The Rimba Raya Biodiversity Reserve REDD Project

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G3.3. Project Boundaries and Location of MajorProject ActivitiesProvide a map identifying the project location and boundaries of theproject area(s), where the project activities will occur, of the projectzone and of additional surrounding locations that are predicted to beimpacted by project activities (e.g. through leakage).Figure 33 depicts the Project Area, Project Zone, and surroundingregion. Most major project activites related to climate andbiodiversity will take place throughout the Project Area, whilemost activities related to community goals will take placethroughout the Project Zone communities. These activities havenot been depicted here, but full descriptions are available inSection G3.2 above. Many leakage mitigation activities are alsoregional or not amenable to depiction in this format, but a fulldescription is available in Section CL2 below.Figure 33. Map of major project activities147
G3.4. Project Lifetime, Accounting Period, andImplementation ScheduleDefine the project lifetime and GHG accounting period and explain andjustify any differences between them. Define an implementationschedule, indicating key dates and milestones in the project’sdevelopment.Project Lifetime and GHG Accounting PeriodProject lifetime. The official lifetime for the Rimba Raya projectis 60 years, equal to the term of the IUPHHK-‐RE concessionlicense issued for the Project Area by the Minister of Forestry.This license is for an ecosystem restoration concession, and thereare mandated forest restoration requirements over the life of thelicense.Accounting period. The GHG crediting period for the project is30 years, consistent with the date determined by the BaselineScenario. The project has adopted a planned deforestationapproach with oil palm as the driver of deforestation. Givenestimated peat depths in the Project Area, our methodologyestimates that all peat deposits would have been completelyoxidized in the “without project” scenario at the end of thisperiod, marking a natural conclusion to the crediting period.Mechanisms have been put in place to ensure adequate fundingfor mandated ecosystem restoration activities from years 30 to60 and for all major project activities in perpetuity after the GHGcrediting period. A portion of the credits generated by theproject will be sold, and the revenues invested in an endowmentfund explicitly designated for project continuity after creditingrevenues expire (see Section G3.7, below). In addition, many ofthe major project activities are designed to become self-‐sustaining over the project lifetime, such that they will notrequire crediting revenues to continue after the project comes toan end.Certification schedule. Project proponents expect to undertakeannual certification of carbon credits for the first ten years of theproject, followed by certification every two years for theremaining twenty years, as indicated in Table 27:VerificationNumberTable 27. Verification Schedule for theRimba Raya Crediting PeriodVerificationYear VintageYearNumberVintage1 2010 2009 11 2021 2019-‐20202 2011 2010 12 2023 2021-‐20223 2012 2011 13 2025 2023-‐20244 2013 2012 14 2027 2025-‐20265 2014 2013 15 2029 2027-‐20286 2015 2014 16 2031 2029-‐20307 2016 2015 17 2033 2031-‐20328 2017 2016 18 2035 2033-‐20349 2018 2017 19 2037 2035-‐203610 2019 2018 20 2039 2037-‐2038148
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The Rimba Raya Biodiversity Reserve
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AcknowledgementsWith Special Recogn
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ContentsContents ..................
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BIODIVERSITY SECTION ..............
