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Second World Congress of AgroforestryNairobi, Kenya, 23-28 August 2009Session 31A :Rewards for Environmental Services of Agroforestry Private and Social Values derived from a Tunisian  cork oak agroforestry production system  Hamed Daly-Hassen and Ameur Ben Mansoura  INRGREF,  Tunisia Dalyhassen.hamed@iresa.agrinet.tn
Outline Introduction Objectives Methods Results Conclusions
Introduction : The Cork Oak Forest The second most important forest cover in Tunisia, and one of the world’s hot spots in biodiversity conservation. Lack of clearly defined property rights Main activities : cork stripping,  livestock grazing, fuelwood collection Animal production insures more than half of the household’s income (Chebil & al. 2008).
Failure to consider full economic values Farmers and local forest users maximize their current commercial incomes from an intensive use of natural resources at present (subsistence economy) Costs of degradationare not considered Non market benefits and off site effects are not usually considered Need for compromises in order to maximize the social values and benefits.
Objectives ,[object Object]
Assess the external costs associated with the resulting forest degradation.
Value the environmental services provided by the country’s cork oak forests.
To identify appropriate economic instruments for the purpose of attaining greater sustainability of forest management.,[object Object]
Private Economic Value (PEV) vs. Social Economic Value (SEV) PEV = PB - PC With: PB = Private Benefts, and           PC = Private Costs   Wheras : SEV = (PB + EB) – (PC + EC) With: PB and PC as above, and           EB = External Benefits, and            EC = External Costs
Benefitsgenerated by the use of the Cork OakAgroforestry System
Costsrelated to the use ofCork OakAgroforestry System
Linking Cork Oak Production to Social Benefits Watershed protection Gain in agricultural income  Reduced dam sedimentation Carbon sequestration Reduced carbon emissions value at  carbon shadow price Recreation WTP for visiting forests Social welfare enhanced Biodiversity Opportunity cost of  cork oak production
Linking Cork Oak Forest Degradation to Social Costs Overgrazing Cost of forage substitute  Reduced forage potential  Soil erosion Increased dam sedimentation Loss of agricultural income  Tree cutting, forest degradation and lack of regeneration Loss of  current and future cork and acorns revenues  Reduced potential of cork and acorns Resource depletion Forest fires
Valuation techniques
Results : I. Private Benefits (PB) Private benefits attained $96.8/ ha. Equally distributed among the State (forest owner) and the local population.
Results : II. Private Costs (PC) Private costs attained $ 33.4/ ha. The overuse of common resources results in the induced private costs.
Results : III. External Benefits (EB) ,[object Object],[object Object]
Results : V. Private Benefits (PB) and Social Benefits (SB) ,[object Object]
 Degradation induces high social costs.,[object Object]
Conclusions (II)  Payment for environmental services : Involvement of downstream water users. More resources are needed from the global community concerned by carbon sequestration and biodiversity conservation.  Compensation for loss of income.   Comparison with the cost of degradation.  It can be fully covered by the resource rent.

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Hamed Daly-Hassen - Private and social values from Tunisian cork-oak agroforestry - Aug 2009

  • 1. Second World Congress of AgroforestryNairobi, Kenya, 23-28 August 2009Session 31A :Rewards for Environmental Services of Agroforestry Private and Social Values derived from a Tunisian cork oak agroforestry production system Hamed Daly-Hassen and Ameur Ben Mansoura INRGREF, Tunisia Dalyhassen.hamed@iresa.agrinet.tn
  • 2. Outline Introduction Objectives Methods Results Conclusions
  • 3. Introduction : The Cork Oak Forest The second most important forest cover in Tunisia, and one of the world’s hot spots in biodiversity conservation. Lack of clearly defined property rights Main activities : cork stripping, livestock grazing, fuelwood collection Animal production insures more than half of the household’s income (Chebil & al. 2008).
  • 4. Failure to consider full economic values Farmers and local forest users maximize their current commercial incomes from an intensive use of natural resources at present (subsistence economy) Costs of degradationare not considered Non market benefits and off site effects are not usually considered Need for compromises in order to maximize the social values and benefits.
  • 5.
  • 6. Assess the external costs associated with the resulting forest degradation.
  • 7. Value the environmental services provided by the country’s cork oak forests.
  • 8.
  • 9. Private Economic Value (PEV) vs. Social Economic Value (SEV) PEV = PB - PC With: PB = Private Benefts, and PC = Private Costs Wheras : SEV = (PB + EB) – (PC + EC) With: PB and PC as above, and EB = External Benefits, and EC = External Costs
  • 10. Benefitsgenerated by the use of the Cork OakAgroforestry System
  • 11. Costsrelated to the use ofCork OakAgroforestry System
  • 12. Linking Cork Oak Production to Social Benefits Watershed protection Gain in agricultural income Reduced dam sedimentation Carbon sequestration Reduced carbon emissions value at carbon shadow price Recreation WTP for visiting forests Social welfare enhanced Biodiversity Opportunity cost of cork oak production
  • 13. Linking Cork Oak Forest Degradation to Social Costs Overgrazing Cost of forage substitute Reduced forage potential Soil erosion Increased dam sedimentation Loss of agricultural income Tree cutting, forest degradation and lack of regeneration Loss of current and future cork and acorns revenues Reduced potential of cork and acorns Resource depletion Forest fires
  • 15. Results : I. Private Benefits (PB) Private benefits attained $96.8/ ha. Equally distributed among the State (forest owner) and the local population.
  • 16. Results : II. Private Costs (PC) Private costs attained $ 33.4/ ha. The overuse of common resources results in the induced private costs.
  • 17.
  • 18.
  • 19.
  • 20. Conclusions (II) Payment for environmental services : Involvement of downstream water users. More resources are needed from the global community concerned by carbon sequestration and biodiversity conservation. Compensation for loss of income. Comparison with the cost of degradation. It can be fully covered by the resource rent.
  • 21.
  • 22. Public owner and society are better off: avoid higher loss from current practice