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Deforestation drivers, carbon
emission estimate and setting
forest reference levels
Arief Wijaya1, Lou Verchot1, Martin Herold2, Arild
Angelsen3, Erika Romijn2 and John-Herbert
Ainembabazi3
1 Forest and Environment Programme, Center for International Forestry
Research (CIFOR), Bogor, Indonesia
2 Center for Geo-Information Science, Wageningen University, Wageningen,
The Netherlands
3 Department of Plants and Environmental Sciences, Norwegian University of
Life Sciences (UMB), Oslo, Norway
THINKING beyond the canopy
THINKING beyond the canopy
Background
 CIFOR Global Comparative Study (GCS) on REDD+
 Component 3: MRV and reference levels
• Monitoring, reporting, verification (MRV) for REDD+
• Setting national reference emission levels (RELs)
• 6 case study countries: Indonesia, Vietnam, Tanzania,
Cameroon, Brazil, Peru
THINKING beyond the canopy
Specific objectives
 To detect areas and activities (drivers) of deforestation
 To calculate carbon emissions and sequestration of
deforested and degraded regions
 To explore the concepts for developing RELs at national
and sub-national levels
THINKING beyond the canopy
Stepwise approach for RELs
(Herold, et.al, 2011)
THINKING beyond the canopy
Carbon biomass estimation approach
 Field data (e.g. National forest inventory)
 Direct remote sensing measurement
• Empirical models where RS data is calibrate to field estimates
(Baccini et al. 2004, 2008, Saatchi et al. 2007, Blackard et al.
2008)
 Stratify and Multiply (SM) method
• Assign an average biomass value to land cover/vegetation type
map (Asner et al. 2010)
 Combine and Assign approach
• Extension of SM, GIS and multi-layers information (Gibbs et al.
2007)
 Ecological Models approach
• RS data to parameterize the biomass model (Hurtt et al. 2004)
THINKING beyond the canopy
Mosaic Landsat GLS Data
Source: USGS downloaded from ArcGIS server
THINKING beyond the canopy
NDVI change 1990 - 2000
Source: USGS downloaded from ArcGIS server
THINKING beyond the canopy
Direct remote sensing measurement
Biomass map based on study by Baccini et al. (2012) including LIDAR shots data obtained
during Biomass mapping training at BIG
THINKING beyond the canopy
Available national biomass map
THINKING beyond the canopy
Available national biomass map
THINKING beyond the canopy
Stratify and Multiply Method
Landuse/cover classification of Indonesia for the years 2000, 2003, 2006 and 2009
Data source: LANDSAT satellite data (30 m resolution) (MOF, 2009)
No Classification
1 Primary Upland Forest
2 Secondary Upland Forest/Logged Forest
3 Primary Swamp Forest
4 Secondary Swamp Forest/Logged Area
5 Primary Mangrove Forest
6 Secondary Mangrove Forest/Logged
7 Crop Forest
8 Oil Palm and Estate Crops
9 Bushes/Shrubland
10 Swampy Bush
11 Savanna
12 Upland Farming
No Classification
13 Upland Farming Mixed with Bush
14 Rice field
15 Cultured Fisheries/Fishpond
16 Settlement/Developed Land
17 Transmigration
18 Open Land
19 Mining/mines
20 Water Body
21 Swamp
22 Cloud
23 Airport/Harbor
THINKING beyond the canopy
Deforestation 2000-2009
Island
Area of deforestation (×1000 ha) Area of degradation (×1000 ha)
2000-2003 2003-2006 2006-2009 2000-2003 2003-2006 2006-2009
Sumatera 278.95 709.89 1063.01 0.00 5.02 101.66
Java 0.27 51.05 2.92 9.08 64.32 0.00
Bali & Nusa Tenggara 45.10 38.52 3.74 3.25 3.31 54.08
