The Rimba Raya Biodiversity Reserve REDD Project

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Existing Conditions: Field Surveys of Peat and BiomassOverviewForest Carbon consultants and Orangutan FoundationInternational (OFI) conducted a field survey June 22 – July 4, 2009on behalf of InfiniteEARTH to support the Rimba Raya carbonassessment. Two 8-‐person field teams, including experiencedforest surveyors, OFI staff and local residents familiar with RimbaRaya forests conducted the survey. In the initial 6 transectssurveyd, a total of 12,750 meters of transect were marked andsurveyed with peat depth measured in 131 locations and biomassdata recorded across 28 plots representing 7 hectares of forest.27 of 28 plots were located in logged peat swamp forest which isthe predominant forest type in Rimba Raya.Survey results indicate that despite the history ofselective-‐hand logging in the area, forest biomass ismoderately high and relatively consistent across majorforest blocks in Rimba Raya.Unexpectedly, peats were moderately deep across allsurvey transects. Most peat measurements exceeded thereach of the peat probe at 4 or 5 meters. Peats were 2-‐3meters deep on the southernmost transect within 10 kmof the Java Sea.DBH measurements of subplot treesMeasuring peat depth and using the prism to sample basal area87
All survey data has been entered into an Excel workbook andprovided to InfiniteEARTH, Forest Carbon and OrangutanFoundation International (OFI). These data provide the firstdetailed ground information on the condition and characteristicsof forest and peat in Rimba Raya which will be used in carbonstock assessments and other ecological analyses conducted byproject participants.Field Work Areas and Transect LocationsField survey areas were distributed north to south and located tocover a broad geographic area representing forest typesthroughout Rimba Raya (Figure 26). Inititally, six transects wereused to organize survey points, plots and subplots. Available landcover maps and satellite imagery of the area were reviewed inorder to locate transects in forest across a variety of hydrologicconditions and levels of disturbance.Field teams staged field work out of OFI monitoring posts andtemporary camps near transects. Transects 1 and 2 weresurveyed by combined teams at the start of the fieldwork.Following completion of these surveys, separate teams movedsouth to survey Transects 3 and 4 (Central Team) and Transects 5and 6 (Southern Team). From overnight camps, teams navigatedto the transect start to cut and mark the centerline.On 4 of the original 6 transects, the transect center was used asthe start point to provide an efficient means of accomplishingmulti-‐day surveys from centrally-‐located camps or site accesspoints. At these sites (T2, T3, T4, T6), transect layout proceededin two parts: 1-‐1.25 km to the East and 1-‐1.25 km to the West. Atthe other sites (T1 and T5), forest conditions relative to site entrypoints required transect layout from the endpoints.Northern transects 1 and 2 were located in the vicinity of BaungRiver and OFI’s Post Sitiung. Central transects 3 and 4 werelocated in the interior of Rimba Raya from Muara Dua village onthe Seruyan River accessed by the Sigintung River and Tatah “J”Canal. Southern transects 5 and 6 were located in Rimba Raya inthe vicinity of Tanjung Rengas village on the Seruyan, accessed bycanals.Transect and Plot LayoutThe survey was designed to orient all transects east-‐west tofacilitate accuracy and consistency in layout. All transects followthis east-‐west orientation except Transect 5 which follows theorientation of the relatively narrow forest patch. Transects were2.0 -‐ 2.25 km in length oriented on a bearing of 90° -‐ 270°.Transect 5 was oriented on a bearing of 310° -‐ 130° to traversethe existing forest patch. Transect centerlines were marked every10 meters with poles and flagging which provided orientation forsurvey plots.Along the transects, tree counts for volume estimates wererecorded every 50 meters and peat depth was measured every100 meters. Biomass plots 250m x 10m (¼ hectare), were locatedat 250 meter intervals on the transect. Tree diameter, tree heightand tree canopy measurements were recorded in biomass plotsfor large trees (> 20 cm dbh) across the entire plot and withintwo nested subplots (50 x 10m) for small trees (10-‐20 cm dbh). Atotal of 12.75 km of transect were surveyed including 131 samplelocations for peat depth, 262 sample locations for tree volumeand 28 biomass plots representing 7 hectares of detailed treesurveys.For a complete report on the Carbon Assessment Surveys, seeAnnex 5.88
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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
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
Page 87 and 88: G1.8.6. Areas Critical for Traditio
Page 89 and 90: 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
Page 95: Baseline analysis: LandcoverIn orde
Page 99 and 100: For a complete report on the Carbon
Page 101 and 102: Identification of Baseline Scenario
Page 103 and 104: Under Indonesian legislation, Law (
Page 105 and 106: drained due to the realization that
Page 107 and 108: conversion for urban, rural, and in
Page 109 and 110: to 2002. Furthermore, deforestation
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
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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
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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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