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Lessons from operationalizing integrated
landscape approaches
cifor.org/colands
James Reed
9th Landscape Sustainability Science Forum
11th May 2024
1980s 1990s 2000s 2010s ------------------- present
1980s: Integrated Rural
Development
1998: Integrated Natural Resource
Management (INRM)
1985 onwards: Integrated
Conservation & Development
projects (ICDPs)
Contributing Sciences:
Ecosystem Management
Landscape Ecology
Island biogeography
Conservation rooted frameworks
e.g. “Ecosystem Approach”
1983: “Landscape Approach”
first documented (Noss, 1983) 2013 - present:
(Integrated) Landscape
Approaches
2013: “Ten Principles for a
Landscape Approach”
(Sayer et al. 2013)
The evolution of integrated (landscape) approaches
(Reed et al. 2016,
Global Ch. Biol.)
• Global challenges are interrelated and require integrated solutions
• Sustainability transformations call for cross-sectoral thinking and approaches
• Implementation of GBF requires integrative governance
• Parties recognize the importance of integrated, holistic, and balanced non-market approaches
• Funding now increasingly targeted towards integrated projects
(Reed et al. 2020 One Earth)
Integrated approaches increasingly endorsed and
funded
Integrated
landscape
approaches
might aim to
Inspire transformational
change
Enhance resilience
Improve governance
Conserve biodiversity
Restore ecosystems
Mitigate climate change
Alleviate poverty
Why so popular?
• conceptual ambiguity leaves the approach open to
interpretation and in the realm of subjectivity and uncertainty
• greatly enhances the potential for the concept to be abused,
mis-assimilated, or co-opted
• implies a lack of basic norms and rules to follow with potential
for conceptually weak and poorly designed implementation
efforts
Despite enthusiasm, ILA definition or conceptual
framework is lacking
Latin America &
Caribbean (n 38)
Southern Africa (n 13)
South Asia (n 16)
East Asia & Pacific (n 33)
West Africa (n 16)
East Africa (n 41)
Multi-region (n 9)
Evidence of implementation
Reed et al. 2017 Land Use Policy
Evidence of impact?
Enhanced soil and water conservation, income, and crop production were the most frequently cited impacts (Reed et al. 2017)
Evidence of effectiveness?
“We show that despite considerable enthusiasm for
landscape approaches, the evidence base within the
scientific literature remains poorly developed”.
Peer
reviewed
articles
Grey
literature
(web
screening)
Grey
literature
(document
screening)
Totals
Case studies 24 97 53 174
Countries 16 52 42 61
Success 13 46 20 79
Reliable data 6 8 1 15
Generating impact from ILAs
• What gets measured, gets managed
(Drucker 1956, Stiglitz, 2010)
• An (unhealthy) obsession with
numbers, outcomes, and exit
strategies
• However, performance monitoring
tools are often not very useful in
answering how or why values change
• Meanwhile, traditional impact
assessment is challenging as
appropriate counterfactuals are lacking
(Chervier et al. 2020)
Not everything in life can be measured
• Not everything that matters can be measured, not everything that we
can measure, matters (Ridgway, 1956)
• What is really cared about might often be very difficult to measure
• Raising a child, performing a good deed, demonstrating good
judgement, humility, empathy, love…….
• Similarly, ILAs need to better capture social values and perceptions,
address power asymmetries, support community action, evaluate
governance performance, and account for conservation/development
trade-offs
Taking ILAs from theory to practice
Address knowledge-
implementation gap
Empower
marginalized
stakeholders
Facilitate multi-
stakeholder
dialogue
Raise awareness of
value of biodiversity
Test potential of
ILAs to reduce land
use conflicts
• Ecological experiments can support ILAs by (i) allowing researchers to determine
drivers and understand mechanisms which are often hard to elucidate in
observational studies in complex systems, and (ii) helping predict the outcome of
future events that have yet to happen.
