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Centro de Sensoriamento Remoto UNIVERSIDADE FEDERAL DE MINAS GERAIS Modelling spatially explicit forward-looking baselines Claudia Stickler REDDex, July 13-15, 2010
Applications of the Amazon Scenarios  modeling system in Amazon REDD projects ,[object Object]
Surui (Rondonia indigenous land project)**
State of Acre
Northwestern MatoGrosso project**
Xingu Social-environmental Carbon
Brazilian Amazon** Used model results not developed for reference level estimation
MatoGrosso REDD targets within a national program Annual Deforestation (km2)
Indigenous Lands ~60% of area Protected Areas Sustainable Use Areas ~98% of deforestation Private Lands 508,474 km2 >95% of possible REDD+ participant nations
Historical average 3.3% = 10,502 ha/yr 2.3% = 216,376 ha/yr 1.3% = 483,380 ha/yr 0.0035% = 3791 ha/yr Nepstad et al. 2010
Simulated (modeled) baseline ,[object Object]
High to medium resolution (100-m to 1-km)
Calibrated and run at nested sub-basin levels
Regrows forests and cerradoStickler et al. 2009 GCB; Stickler 2009
Sub-basins (2nd order) Variable types for calibration clearing roads topography population centers streams protected areas soils/suitability
Basic units of change Microbasins (7th order +) 7572 watersheds mean = 5981 ha range: 1 – 70,766 ha Cells 2940 x 7434 cells 4 ha (200 x 200-m)
Scenarios Business as Usual historical rate and pattern of deforestation continues historical level of compliance with environmental legislation continues low, high, average varying weight of historical protection of PAs, ILs, etc. Current Forest Code  80% “legal reserve” (RL) in forest biome; 35% RL in cerrado; 100% forest in riparian zone Varying protection of indigenous lands, protected areas State Zoning Plans 4 zones: 80% forest RL in 2 zones; 50% forest RL in 1 zone; 35% cerrado RL in 3 zones; 100% forest in riparian zone Varying protection of indigenous lands, protected areas  Stickler 2009; Nepstad et al. 2010
High Low Nepstad et al. 2010
Comparison of modeled baselines with historical average, Xingu River Basin Nepstad et al. 2010
Initial (2007) BAU Average (2037) BAU Low (2037) BAU High (2037)
Comparison of modeled baselines with policy intervention scenarios Nepstad et al. 2010
BAU Average (2037) Forest Code (2037) Zoning (2037) Forest Code + 20% in ILs (2037)
Emissions avoided (Xingu River Basin) Implementation of Forest Code (private lands) & strict protection of ILs and PAs
Comparison of modeled baselines for private lands in the Xingu River basin Nepstad et al. 2010
Comparison of modeled baselines for indigenous lands in the Xingu River basin Nepstad et al. 2010
Nepstad et al. 2010
Carbon stocks & emissionsonindigenouslands in theBrazilian Amazon Nivel de amenaza Priorización de áreas protegidas Soares-Filho et al. 2010 PNAS
Modeledbaselinesbased on forest transition? North Amazon Basin Congo Basin  South Amazon Basin National forest cover Europe  North America South East Asia North East Asia South Asia West Africa Oceania Atlantic forest Time (Zarin et al. 2009)

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stickler_modeling_baselines

  • 1. Centro de Sensoriamento Remoto UNIVERSIDADE FEDERAL DE MINAS GERAIS Modelling spatially explicit forward-looking baselines Claudia Stickler REDDex, July 13-15, 2010
  • 2.
  • 3. Surui (Rondonia indigenous land project)**
  • 7. Brazilian Amazon** Used model results not developed for reference level estimation
  • 8.
  • 9. MatoGrosso REDD targets within a national program Annual Deforestation (km2)
  • 10. Indigenous Lands ~60% of area Protected Areas Sustainable Use Areas ~98% of deforestation Private Lands 508,474 km2 >95% of possible REDD+ participant nations
  • 11. Historical average 3.3% = 10,502 ha/yr 2.3% = 216,376 ha/yr 1.3% = 483,380 ha/yr 0.0035% = 3791 ha/yr Nepstad et al. 2010
  • 12.
