03 a03 marubeni indoneseiafsreportingmeeting
TRANSCRIPT
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GHG reduction project through forest preservationin peat land in Central Kalimantan
February 21, 2013
Marubeni Corporation
Ministry of Forestry,
Indonesia
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1. Project Overview
2. Progress and Project Implementation Time Frame
3. Reference Scenario
4. MRV Methods and Field Survey
5. Estimation of Net Emission Reductions
6. Social Safeguards
7. Environmental Safeguards
8. Scale of Investment
Context
2
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1. Project Overview
Location
Concession type
Peat forest in Kabupaten
Kotawaringin Timur and
Katingan, Central Kalimantan
(203,570 ha)
Ecosystem Restoration Concession (ERC)
Potential concession owner
PT. Rimba Makmur Utama
Local partners in Indonesia
Ministry of Forestry, Mazars Starling Resources,
Yayasan Puter Indonesia
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2. Progress and Project Implementation Timeframe
4
FS 2012
1. Land cover stratification
2. Full carbon stock analysis
3. Estimation of emission
factors and net emission
reductions
4. Development of
participatory community
mapping5. Development of
sustainable agroforestry
systems and land
husbandry practices
6. Jurisdictional Nested
REDD+
7. FS review and
consideration on theproject strategy through
the experts meeting
FS 2011
1. Analysis of current situation
2. Development and testing of
a carbon MRV methodology
and monitoring plan based
on the existing VCS
methodology
3. Methodology design
document (MDD)development
4. Social safeguards
5. Environmental safeguards
6. Consideration of REDD+
jurisdictional and nested
approach
7. Feasibility assessment /
investment structure andexamination of legal/tax
aspects
8. Experts meeting
FS 2010
1. Analysis of current
situation
2. Formulations of REDD+
project plans
3. Investigation of MRV
applicable methodologies
4. Formulation of REDD+
project schemes5. Economic profitability
analysis of REDD+
projects
6. Comparisons of MRV
methodologies in experts
group discussion
7. Issues/Countermeasures
Site selection Methodologydevelopment
Testing andImplementation
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In 2011, we made Methodology Design Document (MDD) for the Joint
Crediting Mechanism (JCM) including measuring the peat, the
belowground water level, forest biomass and so on.
Our Past Feasibility Study (F/S) in 2011
Forest Type Carbon PoolsCarbon Stock
(ton/ha)
Ex-Burnt
Secondary ForestStand (above & belowground-
root) 24.54
Understorey 14.52
Litter 12.28
Necromass 6.22
Peat 596.80
Total 654.36
Logged-over
Secondary ForestStand (above & belowground-
root) 51.01
Understorey 6.83
Litter 16.89
Necromass 2.72
Peat 3103.50
Total 3180.93
Primary Forest Stand (above & belowground-root) 101.90
Understorey 6.15
Litter 17.99
Necromass 3.22
Peat 3295.09
Total 3424.36
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O Consideration on Social / Environmental safeguard for REDD+ project
O Consideration on the pre-national and national nested approach on JCM
O Consideration on economic feasibility, investment structure, legal & accounting
issues
Our Past Feasibility Study (F/S) in 2011
In addition to the development of the MRV methodologies for JCM,
we implemented following activities.
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Objectives of Feasibility Study in FY2012
O To analyze the full carbon stock amount in the project site
O To estimate the net GHG emission reduction amountO To develop the community mapping in the project site and the sustainable agroforestry
systems and land husbandry practices.
F/S members
ITTO(International Tropical
Timber Organization)
Ministry of
Economy, Trade
and Industry
Commission
Ministry ofForestry in
Indonesia
Hokkaido University
PT. Mazars Bali (Starling Resources)
Yayasan Puter Indonesia
Verified Carbon Standard
Recommission Re-recommission
Outsourcing
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3. Reference Scenario
Analysis of land cover and land cover changes
Calculation of emission factors in each forest stratification
Calculation of net emission reductions
According to MDD:
Option a) Legally approved conversion rate
Option b) Historical conversion analysis in a reference region
Option c) Conservative Estimate of a conversion rate based on literature review
Methodology:
Baseline deforestation rate in Central Kalimantan from
1985 - 2010:
Average 0.397% per year
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4. MRV Methods and Field Survey
The design of a nested sampling plot
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5. Estimation of Net Emission Reductions
Net Emission Reductions (NERs) =
(Emissions from forest fires + Emissions from logging) natural forest regeneration
No. Ecosystem Types based on Stratification AverageBiomass
(tonnes/ha)
1. Disturbed High Density, Secondary freshwaterswamp forest
94.238
2. Disturbed high density, Secondary peat swampforest
126.454
3. Intact low density, primary peat swamp forest 150.330
4. Intact medium density, primary peat swamp
forest
139.736
5. Intact high density, primary peat swamp forest 185.905
6. Heath, non forest 68.464
7. Disturbed high density, secondary heath forest 116.692
8. Non forest, freshwater swamp 45.783
(100.717,07tonC/year + 231.368,80 tonC/year) - 40.858,70 tonC/year
= 291.227,17 tonC/year
Emission factors
estimated from
land use change
Example:
From Primary PSF
high density to
Secondary PSFlow density
-134.33 tonC/ha
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6. Social Safeguards
Socio-economic baseline studies
Community mapping Agroforestry system development
Improved soil management systems
ConsultationParticipatory
mapping
Communitymap
Agroforestry
system
development
Soil
management
training
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7. Environmental Safeguards
Katingan Peat Swamp Forest hosts
2.4 3.7 orangutans per km2
Morrogh-Bernard, Helen (2008). Wildlife Research Group, the Anatomy
School, University of Cambridge, Cambridge , UK.
PT RMU
The Clouded Leopard
(Neofelis nebulosa)
Rhinoceros Hornbill
(Buceros rhinoceros)
Orangutan(Pongo pygmaeus)
Katingan supports the sixth largest
population of orangutans in the world
(Singleton et al., 2004),
Areas used as habitats for viable population of species
which are threatened, restricted ranged or protected
(results from a rapid HCV 1.3 assessment)
Source: Ministry of Economy, Trade and Industry Japan. (2012). Methodology Design Document for
Reducing Emissions from Deforestation and Degradation of UndrainedPeat Swamp Forests in Central
Kalimantan, Indonesia.
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Thank you for your attention!