• Public problems that contain a high level of complexity such as landscape
management (i.e. multiple dynamic systems, multiple problems and multiple
objectives, high level of risk, sociopolitical complexity, biological complexity, and
scientific uncertainty) make broader stakeholder involvement an absolute
necessity
• Research will be more effective if knowledge is co-produced with local people as
active participants rather than merely unrecognized sources or disengaged
recipients of information
• Requires the integration of two approaches: one focusing on conventional
scientific studies of biodiversity and biophysical parameters; and the other
focusing on the participation of relevant stakeholders, using various
participatory methods to co-create options that meet multiple stakeholder
needs (Reed et al. 2021, Landscape Ecology)
Re-integrating ecology into ILAs
Extensive policy and network analysis in each country
Political partners (Ghana: Forestry Commission, Zambia: Forestry Dept. and Ministry of
Land and Natural Resources, Indonesia: Executive Office of the President)
• Ensures the project becomes part of the inter-ministerial committee on climate change
• Promote the project at all levels of government
• Access data and information from other departments, including forest and land use data
Implementing partners (Ghana: UDS, Zambia: ZCBNRMF, Indonesia: Riak Bumi)
• Promote the implementation of landscape approaches for conservation, livelihoods and
adaptation to climate change, biodiversity conservation, democracy and governance
• Outreach through networks
Scientific partners
• University of Amsterdam (4 PhD candidates)
• University of British Columbia (2 Post-docs, 2 PhD candidates, MSc students)
Linking policy, practice, research
Core team and sites
Zambia – COLANDS site
ZCBNRM (partner)
Kaala Moombe country lead
Office and support staff
3 PhD students, 2 MSc
Indonesia – COLANDS site
Riak Bumi (partner)
Linda Yuliani country lead
Office and support staff
1 PhD
Ghana- COLANDS site
UDS (partner)
Mathurin Zida
country lead
3 PhDs, 2 MSc
UBC (Terry Sunderland)
Host 1 post-doc,
2 PhDs, MSc students
UvA (Mirjam Ros-Tonen)
Host 4 PhD students
Our focus in Zambia
Delayed or absent strategic dialogue: conversation over protected areas/encroachments typically
not held until issues get out of hand.
High levels of mistrust of the government by the customary communities/ illegal settlers’, caused by
lack of dialogue/honest communication about the different perceptions and facts related to
landscape (e.g., the KFR13 case)
Fragmented approach to development Uncoordinated efforts of agriculture and forestry depts. Lack
of cross-scale/sector dialogue
Ignoring local histories/colonial legacies (culture, etc.) and realities. Settlement in KFR13 was
authorized in the early years of its establishment. Weak governance and local capacity, native land
tenure and ownership rights ignored (e.g., on cultural heritages…sacred landscapes), env. change,
have led to frequent contestation and conflicts over access
Unrealistic application of external institutions (e.g., forest law/development interventions). Lack of
adaptive capacity/governance or understanding of implications of interventions to ‘restore’ the
landscape. Failure has led to conflicts and reduced trust/potential for trade-off negotiations.
Misaligned traditional and state governance systems: different claims, legal mandates, histories
Lack of self-mobilization/insufficient external support
Power asymmetries and gender disparity
Kalomo contextual background
Co-producing theory of change
(Reed et al. 2023, Sustainability Science)
Established common concerns in Kalomo
An agreement towards a shared future
Wants and desires:
• Improved actor and institutional coordination to
improve collective decision-making;
• Clarification of land-use boundaries;
• Better enforcement of regulations;
• Recognized and secured access rights;
• Enhanced resources for alternative and sustainable
land-use practices
Shared vision:
Improved consultation across scales of influence leading to
reduced deforestation, landscape restoration, and sustainable
NRM that improves river flow, water and food security, rural
infrastructure, income, and livelihoods.
What hinders implementation?
Interaction
• Lack of communication, collaboration, coordination
-CIFOR as brokering partner convenes regular CWG meetings
• Lack of agreement due to differing visions
- Scenario building and theory of change (Reed et al. 2023)
• Power relations
- Navigating power imbalances in landscape governance
(Siangulube et al. 2023)
Participation
• Absence of stakeholder groups
- Assessing the potential for private sector engagement in
integrated landscape approaches: Insights from value-
chain analyses in Southern Zambia (Upla et al. 2022)
• Varying levels of engagement
- Perceptions across scales of governance reveal demand
for forest landscape restoration in southern Zambia
(Siangulube et al.)
