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Prof Mark Reed
Birmingham City University
Research Manager, IUCN UK Peatland Programme
Payments for Ecosystem Services:
A Place-Based Approach
Introduction
The problem
2 What are our options?
 Nationalisation of land
 Information provision and capacity building
 Regulation
 Financial mechanisms
 Creation of new markets
What are our options?
 Nationalisation of land
 Information provision and capacity building
 Regulation
 Financial mechanisms
 Creation of new markets
Payments for Ecosystem Services
 A voluntary transaction where
 A well-defined ecosystem service (or land use
likely to secure that service)
 Is being “bought” by a (minimum one)
ecosystem service buyer
 From a (minimum one) ecosystem service
provider
 If and only if the ecosystem service provider
secures provision (conditionality)
Who should pay?
Putting a price-tag on nature?
Problems with PES
 How do you (cost-effectively) quantify the
ecosystem service benefits?
 How do you attribute ecosystem service
enhancements in complex systems where their
delivery is influenced by many factors?
 How do you prevent markets for one ecosystem
service compromising other services?
 Main approach to date: bundling and layering
Bundling and layering
Problems with bundling/layering
 Tend to target single habitats (ignore
interactions between wider ecosystems and
underplay role of cultural ecosystem services)
 Pay little attention to governance of ecosystem
services in complex social-ecological systems
 To be robust, PES schemes need multi-level
governance, based on a better understanding of
social dynamics and shared, cultural values
associated with habitats and ecosystem services
Bundling and/or
layering of the
widest possible
range of ecosystem
services over
multiple spatial and
temporal scales in
the same location
Multi-level
governance
mechanisms
Prices that reflect
the shared values
of multiple
ecosystem service
beneficiaries
A place-based approach to PES
Case Study
Approach
Deliberative, non-monetary
valuation with the development
of multi-level governance
mechanisms, including new
methods for monitoring and
verifying ecosystem service
delivery
Elicitation process
Deliberated values
Non-deliberated values
Value intention
Other-
regarding
values
Self-regarding
values
Value
dimensions
Value scale
Value to
society
Value to
individual
Value concept
Transcendental
values
Contextual
values
Value
Indicators
Value provider
Societal & cultural
values
Communal
values
Individual
values
Group
values
Deliberative value formation model
Phases
Phase 1 Underpinning
research
Phase 2 Piloting
Phase 3 Code
development
Phase 1: underpinning research
 Market research (interviews with businesses) & draft UK Code
 Analysis of international cases, to develop PES Best Practice Guide
 24 ecosystem service beneficiary interviews from selected sectors
 2 workshops & comparative analysis of pilot Peatland Code &
MoorFutures
 Stakeholder workshop & fieldwork with Local Nature Partnership to
develop a place-based approach for South Pennines
 Interviews with visitor giving schemes across the UK, with case
study research in Lake District National Park leading to phone apps
 Economic assessment of Code leading to project feasibility tool
 Emissions factors to cost-effectively monitor GHG emission
reductions from restoration projects
Phase 2: piloting
 Piloting with project developers: pilot restoration
and research projects in North Pennines,
Exmoor, Lake District and South Pennines, and
Peatland Action in Scotland. Field protocol for
assessing GHG emission reductions trialled in
further 22 sites
 Piloting with landowning community: 5 focus
groups with landowners and other stakeholders
 Piloting with the business community through
events organised by IUCN UK Peatland
Programme
Phase 3: Code development
 Governance structures: to oversee the operation
of the Code
 Peatland Restoration Handbook
 The UK Peatland Code 1.0 and final draft of the
Project Design Document were launched at the
World Forum on Natural Capital in Edinburgh, in
November 2015
Bundling and/or
layering of the
widest possible
range of ecosystem
services over
multiple spatial and
temporal scales in
the same location
Multi-level
governance
mechanisms
Prices that reflect
the shared values
of multiple
ecosystem service
beneficiaries
Findings
Findings
 Supply side:
 Complementary ecosystem services and trade-offs
associated with peatland restoration
 Interest from many stakeholders in layered schemes
that target payments for different ecosystem services
from different beneficiaries
 Bundled approach more realistic and likely to avoid
tradeoffs
 Potential to integrate payments for cultural services
via visitor giving schemes
Helping walkers and cyclists learn about
nature – and pay for it
Findings
 Initial business survey: limited awareness and
immediate opportunities (passing the buck down
the supply chain), local authorities more likely to
be sellers/intermediaries than buy on behalf of
taxpayers
 Market research for a peatland scheme: niche
but strong demand
 Result: water company funding for pilot phase,
launched Peatland Code 1.0 with initial
investment from a multinational
Bundling and/or
layering of the
widest possible
range of ecosystem
services over
multiple spatial and
temporal scales in
the same location
Multi-level
governance
mechanisms
Prices that reflect
the shared values
of multiple
ecosystem service
beneficiaries
A place-based approach to PES
Findings
 Highly dependent on institutional capacity of
local actors
 NGOs more likely to benefit in early phases
 Working with Welsh Government to open up to
commoners
 Developed methods for practitioners to cost-
effectively and easily monitor GHG emission
reductions
Bundling and/or
layering of the
widest possible
range of ecosystem
services over
multiple spatial and
temporal scales in
the same location
Multi-level
governance
mechanisms
Prices that reflect
the shared values
of multiple
ecosystem service
beneficiaries
A place-based approach to PES
Findings
 Social valuation of ecosystem services can help
quantify cultural and social value/impacts of
changes in ecosystem services arising from
restoration
 Impacts on production
(way of life?)
