This presentation, delivered at the International Workshop on Forest Carbon Emissions in Jakarta, examines the need to improve national forest monitoring approaches. CIFOR's Global Comparative Study and the importance of definition are discussed in the context of Indonesia.
Call Girls In R.K. Puram 9953056974 Escorts ServiCe In Delhi Ncr
Towards the Improvement of National Forest Monitoring Approaches
1. Towards the Improvement of National
Forest Monitoring Approaches
International Workshop on Forest Carbon Emissions
Technical Session 3: State of the Art Technology for Carbon Stock
Assessment and Monitoring
Jakarta, 3 – 5 March 2015
Arief Wijaya
Center for International Forestry Research (CIFOR), Indonesia
Contributors: Ruandha Agung Sugardiman, Budiharto, Anna Tosiani, Judin
Purwanto, Lou Verchot, Daniel Murdiyarso, Erika Romijn and Martin Herold
2. CIFOR Global Comparative Study on REDD+
GCS Module 3: REDD+ MRV and Carbon Emissions
measurement
– Assessment of major deforestation drivers
– Setting national reference emission levels (RELs)
– Monitoring, reporting, verification (MRV) for REDD+
– Six case study countries: Brazil, Peru, Indonesia,
Vietnam, Tanzania and Cameroon
Further information: www.cifor.org/gcs/
3. Opportunity/Challenges of National Forest
Monitoring
Estimation of future carbon emissions from LULUCF sector
is yet challenging for many developing countries, including
in Indonesia
Opportunity: Indonesia has several spatially explicit
deforestation maps/estimates
Objective of the talk: to share our approach to assess and
improve the reliability of national deforestation estimate
4. Approaches for estimating area change in
land use (activity data) – IPCC 2006
Approach 1: total area for each land use category recorded,
but no information included on conversions (only net
changes)
Approach 2: tracking of conversions between land use
categories (only between 2 points in time)
Approach 3: spatially explicit tracking of land use
conversions over time.
5. Materials
Land cover map of MOF (1990-2012)
Annual deforestation map of University of Maryland – both from
Hansen and Margono (2000-2012)
Land cover change map of CRISP (2000-2010)
Stratified sample of land cover change map of EU Joint Research
Centre (2000-2010)
6. Land Cover Classification System
Landuse/cover classification of Indonesia for the years 1990, 1996, 2000, 2003, 2006,
2009, 2011, 2012 and 2013.
Data source: LANDSAT satellite data (30 m resolution) (MOF, 2014)
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
13. Deforestation Data and Forest Definitions
Source Resolution
MMU
Forest definition
MOFOR
Official
(Landsat)
6.25 ha Vegetation with canopy cover of more than 30% with minimum area
of 0.25 ha and tree height above 5 meter. Plantation forests (e.g.
Acacia, Eucalyptus, Teak, etc.) can be considered as a forest
MOFOR
FAO
6.25 ha Forest is defined by the FAO as land spanning more than 0.5 ha with
more than 10% tree canopy cover and trees higher than 5 m (or
having the potential to reach a height of 5 m).
CRISP
(MODIS)
25 ha Not defined
Hansen
(Landsat)
0.09 ha
0.36 ha
Forest cover was defined as areas with canopy cover >25 and change
was measured disregards to forest land use. All tree cover
assemblages that met the 25% threshold, including intact forests,
plantations, and forest regrowth, were defined as forests.
EU-JRC
(Landsat)
5 ha More than 5 m height, forest prop. In polygon (FP)>70, canopy cover
(CC)>10
14. CO2 Emissions from Deforestation, Peat
Drainage and Peat Fires in Indonesia
16. Four Decades of Forests
Persistence, clearance and
logging in Borneo
(1973-2010)
Source: Gaveau, et.al (2014)
76% of forest cover (1973) 46% of forest cover (2010)
http://gislab.cifor.cgiar.org/wm/borneo/
Extend period of
observation
17. CIFOR Study
(Subset of Borneo-wide Data 1973 – 2010)
Class labels Area (Mha)
Intact Forest 2010 4.12
Logged Forest 2010 4.04
Deforestation from 1973 to 2010 3.86
Non-Forest 1973 2.97
Clouds 0.26
Total 15.24
Courtesy: David Gaveau (CIFOR)
Detailed analysis at sub-national
18. Lesson learnt from CIFOR Global Comparative
Study on REDD+
Countries should start as soon as possible to monitor their
forestlands and forest cover change using the best available
data
– If we have less data the more we depend on the data
Countries should invest for collecting national datasets (i.e.
time series forest cover change and local emissions factor
data)
Follows international convention (such as IPCC guidelines)
for estimating deforestation and forest degradation
– How to differentiate between net and gross estimates
– Include natural forest recovery and forest rehabilitation efforts
19. Observations so far…
Recommendations for further research to support policy
makers:
– Systematic assessment of national land cover map – comparison of
different maps, uncertainty of visual vis-à-vis semi-automatic
classification approaches
– Further analysis to address drivers of deforestation
– Extend observation period of land cover map (e.g. back to 1980)
– Include forest degradation and its associated emissions in the equation
20.
21. Research and systematic observation (RSO) for forest-peat
carbon
To come up with position draft to feed COP 21 Paris –
relates to SDG – objectives 13-15
Which science are still required to support policy makers in
mitigating climate change?
Editor's Notes
REDD+ Policies
examines how REDD+ is unfolding in the national policy arena.
REDD+ Subnational Initiatives
examines how REDD+ projects can be designed and implemented so that their outcomes are effective, efficient and equitable and they deliver co‑benefits.
Measuring Carbon Emissions
looks for ways to enable better carbon accounting so that emission reductions can be reliably measured and verified.
Mitigation–Adaptation Synergies
looks for ways to exploit the synergies between REDD+ and climate change adaptation, to ensure that REDD+ has an impact beyond mitigation and is sustainable in a changing climate.
REDD+ Benefit Sharing
aims to provide policy options and guidance for the design, development and implementation of REDD+ benefit‑sharing mechanisms