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GLOSSARY OF PROJECT SPECIFIC TERMSC
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REDD, which is necessarily conserva
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Rehabilitation Center (OFI), home t
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estricted-‐range, or otherwise
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HydrologyWatersheds in the Project
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SoilA soil map for the Project Zone
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ClimateRainfall in the Project Zone
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Compositionally, freshwater swamps
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selective logging, intensive loggin
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G1.3. Boundaries of the Project Are
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Communities in the Project ZoneThe
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Delineation of the Project Zone. To
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the project and recommending that t
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During the ground surveys, aerial s
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Stratification by Peat Distribution
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G1.5. Description of Project Zone C
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Only a few of the communities have
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livelihoods, providing protection f
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Similar to the other villages along
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company. On average, farmers and fi
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categories: housing, office, agricu
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Table 6. Current Community Conflict
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and six are Vulnerable (VU). CR spe
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eight are listed as Vulnerable. Eig
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2004). These losses highlight the i
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small mammal species richness decli
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even fewer forest species than plan
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Other threats to biodiversityAdditi
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HCV1.1Table 8. Preliminary evaluati
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of water supplies and prevention of
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ladang agriculture, scrub, short se
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Table 11. Critically Endangered Hig
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d. areas that support significant c
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G1.8.2. Significant Large Landscape
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It is possible that a degree of per
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The revised Toolkit for Indonesia i
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the assessment area; and second, an
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HCV 4.3HCV 4.3 aims to identify and
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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
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Figure 23. Comparison of the new dr
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Table 15. Extent of Overlap w/ Oil
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Baseline analysis: LandcoverIn orde
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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
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Under Indonesian legislation, Law (
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Page 107 and 108: conversion for urban, rural, and in
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Page 111 and 112: Local Perspective. Tanjung Puting N
Page 113 and 114: Table 17. 2000-‐2008 Palm Oil E
Page 115 and 116: Provincial Government Targets Rimba
Page 117 and 118: to recovery from past disturbance,
Page 119 and 120: StratumTable 20. Calculations of CO
Page 121 and 122: Year ofProjectArea loggedyr-‐1T
Page 123 and 124: GHG removals from oil palm sequestr
Page 125 and 126: Year ofProjectArea burnedyr-‐1T
Page 127 and 128: Year ofProjectArea burnedyr-‐1T
Page 129 and 130: Yr ofProjectTable 26. Net baseline
Page 131 and 132: environmental impacts and the need
Page 133 and 134: triggered by palm-‐oil companie
Page 135 and 136: G3. Project Design and GoalsG3.1. S
Page 137 and 138: elements and an assessment of the P
Page 139 and 140: habitat in terms of canopy and food
Page 141 and 142: Funding of OFI activitiesTanjung Pu
Page 143 and 144: interventions can improve the poor
Page 145 and 146: Community Agro-‐Forestry. In ke
Page 147 and 148: The only requirement is to pump the
Page 149 and 150: The Rimba Raya project proponents i
Page 151 and 152: www.kiva.org as highly reputable fi
Page 153 and 154: purchases more than $24 million dol
Page 155: The comparative analysis will be us
Page 159 and 160: Table 28. Rimba Raya Implementation
Page 161 and 162: 2-‐Establishment ofRimba RayaRe
Page 163 and 164: 6-‐Development ofSocial Buffer2
Page 165 and 166: 7-‐Outreach andEducation3-‐
Page 167 and 168: Pembuang Hulu and Tanjung Hanau reg
Page 169 and 170: .7. Determination of the need for s
Page 171 and 172: elationship with oil palm companies
Page 173 and 174: capital.” In order to ensure that
Page 175 and 176: G3.8. Stakeholder Identification an
Page 177 and 178: 2. Improve multi-‐stakeholder p
Page 179 and 180: Community Involvement during Projec
Page 181 and 182: 31 26/12/08 Burhanudin Merchant Des
Page 183 and 184: Table 31. Rimba Raya Project Proces
Page 185 and 186: G3.9. CCBA Public Comment PeriodDes
Page 187 and 188: In some contexts, for example where
Page 189 and 190: Table 32. Required Skill Sets , Key
Page 191 and 192: Develop areforestationprogramaround
Page 193 and 194: Figure 38 PT Rimba Raya Conservatio
Page 195 and 196: Figure 40. Project Organizational C
Page 197 and 198: manipulated to serve someone’s pe
Page 199 and 200: 13). One area of special considerat
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Page 205 and 206: 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
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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
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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
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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
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Table 44. Endangered & Critically E
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GL3.2.2. Species with Large but Clu
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BIBLIOGRAPHYAnderson, J.A.R. (1972)
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Gibbs, H., (2008) Carbon payback ti
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Nicolas, Marc V.J. and Grant S. Bee
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Islands]. In Press.Susilo, H.D. (19
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The Rimba Raya Biodiversity Reserve REDD Project

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