 Cultural benefits e.g.
aesthetics, access,
recreation
Findings
 A sense of duty and responsibility:
 “This is all about custodianship…It’s all about
sustainability. It’s about handing over something in a better
state than what you were lucky enough to get it at.”
(Cairngorms, storyteller 1)
 “You never become an estate owner through financial
reasoning…I think we are just stewards and passing
through and doing the best we can in many ways.”
(Dumfries, storyteller 2)
 “I do feel I am probably a better steward than a public
organisation because I have a heart, I have a stake in it.”
(Thurso, storyteller 2)
 “Because I’ve been there a long time, so know how it
changes. I’ve seen it for a long time now.” (Thurso,
storyteller 2)
Findings
 A sense of achievement, self-respect and belonging:
 “The hills have to have sheep, because this is the one and only
place where you find the Shetland sheep.” (Shetland, storyteller
1)
 “Shetland men have sheep.” (Shetland, storyteller 2)
 “The first time I went I was 1 year old. My mother had been going
since she was 11. In family terms, there’s a certain responsibility
over the years.” (Dumfries, storyteller 1)
 “I can see five kingdoms from up there… To be master of all you
survey is a wonderful thing.” (Dumfries, storyteller 1)
 “I love creating all the different habitats.” (Dumfries, storyteller 2)
 “You’ve got to understand a bit how it developed, why it looks
like that…how it got there and how old it is…you’ve got to have a
perception of that before you can appreciate them fully.” (Thurso,
storyteller 1)
Findings
 Concerns over threats to traditional way of life
 Managed burning and grouse in the Peak District
 Peak District burning
premium: example of
transcendental values
being reflected in fair
price negotiation
Findings
 Fair prices:
 Deliberated fair price ranged from £11.18 per tonne of
CO2 equivalent in Dumfries to £15.65 per tonne in
Thurso, with substantially higher prices reached in the
Peak District of £54 and £107 per tonne for
revegetation and ditch blocking respectively
 Additional payment sought by landowners, after
meeting the costs of restoring peatland under the
Code, was £2 per tonne of CO2 equivalent generated
through restoration in Thurso, £3 per tonne in
Dumfries and the Cairngorms, £3.50 per tonne in
Shetland and £4.30 per tonne in the Peak District
Conclusions
Benefits of place-based approach
 Co-ordinate delivery of ecosystem services between
different ecosystems and habitats to minimize
ecosystem service trade-offs
 Social valuation of ecosystem services, using a
structured, deliberative approach has the potential to
engage with and empower diverse stakeholders in the
design and governance of PES schemes
Benefits of place-based approach
 Monitoring and verification can engage empower
landowners and managers to monitor ecosystem
services, providing important feedbacks to sustainable
land management
 By eliciting a broader range
of shared values, including
transcendental values, it is
possible to better capture
cultural ecosystem services
and deliver value from PES to
a wider range of stakeholders
(not just buyers and sellers)
Challenges
Incompatibilities
with landowner
objectives
High perceived
risks among
sellers
Lack of business
awareness
Quantifying
biodiversity co-
benefits
Barriers to
collaboration
across property
boundaries
Future research
 Research challenges:
 Developing cost-effective
monitoring
 Understand & overcoming
barriers to collaboration for place-based PES
partnerships
 Different sellers have different motives, perceptions of
risk and values
Future policy
 Policy challenges:
 Integrating schemes for
multiple habitats and services:
a role for Government?
