alto mayo protected forest redd initiative, peru
DESCRIPTION
To measure the success of REDD (Reducing Emissions from Deforestation and forest Degradation), it is crucial to first set baseline emissions from which the reduction can be measured in each project or region. In this presentation, Fabiano Godoy from Conservation International shared experiences with applying the VCS VM0015 model in the Alto Mayo protected forest of Peru in order to set baseline emissions. Fabiano Godoy gave this presentation on 8 March 2012 at a workshop organised by CIFOR, ‘Measurement, Reporting and Verification in Latin American REDD+ Projects’, held in Petropolis, Brazil. Credible baseline setting and accurate and transparent Measurement, Reporting and Verification (MRV) of results are key conditions for successful REDD+ projects. The workshop aimed to explore important advances, challenges, pitfalls, and innovations in REDD+ methods — thereby moving towards overcoming barriers to meeting MRV requirements at REDD+ project sites in two of the Amazon’s most important REDD+ candidate countries, Peru and Brazil. For further information about the workshop, please contact Shijo Joseph via s.joseph (at) cgiar.orgTRANSCRIPT
Photo 25.51” x 10.31”
Position
x: 8.53”, y: .18”
Photo 14.2” x 10.31”
Position
x: 4.36”, y: .18”
Alto Mayo Protected
Forest
REDD Initiative
Peru
Fabiano Godoy
March- 2012
REDD initiative profile
Alto Mayo Protected Forest – Department San Martin –Peru
� National protected area with highest deforestation rate in Peru (0.34% yr-1)
� ~ 5000 families live within the AMPF
� AMPF size: 182,000 ha
� project start date: 2008
� main threat: forest conversion to coffee plantation
� co-benefit: provision of water supply
� strategy: capacity building and incentives
to improve coffee production through
conservation agreements
Historical
deforestationCO2 emission
reductions
Major Steps and Inputs – VM00151996
2001
2006
Carbon maptC ha-1
Spatial
boundaries
Drivers ofdeforestation
Defor rate
Ref area
Elevation
Dist to roads
Land change
modeling
Trans. Potent.
2020
Historical land cover and change
In-house processing
� Image acquisition - Landsat 5 & 7
1996-2001-2006
(path-row 8-64 and 9-64)
� Interpretation and classification
Ortho, cloud removal
Decision tree algorithm (See5-ERDAS)
Forest, non-forest, cloud and water
� Post-processing and map accuracy
MMU 2ha
Field visit – high resolution satellite images – aerial photos
accuracy 92% forest-non forest
Spatial Boundaries
� Spatial Boundaries
� Project Area� forested area inside AMPF
� 153, 929 ha
� Reference Region� similarity with project area
� same drivers & agents of
deforestation
� Leakage Belt
� mobility analysis
� MCE
� Fuzzy based on
hist deforestation
Carbon Pools
Carbon poolsIncluded / TBD /
ExcludedJustification / Explanation of choice
Above-ground tree includedRepresents the pool where the greatest carbon stock change will
occur.
Above-ground non-tree included
The baseline land use in the project area is conversion of forest
to perennial crops (coffee), therefore the carbon stock in this pool
is likely to be relatively large compared to the project scenario.
Below-ground includedRecommended by the methodology as it usually represents
between 15% and 30% of the above-ground biomass.
Dead wood excluded
Conservatively excluded (the carbon stock in this pool is not
expected to be higher in the baseline compared to the project
scenario).
Harvested wood products excluded
Under the baseline scenario, illegal selective logging occurs in
very small scale and, therefore, harvested wood products have
been considered insignificant.
Litter excludedNot to be measured according to the latest VCS AFOLU
Requirements (version 3.0).
Soil organic carbon excluded
The baseline land-use of the project area is conversion of forest
to perennial crop (coffee) followed by conversion to pasture. The
soil organic carbon is not to be measured in such cases
according to the latest VCS AFOLU Requirements (version 3.0).