• Lack of capacity, skills
- Training of trainers in spatial mapping, applying ILA
principles
- Biodiversity guidelines (Reed et al. 2022)
Resource
• Limited financial resources
- Multiple funding applications
• Lack of/inaccessible data
- Monitoring forest cover change in Kalomo Hills local
forest using remote sensing and GIS: 1984–2018 (Mbanga
et al. 2021)
Institutional
• Incompatible national policies
- Potential for integration? An assessment of national
environment and development policies (O’Connor et al. 2020)
• Misaligned institutional structures
- Efforts to integrate local and scientific knowledge: The need
for decolonising knowledge for conservation and natural
resource management (Yanou et al. 2023)
Overcoming the barriers to implementation
Vermunt et al. 2020 Current Landscape Ecology Reports
• Uncertainty and project/process misalignment
• Getting everyone ‘around the table’ and who is a legitimate ‘stakeholder’
• Confronting distant drivers of harm
• Incomplete characterisation of ILAs/Understanding of how to do ILAs
• Poor incorporation of gender-related dimensions
• Lack of attention to deeply embedded socio-political issues and historical
legacies
• Poor understanding of cross-scale dynamics, interdependencies among levels of
governance, and inherent power structures
• Financing and capacity issues, lack of continuity/presence
• Trust / research fatigue with high-turnover projects
• Overlapping structures and sectoral planning
Other (ongoing) challenges
Clear need to redefine
conservation actions
• Widespread decline in environmental
health
• Falling capacity of nature to sustain NCP
Main drivers of biodiversity decline
• Related to wealth
• Stemming from ‘distant’
geographies
• Disproportionate impact
Telecoupled landscapes: distant wealth
and consumption threatens biodiversity
Three examples within the IUCN anthropogenic driver of ‘agriculture and aquaculture’
• Actions in biocultural landscapes
• Through
• protected areas: sectoral solution, ~bioD gains, yet
displacement, detachment, dispossession
• alternative livelihoods -alternative occupation/income or
method of extraction; substituting a livelihood strategy
• ‘Resolve poverty’ - a virtuous act propagates the white
saviour colonial style, rather than critically examine
poverty, or seeking to enhance wellbeing within diverse
notions of development
• Despite evidence on wealth, and shifts in policy fora
Contemporary conservation is not equipped for
addressing transboundary wealth-related flows
Site-level emphasis alone cannot deliver
justice or sustainability
• Unduly exonerates actors most responsible
for the biodiversity crisis
• Forfeits learning from biodiversity
stewards
• Ultimately is not (and will not) deliver
conservation
• Forced removals, payments/rewards can
perversely nudge in to supply chains
driving D, motivational crowding out
• Prohibition of practices resulting in erosion
of cultural lived experience marineconservationphilippines.org
Resource draining and intentional cost-shifting, e.g. agricultural
expansion (and related pollution), deforestation, over-fishing, IWT.
Extreme climatic events (e.g. floods, droughts, fires) drive
biodiversity loss in terrestrial, marine and fresh-water systems.
Progress defined as never-ending growth in capitalist economies,
homogenizes biological and cultural diversity, drives alienation and
rootlessness, powerful underlying driver of CC and Trade.
Conservation must disrupt and diminish the
dominant flows reducing biodiversity
Marginalized flows, yet contribute to conservation
Even while being eroded, local governance stands in direct contrast
to one-world development, supports biocultural centres to flourish
Ways of knowing & experiencing the world, influences species
mixes, agro-BioD, sustainable resource use and ‘intact’ landscapes.
Diverse and plural values; norms and accolades of ‘success’; moral,
gift and solidarity economies; diverse conceptions of a good life;
stewardship, reciprocity, connection.
