The Rimba Raya Biodiversity Reserve REDD Project

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Stratification by Landcover TypeMapped land cover classes represent vegetation type (e.g. peatswamp forest, kerangas forest, peat shrubland) and level ofanthropogenic disturbance in peat swamp forest (e.g. lightlydegraded, highly degraded), both of which are expected to affectcarbon stocks in aboveground biomass. Landcover classificationand mapping for Rimba Raya was conducted to improve regionallandcover maps by the Indonesian Ministry of Forestry. Methodsand results are briefly described below and detailed in theLandcover Assessment Report (Annex 2).Land cover mapping was accomplished following a two-‐partapproach including automated image classification followed bymanual image interpretation in GIS. In the first phase, pixel-‐basedimage classification was conducted to make use of spectralinformation in Landsat7 ETM+ bands that are sensitive tovegetation. The results of this classification provided importantverification of broad land cover types such as forest and no-forestvegetative cover and bare soil. In the second phase, landcover was interpreted and digitized using classified and originalLandsat data in a GIS. Interpretation was therefore able toincorporate key ancillary data including aerial photos, surveydata and other GIS data compiled for Rimba Raya, whichimproved the classification.Results of landcover classification (Table 2 and Figure 11) showthat the Carbon Accounting Area is predominated by lightlydegraded peat swamp forest (40.5%) and peat shrublands(25.6%) with some kerangas forest (10.2%) and open scrub(11.4%).Biomass SurveyIn order to quantify biomass associated with landcover types, acombination of ground and aerial surveys were conducted.Survey transect locations are shown in Figure X. Survey methodsand results are briefly described below and detailed in theCarbon Assessment Survey Report (Annex 5). Two 8-‐personteams of trained and experienced field staff conducted theground survey. A total of 16,000 meters of transect were markedand surveyed with biomass data recorded across 36 plotsrepresenting 9 hectares of forest. Biomass measurementsincluded tree diameter, tree height and tree crownmeasurements.Table 2. Land Cover Classification and Extent in the ProjectCarbon Accounting AreaLand Cover Description Extent (Ha) % TotalPeat Swamp Forest (lightly degraded) 18,983 40.4Peat swamp forest (highly degraded_ 1,734 3.7Peat Shrubland (
During the ground surveys, aerial surveys were also conducted. Atotal of 3,382 photos were taken over the Rimba Rayaconcession. Photos with high cloud cover were excluded andremaining photos were ortho-‐rectified and georeferenced asdescribed in the baseline report. One-‐hectare plots wereinstalled in the center of each photo and tree crowns wereidentified and measured in order to estimate above ground treebiomass. Example aerial photos with plots and tree-‐crowndelineations are shown below for lightly degraded peat swampforest (Figure 12a) and kerangas forest/open scrub (Figure 12b).Biomass by landcover class for Rimba Raya based on ground andaerial survey analysis is shown in Table 3.Land Cover DescriptionTable 3. Biomass of Land Cover typesBiomass in trees > 10cm DBH (t d.m. ha-‐1)Peat Swamp Forest (lightly degraded) 206Peat swamp forest (highly degraded) 140Peat Shrubland (
Page 1 and 2: The Rimba Raya Biodiversity Reserve
Page 3 and 4: AcknowledgementsWith Special Recogn
Page 5 and 6: ContentsContents ..................
Page 7 and 8: BIODIVERSITY SECTION ..............
Page 9 and 10: GLOSSARY OF PROJECT SPECIFIC TERMSC
Page 11 and 12: REDD, which is necessarily conserva
Page 13 and 14: Rehabilitation Center (OFI), home t
Page 15 and 16: estricted-‐range, or otherwise
Page 17 and 18: HydrologyWatersheds in the Project
Page 19 and 20: SoilA soil map for the Project Zone
Page 21 and 22: ClimateRainfall in the Project Zone
Page 23 and 24: Compositionally, freshwater swamps
Page 25 and 26: selective logging, intensive loggin
Page 27 and 28: G1.3. Boundaries of the Project Are
Page 29 and 30: Communities in the Project ZoneThe
Page 31 and 32: Delineation of the Project Zone. To
Page 33: the project and recommending that t
Page 37 and 38: Stratification by Peat Distribution
Page 39 and 40: G1.5. Description of Project Zone C
Page 41 and 42: Only a few of the communities have
Page 43 and 44: livelihoods, providing protection f
Page 45 and 46: Similar to the other villages along
Page 47 and 48: company. On average, farmers and fi
Page 49 and 50: categories: housing, office, agricu
Page 51 and 52: Table 6. Current Community Conflict
Page 53 and 54: and six are Vulnerable (VU). CR spe
Page 55 and 56: eight are listed as Vulnerable. Eig
Page 57 and 58: 2004). These losses highlight the i
Page 59 and 60: small mammal species richness decli
Page 61 and 62: even fewer forest species than plan
Page 63 and 64: Other threats to biodiversityAdditi
Page 65 and 66: HCV1.1Table 8. Preliminary evaluati
Page 67 and 68: of water supplies and prevention of
Page 69 and 70: ladang agriculture, scrub, short se
Page 71 and 72: Table 11. Critically Endangered Hig
Page 73 and 74: d. areas that support significant c
Page 75 and 76: G1.8.2. Significant Large Landscape
Page 77 and 78: It is possible that a degree of per
Page 79 and 80: The revised Toolkit for Indonesia i
Page 81 and 82: the assessment area; and second, an
Page 83 and 84: HCV 4.3HCV 4.3 aims to identify and
Page 85 and 86:
Within the Project Area and neighbo
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G1.8.6. Areas Critical for Traditio
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In 2004, five oil palm estates were
Page 91 and 92:
Figure 23. Comparison of the new dr
Page 93 and 94:
Table 15. Extent of Overlap w/ Oil
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Baseline analysis: LandcoverIn orde
Page 97 and 98:
All survey data has been entered in
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For a complete report on the Carbon
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Identification of Baseline Scenario
Page 103 and 104:
Under Indonesian legislation, Law (
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drained due to the realization that
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conversion for urban, rural, and in
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to 2002. Furthermore, deforestation
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Local Perspective. Tanjung Puting N
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Table 17. 2000-‐2008 Palm Oil E
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Provincial Government Targets Rimba
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to recovery from past disturbance,
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StratumTable 20. Calculations of CO
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Year ofProjectArea loggedyr-‐1T
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GHG removals from oil palm sequestr
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Year ofProjectArea burnedyr-‐1T
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Year ofProjectArea burnedyr-‐1T
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Yr ofProjectTable 26. Net baseline