 Need to integrate public & private PES
 Opportunities: shrinking CAP
 Challenges: incompatible timescales?
 Social justice concerns: PES for commoners?
Find out more
www.profmarkreed.com
Twitter: @profmarkreed

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Place-based Payments for Ecosystem Services

  • 1. Prof Mark Reed Birmingham City University Research Manager, IUCN UK Peatland Programme Payments for Ecosystem Services: A Place-Based Approach
  • 4. 2 What are our options?  Nationalisation of land  Information provision and capacity building  Regulation  Financial mechanisms  Creation of new markets
  • 5. What are our options?  Nationalisation of land  Information provision and capacity building  Regulation  Financial mechanisms  Creation of new markets
  • 6. Payments for Ecosystem Services  A voluntary transaction where  A well-defined ecosystem service (or land use likely to secure that service)  Is being “bought” by a (minimum one) ecosystem service buyer  From a (minimum one) ecosystem service provider  If and only if the ecosystem service provider secures provision (conditionality)
  • 8. Putting a price-tag on nature?
  • 9. Problems with PES  How do you (cost-effectively) quantify the ecosystem service benefits?  How do you attribute ecosystem service enhancements in complex systems where their delivery is influenced by many factors?  How do you prevent markets for one ecosystem service compromising other services?  Main approach to date: bundling and layering
  • 11. Problems with bundling/layering  Tend to target single habitats (ignore interactions between wider ecosystems and underplay role of cultural ecosystem services)  Pay little attention to governance of ecosystem services in complex social-ecological systems  To be robust, PES schemes need multi-level governance, based on a better understanding of social dynamics and shared, cultural values associated with habitats and ecosystem services
  • 12. Bundling and/or layering of the widest possible range of ecosystem services over multiple spatial and temporal scales in the same location Multi-level governance mechanisms Prices that reflect the shared values of multiple ecosystem service beneficiaries A place-based approach to PES
  • 14.
  • 15. Approach Deliberative, non-monetary valuation with the development of multi-level governance mechanisms, including new methods for monitoring and verifying ecosystem service delivery
  • 16. Elicitation process Deliberated values Non-deliberated values Value intention Other- regarding values Self-regarding values Value dimensions Value scale Value to society Value to individual Value concept Transcendental values Contextual values Value Indicators Value provider Societal & cultural values Communal values Individual values Group values
  • 18. Phases Phase 1 Underpinning research Phase 2 Piloting Phase 3 Code development
  • 19. Phase 1: underpinning research  Market research (interviews with businesses) & draft UK Code  Analysis of international cases, to develop PES Best Practice Guide  24 ecosystem service beneficiary interviews from selected sectors  2 workshops & comparative analysis of pilot Peatland Code & MoorFutures  Stakeholder workshop & fieldwork with Local Nature Partnership to develop a place-based approach for South Pennines  Interviews with visitor giving schemes across the UK, with case study research in Lake District National Park leading to phone apps  Economic assessment of Code leading to project feasibility tool  Emissions factors to cost-effectively monitor GHG emission reductions from restoration projects
  • 20. Phase 2: piloting  Piloting with project developers: pilot restoration and research projects in North Pennines, Exmoor, Lake District and South Pennines, and Peatland Action in Scotland. Field protocol for assessing GHG emission reductions trialled in further 22 sites  Piloting with landowning community: 5 focus groups with landowners and other stakeholders  Piloting with the business community through events organised by IUCN UK Peatland Programme
  • 21. Phase 3: Code development  Governance structures: to oversee the operation of the Code  Peatland Restoration Handbook  The UK Peatland Code 1.0 and final draft of the Project Design Document were launched at the World Forum on Natural Capital in Edinburgh, in November 2015
  • 22. Bundling and/or layering of the widest possible range of ecosystem services over multiple spatial and temporal scales in the same location Multi-level governance mechanisms Prices that reflect the shared values of multiple ecosystem service beneficiaries Findings
  • 23. Findings  Supply side:  Complementary ecosystem services and trade-offs associated with peatland restoration  Interest from many stakeholders in layered schemes that target payments for different ecosystem services from different beneficiaries  Bundled approach more realistic and likely to avoid tradeoffs  Potential to integrate payments for cultural services via visitor giving schemes
  • 24. Helping walkers and cyclists learn about nature – and pay for it
  • 25. Findings  Initial business survey: limited awareness and immediate opportunities (passing the buck down the supply chain), local authorities more likely to be sellers/intermediaries than buy on behalf of taxpayers  Market research for a peatland scheme: niche but strong demand  Result: water company funding for pilot phase, launched Peatland Code 1.0 with initial investment from a multinational
  • 26. Bundling and/or layering of the widest possible range of ecosystem services over multiple spatial and temporal scales in the same location Multi-level governance mechanisms Prices that reflect the shared values of multiple ecosystem service beneficiaries A place-based approach to PES
  • 27. Findings  Highly dependent on institutional capacity of local actors  NGOs more likely to benefit in early phases  Working with Welsh Government to open up to commoners  Developed methods for practitioners to cost- effectively and easily monitor GHG emission reductions
  • 28.