Moves beyond conservation’s site-level emphasis
Actions in centres of wealth Actions in Biocultural Centres
• Desired states within which both biodiversity and humanity
can flourish
In centres of wealth:
• Gratification not growth – redefining ‘prosperity’
• Accountable trade – transparent, internalized externalities
In Biocultural centres:
• Autonomy and rights – empowered and enhanced
• Knowledge and value diversity – legitimized and recognized
Deconstruct norms and models, combined with articulating alternatives for
sustainable futures (Feola et al, 2021)
But moving towards what?
• Works to disrupt and diminish dominant flows, enhance and amplify
marginalized flows
• Requires actions across scales, interdisciplinary, and multi-sectoral
• Unconstrained by colonial ideas of site-level conservation
• Invites conservation to become more political
• Challenges the networks and norms of contemporary conservation
Connected conservation in summary
• Secure funding to continue transforming ToC into action
• Perspective on pervasive assumptions behind poverty-biodiversity
loss association
• Strengthening engagement with local and international institutions
• Two open special issue collections
Current efforts
Final takeaways
• To better engage with the realities of complex tropical landscapes, integrated
landscape approaches need to be long-term and transdisciplinary
• Moving away from the dichotomous language of success and failure, and rather
adopting a systems approach that prioritizes process and adaptation to
determine enabling conditions and lessons learned, will likely be more
constructive to the long-term sustainability of integrated landscape approaches
• Research that attempts to measure the things that count as well as counting
what can be measured is fundamental to building the evidence base and helping
understand under what conditions ILAs are workable and who benefits
• Conservation needs to expand its focus and extend its collaborations across
sectors to deliver to transformative change
Maybe the real treasure is the friends we made along the way
Thank you!
cifor.org/colands

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Lessons from operationalizing integrated landscape approaches

  • 1. Lessons from operationalizing integrated landscape approaches cifor.org/colands James Reed 9th Landscape Sustainability Science Forum 11th May 2024
  • 2. 1980s 1990s 2000s 2010s ------------------- present 1980s: Integrated Rural Development 1998: Integrated Natural Resource Management (INRM) 1985 onwards: Integrated Conservation & Development projects (ICDPs) Contributing Sciences: Ecosystem Management Landscape Ecology Island biogeography Conservation rooted frameworks e.g. “Ecosystem Approach” 1983: “Landscape Approach” first documented (Noss, 1983) 2013 - present: (Integrated) Landscape Approaches 2013: “Ten Principles for a Landscape Approach” (Sayer et al. 2013) The evolution of integrated (landscape) approaches (Reed et al. 2016, Global Ch. Biol.)
  • 3. • Global challenges are interrelated and require integrated solutions • Sustainability transformations call for cross-sectoral thinking and approaches • Implementation of GBF requires integrative governance • Parties recognize the importance of integrated, holistic, and balanced non-market approaches • Funding now increasingly targeted towards integrated projects (Reed et al. 2020 One Earth) Integrated approaches increasingly endorsed and funded
  • 4. Integrated landscape approaches might aim to Inspire transformational change Enhance resilience Improve governance Conserve biodiversity Restore ecosystems Mitigate climate change Alleviate poverty Why so popular?
