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A Cost-Benefit Analysis Tool for
Zero Net Land Degradation Schemes




            Alan Grainger
            University of Leeds
Different Approaches

• Compare Benefits of Restoration With Costs
  of Land Degradation

• Compare Benefits/Costs of Restoration with
  Benefits/Costs of Land Degradation
Zero Net Land Degradation
            Reduce the rate of desertification +
             Increase the rate of restoration of
                      desertified land

             African Union (2012) Rio + 20 Conference

   A modest intermediate step to halting desertification:
"While completely halting [desertification] by 2030 may be difficult,
setting a target of Zero Net Land Degradation by 2030 is realistic."

                    UNCCD Secretariat (2012)
UNCCD Strategy
• Adopt sustainable land management practices

• Avoid degradation on non-degraded lands by
  intensifying use of existing agricultural lands

• Employ community-based implementation

• Introduce payments for ecosystem services

• Involve governments, private sector, farmers

• Possibly add a ZNLD Protocol to the UNCCD
Estimating Economic Costs of
          Land Degradation

• Direct Costs

• Indirect Costs

• Economy-wide Costs
Estimates of National Direct Costs Vary
               Widely
                 Estimates for the 1980s

Country      Value   % GDP     % Agricultural GDP Source
Burkina Faso -       9         20                 Lallement
                                                   (1989)
Ethiopia    -        -         2                   Bojö and
                                                   Castells (1995),
                                                   based on Hurni
                                                   (1988)
India       Rs 75 bn 2        4                    Reddy (2003)

Mali        -        0.9-12.5 2-30                 Bishop and
                                                   Allen (1990)
USA         $27 bn   0.4       20                  Pimentel et al.
                                                   (1995)
Reasons for Variation:
    1. Different Information and Data Resolution
• Estimates of Area Affected by Soil Erosion in India

• Reddy (2003): 32 million ha
   – Satellite images

• Agro-Climatic & Regional Planning Unit: 58 million ha
   – Regional statistics

• Sehgal and Abrol:166 million ha
   – GLASOD method
Reasons for Variation:
        2. Different Estimation Methods
• Replacement Cost Method
  – Cost of fertilizers to replace lost nutrients
  – Reddy (2003): $1 billion (satellite data)


• Loss of Production Method
  – Value of cut in crop/livestock production
  – Reddy (2003): $3.7 billion (satellite data)
Reasons for Variation:
   3. Differences with Loss of Production Method
                 in Ethiopia in 1980s
Study                   Projection Discount   Direct Cost (%
                        Period     Rate (%)   AGDP)
                        (Years)
Ethiopian Highlands     25         9          2.2
Reclamation Study
Soil Conservation       0          -          2.0
Research Project
National Conservation   25         Na         6.8
Strategy Secretariat
World Bank              100        10         3.0
Reassessment
Indirect Economic Costs

• Water erosion
  – Siltation of rivers, reservoirs, irrigation canals


• Wind erosion
  – Dust storm effects: car accidents, airplane delays
Estimates of
   Indirect Economic Costs Vary Too
• US estimate – Pimentel et al. (1995)
  – $17 billion = 13% AGDP


• China estimates – Transportation alone
  – Liu (2006): $6 million
  – Zhang et al. (1996): $32 million
Reasons for Variation in Estimates of
         Indirect Economic Costs
•   Lack of reliable biophysical information
•   Many studies focus on few impacts
•   Many costs lack market prices
•   Different methods used to estimate costs
     – Contingent valuation – willingness to pay
     – Choice experiment – choose from range of options
     – Avoided cost – cost of avoiding damage
     – Replacement cost – replace service by alternative
Economy-Wide Costs
• % GDP Estimates Ignore Multiplier Effects

• Chains of Influences
  – Water erosion
  – Siltation of reservoirs
  – Power outages
  – Industrial production losses
  – Short-time working
  – Reduced wages
Comparing Benefits and
         Costs of Land Degradation

• Costs-only approaches ignore land use benefits
  – Income from crops offset costs of lost production
• Optimal rates of land degradation
• Kirby and Blyth (1987):
  – "A problem exists from the social viewpoint only if
    the actual rate of degradation differs from the
    optimal rate."
Comparing Benefits and Costs of
      Land Restoration
Comparing Benefits and Costs of Land
             Restoration
• Benefits
  –   Increases land productivity
  –   Increases values of provisioning/regulating services
  –   Increases direct use values and indirect use values
  –   but biophysical suitability> actual availability
• Costs
  – Financial costs
  – Knock-on effects: displacing people to marginal lands
  – Giving priority to restoring most fertile areas first
       • Increase net rate of return
Conclusions

• Compare Benefits/Costs of Restoration with
  Benefits/Costs of Land Degradation
• ZNLD more feasible than eliminating degradation
  physically and economically
• Comparing development vs conservation projects:
  – (Bd - Cd) - (Bc - Cc) > 0
• Combining degradation control and restoration
  – (Bd - Cd) + (Br - Cr) > t

