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Advancing knowledge on the costs,
 risks and benefits of using carbon
 markets to finance REDD+ at the
            country level

           Maryanne Grieg-Gran

                maryanne@iied.org
  Financing for Forests and Climate Change
                CIFOR Forest Day 3
                    Copenhagen
                13th December 2009
From global to local
   Global REDD cost/benefit estimates
    generalise over large areas
   Country level decisions on REDD need
    more locally-specific data
       Capture variation in opportunity costs
       Transaction costs and implementation
       Effects on costs and benefits of REDD design
            International level design options
            National level design options
Poverty and sustainable development
   impacts of REDD architecture
   Partners
       IIED, UMB (Norway), Sustainable Amazonas
        Foundation Brazil,Civic Response
        (Ghana),Sokoine University (Tanzania), Makerere
        University (Uganda), SNV (Vietnam)
   Funding: Norad: Climate and Forest Initiative,
   Aim: Advance knowledge on how different design
    options for REDD at national and international level
    will affect livelihoods and poverty reduction
Key design issues
   Integration with the carbon market
   Scope: RED/REDD/REDD+/REDD++
   Reference levels
   Monitoring, reporting and verification
   Managing delivery risk – permanence
   In-country distribution mechanism
Vietnam
Key issues:Reference levels
        and scope
In Vietnam, net national
deforestation rates are very close
to zero. However, there is quite
significant deforestation in
certain areas.
Relevance of REDD may depend
on:
• targeting high deforestation
areas
• REDD+ and carbon
enhancement.
Spatial information on deforestation rates can be
combined with IPCC tier 1 estimates of carbon
density to identify priority areas for REDD
intervention (right).
Opportunity costs
• Comparison of different crop types
• Preliminary study completed covering three districts in each
of three provinces (9 total).
• Interviewed local government officials for data on crop areas,
crop productivity, prices at market, and costs of production.
• Calculated NPV using a discount rate of 10% and a 30 year
time horizon
Agricultural
opportunity costs
in Vietnam
Issue: How much is needed
on top of opportunity costs?

   Lessons from Juma
 Sustainable Development
      Reserve, Brazil
Payment and support programmes in Juma
Project scenario (carbon stock changes)
                                              CBASELINE                                                          CACTUAL                                                        CRED

Project year            Carbon stocks                       non CO2 GHG*                   Carbon stocks                    non CO2 GHG*                Carbon stocks                     non CO2 GHG*
                   annual             cum                 annual         cum            annual           cum           annual           cum         annual            cum              annual          cum

 Nr       yr        tCO2e            tCO2e                tCO2e         tCO2e           tCO2e           tCO2e              tCO2e       tCO2e        tCO2e            tCO2e              tCO2e         tCO2e
  0      2006         0,00             0,00                 0,00          0,00            0,00            0,00              0,00        0,00          0,00             0,00               0,00          0,00

  1      2007         0,00             0,00                 0,00          0,00         28.157,65       28.157,65       1.858,41       1.858,41     -28.157,65       -28.157,65         -1.858,41      -1.858,41

  2      2008         0,00             0,00                 0,00          0,00            0,00         28.157,65            0,00      1.858,41        0,00          -28.157,65            0,00        -1.858,41

  3      2009      32.964,40        32.964,40             2.175,65      2.175,65        3.296,44       31.454,09           217,57     2.075,97      29.667,96        1.510,31           1.958,09       99,68

  4      2010       3.782,80        36.747,20              249,66       2.425,32         378,28        31.832,37           24,97      2.100,94      3.404,52         4.914,83           224,70         324,38

  5      2011     403.138,40       439.885,60             26.607,13    29.032,45       40.313,84       72.146,21       2.660,71       4.761,65     362.824,56      367.739,39          23.946,42     24.270,80

  6      2012      85.383,20       525.268,80             5.635,29     34.667,74        8.538,32       80.684,53           563,53     5.325,18      76.844,88      444.584,27           5.071,76     29.342,56

  7      2013     1.054.142,90     1.579.411,70           69.573,43    104.241,17      105.414,29      186.098,82      6.957,34       12.282,52    948.728,61      1.393.312,88        62.616,09     91.958,65

  8      2014     537.573,75       2.116.985,45           35.479,87    139.721,04      53.757,38       239.856,20      3.547,99       15.830,51    483.816,38      1.877.129,25        31.931,88     123.890,53