  • 5. • conceptual ambiguity leaves the approach open to interpretation and in the realm of subjectivity and uncertainty • greatly enhances the potential for the concept to be abused, mis-assimilated, or co-opted • implies a lack of basic norms and rules to follow with potential for conceptually weak and poorly designed implementation efforts Despite enthusiasm, ILA definition or conceptual framework is lacking
  • 6. Latin America & Caribbean (n 38) Southern Africa (n 13) South Asia (n 16) East Asia & Pacific (n 33) West Africa (n 16) East Africa (n 41) Multi-region (n 9) Evidence of implementation Reed et al. 2017 Land Use Policy
  • 7. Evidence of impact? Enhanced soil and water conservation, income, and crop production were the most frequently cited impacts (Reed et al. 2017)
  • 8. Evidence of effectiveness? “We show that despite considerable enthusiasm for landscape approaches, the evidence base within the scientific literature remains poorly developed”. Peer reviewed articles Grey literature (web screening) Grey literature (document screening) Totals Case studies 24 97 53 174 Countries 16 52 42 61 Success 13 46 20 79 Reliable data 6 8 1 15
  • 9. Generating impact from ILAs • What gets measured, gets managed (Drucker 1956, Stiglitz, 2010) • An (unhealthy) obsession with numbers, outcomes, and exit strategies • However, performance monitoring tools are often not very useful in answering how or why values change • Meanwhile, traditional impact assessment is challenging as appropriate counterfactuals are lacking (Chervier et al. 2020)
  • 10. Not everything in life can be measured • Not everything that matters can be measured, not everything that we can measure, matters (Ridgway, 1956) • What is really cared about might often be very difficult to measure • Raising a child, performing a good deed, demonstrating good judgement, humility, empathy, love……. • Similarly, ILAs need to better capture social values and perceptions, address power asymmetries, support community action, evaluate governance performance, and account for conservation/development trade-offs
  • 11. Taking ILAs from theory to practice Address knowledge- implementation gap Empower marginalized stakeholders Facilitate multi- stakeholder dialogue Raise awareness of value of biodiversity Test potential of ILAs to reduce land use conflicts
  • 12. • Ecological experiments can support ILAs by (i) allowing researchers to determine drivers and understand mechanisms which are often hard to elucidate in observational studies in complex systems, and (ii) helping predict the outcome of future events that have yet to happen. • Public problems that contain a high level of complexity such as landscape management (i.e. multiple dynamic systems, multiple problems and multiple objectives, high level of risk, sociopolitical complexity, biological complexity, and scientific uncertainty) make broader stakeholder involvement an absolute necessity • Research will be more effective if knowledge is co-produced with local people as active participants rather than merely unrecognized sources or disengaged recipients of information • Requires the integration of two approaches: one focusing on conventional scientific studies of biodiversity and biophysical parameters; and the other focusing on the participation of relevant stakeholders, using various participatory methods to co-create options that meet multiple stakeholder needs (Reed et al. 2021, Landscape Ecology) Re-integrating ecology into ILAs
  • 13. Extensive policy and network analysis in each country Political partners (Ghana: Forestry Commission, Zambia: Forestry Dept. and Ministry of Land and Natural Resources, Indonesia: Executive Office of the President) • Ensures the project becomes part of the inter-ministerial committee on climate change • Promote the project at all levels of government • Access data and information from other departments, including forest and land use data Implementing partners (Ghana: UDS, Zambia: ZCBNRMF, Indonesia: Riak Bumi) • Promote the implementation of landscape approaches for conservation, livelihoods and adaptation to climate change, biodiversity conservation, democracy and governance • Outreach through networks Scientific partners • University of Amsterdam (4 PhD candidates) • University of British Columbia (2 Post-docs, 2 PhD candidates, MSc students) Linking policy, practice, research
  • 14. Core team and sites Zambia – COLANDS site ZCBNRM (partner) Kaala Moombe country lead Office and support staff 3 PhD students, 2 MSc Indonesia – COLANDS site Riak Bumi (partner) Linda Yuliani country lead Office and support staff 1 PhD Ghana- COLANDS site UDS (partner) Mathurin Zida country lead 3 PhDs, 2 MSc UBC (Terry Sunderland) Host 1 post-doc, 2 PhDs, MSc students UvA (Mirjam Ros-Tonen) Host 4 PhD students
  • 15. Our focus in Zambia Delayed or absent strategic dialogue: conversation over protected areas/encroachments typically not held until issues get out of hand. High levels of mistrust of the government by the customary communities/ illegal settlers’, caused by lack of dialogue/honest communication about the different perceptions and facts related to landscape (e.g., the KFR13 case) Fragmented approach to development Uncoordinated efforts of agriculture and forestry depts. Lack of cross-scale/sector dialogue Ignoring local histories/colonial legacies (culture, etc.) and realities. Settlement in KFR13 was authorized in the early years of its establishment. Weak governance and local capacity, native land tenure and ownership rights ignored (e.g., on cultural heritages…sacred landscapes), env. change, have led to frequent contestation and conflicts over access Unrealistic application of external institutions (e.g., forest law/development interventions). Lack of adaptive capacity/governance or understanding of implications of interventions to ‘restore’ the landscape. Failure has led to conflicts and reduced trust/potential for trade-off negotiations. Misaligned traditional and state governance systems: different claims, legal mandates, histories Lack of self-mobilization/insufficient external support Power asymmetries and gender disparity Kalomo contextual background
  • 16. Co-producing theory of change (Reed et al. 2023, Sustainability Science)
  • 18. An agreement towards a shared future Wants and desires: • Improved actor and institutional coordination to improve collective decision-making; • Clarification of land-use boundaries; • Better enforcement of regulations; • Recognized and secured access rights; • Enhanced resources for alternative and sustainable land-use practices Shared vision: Improved consultation across scales of influence leading to reduced deforestation, landscape restoration, and sustainable NRM that improves river flow, water and food security, rural infrastructure, income, and livelihoods.