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environmental impacts and the need
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triggered by palm-‐oil companie
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G3. Project Design and GoalsG3.1. S
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elements and an assessment of the P
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habitat in terms of canopy and food
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Funding of OFI activitiesTanjung Pu
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interventions can improve the poor
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Community Agro-‐Forestry. In ke
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The only requirement is to pump the
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The Rimba Raya project proponents i
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www.kiva.org as highly reputable fi
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purchases more than $24 million dol
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The comparative analysis will be us
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G3.4. Project Lifetime, Accounting
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Table 28. Rimba Raya Implementation
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2-‐Establishment ofRimba RayaRe
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6-‐Development ofSocial Buffer2
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7-‐Outreach andEducation3-‐
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Pembuang Hulu and Tanjung Hanau reg
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.7. Determination of the need for s
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elationship with oil palm companies
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capital.” In order to ensure that
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G3.8. Stakeholder Identification an
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2. Improve multi-‐stakeholder p
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Community Involvement during Projec
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31 26/12/08 Burhanudin Merchant Des
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Table 31. Rimba Raya Project Proces
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G3.9. CCBA Public Comment PeriodDes
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In some contexts, for example where
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Table 32. Required Skill Sets , Key
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Develop areforestationprogramaround
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Figure 38 PT Rimba Raya Conservatio
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Figure 40. Project Organizational C
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manipulated to serve someone’s pe
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13). One area of special considerat
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also provide training in the skills
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Communitycenters &librariesWater fi
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C102 - Social Security (Minimum Sta
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G5.2. Documentation of Project Appr
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Figure 42. Official Land Area Verif
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Figure 44. Original Letter from Gov
Page 213 and 214:
Figure 45. Original Minister’s De
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Encroachment by Palm Oil Plantation
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CLIMATE SECTIONCL1. Net Positive Cl
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CL1.5. Double Counting of Emissions
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Negative leakage is the unanticipat
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undervalued. Moreover, the argument
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et. al., 2005). However the long te
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edistributed such that the most eff
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The intersection of the hypothetica
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dedicated to bio-‐fuel producti
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Without project activities are disp
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Table 36. Assessment of risk factor
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Table 36. ...continuedRiskFactorLik
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Table 37. ...continuedRisk Factor %
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degraded portions of the Project Ar
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CL2.4. Leakage and non-CO2 GasesNon
Page 245 and 246:
Monitoring of the boundary of the p
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Monitoring will be conducted by a p
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Table 38. InfiniteSUSTAINABILITY Ma
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Phinisi FloatingClinicMicro-Finance
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Table 39. Threats and management re
Page 255 and 256:
Hunting - Communities in the Projec
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All five of these capital assets ar
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Hygiene improvesProportion of house
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LARASITAProject proponents will wor
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B1.2. Impact of Project Activities
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HCV 1.1 Support Function to Protect
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further losses. Protection of non-
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five are listed as Endangered by IU
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HCV 2.3 Areas that Contain Populati
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Table 42. Species to be used for Ri
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negative. In this scenario, net bio
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permanent 10-‐20 km transects s
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high resolution imagery) and field
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e present in the Seruyan River insi
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The Rimba Raya Project is located i
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intentionally or unintentionally, f
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GL3. Exceptional Biodiversity Benef
Page 289 and 290:
Table 44. Endangered & Critically E
Page 291 and 292:
GL3.2.2. Species with Large but Clu
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BIBLIOGRAPHYAnderson, J.A.R. (1972)
Page 295 and 296:
Gibbs, H., (2008) Carbon payback ti
Page 297 and 298:
Nicolas, Marc V.J. and Grant S. Bee
Page 299 and 300:
Islands]. In Press.Susilo, H.D. (19
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The Rimba Raya Biodiversity Reserve REDD Project

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