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GeneratingForestBiomassCarbonStockEstimatesforMappingthePotentialofREDD+toDeliverBiodiversityConservationinVietnam Benktesh D Sharma, Vu Tan Phuong & Steven R Swan September 2013 SNV REDD+ www.snvworld.org/redd Acknowledgements Theforestbiomasscarbonstock density estimates summarised in this report were commissioned by SNV – The Netherlands Development Organisation as part ofthe project ‘Exploring Mechanisms to Promote High-Biodiversity REDD+: Piloting in Vietnam’ (HB-REDD) Initial estimates were prepared by Green Field Consulting Co Ltd., in collaboration with the Research Centre forForest Ecology and Environment (RCFEE), with technical assistance from the United Nations Environment Programme – World Conservation Monitoring Centre (UNEP-WCMC) as part oftheREDD+ Policy Assessment Center (REDD-PAC) project Both the HB-REDD and REDD-PAC projects are part ofthe International Climate Initiative The German Federal Ministry forthe Environment, Nature Conservation and Nuclear Safety supports this initiative on the basis of a decision adopted by the German Bundestag This report documents methods and results of basic nationwide forestbiomasscarbonstock estimation as a contribution tothe preliminary spatial analysis ofpotentialforREDD+todeliverbiodiversityconservationinVietnam (Mant et al 2013) Thanks to Florian Werner, of Deutsche Gesellschaft für Internationale Zusammenarbeit (GIZ), who provided comments on a draft version ofthe report Disclaimer Theforestbiomasscarbonstock density estimates and accompanying tables presented in this report were produced using publicly available data and reports available at the time of analysis This report does not present any official assessment or statement on Vietnam’s forestbiomasscarbon on the part ofthe Government ofVietnam or any other entity The analysis reported herein was conducted as a contribution to preliminary spatial analyses ofthepotentialforREDD+todeliverbiodiversityconservationinVietnam (see Mant et al 2013) The results are for illustrative purposes only, with a view to stimulating further work on estimating and mappingbiomasscarbonstock density forREDD+ planning purposes inVietnamThe example results here are not intended to promote any particular process or approach toREDD+inVietnamThe outputs cannot be applied as a basis for establishing reference levels or to meet the detailed requirements for measuring, reporting and verification of greenhouse gas emission reductions or enhanced removals under the National REDD+ Action Programme Authors: B Sharma Participatory Forest Monitoring Advisor, SNV - The Netherlands Development Organisation, San Francisco Vu Tan Phuong Director, Research Centre forForest Ecology & Environment, VietnamForest Science Institute, Hanoi S Swan Senior REDD+ Advisor, SNV - The Netherlands Development Organisation, Hanoi Citation: Sharma, B.D., Vu Tan Phuong & S.R Swan (2013) GeneratingForestBiomassCarbonStockEstimatesforMappingthePotentialofREDD+todeliverbiodiversityconservationinVietnam SNV – The Netherlands Development Organisation, Ho Chi Minh City SNV REDD+ www.snvworld.org/redd Table of Contents Page Acknowledgements Abbreviations Summary Introduction 1.1 Aims 1.2 Scope 1.3 Review offorestbiomasscarbonstock estimation inVietnam Methods 2.1 Overview 2.2 Data availability 2.2.1 Wood volume estimation 2.2.2 Biomass expansion factors 2.3 Method used for Tier type forestbiomasscarbon estimation 2.3.1 Forest stratification and area estimation 11 2.3.2 Estimation offorestbiomass 11 2.3.3 Estimation offorestbiomasscarbonstock density 12 Results and Discussion 13 List of tables and figures: Table Mean value of wood volume (m3 ha-1) by forest strata in 2001-2005 Table Biomass Expansion Factor for different forest types inVietnam using 2001-2005 inventory data on wood volume Table Forest area by forest stratum in 2005 11 Table Estimated biomasscarbonstock by forest types in 2005 13 Figure Simple methodological framework used to estimate forestbiomasscarbon densities Rectangles depict process while parallelograms depict specific outputs or inputs to these processes 10 Figure Tier 2-type forestbiomasscarbon map for Vietnam, 2001-2005 14 Figure Tier 1-type forestbiomasscarbon map for Vietnam, c 2000 15 Figure Average land cover carbon density by km pixel in Vietnam, 2000 16 SNV REDD+ www.snvworld.org/redd Abbreviations AGB above-ground biomass BEF biomass expansion factors BGB below-ground biomass FAO Food and Agriculture Organisation FIPI Forest Planning and Inventory Institute FRA Forest Resource Assessment FSIV Forest Science Institute ofVietnam GHG greenhouse gas GPG Good Practice Guidance IPCC Intergovernmental Panel on Climate Change LULUCF land use, land-use change and forestry NFIMAP National Forest Inventory, Monitoring and Assessment Programme NRAP National REDD+ Action Programme RCFEE Research Centre forForest Ecology and Environment REDD+ SNV REDD+ Reducing emissions from deforestation and forest degradation, and the role of conservation, sustainable management of forests and enhancement offorestcarbon stocks in developing countries www.snvredd.com Summary This report presents a simple approach to estimating thebiomasscarbonstock density for an area based on publicly available information such as timber volumes and forest area, as applied in a recent effort to map thepotentialforREDD+todeliverbiodiversityconservationinVietnamThe procedure presented here combines remote sensing products and forest inventory data in deriving forestbiomasscarbonestimates as a contribution to prioritising areas for future REDD+ activities under