glacial outwash and peat • annual precipitation: 850 mm (valley floor)-1500 mm (summits) • steeper slopes east of main stem => flashy runoff: gentler slopes west of main stem => delayed flow. QMED c. 23 m3s-1 , Q10 c. 38 m3s-1 • ideal exemplar of “source-pathway- receptor” flood risk management model
  • 7. Characterisation and current status: land cover Land cover • improved grassland dominate valley floor and lower slopes • extensive Forestry Commission woodland west side of catchment • small areas of fen and incipient wetlands adjacent to main stem Km
  • 8. Characterisation and current status: landscapes Sources Pathways
  • 9. Characterisation and current status: channelisation Roy Map Main stem sinuous c.1750: but extensively channelised by 1811 Minimal recovery since and main reason for ‘poor’ WFD status because of current hydromorphology
  • 10. Characterisation and current status: habitat Bad Poor Moderate Satisfactory Good Very good
  • 11. Characterisation and current status: fisheries
  • 12. Characterisation and current status: hydrometry Poor current hydrometry: 2 stage only gauging stations and 1 raingauge. Estimates of bankfull discharge on tributaries (blue) and main stem (yellow) Waterheads: c. 3 m3s-1 Eddleston Village c. 10 m3s-1 Peebles c. 19 m3s-1
  • 13. Characterisation and current status: flood risk Annual flood Return Discharge risk probability period (yrs) (m3s-1) QMED 2 22.8 0.2 15 31.7 0.1 10 38.1 0.05 20 47.1 0.02 50 54.8 0.01 100 63.5 0.005 200 73.2 Source: JBA Consulting 2008 Peebles flooded every 5-10 years. Currently no structural Scottish Borders defences, Council identifies 589 only flood properties within warning SEPA’s 1:200 year flood scheme. envelope.
  • 14. Characterisation and current status: summary • fails to achieve WFD ‘good’ status – because of ‘poor’ hydromorphology • channelised reaches of main stem poor habitat (poor mix of channel types, lack of riparian vegetation) • highest runoff from eastern tributaries and rapid increase in downstream bankfull discharge • catchment ideal exemplar for flood risk management measures (source-pathway- receptor) no structural defences
  • 15. Proposed measures: overall aim ... “to restore river and its whole catchment whilst at the same time promoting livelihoods of those who derive income from the sustainable management of farms, forests and fishery”: • improved physical habitat; • reduction in flood risk; whilst promoting sustainable management of farms, fisheries and forestry and recreational opportunities for tourists.
  • 16. Proposed measures: typology Groups of 15 measures: 1 and 2 designed to improve habitat (planting riparian vegetation and restricting stock access to the channel); 3, 4 and 5 create more natural channel morphology (increased sinuosity with decreased plane beds and greater differentiation into pools, riffles and glides) 6, 7 and 8 (breaching/removing embankments, planting floodplain forests, introducing large woody debris) to provide temporary flood storage, increase roughness and enhance riparian habitat 9 to 15 to reduce flood risk by decreasing the rate at which runoff is generated in source areas: • by increasing infiltration and storage of surface and soil water (9, 10, 11, 12 and 13) • by slowing rate at which runoff is conveyed via tributaries to main stem (14, 15).
  • 17. Proposed measures: location Selected groups of measures: A: breach/set back embankments, new fence margins, riparian woodland, wet woodland, large woody debris C: re-meander channel, riparian woodland L: Reduced stocking density, tributary woodland, floodplain forest N: create ponds, wetlands, riparian woodland block ditches, large woody debris
  • 18. Proposed measures: flood storage Site A
  • 19. Opportunities, constraints and barriers • Interviews with key stakeholders: Scottish Govt, SEPA, Tweed Forum, Scottish Borders Council, SNH, Tweed Foundation, Scottish Water, NFU(Scotland), Scottish Wildlife Trust, Country Landowners Business Association. • Interviews with five landowners (three floodplain and two upland famers) middle-aged, male, long-term landowners in the valley (>30 years) with several sources of income.
  • 20. Opportunities, constraints and barriers: institutional • Legal constraints: EC Environmental regulation (Water Framework Directive and Habitats Directives) operation of statutory duties by SEPA and SNH; • Land use policy: high quality agricultural land on floodplains for food or flood control? Delivery of agri-environmental schemes over longer timespans (eg planting woodlands); • Land tenure: contrasting planning horizons for tenant farmers, owner-occupiers and large estates – value of multiple benefit measures (eg Coed Cymru project in Central Wales); • Quality of science: nature of science evidence base crucial in persuading land managers;
  • 21. Opportunities, constraints and barriers: farmers • understand aspirations and land tenure systems of the farming community – a real opportunity and a threat; • develop trust and a common vision for aims of the restoration programme; • role of intermediary, stakeholder-led organisation, via technical and social support networks (Tweed Forum highly valued);
  • 22. Opportunities, constraints and barriers: farmers • local expert knowledge must be factored in to any planning; • financial incentives must be set at the right level – to sustain farm units and to attract engagement; • long-term, guaranteed contractual arrangements to deliver focused outcomes; • simplicity in any contractual arrangements.
  • 23. Conclusions • Scientists lose some professional autonomy and deliver to agendas set by the stakeholders – this a challenging change; • Significant time and effort to engage with the local community and landowners in framing project prior to implementation – building up trust key to success; • “Politics is the art of the possible”. Insights in terms of potential legal, organisational, socio-economic, cultural and scientific barriers should facilitate next phase and increase chances of success; • Crucial to work ‘with nature’ in ways that sustainably maintain livelihoods of those who derive their living from the river basin.