  • 19. What hinders implementation? Interaction • Lack of communication, collaboration, coordination -CIFOR as brokering partner convenes regular CWG meetings • Lack of agreement due to differing visions - Scenario building and theory of change (Reed et al. 2023) • Power relations - Navigating power imbalances in landscape governance (Siangulube et al. 2023) Participation • Absence of stakeholder groups - Assessing the potential for private sector engagement in integrated landscape approaches: Insights from value- chain analyses in Southern Zambia (Upla et al. 2022) • Varying levels of engagement - Perceptions across scales of governance reveal demand for forest landscape restoration in southern Zambia (Siangulube et al.) • Lack of capacity, skills - Training of trainers in spatial mapping, applying ILA principles - Biodiversity guidelines (Reed et al. 2022) Resource • Limited financial resources - Multiple funding applications • Lack of/inaccessible data - Monitoring forest cover change in Kalomo Hills local forest using remote sensing and GIS: 1984–2018 (Mbanga et al. 2021) Institutional • Incompatible national policies - Potential for integration? An assessment of national environment and development policies (O’Connor et al. 2020) • Misaligned institutional structures - Efforts to integrate local and scientific knowledge: The need for decolonising knowledge for conservation and natural resource management (Yanou et al. 2023) Overcoming the barriers to implementation Vermunt et al. 2020 Current Landscape Ecology Reports
  • 20. • Uncertainty and project/process misalignment • Getting everyone ‘around the table’ and who is a legitimate ‘stakeholder’ • Confronting distant drivers of harm • Incomplete characterisation of ILAs/Understanding of how to do ILAs • Poor incorporation of gender-related dimensions • Lack of attention to deeply embedded socio-political issues and historical legacies • Poor understanding of cross-scale dynamics, interdependencies among levels of governance, and inherent power structures • Financing and capacity issues, lack of continuity/presence • Trust / research fatigue with high-turnover projects • Overlapping structures and sectoral planning Other (ongoing) challenges
  • 21. Clear need to redefine conservation actions • Widespread decline in environmental health • Falling capacity of nature to sustain NCP
  • 22. Main drivers of biodiversity decline • Related to wealth • Stemming from ‘distant’ geographies • Disproportionate impact
  • 23. Telecoupled landscapes: distant wealth and consumption threatens biodiversity Three examples within the IUCN anthropogenic driver of ‘agriculture and aquaculture’
  • 24. • Actions in biocultural landscapes • Through • protected areas: sectoral solution, ~bioD gains, yet displacement, detachment, dispossession • alternative livelihoods -alternative occupation/income or method of extraction; substituting a livelihood strategy • ‘Resolve poverty’ - a virtuous act propagates the white saviour colonial style, rather than critically examine poverty, or seeking to enhance wellbeing within diverse notions of development • Despite evidence on wealth, and shifts in policy fora Contemporary conservation is not equipped for addressing transboundary wealth-related flows
  • 25. Site-level emphasis alone cannot deliver justice or sustainability • Unduly exonerates actors most responsible for the biodiversity crisis • Forfeits learning from biodiversity stewards • Ultimately is not (and will not) deliver conservation • Forced removals, payments/rewards can perversely nudge in to supply chains driving D, motivational crowding out • Prohibition of practices resulting in erosion of cultural lived experience marineconservationphilippines.org
  • 26. Resource draining and intentional cost-shifting, e.g. agricultural expansion (and related pollution), deforestation, over-fishing, IWT. Extreme climatic events (e.g. floods, droughts, fires) drive biodiversity loss in terrestrial, marine and fresh-water systems. Progress defined as never-ending growth in capitalist economies, homogenizes biological and cultural diversity, drives alienation and rootlessness, powerful underlying driver of CC and Trade. Conservation must disrupt and diminish the dominant flows reducing biodiversity
