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This presentation was given by CIFOR scientist Louis Verchot on 28 November 2012 at a joint CIFOR and GOFC-GOLD (Global Observation of Forest Cover and Land Dynamics) UNFCCC COP18 side-event in Doha, Qatar.
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A stepwise approach to reference levels
Louis Verchot
THINKING beyond the canopy
• Activity data – types of deforestation and forest degradation • Emission factors – carbon loss per unit area for a specific
activity • Drivers – to describe how much DD are caused by each
specific change activity • Data on existing national monitoring capacities
Business as usual and national capacity
THINKING beyond the canopy
Ac#vity data
Approach 1 Approach 2 Approach 3 Data on forest change (or emissions) following IPCC approaches
TOTAL LAND-‐USE AREA, NO DATA ON CONVERSIONS BETWEEN LAND USES Example: FAO FRA data
TOTAL LAND-‐USE AREA, INCLUDING CHANGES BETWEEN CATEGORIES Example: Na:onal level data on gross forest changes through a change matrix (i.e. deforesta:on vs. reforesta:on), ideally disaggregated by administra:ve regions
SPATIALLY-‐EXPLICIT LAND-‐USE CONVERSION DATA Example: data from remote sensing
Table 9: Activity data on the national level can be estimated from the different approaches as suggested by the IPCC GPG:
THINKING beyond the canopy
Three levels of emission factors • Tier 1 methods are designed to be the simplest to use,
for which equations and default parameter values (e.g., emission and stock change factors) are provided by IPCC Guildelines.
• Tier 2 can use the same methodological approach as Tier 1 but applies emission and stock change factors that are based on country- or region-specific data
• Tier 3, higher order methods are used, including models and inventory measurement systems tailored to address national circumstances, repeated over time, and driven by high-resolution activity data and disaggregated at sub-national level.
THINKING beyond the canopy
Deforestation/degradation drivers for each continent
-‐39%
-‐35%
-‐13%
-‐11%
-‐2%
-‐57% -‐36%
-‐2% -‐4% -‐1%
-‐41%
-‐37%
-‐7%
-‐10% -‐7%
26%
62%
4% 8%
70%
9%
17%
4%
67%
20%
6% 7%
Forest degrada#on driver Deforesta#on driver
AMERICA AFRICA ASIA
Deforesta#on
Degrada#on
THINKING beyond the canopy
Changes of Deforestation Drivers: Important for assessing historical deforestation
Using national data from 46 countries: REDD-related data and publications
Time
Phase1 Pre
Transition
Phase4 Post
Transition
Phase2 Early
Transition
Phase3 Late
Transition
Fore
st C
over
(%)
THINKING beyond the canopy
Deforestation Drivers
n Agriculture (commercial) is 45%, agriculture (local/subsistence) 38%, mining 7%, infrastructure 8%, urban expansion 3% and only agriculture make up 83% of total
n Ratio of mining is decreasing and urban expansion is relatively increasing over time
Deforested-‐area ra:o of deforesta:on drivers
Deforested area
0
100
200
300
400
500
600
700
pre early late post
Urban expansion
Infrastructure
Mining
Agriculture (local-‐slash & burn) Agriculture (commercial)
km2
0%
20%
40%
60%
80%
100%
pre early late post
Distribu:on of 46 countries -‐ Pre: 7, early: 23, late: 12, post: 4
(subsistence)
Criteria for comparing country circumstances and strategies
Criteria for comparing country circumstances and strategies
THINKING beyond the canopy
RLs using regression models – Simple, easy to understand and test new variables – But, data demanding – Predic:ng deforesta:on in a period: Pt – Pt+1, based on deforesta:on in the previous period Pt-‐1 – Pt and a set of other factors (observed at :me t).
– Using structure (coefficients) from the es:mated regression equa:on to predict deforesta:on in period Pt+1 – Pt+2, based on observed values at :me t+1
10
2000 2009 2005 2004 2010
Es:mated/Predicted deforesta:on Historical deforesta:on
Predic#ve model, based on structure from regression model
Regression model
Tier 1 case for 4 countries using FAO FRA data
0
500
1,000
1,500
2,000
2,500
3,000
3,500
1985 1990 1995 2000 2005 2010 2015 2020 2025
Fore
st C
sto
ck (
Mt)
Year
Cameroon
0 2,000 4,000 6,000 8,000
10,000 12,000 14,000 16,000 18,000
1985 1990 1995 2000 2005 2010 2015 2020 2025
Fore
st C
sto
ck (
Mt)
Year
Indonesia
0
300
600
900
1,200
1,500
1985 1990 1995 2000 2005 2010 2015 2020 2025
Fore
st C
sto
ck (
Mt)
Year
Vietnam
0
10,000
20,000
30,000
40,000
50,000
60,000
70,000
80,000
1985 1990 1995 2000 2005 2010 2015 2020 2025
Fore
st C
sto
ck (
Mt)
Year
Brazil
THINKING beyond the canopy
Step 2: Brazil Predict deforesta#on rates for legal Amazon 2005-‐ 2009
12
Category Regression coefficient
Deforesta#on rate (2000-‐2004) 0.395 Trend variable -‐0.136 -‐0.145 Deforesta#on dummy -‐0.373 -‐0.773 Forest stock 2.18 4.756 Forest stock squared -‐1.8 -‐3.826 Log per capita GDP -‐0.034 -‐0.13 Agric GDP (%GDP) 0.28 0.28 Popula#on density 0.081 -‐0.81 Road denisty 0.039 0.076
R2 0.831 0.789 N 3595 3595
THINKING beyond the canopy
Step 2: Vietnam Predict deforesta#on rates 2005-‐ 2009
13
Category Regression coefficient
Deforesta#on rate (2000-‐2004) 01.464 Trend variable -‐0.006 0.003 Deforesta#on dummy -‐0.011 -‐0.031 Forest stock 0.067 0.260 Forest stock squared -‐0.189 -‐0.463 Popula#on density -‐1.177 1.036 Road denisty 0.004 -‐0.001
R2 0.515 0.052 N 301 301
THINKING beyond the canopy
Conclusions • Historical def. is key to predict future deforesta:on
– Coefficients below one → simple extrapola:on can be misleading
• Some evidence of forest transi:on (FT) hypothesis – Robustness of FT depends on the measure of forest stock
• FT supported when forest stock is measured rela:ve to total land area, otherwise mixed results emerge
• Other na:onal circumstances have contradictory effects
• Contradictory rela:onships may be linked to data quality and interrela:ons of econ. & ins:tu:ons differ
14
MRV capacity gap analysis
MRV capacity gap in rela:on to the net change in total forest area between 2005 and 2010 (FAO FRA)
-‐3000
-‐2000
-‐1000
0
1000
2000
3000
Very large Large Medium Small Very small
Net cha
nge in fo
rest area since 1990
(1000h
a)
Capacity gap
THINKING beyond the canopy
§ 53% use site specific biomass equations
§ 24% had methods for belowgound C
§ 41% had methods for dead wood and litter
§ Most projects will use IPCC defaults for soil-C
We surveyed 17 REDD+ demonstration projects
Thank you