Kalimantan 367.24 963.60 705.48 825.38 304.11 74.57
Sulawesi 200.25 283.48 49.62 230.07 1655.13 52.95
Maluku 24.24 24.30 18.09 8.48 10.67 0.22
Papua 79.15 186.78 728.10 298.20 634.66 777.24
Total 995.20 2257.62 2570.96 1374.46 2677.22 1060.72
Annual deforestation
647 thousand ha/year
vs FRA FAO Report
(2010) 498 thousand
ha/year
THINKING beyond the canopy
Deforestation based on forest type
Thousandhectare
Deforestation Forest degradation
THINKING beyond the canopy
Deforestation drivers
THINKING beyond the canopy
Carbon emission estimate
(Sugardiman, 2011 modified from the IPCC report)
THINKING beyond the canopy
Carbon density by landcover type
Forest classes carbon (ton/ha) SD (ton/ha)
Primary dry forest (PF 2001) 179.9 16.9
Secondary dry/logged over forest (SF 2002) 173.7 15.2
Primary Swamp Forest (PSF 2005) 155.5 19.2
Secondary swamp forest(SSF 20051) 143.8 19.7
Primary mangrove forest (PMF 2004) 87.4 13.4
Secondary mangrove forest (SMF 20041) 62.6 8.9
Crop forest (CF 2006) 111.4 17.0
Non-forest classes (vegetated) carbon (ton/ha) SD (ton/ha)
Oil Palm and estate crops (PG 2010) 95.6 19.9
Bushes/Shrubland (B2007) 123.9 13.7
Swampy bush (SB 20071) 77.6 14.1
Savanna (S 3000) 63.1 11.3
Upland farming (UF 20091) 79.9 14.5
Upland farming mixed with bushes (Pc 20092) 115.2 17.2
Rice field (Sw 20093) 62.8 12.0
THINKING beyond the canopy
Carbon stocks change 2000 - 2009
Based on Multiply and Stratify approach. The figure shows only C stocks above ground
excluding on peat soils.
Biomass map based on study by Saatchi (2011) and land cover map from the Ministry of
Forestry (2009)
2000
THINKING beyond the canopy
Carbon stocks change 2000 - 2009
2009
THINKING beyond the canopy
Carbon stocks change 2000 - 2009
2009
THINKING beyond the canopy
Landcover and carbon density
Landcover 2000 Landcover 2009
(a) (b)
(c) (d)
THINKING beyond the canopy
Why one map policy is important?
 Land cover/land use map
 Biomass/C stocks map
THINKING beyond the canopy
Deforestation rates (official data MOF)
THINKING beyond the canopy
Comparison of different studies
0
100
200
300
400
500
600
700
800
900
1000
AnnualDeforestation(x1000ha)
Indonesia MOFOR Indonesia Hansen
Indonesia JRC Indonesia Mean
THINKING beyond the canopy
Cumulative LUCF carbon emissions
Source
Cumulative Emission from
LUCF 2000 -2009
(in Gg CO2e)*
Methods Remarks
FAOStat 3,140,033
FRA country report
(EF = 138 ton C/ha)
Net forest conversion
MoE - Second National
Communication to UNFCCC
7,443,064 IPCC Guidelines 2006 Net forest conversion
Winrock International
(Harris, 2012)
3,468,150
Carbon Bookkeping model
(RS + Field)
Gross deforestation
MOF (official) 1,760,000
Approach 1 + NFI
(Tier 1 or 2)
Net forest conversion
(peat?) - carbon
emissions potential
MOF + Saatchi (CIFOR) 1,811,396
Approach 1 + Global EF
(Tier 1 or 2)
Net forest conversion
Mean 3,524,529
* does not include peat emissions and peat fire
THINKING beyond the canopy
Annual LUCF Carbon emissions
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
1.1
1.2
1.3
1.4
1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
AnnualCarbonEmissionsfromLUCF(inPgCO2e)
FAOStat
LUCF - Second NatCom MoE
MOF + Saatchi (CIFOR)
THINKING beyond the canopy
Combining socio-economic data
Population density
Family ratio below poverty level
Agriculture family ratio
THINKING beyond the canopy
Combined with forest transition curve?
