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A stepwise approach to reference levels Louis Verchot

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Page 1: Stepwise approach to Reference Levels REDD+

A stepwise approach to reference levels

Louis Verchot

Page 2: Stepwise approach to Reference Levels REDD+

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

Business as usual and national capacity

Cronin, Timothy
Confirm image source
Page 3: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

Activity data

Approach 1 Approach 2 Approach 3Data on forest change (or emissions) following IPCC approaches

TOTAL LAND-USE AREA, NO DATA ON CONVERSIONSBETWEEN LAND USES

Example: FAO FRA data

TOTAL LAND-USE AREA, INCLUDING CHANGESBETWEEN CATEGORIES

Example: National level data on gross forest changes through a change matrix (i.e. deforestation vs. reforestation), ideally disaggregated by administrative 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:

Page 4: Stepwise approach to Reference Levels REDD+

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 Guidelines.

• 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.

Page 5: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

Deforestation/degradation drivers for each continent

39%

35%

13%

11%

2%

57%36%

2%4%

1%

41%

36%

7%

10%

7%

26%

62%

4% 8%

70%

9%

17%

4%

67%

19%

6%7%

Forest degradation driverDeforestation driver

AMERICA AFRICA ASIA

Deforestation

Degradation

Page 6: Stepwise approach to Reference Levels REDD+

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

   

 

Phase1Pre

Transition

Phase4Post

Transition

Phase2Early

Transition

Phase3Late

Transition

Fo

rest

Co

ver

(%)

Page 7: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

Deforestation Drivers

Agriculture (commercial) is 45%, agriculture (local/subsistence) 38%, mining 7%, infrastructure 8%, urban expansion 3% and only agriculture make up 83% of total

Ratio of mining is decreasing and urban expansion is relatively increasing over time

Deforested-area ratio of deforestation drivers

Deforested area

pre early late post0

100

200

300

400

500

600

700Urban expansion

Infrastructure

Mining

Agriculture (local-slash & burn)

Agriculture (commercial)

km2

pre early late post0%

10%20%30%40%50%60%70%80%90%

100%

Distribution of 46 countries - Pre: 7, early: 23, late: 12, post: 4

(subsistence)

Page 8: Stepwise approach to Reference Levels REDD+

Criteria for comparing country circumstances and strategies

Page 9: Stepwise approach to Reference Levels REDD+

Criteria for comparing country circumstances and strategies

Page 10: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

RLs using regression models– Simple, easy to understand and test new variables– But, data demanding

– Predicting deforestation in a period: Pt – Pt+1, based on deforestation in the previous period Pt-1 – Pt and a set of other factors (observed at time t).

– Using structure (coefficients) from the estimated regression equation to predict deforestation in period Pt+1 – Pt+2, based on observed values at time t+1

10

2000 200920052004 2010

Estimated/Predicted deforestation Historical deforestation

Predictive model, based on structure from regression model

Regression model

Page 11: Stepwise approach to Reference Levels REDD+

Tier 1 case for 4 countries using FAO FRA data

1985 1990 1995 2000 2005 2010 2015 2020 20250

500

1,000

1,500

2,000

2,500

3,000

3,500

Cameroon

Year

Fore

st

C s

tock (

Mt)

1985 1990 1995 2000 2005 2010 2015 2020 20250

2,0004,0006,0008,00010,00012,00014,00016,00018,000

Indonesia

Year

Fore

st

C s

tock (

Mt)

1985 1990 1995 2000 2005 2010 2015 2020 20250

300

600

900

1,200

1,500Vietnam

Year

Fore

st

C s

tock (

Mt)

1985 1990 1995 2000 2005 2010 2015 2020 20250

10,000

20,000

30,000

40,000

50,000

60,000

70,000

80,000

Brazil

Year

Fore

st

C s

tock (

Mt)

Page 12: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

Step 2: Brazil

Predict deforestation rates for legal Amazon2005- 2009

12

Category Regression coefficient

Deforestation rate (2000-2004) 0.395Trend variable -0.136 -0.145Deforestation dummy -0.373 -0.773Forest stock 2.18 4.756Forest stock squared -1.8 -3.826Log per capita GDP -0.034 -0.13Agric GDP (%GDP) 0.28 0.28Population density 0.081 -0.81Road denisty 0.039 0.076

R2 0.831 0.789N 3595 3595

Page 13: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

Step 2: Vietnam

Predict deforestation rates 2005- 2009

13

Category Regression coefficient

Deforestation rate (2000-2004) 01.464Trend variable -0.006 0.003Deforestation dummy -0.011 -0.031Forest stock 0.067 0.260Forest stock squared -0.189 -0.463Population density -1.177 1.036Road denisty 0.004 -0.001

R2 0.515 0.052N 301 301

Page 14: Stepwise approach to Reference Levels REDD+

THINKING beyond the canopy

Conclusions• Historical def. is key to predict future

deforestation– Coefficients below one simple extrapolation can be

misleading

• Some evidence of forest transition (FT) hypothesis– Robustness of FT depends on the measure of forest

stock • FT supported when forest stock is measured

relative to total land area, otherwise mixed results emerge

• Other national circumstances have contradictory effects

• Contradictory relationships may be linked to data quality and interrelations of econ. & institutions differ

14

Page 15: Stepwise approach to Reference Levels REDD+

MRV capacity gap analysis

MRV capacity gap in relation to the net change in total forest area between 2005 and 2010 (FAO FRA)

Very large Large Medium Small Very small-3000

-2000

-1000

0

1000

2000

3000

Capacity gap

Net

cha

nge

in fo

rest

are

a s

ince

199

0 (1

000h

a)

Page 16: Stepwise approach to Reference Levels REDD+

Thank you