Kalimantan Forests and Climate Partnership (KFCP) Design ...

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1. Existing Soil Maps developed by various sources and at various scales from 1:250,000 to 1:1000,000 at different times using methodologies to be identified and assessed; 2. Information on peatland thickness, types and area from various sources collected at different times using methodologies that do not appear to be heavily documented; and 3. Bulk density and carbon contents of peatlands where available, though this does not appear to have been widely collected using methodologies to be identified and assessed. Refinements required to assess peatland for national carbon accounting include: 1. Effective mapping of peatland distribution, peatlands and peat characteristics (such as depth, density and type) through: ο Compilation and analysis of existing data for preparation of base maps, data compilation and processing; ο Assessment of existing methodologies for assessing peatland and peat characteristics and the setting out of methodologies for peer review and confirmation to establish standardised methods; ο Ground survey to confirm presence and characteristics of peatlands using standardised methods; ο Development of correlations and relationships with remotely sensed data; ο Review of existing methods, including the field guide developed by Murdiyarso et al (2004), and others to identify a standardised method or methods to evaluate in field trials; 2. Area burnt is a key input for estimating GHG emissions from peat soils; ο Burnt area assessment using remote sensing techniques has been researched with some management applications; ο Ground truthing and field verification is needed to confirm the reliability of estimates based on remote sensing; 3. Combustion of peat: ο The amount of peat actually burnt in wildfire or in management burns is a critical determinant of GHG emissions, and highly spatially variable with subjective judgements of this variable having been used; ο Moisture content of the peat, which is determined by seasonal rainfall and by peat drainage activities, appears to be the most important variable; ο Field studies under a wide range of conditions are needed to determine the relationship between moisture content and the depth and mass of peat burnt; 4. Emission factors for CO 2 , N 2 O and CH 4 emissions during peat fires; ο Very little data is available for peat fires and measurements of GHG emissions during combustion of different peat under a range of burning conditions are needed; and 5. Temporal trends in CO 2 and non-CO 2 GHG emissions: ο Systematic field measurements to quantify the effects of disturbance in peat systems should aim to develop a process-based understanding of the observed GHG fluxes that can then be used, through tested models, to make broader-scale estimates. Additional Aspects of Peat In the mission there was the opportunity to visit and consider field activities and operations that have been conducted by the stakeholders and actors working in the EMRP area and in Sebangau National Park. The team and those they met noted the issues of remote sensing to track changes in peat emissions. There were a number of aspects about peatlands that require clarification and further consideration: 1. Peat Hydrology: 6-4 KALIMANTAN FORESTS AND CLIMATE PARTNERSHIP (KFCP) DESIGN DOCUMENT
ο The efficacy of canal blocking and planning the restoration of peatlands requires a clear understanding of how water moves through peat: • Where does the water come from? • How fast does it move through the peat dome? • What influences the movement of water through the peat and peat domes? Gravity? Hydraulic forces? Capillary action? ο Water table movements: • There are a number of records of the water table height. The method for obtaining that data requires validation and is not clear; • The ‗natural‘ variation of water tables in undisturbed peatland and in peatland under various types of management does not appear to be identified; • The response of water tables to actions such as canal blocking and replanting has been recorded but the patterns are not clear, the influences on the water table may vary depending on: Peat characteristics; Canal size; Type of dam for blocking; Water flow in the canal; Hydrology of peat; Peat dome shape and height; • The influence of replanting trees on water tables; 2. Canal blocking: ο Observations in the field and the data on water tables do not paint a clear picture of the effectiveness of canal blocking in re-flooding and restoration of peatlands; ο Discussion with some wetland and hydrology specialists and the University suggest that the effectiveness of dams blocking canals is not clear and needs to be confirmed; and ο It may be that the apparent variation in performance of canal blocking is due to the varying characteristics of peat among and between the locations. KALIMANTAN FORESTS AND CLIMATE PARTNERSHIP (KFCP) DESIGN DOCUMENT 6-5
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2009 KALIMANTAN FORESTS AND CLIMATE
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TABLE OF CONTENTS Table of Contents
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Establishing a REL ................
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GIS GoA GoI GTZ Handil IAFCP ICRAF
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LIST OF FIGURES Map 1. Location Map
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MAP 1. LOCATION MAP KALIMANTAN FORE
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MAP 3. LAND COVER MAP OF KFCP DEMON
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MAP 5. FIRE FREQUENCY IN KFCP DEMON
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which government-to-government acti
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1.3 IMPLEMENTATION APPROACH The KFC
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There is currently no international
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2.0 INTRODUCTION 2.1 PURPOSE OF THI
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Text Box 2.1. The following GoI Pla
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Issues relating to additionality, l
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2.4 OVERVIEW OF THE DEMONSTRATION A
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TABLE 2. CO-BENEFITS OF KFCP’S IN
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2.5.2 Location The KFCP field demon
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2.6.1 Preparatory Activities Partne
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3.0 IMPLEMENTATION STRATEGY AND COM
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Incentives to encourage sustainable
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The KFCP will identify potential co
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FIGURE 3. FLOW CHART OF STEPS TO EN
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Peatland Rehabilitation Plan for Bl
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GHG Emissions Estimation and Monito
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emote sensing products to use will
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take the form of a trust fund, whic
Page 54 and 55: Implementation Process Early Implem
Page 56 and 57: Capacity for Effective Governance S
Page 58 and 59: 4.1 MANAGEMENT STRUCTURE AND COORDI
Page 60 and 61: Text Box 4.2. Roles of Groups withi
Page 62 and 63: (ii) develop a strategic plan for R
Page 64 and 65: Information Feedback for Management
Page 66 and 67: Screen KFCP interventions and payme
Page 68 and 69: 6.0 RISK MANAGEMENT AND SUSTAINABIL
Page 70 and 71: . A review of the program logic and
Page 72 and 73: 8.0 ESTIMATED BUDGET AND STRATEGY F
Page 75: ATTACHMENTS Attachment 1. Livelihoo
Page 78 and 79: cause conflict between forestry, co
Page 80 and 81: Health Key human health issues are
Page 83 and 84: ATTACHMENT 2. VILLAGE ENGAGEMENT PR
Page 85 and 86: . Bring land tenure and land use to
Page 87 and 88: FIGURE 2-2. CONDENSED VILLAGE PROCE
Page 89: INTERNATIONAL FOREST CARBON INITIAT
Page 92 and 93: Papua New Guinea-Australia Forest C
Page 94 and 95: Hydrological Rehabilitation Hydrolo
Page 97 and 98: ATTACHMENT 5. PAYMENT MECHANISMS DI
Page 99 and 100: What types of in-kind payments woul
Page 101 and 102: ATTACHMENT 6. GHG EMISSIONS REL AND
Page 103: Present Methodologies for Assessing
Page 108 and 109: What makes the area so vulnerable t
Page 110 and 111: The 2006 fire episode underlines th
Page 112 and 113: — Intensive agriculture on levees
Page 115 and 116: ATTACHMENT 9. INDICATIVE PERFORMANC
Page 117 and 118: Objective statements Potential Indi
Page 119 and 120: ATTACHMENT 10. PRELIMINARY IMPLEMEN
Page 121: KALIMANTAN FORESTS AND CLIMATE PART
Page 124 and 125: Potential Risk 1. Land use disputes
Page 126 and 127: Potential Risk 11. Carbon prices ar
Page 128 and 129: INDONESIA AND AUSTRALIA Reducing em
Page 130 and 131: Attachment A The Kalimantan Forests
Page 132 and 133: Australia is also offering Indonesi
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Kalimantan Forests and Climate Partnership (KFCP) Design ...

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