  • 29.
  • 30.
  • 31.
  • 32.
  • 33.
  • 34. Bundling and/or layering of the widest possible range of ecosystem services over multiple spatial and temporal scales in the same location Multi-level governance mechanisms Prices that reflect the shared values of multiple ecosystem service beneficiaries A place-based approach to PES
  • 35. Findings  Social valuation of ecosystem services can help quantify cultural and social value/impacts of changes in ecosystem services arising from restoration  Impacts on production (way of life?)  Cultural benefits e.g. aesthetics, access, recreation
  • 36. Findings  A sense of duty and responsibility:  “This is all about custodianship…It’s all about sustainability. It’s about handing over something in a better state than what you were lucky enough to get it at.” (Cairngorms, storyteller 1)  “You never become an estate owner through financial reasoning…I think we are just stewards and passing through and doing the best we can in many ways.” (Dumfries, storyteller 2)  “I do feel I am probably a better steward than a public organisation because I have a heart, I have a stake in it.” (Thurso, storyteller 2)  “Because I’ve been there a long time, so know how it changes. I’ve seen it for a long time now.” (Thurso, storyteller 2)
  • 37. Findings  A sense of achievement, self-respect and belonging:  “The hills have to have sheep, because this is the one and only place where you find the Shetland sheep.” (Shetland, storyteller 1)  “Shetland men have sheep.” (Shetland, storyteller 2)  “The first time I went I was 1 year old. My mother had been going since she was 11. In family terms, there’s a certain responsibility over the years.” (Dumfries, storyteller 1)  “I can see five kingdoms from up there… To be master of all you survey is a wonderful thing.” (Dumfries, storyteller 1)  “I love creating all the different habitats.” (Dumfries, storyteller 2)  “You’ve got to understand a bit how it developed, why it looks like that…how it got there and how old it is…you’ve got to have a perception of that before you can appreciate them fully.” (Thurso, storyteller 1)
  • 38. Findings  Concerns over threats to traditional way of life  Managed burning and grouse in the Peak District  Peak District burning premium: example of transcendental values being reflected in fair price negotiation
  • 39. Findings  Fair prices:  Deliberated fair price ranged from £11.18 per tonne of CO2 equivalent in Dumfries to £15.65 per tonne in Thurso, with substantially higher prices reached in the Peak District of £54 and £107 per tonne for revegetation and ditch blocking respectively  Additional payment sought by landowners, after meeting the costs of restoring peatland under the Code, was £2 per tonne of CO2 equivalent generated through restoration in Thurso, £3 per tonne in Dumfries and the Cairngorms, £3.50 per tonne in Shetland and £4.30 per tonne in the Peak District
  • 41. Benefits of place-based approach  Co-ordinate delivery of ecosystem services between different ecosystems and habitats to minimize ecosystem service trade-offs  Social valuation of ecosystem services, using a structured, deliberative approach has the potential to engage with and empower diverse stakeholders in the design and governance of PES schemes
  • 42. Benefits of place-based approach  Monitoring and verification can engage empower landowners and managers to monitor ecosystem services, providing important feedbacks to sustainable land management  By eliciting a broader range of shared values, including transcendental values, it is possible to better capture cultural ecosystem services and deliver value from PES to a wider range of stakeholders (not just buyers and sellers)
  • 43. Challenges Incompatibilities with landowner objectives High perceived risks among sellers Lack of business awareness Quantifying biodiversity co- benefits Barriers to collaboration across property boundaries
  • 44. Future research  Research challenges:  Developing cost-effective monitoring  Understand & overcoming barriers to collaboration for place-based PES partnerships  Different sellers have different motives, perceptions of risk and values
  • 45. Future policy  Policy challenges:  Integrating schemes for multiple habitats and services: a role for Government?  Need to integrate public & private PES  Opportunities: shrinking CAP  Challenges: incompatible timescales?  Social justice concerns: PES for commoners?