  • 27. Marginalized flows, yet contribute to conservation Even while being eroded, local governance stands in direct contrast to one-world development, supports biocultural centres to flourish Ways of knowing & experiencing the world, influences species mixes, agro-BioD, sustainable resource use and ‘intact’ landscapes. Diverse and plural values; norms and accolades of ‘success’; moral, gift and solidarity economies; diverse conceptions of a good life; stewardship, reciprocity, connection.
  • 28. Moves beyond conservation’s site-level emphasis Actions in centres of wealth Actions in Biocultural Centres
  • 29. • Desired states within which both biodiversity and humanity can flourish In centres of wealth: • Gratification not growth – redefining ‘prosperity’ • Accountable trade – transparent, internalized externalities In Biocultural centres: • Autonomy and rights – empowered and enhanced • Knowledge and value diversity – legitimized and recognized Deconstruct norms and models, combined with articulating alternatives for sustainable futures (Feola et al, 2021) But moving towards what?
  • 30. • Works to disrupt and diminish dominant flows, enhance and amplify marginalized flows • Requires actions across scales, interdisciplinary, and multi-sectoral • Unconstrained by colonial ideas of site-level conservation • Invites conservation to become more political • Challenges the networks and norms of contemporary conservation Connected conservation in summary
  • 31. • Secure funding to continue transforming ToC into action • Perspective on pervasive assumptions behind poverty-biodiversity loss association • Strengthening engagement with local and international institutions • Two open special issue collections Current efforts
  • 32. Final takeaways • To better engage with the realities of complex tropical landscapes, integrated landscape approaches need to be long-term and transdisciplinary • Moving away from the dichotomous language of success and failure, and rather adopting a systems approach that prioritizes process and adaptation to determine enabling conditions and lessons learned, will likely be more constructive to the long-term sustainability of integrated landscape approaches • Research that attempts to measure the things that count as well as counting what can be measured is fundamental to building the evidence base and helping understand under what conditions ILAs are workable and who benefits • Conservation needs to expand its focus and extend its collaborations across sectors to deliver to transformative change
  • 33. Maybe the real treasure is the friends we made along the way Thank you! cifor.org/colands

Editor's Notes

  • #10: Full quote – even when pointless to measure or manage and therefore lead to undesirable results Measures set up incentives that drive people's behaviour
  • #11: Ridgway – Dysfunctional consequences of performance measurements
  • #20: A review by Vermunt helpfully provides a typology of barriers that obstruct implementation efforts (describe some – maybe show how your research maps to this)
  • #22: The starting point is a positional view that by enlarge, conservation is failing.
  • #24: Global portrait of biodiversity loss three examples within the IUCN anthropogenic driver of agriculture and aquaculture. Pink line = harvested area, and weight. Green line = export amount ave over last 3 yrs
  • #25: Note that high-level policy discourse shift to recognize contribution of IPLCs more, e.g. through ICCAs through CBD working groups etc
  • #29: Addressing biodiversity in an economically interconnected world challenges us to develop a revised model of conservation based on greater awareness of connections among actors. Targets dominant role of wealth in environmental health collapse.
  • #30: Generalized overarching themes or states