  9      2015     939.161,95       3.056.147,40           61.984,69    201.705,73      93.916,20       333.772,39      6.198,47       22.028,98    845.245,76      2.722.375,01        55.786,22     179.676,75

 10      2016     1.157.988,45     4.214.135,85           76.427,24    278.132,97      115.798,85      449.571,24      7.642,72       29.671,70   1.042.189,61     3.764.564,61        68.784,51     248.461,26

 20      2026     4.077.651,35    37.056.474,70       269.124,99      2.445.727,33     407.765,14     3.733.805,12     26.912,50     246.431,14   3.669.886,22    33.322.669,58        242.212,49   2.199.296,19

 30      2036     8.889.921,25    82.702.851,90       586.734,80      5.458.388,23     888.992,13     8.298.442,84     58.673,48     547.697,23   8.000.929,13    74.404.409,06        528.061,32   4.910.691,00

 40      2046     8.118.717,20    150.475.702,10      535.835,34      9.931.396,34     811.871,72     15.075.727,86    53.583,53     994.998,04   7.306.845,48    135.399.974,24       482.251,80   8.936.398,30

 44      2050    13.495.158,75    197.828.897,15      890.680,48      13.056.707,21   1.349.515,88    19.811.047,37    89.068,05     1.307.529,13 12.145.642,88 178.017.849,78         801.612,43   11.749.178,09

 Partial TOTAL   197.828.897,15                      13.056.707,21                    19.811.047,37                   1.307.529,13                178.017.849,8                    11.749.178,1

      TOTAL                              210.885.604,4                                                      21.118.576,5                                                 189.767.027,9
Unit costs depend
on assumptions
about long-term
ability to control
deforestation,
permanence and
discount rates
Tanzania
   Design issues:
       Scope: needs REDD++ to be pro-poor
       Distribution mechanism –
   Carbon revenues can accelerate adoption of
    participatory forest management (Zahabu 2008)
       Potential to affect 16 million ha forest
   Concerns about existing inequity in PFM
   REDD needs to incorporate equitable cost
    and benefit sharing
Conclusions
   Financing needs for REDD+ depends on key
    design choices such as scope
   Extending the scope of forest carbon gives
    more opportunities for pro-poor actions
   Transaction/implementation costs may be
    high and particularly if REDD+ is to be pro-
    poor
Thank
                         you!
Maryanne Grieg-Gran


International Institute for
Environment and Development
3, Endsleigh Street
London WC1H 0DD
Email:maryanne@iied.org
www.iied.org

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Advancing knowledge on the costs, risks and benefits of using carbon markets to finance REDD+ at the country level

