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Key governance issues and the fate of
secondary forests as a tool for large-
scale forest restoration
Manuel R. Guariguata
ATBC
12 July 2017
The “three pillars” of forest governance
1. Policy, legal, institutional and
regulatory frameworks within and
outside the forest sector
2. Planning and decision-making
processes
3. Implementation, enforcement and
compliance
The key variables of “good” forest governance
• Clear user rights and responsibilities
• Participation by those who depend on forests
• Accountability of both users and decision-
makers
• Monitoring of management outcomes
• Enforcement of property rights
• Institutional capacities
From central - to - local
Governance and secondary
forest “permanence” – some
examples
Peru – agricultural and environmental benefits
of secondary forests politically divorced
 Land use planning falls under Ministry of Environment
yet Ministry of Agriculture governs land use change by
issuing titles and permits
 Hence the Ministry of Environment has little leverage to
support secondary forest conservation in spite of
implementing REDD+ payments
Indonesia – forestry agencies largely control
‘degraded’ forest landscapes, funneling capital
subsidies to companies for masssive land use
change (displacing local communities) Ucayali, Perú
Ethiopia – lack of inclusiveness in
decision making
• “area exclosures” estimated at 3 M ha of
naturally regenerated forest
• Little local involvement through top-
down and paternalistic approaches
• Unclear co-management schemes
between governments and communities
• Poorly defined user rights thus generating
conflict
• Lack of proper planning influenced
success Tigray region; H Kassa
Mexico, Costa Rica – technocratic prescriptions disregarded local
needs….but progress was made!
• Up until 2016, a secondary forest needed a
management plan above 4 m2/ha and 15
trees/ha (dbh > 25 cm)
 Limited traditional harvesting of small-diameter
trees and incentivized clearing
 In the process of being modified to allow young
forest use without overregulation
• From 1999-2016, timber harvesting “shall
avoid the establishment of monoespecific
forest stands” in secondary forests
 Since this year, monocyclic systems are allowed
Some thoughts for moving forward
• Disaggregate “passive restoration”
 When (land) opportunity costs are low, human use is
minimal or else strict protection is to be applied
 When human use is an integral part of the system?
• Recognize that secondary forests are part of highly
dynamic socio-ecological systems unlikely to be
managed either by a single government sector or
scientific discipline
• Understand, from a political-institutional dimension,
what drives or hampers the permanence of
secondary forests (and for how long)
• Work towards curricular innovation and stimulate
cross-disciplinarity
Bibliography
Barr & Sayer. 2012. Biol. Cons. 154: 9-19
Guariguata & Brancalion. 2014. Forests 5(12)
Henao. 2014. M.Sc. Thesis, CATIE.
Lemenih & Kassa. 2014. Forests 5(8)
Ravikumar et al. 2015. Int. J. Comms. 9(2)
Roman-Dañobeytia et al. 2014. Forests 5(5)
Vieira et al. 2014. Forests 5(7)
cifor.org
blog.cifor.org
ForestsTreesAgroforestry.org
Gracias !

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Key governance issues and the fate of secondary forests as a tool for large-scale forest restoration

  • 1. Key governance issues and the fate of secondary forests as a tool for large- scale forest restoration Manuel R. Guariguata ATBC 12 July 2017
  • 2. The “three pillars” of forest governance 1. Policy, legal, institutional and regulatory frameworks within and outside the forest sector 2. Planning and decision-making processes 3. Implementation, enforcement and compliance
  • 3. The key variables of “good” forest governance • Clear user rights and responsibilities • Participation by those who depend on forests • Accountability of both users and decision- makers • Monitoring of management outcomes • Enforcement of property rights • Institutional capacities From central - to - local
  • 4. Governance and secondary forest “permanence” – some examples
  • 5. Peru – agricultural and environmental benefits of secondary forests politically divorced  Land use planning falls under Ministry of Environment yet Ministry of Agriculture governs land use change by issuing titles and permits  Hence the Ministry of Environment has little leverage to support secondary forest conservation in spite of implementing REDD+ payments Indonesia – forestry agencies largely control ‘degraded’ forest landscapes, funneling capital subsidies to companies for masssive land use change (displacing local communities) Ucayali, Perú
  • 6. Ethiopia – lack of inclusiveness in decision making • “area exclosures” estimated at 3 M ha of naturally regenerated forest • Little local involvement through top- down and paternalistic approaches • Unclear co-management schemes between governments and communities • Poorly defined user rights thus generating conflict • Lack of proper planning influenced success Tigray region; H Kassa
  • 7. Mexico, Costa Rica – technocratic prescriptions disregarded local needs….but progress was made! • Up until 2016, a secondary forest needed a management plan above 4 m2/ha and 15 trees/ha (dbh > 25 cm)  Limited traditional harvesting of small-diameter trees and incentivized clearing  In the process of being modified to allow young forest use without overregulation • From 1999-2016, timber harvesting “shall avoid the establishment of monoespecific forest stands” in secondary forests  Since this year, monocyclic systems are allowed
  • 8. Some thoughts for moving forward • Disaggregate “passive restoration”  When (land) opportunity costs are low, human use is minimal or else strict protection is to be applied  When human use is an integral part of the system? • Recognize that secondary forests are part of highly dynamic socio-ecological systems unlikely to be managed either by a single government sector or scientific discipline • Understand, from a political-institutional dimension, what drives or hampers the permanence of secondary forests (and for how long) • Work towards curricular innovation and stimulate cross-disciplinarity
  • 9. Bibliography Barr & Sayer. 2012. Biol. Cons. 154: 9-19 Guariguata & Brancalion. 2014. Forests 5(12) Henao. 2014. M.Sc. Thesis, CATIE. Lemenih & Kassa. 2014. Forests 5(8) Ravikumar et al. 2015. Int. J. Comms. 9(2) Roman-Dañobeytia et al. 2014. Forests 5(5) Vieira et al. 2014. Forests 5(7)

Editor's Notes

  1. Say something about the photo, when we took foresters they said it was not a plantation since it was not 3x3; Herborn et al on what drives success