The Rimba Raya Biodiversity Reserve REDD Project

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Monitoring of forest protection activitiesAs part of monitoring forest protection activities, any increases inGHG emissions that occur within the project boundary after thestart of the project must be recorded and deducted from the exante estimate of baseline emissions. The following categories shallbe recorded in the project database and reported at the time ofverification: Area where natural or anthropogenic disturbances(including fire, illegal logging and other land use change)occurred within the project boundary by date, location,biomass lost or affected, and the preventative or curativemeasures, if any implemented Number and location of logging gaps by date, location,biomass lost or affected, and the preventative or curativemeasures, if any implemented Area and depth of peat burned within the project area bydate, location, estimated peat emissions, and thepreventative or curative measures, if any implemented Area of peat, if any, that was drained within the projectboundary by date, location, estimated peat emissions, andthe preventative or curative measures, if any implemented Information on forest protection practicesMonitoring of project emissionsEmissions in peat swamp normally occur due to fire, man-‐madedrainage, and through extractive or conversion activities, andoccasionally could occur due to extended droughts. Themonitoring system will have built-‐in checks and take ahierarchical approach starting first with satellite imagery, aerialsurveys, and then ground patrols. The hierarchical system willutilize medium resolution imagery (28-‐30m) and local knowledgeto identify high risk areas, which will be monitored on a quarterlybasis either using overflights or through patrol teams. ALOSimagery will be downloaded every year and is at a resolutionsimilar to LANDSAT. The 2008 ALOS image is shown on thefollowing page.Due to hydrostatic pressure, canals can have impacts on drainingpeat forest several kilometers away, causing subsidence,oxidation, and the eventual collapse of peat domes. To avoid thisissue, the methodology calls for a buffer of 3km that excludesman-‐made canals from the carbon accounting area andmonitoring will need to track whether any canals are being builtin this buffer. The Rimba Raya border has been designed tominimize risks from man-‐made drainage with its western borderabutting Tanjung Puting NP, while its eastern border follows theSeruyan River. There are several pre-‐existing small canals in theproject area that were built to extract timber from small-‐scaleillegal logging operations. Small dams will be built to stop thedrainage in years two and three of the project once the level ofsupport for the project among the communities has considerablystrengthened.The project area has been divided into forest strata where eachstratum represents a unique forest type (peat, lowland, heathforests) and land use class (unlogged or degraded). The area wasstratified before the biomass survey in order to increaseefficiency and precision of the survey. Following the biomasssurvey, the strata were revised using information gained bothfrom field plots and high resolution aerial photography. Annualmonitoring will assess if there are any changes to the strataboundaries.237
Monitoring will be conducted by a professional team consistingof a coordinator, a field team, and a GIS technician. Thecoordinator will report directly to the General Manager.All monitoring activities will be implemented using StandardOperational Procedures (SOPs) and personnel will be trainedpermanently to ensure the data quality.238
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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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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
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
Page 201 and 202: also provide training in the skills
Page 203 and 204: Communitycenters &librariesWater fi
Page 205 and 206: C102 - Social Security (Minimum Sta
Page 207 and 208: G5.2. Documentation of Project Appr
Page 209 and 210: Figure 42. Official Land Area Verif
Page 211 and 212: Figure 44. Original Letter from Gov
Page 213 and 214: Figure 45. Original Minister’s De
Page 215 and 216: Encroachment by Palm Oil Plantation
Page 217 and 218: CLIMATE SECTIONCL1. Net Positive Cl
Page 219 and 220: CL1.5. Double Counting of Emissions
Page 221 and 222: Negative leakage is the unanticipat
Page 223 and 224: undervalued. Moreover, the argument
Page 225 and 226: et. al., 2005). However the long te
Page 227 and 228: edistributed such that the most eff
Page 229 and 230: The intersection of the hypothetica
Page 231 and 232: dedicated to bio-‐fuel producti
Page 233 and 234: Without project activities are disp
Page 235 and 236: Table 36. Assessment of risk factor
Page 237 and 238: Table 36. ...continuedRiskFactorLik
Page 239 and 240: Table 37. ...continuedRisk Factor %
Page 241 and 242: degraded portions of the Project Ar
Page 243 and 244: CL2.4. Leakage and non-CO2 GasesNon
Page 245: Monitoring of the boundary of the p
Page 249 and 250: Table 38. InfiniteSUSTAINABILITY Ma
Page 251 and 252: Phinisi FloatingClinicMicro-Finance
Page 253 and 254: Table 39. Threats and management re
Page 255 and 256: Hunting - Communities in the Projec
Page 257 and 258: All five of these capital assets ar
Page 259 and 260: Hygiene improvesProportion of house
Page 261 and 262: LARASITAProject proponents will wor
Page 263 and 264: B1.2. Impact of Project Activities
Page 265 and 266: HCV 1.1 Support Function to Protect
Page 267 and 268: further losses. Protection of non-
Page 269 and 270: five are listed as Endangered by IU
Page 271 and 272: HCV 2.3 Areas that Contain Populati
Page 273 and 274: Table 42. Species to be used for Ri
Page 275 and 276: negative. In this scenario, net bio
Page 277 and 278: permanent 10-‐20 km transects s
Page 279 and 280: high resolution imagery) and field
Page 281 and 282: e present in the Seruyan River insi
Page 283 and 284: The Rimba Raya Project is located i
Page 285 and 286: intentionally or unintentionally, f
Page 287 and 288: 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
Page 293 and 294: BIBLIOGRAPHYAnderson, J.A.R. (1972)
Page 295 and 296: 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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