(Angelsen, 2008)
THINKING beyond the canopy
Concluding remarks
 Stepwise approach is useful to handle data uncertainty
and data quality variations in estimating RELs
 Carbon density estimated at different land cover types
can cause combined errors
 Indonesia has capability to implement Tier 3 (or 2.5??) of
the REL estimation (given the availability of reliable forest
inventory data and spatially explicit datasets)
THINKING beyond the canopy
www.cifor.cgiar.org

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Deforestation drivers, carbon emission estimate and setting forest reference levels

  • 1. Deforestation drivers, carbon emission estimate and setting forest reference levels Arief Wijaya1, Lou Verchot1, Martin Herold2, Arild Angelsen3, Erika Romijn2 and John-Herbert Ainembabazi3 1 Forest and Environment Programme, Center for International Forestry Research (CIFOR), Bogor, Indonesia 2 Center for Geo-Information Science, Wageningen University, Wageningen, The Netherlands 3 Department of Plants and Environmental Sciences, Norwegian University of Life Sciences (UMB), Oslo, Norway THINKING beyond the canopy
  • 2. THINKING beyond the canopy Background  CIFOR Global Comparative Study (GCS) on REDD+  Component 3: MRV and reference levels • Monitoring, reporting, verification (MRV) for REDD+ • Setting national reference emission levels (RELs) • 6 case study countries: Indonesia, Vietnam, Tanzania, Cameroon, Brazil, Peru
  • 3. THINKING beyond the canopy Specific objectives  To detect areas and activities (drivers) of deforestation  To calculate carbon emissions and sequestration of deforested and degraded regions  To explore the concepts for developing RELs at national and sub-national levels
  • 4. THINKING beyond the canopy Stepwise approach for RELs (Herold, et.al, 2011)
  • 5. THINKING beyond the canopy Carbon biomass estimation approach  Field data (e.g. National forest inventory)  Direct remote sensing measurement • Empirical models where RS data is calibrate to field estimates (Baccini et al. 2004, 2008, Saatchi et al. 2007, Blackard et al. 2008)  Stratify and Multiply (SM) method • Assign an average biomass value to land cover/vegetation type map (Asner et al. 2010)  Combine and Assign approach • Extension of SM, GIS and multi-layers information (Gibbs et al. 2007)  Ecological Models approach • RS data to parameterize the biomass model (Hurtt et al. 2004)
  • 6. THINKING beyond the canopy Mosaic Landsat GLS Data Source: USGS downloaded from ArcGIS server
  • 7. THINKING beyond the canopy NDVI change 1990 - 2000 Source: USGS downloaded from ArcGIS server
  • 8. THINKING beyond the canopy Direct remote sensing measurement Biomass map based on study by Baccini et al. (2012) including LIDAR shots data obtained during Biomass mapping training at BIG
  • 9. THINKING beyond the canopy Available national biomass map
  • 10. THINKING beyond the canopy Available national biomass map
  • 11. THINKING beyond the canopy Stratify and Multiply Method Landuse/cover classification of Indonesia for the years 2000, 2003, 2006 and 2009 Data source: LANDSAT satellite data (30 m resolution) (MOF, 2009) No Classification 1 Primary Upland Forest 2 Secondary Upland Forest/Logged Forest 3 Primary Swamp Forest 4 Secondary Swamp Forest/Logged Area 5 Primary Mangrove Forest 6 Secondary Mangrove Forest/Logged 7 Crop Forest 8 Oil Palm and Estate Crops 9 Bushes/Shrubland 10 Swampy Bush 11 Savanna 12 Upland Farming No Classification 13 Upland Farming Mixed with Bush 14 Rice field 15 Cultured Fisheries/Fishpond 16 Settlement/Developed Land 17 Transmigration 18 Open Land 19 Mining/mines 20 Water Body 21 Swamp 22 Cloud 23 Airport/Harbor
  • 12. THINKING beyond the canopy Deforestation 2000-2009 Island Area of deforestation (×1000 ha) Area of degradation (×1000 ha) 2000-2003 2003-2006 2006-2009 2000-2003 2003-2006 2006-2009 Sumatera 278.95 709.89 1063.01 0.00 5.02 101.66 Java 0.27 51.05 2.92 9.08 64.32 0.00 Bali & Nusa Tenggara 45.10 38.52 3.74 3.25 3.31 54.08 Kalimantan 367.24 963.60 705.48 825.38 304.11 74.57 Sulawesi 200.25 283.48 49.62 230.07 1655.13 52.95 Maluku 24.24 24.30 18.09 8.48 10.67 0.22 Papua 79.15 186.78 728.10 298.20 634.66 777.24 Total 995.20 2257.62 2570.96 1374.46 2677.22 1060.72 Annual deforestation 647 thousand ha/year vs FRA FAO Report (2010) 498 thousand ha/year