  • 13. High to medium resolution (100-m to 1-km)
  • 14. Calibrated and run at nested sub-basin levels
  • 15. Regrows forests and cerradoStickler et al. 2009 GCB; Stickler 2009
  • 16. Sub-basins (2nd order) Variable types for calibration clearing roads topography population centers streams protected areas soils/suitability
  • 17. Basic units of change Microbasins (7th order +) 7572 watersheds mean = 5981 ha range: 1 – 70,766 ha Cells 2940 x 7434 cells 4 ha (200 x 200-m)
  • 18. Scenarios Business as Usual historical rate and pattern of deforestation continues historical level of compliance with environmental legislation continues low, high, average varying weight of historical protection of PAs, ILs, etc. Current Forest Code 80% “legal reserve” (RL) in forest biome; 35% RL in cerrado; 100% forest in riparian zone Varying protection of indigenous lands, protected areas State Zoning Plans 4 zones: 80% forest RL in 2 zones; 50% forest RL in 1 zone; 35% cerrado RL in 3 zones; 100% forest in riparian zone Varying protection of indigenous lands, protected areas Stickler 2009; Nepstad et al. 2010
  • 19. High Low Nepstad et al. 2010
  • 20. Comparison of modeled baselines with historical average, Xingu River Basin Nepstad et al. 2010
  • 21. Initial (2007) BAU Average (2037) BAU Low (2037) BAU High (2037)
  • 22. Comparison of modeled baselines with policy intervention scenarios Nepstad et al. 2010
  • 23. BAU Average (2037) Forest Code (2037) Zoning (2037) Forest Code + 20% in ILs (2037)
  • 24. Emissions avoided (Xingu River Basin) Implementation of Forest Code (private lands) & strict protection of ILs and PAs
  • 25. Comparison of modeled baselines for private lands in the Xingu River basin Nepstad et al. 2010
  • 26. Comparison of modeled baselines for indigenous lands in the Xingu River basin Nepstad et al. 2010
  • 28. Carbon stocks & emissionsonindigenouslands in theBrazilian Amazon Nivel de amenaza Priorización de áreas protegidas Soares-Filho et al. 2010 PNAS
  • 29. Modeledbaselinesbased on forest transition? North Amazon Basin Congo Basin South Amazon Basin National forest cover Europe North America South East Asia North East Asia South Asia West Africa Oceania Atlantic forest Time (Zarin et al. 2009)
  • 30.
  • 32. Water Quality: Basic indicators (Neill et al. 2006, Nepstad et al. 2007; Macedo et al., in prep.)
  • 33. Habitat Quality & Biodiversity Potential
  • 34. Fire Incidence (and associated CO2 emissions) (Silvestrini et al. 2009, Stickler et al. in prep)
  • 37.
  • 38.
  • 39. Sample of REDD-Relevant Publications from Amazon Scenarios Program Merry, F., B. Soares-Filho, D. Nepstad, G. Amacher, and H. Rodrigues. 2009. Balancing conservation and economic stability: the future of the Amazon timber industry. Environmental Management Nepstad, D., B. Soares-Filho, F. Merry, A. Lima, P. Moutinho, et al. 2009. The end of deforestation in the Brazilian Amazon. Science 326: 1350-1351. Nepstad, D, A. Veríssimo, A. Alencar, etal. 1999. Large-scale impoverishment of Amazonian forests by logging and fire. Nature. 398:505-508. Soares-Filho, B. S., P. Moutinho, D. Nepstad, et al. 2010. Role of Brazilian Amazon protected areas in climate mitigation. Proc. Nat. Acad. Sci. Soares-Filho, B., D. Nepstad, L. Curran, et al. 2006. Modeling Amazon conservation. Nature 440: 520-523. Stickler, C.M., D.C. Nepstad, M.T. Coe, D.G. McGrath, H.O. Rodrigues, et al. 2009. The potential ecological costs and cobenefits of REDD: a critical review and case study from the Amazon region. Global Change Biology 15:2803–2824 Vera-Diaz, M. del C., R. K. Kaufmann, D. C. Nepstad, P. Schlesinger. 2007. An interdisciplinary model of soybean yield in the Amazon Basin: the climatic, edaphic, and economic determinants. Ecological Economics
  • 40.
  • 41. Lima et al. 2010; Nepstad et al. 2010
  • 42. Potential nesting of the Xingu “Socio-environmental Carbon” Project C-REDDs Allocated to Amazon States Mato Grosso C-REDD Allocation C-REDD Allocation to Other States State Institutions/ Governance C-REDD Buffer Private Land Program Protected Area Program Farm Settlement Program Indigenous Land Program 100 MtCO2e $ Regulated Entities, Other Investors Indigenous Land Fund “C-REDDs” Indigenous Land Projects (Xingu, NW, etc.) Mato Grosso Indigenous Land Systemic Program
  • 43. Historical average extended into future Nepstad et al. 2010