  • 1. Advancing knowledge on the costs, risks and benefits of using carbon markets to finance REDD+ at the country level Maryanne Grieg-Gran maryanne@iied.org Financing for Forests and Climate Change CIFOR Forest Day 3 Copenhagen 13th December 2009
  • 2. From global to local  Global REDD cost/benefit estimates generalise over large areas  Country level decisions on REDD need more locally-specific data  Capture variation in opportunity costs  Transaction costs and implementation  Effects on costs and benefits of REDD design  International level design options  National level design options
  • 3. Poverty and sustainable development impacts of REDD architecture  Partners  IIED, UMB (Norway), Sustainable Amazonas Foundation Brazil,Civic Response (Ghana),Sokoine University (Tanzania), Makerere University (Uganda), SNV (Vietnam)  Funding: Norad: Climate and Forest Initiative,  Aim: Advance knowledge on how different design options for REDD at national and international level will affect livelihoods and poverty reduction
  • 4. Key design issues  Integration with the carbon market  Scope: RED/REDD/REDD+/REDD++  Reference levels  Monitoring, reporting and verification  Managing delivery risk – permanence  In-country distribution mechanism
  • 6. In Vietnam, net national deforestation rates are very close to zero. However, there is quite significant deforestation in certain areas. Relevance of REDD may depend on: • targeting high deforestation areas • REDD+ and carbon enhancement.
  • 7. Spatial information on deforestation rates can be combined with IPCC tier 1 estimates of carbon density to identify priority areas for REDD intervention (right).
  • 8. Opportunity costs • Comparison of different crop types • Preliminary study completed covering three districts in each of three provinces (9 total). • Interviewed local government officials for data on crop areas, crop productivity, prices at market, and costs of production. • Calculated NPV using a discount rate of 10% and a 30 year time horizon
  • 10. Issue: How much is needed on top of opportunity costs? Lessons from Juma Sustainable Development Reserve, Brazil
  • 11. Payment and support programmes in Juma
  • 12.
  • 13. Project scenario (carbon stock changes) CBASELINE CACTUAL CRED Project year Carbon stocks non CO2 GHG* Carbon stocks non CO2 GHG* Carbon stocks non CO2 GHG* annual cum annual cum annual cum annual cum annual cum annual cum Nr yr tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e tCO2e 0 2006 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 1 2007 0,00 0,00 0,00 0,00 28.157,65 28.157,65 1.858,41 1.858,41 -28.157,65 -28.157,65 -1.858,41 -1.858,41 2 2008 0,00 0,00 0,00 0,00 0,00 28.157,65 0,00 1.858,41 0,00 -28.157,65 0,00 -1.858,41 3 2009 32.964,40 32.964,40 2.175,65 2.175,65 3.296,44 31.454,09 217,57 2.075,97 29.667,96 1.510,31 1.958,09 99,68 4 2010 3.782,80 36.747,20 249,66 2.425,32 378,28 31.832,37 24,97 2.100,94 3.404,52 4.914,83 224,70 324,38 5 2011 403.138,40 439.885,60 26.607,13 29.032,45 40.313,84 72.146,21 2.660,71 4.761,65 362.824,56 367.739,39 23.946,42 24.270,80 6 2012 85.383,20 525.268,80 5.635,29 34.667,74 8.538,32 80.684,53 563,53 5.325,18 76.844,88 444.584,27 5.071,76 29.342,56 7 2013 1.054.142,90 1.579.411,70 69.573,43 104.241,17 105.414,29 186.098,82 6.957,34 12.282,52 948.728,61 1.393.312,88 62.616,09 91.958,65 8 2014 537.573,75 2.116.985,45 35.479,87 139.721,04 53.757,38 239.856,20 3.547,99 15.830,51 483.816,38 1.877.129,25 31.931,88 123.890,53 9 2015 939.161,95 3.056.147,40 61.984,69 201.705,73 93.916,20 333.772,39 6.198,47 22.028,98 845.245,76 2.722.375,01 55.786,22 179.676,75 10 2016 1.157.988,45 4.214.135,85 76.427,24 278.132,97 115.798,85 449.571,24 7.642,72 29.671,70 1.042.189,61 3.764.564,61 68.784,51 248.461,26 20 2026 4.077.651,35 37.056.474,70 269.124,99 2.445.727,33 407.765,14 3.733.805,12 26.912,50 246.431,14 3.669.886,22 33.322.669,58 242.212,49 2.199.296,19 30 2036 8.889.921,25 82.702.851,90 586.734,80 5.458.388,23 888.992,13 8.298.442,84 58.673,48 547.697,23 8.000.929,13 74.404.409,06 528.061,32 4.910.691,00 40 2046 8.118.717,20 150.475.702,10 535.835,34 9.931.396,34 811.871,72 15.075.727,86 53.583,53 994.998,04 7.306.845,48 135.399.974,24 482.251,80 8.936.398,30 44 2050 13.495.158,75 197.828.897,15 890.680,48 13.056.707,21 1.349.515,88 19.811.047,37 89.068,05 1.307.529,13 12.145.642,88 178.017.849,78 801.612,43 11.749.178,09 Partial TOTAL 197.828.897,15 13.056.707,21 19.811.047,37 1.307.529,13 178.017.849,8 11.749.178,1 TOTAL 210.885.604,4 21.118.576,5 189.767.027,9
  • 14. Unit costs depend on assumptions about long-term ability to control deforestation, permanence and discount rates
  • 15. Tanzania  Design issues:  Scope: needs REDD++ to be pro-poor  Distribution mechanism –  Carbon revenues can accelerate adoption of participatory forest management (Zahabu 2008)  Potential to affect 16 million ha forest  Concerns about existing inequity in PFM  REDD needs to incorporate equitable cost and benefit sharing
  • 16. Conclusions  Financing needs for REDD+ depends on key design choices such as scope  Extending the scope of forest carbon gives more opportunities for pro-poor actions  Transaction/implementation costs may be high and particularly if REDD+ is to be pro- poor
  • 17. Thank you! Maryanne Grieg-Gran International Institute for Environment and Development 3, Endsleigh Street London WC1H 0DD Email:maryanne@iied.org www.iied.org