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Alan GRAINGER "A cost-benefit analysis tool for planning national zero net land degradation schemes"

  • 1. A Cost-Benefit Analysis Tool for Zero Net Land Degradation Schemes Alan Grainger University of Leeds
  • 2. Different Approaches • Compare Benefits of Restoration With Costs of Land Degradation • Compare Benefits/Costs of Restoration with Benefits/Costs of Land Degradation
  • 3. Zero Net Land Degradation Reduce the rate of desertification + Increase the rate of restoration of desertified land African Union (2012) Rio + 20 Conference A modest intermediate step to halting desertification: "While completely halting [desertification] by 2030 may be difficult, setting a target of Zero Net Land Degradation by 2030 is realistic." UNCCD Secretariat (2012)
  • 4. UNCCD Strategy • Adopt sustainable land management practices • Avoid degradation on non-degraded lands by intensifying use of existing agricultural lands • Employ community-based implementation • Introduce payments for ecosystem services • Involve governments, private sector, farmers • Possibly add a ZNLD Protocol to the UNCCD
  • 5. Estimating Economic Costs of Land Degradation • Direct Costs • Indirect Costs • Economy-wide Costs
  • 6. Estimates of National Direct Costs Vary Widely Estimates for the 1980s Country Value % GDP % Agricultural GDP Source Burkina Faso - 9 20 Lallement (1989) Ethiopia - - 2 Bojö and Castells (1995), based on Hurni (1988) India Rs 75 bn 2 4 Reddy (2003) Mali - 0.9-12.5 2-30 Bishop and Allen (1990) USA $27 bn 0.4 20 Pimentel et al. (1995)
  • 7. Reasons for Variation: 1. Different Information and Data Resolution • Estimates of Area Affected by Soil Erosion in India • Reddy (2003): 32 million ha – Satellite images • Agro-Climatic & Regional Planning Unit: 58 million ha – Regional statistics • Sehgal and Abrol:166 million ha – GLASOD method
  • 8. Reasons for Variation: 2. Different Estimation Methods • Replacement Cost Method – Cost of fertilizers to replace lost nutrients – Reddy (2003): $1 billion (satellite data) • Loss of Production Method – Value of cut in crop/livestock production – Reddy (2003): $3.7 billion (satellite data)
  • 9. Reasons for Variation: 3. Differences with Loss of Production Method in Ethiopia in 1980s Study Projection Discount Direct Cost (% Period Rate (%) AGDP) (Years) Ethiopian Highlands 25 9 2.2 Reclamation Study Soil Conservation 0 - 2.0 Research Project National Conservation 25 Na 6.8 Strategy Secretariat World Bank 100 10 3.0 Reassessment
  • 10. Indirect Economic Costs • Water erosion – Siltation of rivers, reservoirs, irrigation canals • Wind erosion – Dust storm effects: car accidents, airplane delays
  • 11. Estimates of Indirect Economic Costs Vary Too • US estimate – Pimentel et al. (1995) – $17 billion = 13% AGDP • China estimates – Transportation alone – Liu (2006): $6 million – Zhang et al. (1996): $32 million
  • 12. Reasons for Variation in Estimates of Indirect Economic Costs • Lack of reliable biophysical information • Many studies focus on few impacts • Many costs lack market prices • Different methods used to estimate costs – Contingent valuation – willingness to pay – Choice experiment – choose from range of options – Avoided cost – cost of avoiding damage – Replacement cost – replace service by alternative
  • 13. Economy-Wide Costs • % GDP Estimates Ignore Multiplier Effects • Chains of Influences – Water erosion – Siltation of reservoirs – Power outages – Industrial production losses – Short-time working – Reduced wages
  • 14. Comparing Benefits and Costs of Land Degradation • Costs-only approaches ignore land use benefits – Income from crops offset costs of lost production • Optimal rates of land degradation • Kirby and Blyth (1987): – "A problem exists from the social viewpoint only if the actual rate of degradation differs from the optimal rate."
  • 15. Comparing Benefits and Costs of Land Restoration
  • 16. Comparing Benefits and Costs of Land Restoration • Benefits – Increases land productivity – Increases values of provisioning/regulating services – Increases direct use values and indirect use values – but biophysical suitability> actual availability • Costs – Financial costs – Knock-on effects: displacing people to marginal lands – Giving priority to restoring most fertile areas first • Increase net rate of return
  • 17. Conclusions • Compare Benefits/Costs of Restoration with Benefits/Costs of Land Degradation • ZNLD more feasible than eliminating degradation physically and economically • Comparing development vs conservation projects: – (Bd - Cd) - (Bc - Cc) > 0 • Combining degradation control and restoration – (Bd - Cd) + (Br - Cr) > t