Sources of GHG emissions
Sources Gas Included/ excluded Justification / Explanation of choice
Biomass
burning
CO2 Excluded counted as carbon stock change
CH4 Excluded
The major baseline activity is conversion of forest
to conventional coffee plantation using slash and
burn techniques. The project aims to reduce this
activity by providing technical assistance to
establish sustainable, shade-grown organic coffee
plantations and therefore, the non-CO2 emissions
related to biomass burning are conservatively
excluded.
N2O Excluded See above explanation.
Livestock
emissions
CO2 Excluded
Raising livestock is not a widespread baseline
activity and the AMCI project will not promote the
raising of livestock or result in an increase of this
activity compared to the baseline. Therefore,
livestock emissions are conservatively excluded.
CH4 Excluded See above explanation.
N2O Excluded See above explanation.
Drivers and Agents of Deforestation� Identify the main drivers of deforestation, the agents and the underlying causes
� compilation of relevant scientific publications + public consultation
� Drivers of deforestation
� conversion to coffee
plantation
� conversion to pastureland
� conversion to agriculture of
subsistence
� conversion to infrastructure
� clearance to illegal land trade
� illegal logging
Drivers and Agents of Deforestation
Drivers and Agents of Deforestation� Identify the main drivers of deforestation, the agents and the underlying causes
� Map the threat distribution
� Understand the deforestation dynamic and provide a comprehensive list of variables to
be used in the modeling of future deforestation
Past Future
Deforestation Rate� The major drive of deforestation in the project area is conversion to coffee plantation
� deforestation rate was model as function of coffee production over time.
� direct correlation between deforestation and coffee production in the past
� constant (increasing) coffee production (1996-2007)
� coffee production do not follow the price trends
0
500
1000
1500
2000
2500
3000
1996 1998 2000 2002 2004 2006 2008
Coffee Price in Peru
y = 604,47x - 1.200.357,57R² = 0,86
0
2.000
4.000
6.000
8.000
10.000
12.000
14.000
16.000
1995 2000 2005 2010
Annual Coffee Production in Rioja + Moyobamba + Huallaga
(proportional to reference area)
AnnualCoffeeProduction
Linear(AnnualCoffeeProduction)
y = 0,1188x - 36,338R² = 0,9417
-
1.000
2.000
3.000
4.000
5.000
0 10.000 20.000 30.000 40.000
Deforestation as function of Coffee Production (in Rioja, Moyobamba and Huallaga proportional to reference
area)
deforestation asfunction of coffeeproduction
Linear(deforestation asfunction of coffeeproduction)
1996-2001 & 2001-2006
Land Cover 1996 Land Cover 2001 Land Cover 2006
Elevation
Dist. Villages
Dist. Roads
Change 96-01
Modeling
Land Proj. 2006
Suitab. Map
Validation
Land Proj 2012
2020
2040
NO
Drivers
YES
Suit. Map
Input Output Process
LCM Tool Concept – IDRISI Taiga
1996 20012006 actual
Elevation
Dist to roads
Trans. Potential
2020
2006 proj
Dist to villages
2025
2030
Change 96-01
Model future land use change
Transition Potential Map
(Neural network)
P-FOM = 60% cloud forest
= 8% pre montane
Projected Deforestation
� based on forest classification
� 89% cloud forest (1000-2500masl)
� 7% pre montane forest (below 1000masl)
� 4% dwarf forest (above 2500masl)
� biomass measurement
� 107 plots
� above ground biomass
� root to shoot ratio
� weighted-area average non-forest
Carbon Map
� Next Steps - REDD project is under VCS validation
� currently addressing the findings (NIR, CAR)
� verification (monitoring report 2008-2011) by Sept
� CCBS validation and verification by December
Photo 25.51” x 10.31”
Position
x: 8.53”, y: .18”
Photo 14.2” x 10.31”
Position
x: 4.36”, y: .18”