  • 13. THINKING beyond the canopy Deforestation based on forest type Thousandhectare Deforestation Forest degradation
  • 14. THINKING beyond the canopy Deforestation drivers
  • 15. THINKING beyond the canopy Carbon emission estimate (Sugardiman, 2011 modified from the IPCC report)
  • 16. THINKING beyond the canopy Carbon density by landcover type Forest classes carbon (ton/ha) SD (ton/ha) Primary dry forest (PF 2001) 179.9 16.9 Secondary dry/logged over forest (SF 2002) 173.7 15.2 Primary Swamp Forest (PSF 2005) 155.5 19.2 Secondary swamp forest(SSF 20051) 143.8 19.7 Primary mangrove forest (PMF 2004) 87.4 13.4 Secondary mangrove forest (SMF 20041) 62.6 8.9 Crop forest (CF 2006) 111.4 17.0 Non-forest classes (vegetated) carbon (ton/ha) SD (ton/ha) Oil Palm and estate crops (PG 2010) 95.6 19.9 Bushes/Shrubland (B2007) 123.9 13.7 Swampy bush (SB 20071) 77.6 14.1 Savanna (S 3000) 63.1 11.3 Upland farming (UF 20091) 79.9 14.5 Upland farming mixed with bushes (Pc 20092) 115.2 17.2 Rice field (Sw 20093) 62.8 12.0
  • 17. THINKING beyond the canopy Carbon stocks change 2000 - 2009 Based on Multiply and Stratify approach. The figure shows only C stocks above ground excluding on peat soils. Biomass map based on study by Saatchi (2011) and land cover map from the Ministry of Forestry (2009) 2000
  • 18. THINKING beyond the canopy Carbon stocks change 2000 - 2009 2009
  • 19. THINKING beyond the canopy Carbon stocks change 2000 - 2009 2009
  • 20. THINKING beyond the canopy Landcover and carbon density Landcover 2000 Landcover 2009 (a) (b) (c) (d)
  • 21. THINKING beyond the canopy Why one map policy is important?  Land cover/land use map  Biomass/C stocks map
  • 22. THINKING beyond the canopy Deforestation rates (official data MOF)
  • 23. THINKING beyond the canopy Comparison of different studies 0 100 200 300 400 500 600 700 800 900 1000 AnnualDeforestation(x1000ha) Indonesia MOFOR Indonesia Hansen Indonesia JRC Indonesia Mean
  • 24. THINKING beyond the canopy Cumulative LUCF carbon emissions Source Cumulative Emission from LUCF 2000 -2009 (in Gg CO2e)* Methods Remarks FAOStat 3,140,033 FRA country report (EF = 138 ton C/ha) Net forest conversion MoE - Second National Communication to UNFCCC 7,443,064 IPCC Guidelines 2006 Net forest conversion Winrock International (Harris, 2012) 3,468,150 Carbon Bookkeping model (RS + Field) Gross deforestation MOF (official) 1,760,000 Approach 1 + NFI (Tier 1 or 2) Net forest conversion (peat?) - carbon emissions potential MOF + Saatchi (CIFOR) 1,811,396 Approach 1 + Global EF (Tier 1 or 2) Net forest conversion Mean 3,524,529 * does not include peat emissions and peat fire
  • 25. THINKING beyond the canopy Annual LUCF Carbon emissions 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 1.1 1.2 1.3 1.4 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 AnnualCarbonEmissionsfromLUCF(inPgCO2e) FAOStat LUCF - Second NatCom MoE MOF + Saatchi (CIFOR)
  • 26. THINKING beyond the canopy Combining socio-economic data Population density Family ratio below poverty level Agriculture family ratio
  • 27. THINKING beyond the canopy Combined with forest transition curve? (Angelsen, 2008)
  • 28. THINKING beyond the canopy Concluding remarks  Stepwise approach is useful to handle data uncertainty and data quality variations in estimating RELs  Carbon density estimated at different land cover types can cause combined errors  Indonesia has capability to implement Tier 3 (or 2.5??) of the REL estimation (given the availability of reliable forest inventory data and spatially explicit datasets)
  • 29. THINKING beyond the canopy www.cifor.cgiar.org

Editor's Notes

  1. Photo: CIFOR Slide Library #12148 – Burkina Faso Women collecting Piliostigma reticulatum pods for animal feed.
  2. Photo: CIFOR Slide Library #12148 – Burkina Faso Women collecting Piliostigma reticulatum pods for animal feed.