the National REDD+ Action Programme (NRAP) The approaches used in deriving these estimates can also be replicated for smaller spatial units, such as provincial or forest management unit levels, and could be extended to include other forestcarbon pools that have not been included in this study A summary of methods used to estimate forestbiomasscarbonstock density in above - and below - ground pools is presented forVietnamforthe period 2000-2005 The results, using ‘Tier 2’ national forest cover and wood volume datasets, estimated that in 2005, Vietnam’s c 12 million offorest contained about 1.2 billion tonnes ofbiomass carbon, distributed across 12 broad ecological forest types, at mean a stocking density of 105 tC ha-1 varying considerably across forest types with lowest carbonstock density in bamboo forest and highest in evergreen broadleaved forests Theforestcarbon density maps produced by the methods reported herein were used to explore the spatial relationship with the distribution of biological diversity inVietnam This preliminary analysis ofREDD+potentialtodeliverbiodiversityconservationinVietnam is presented in a companion report (Mant et al 2013) as an example ofmapping multiple benefits ofREDD+to aid decision makers’ planning and prioritise actions and locations as part ofthe NRAP The methods used to derive forestbiomasscarbon estimate from publicly available information presented here can be used to generate forestcarbonestimatesfor smaller geographical units such as for provinces, districts and forest management units by using more accurate forest inventory data, specific wood density values and more accurate root:shoot ratios as they become available SNV REDD+ www.snvredd.com Introduction 1.1 Aims This report has been prepared to accompany the preliminary analysis ofmappingthepotentialfor REDD+1 todeliverbiodiversityconservationinVietnam (Mant et al 2013) The purpose of this report is to make publicly available the methods and data sources used in estimating forestbiomasscarbon maps used in this analysis ofthe spatial relationship between forestbiomasscarbon and biodiversityinVietnamTheforestbiomasscarbonestimates used the latest information publicly available in 2011, i.e the third cycle ofthe National Forest Inventory, Monitoring and Assessment Programme (NFIMAP III - 2001 to 2005) The method ofbiomasscarbonstock estimation reported here can be used with updated data inthe future, i.e the 2006-2010 NFIMAP IV The approach may also be used to assess theforestbiomasscarbonstock density at smaller spatial scale such as provinces or individual forest management units 1.2 Scope The estimation offorestbiomasscarbon stocks forcarbonstock density mappingin this report focus only on above-ground biomass (AGB) and belowground biomass (BGB) of live trees The other Intergovernmental Panel on Climate Change (IPCC)-recognised carbon pools intheforest ecosystem dead wood, litter and soils - are excluded However, the methods illustrated here can accommodate other carbon pool data in future estimates Indeed, global soil carbon datasets were initially explored by this study as a contribution toforestcarbonstockestimatesfor Vietnam.A global map of terrestrial soil carbon stocks (Scharlemann et al in prep.), based on up-to-date composite datasets summarized inthe Harmonized World Soil Database, was reviewed but not incorporated with forestbiomasscarbon maps forVietnam under this study, since the coarse resolution ofthe global soil data would have obscured the detailed spatial pattern forbiomasscarbon distribution obtained from the national data NFIMAP III data biomasscarbon (Mant et al 2013) 1.3 Review offorestbiomasscarbonstock estimation inVietnam There are a few existing estimations offorestbiomasscarbonstockinVietnamTheVietnam National report on Greenhouse Gases (GHG) Inventory for 1994 (MONRE 2003), and the National Communication tothe United Nation Framework on Climate Change of 2000 (MONRE 2010) estimated emissions in land use, land-use change and forestry (LULUCF) Since 2005, the Food and Agriculture Organisation (FAO) ofthe United Nations has been providing estimatesforforestbiomasscarbonstockin its Forest Resource Assessment (FRA) reports TheVietnam FRA Reports from 2005 and 2010 included an estimate offorestbiomasscarbonstock Both these reports utilised approaches 1 Reducing emissions from deforestation and forest degradation in developing countries; and the role of conservation, sustainable management of forests and enhancement offorestcarbon stocks in developing countries ofthe United Nations Framework Convention on Climate Change SNV REDD+ www.snvworld.org/redd following IPCC Good Practice Guidance (GPG) (IPCC 2006) for estimating biomasscarbon and used the suggested default values wherever relevant At the start oftheREDD+ readiness process in Vietnam, SNV created maps offorestbiomasscarbonstock density as part of an initial attempt to map thepotentialfor REDD inVietnam (Holland & McNally 2009) This analysis used the Vegetation Continuous Fields remote sensing product to create maps offorest cover and forest cover change Forestcarbon maps were derived from an IPCC Tier Global BiomassCarbon Map (Ruesch and Gibbs 2000) to identify priority areas for REDD activities This report presented a biomasscarbonstock density map for all Vietnamforthe first time, using a forest cover map from 2001 and 2005 (NFIMAP III) In 2009, Danish Technical Assistance inthe Development ofthe National REDD Programme ofVietnam also produced estimatesofforestbiomasscarbon (Raae et al 2010) With respect to estimation of spatially explicit biomasscarbonstockof planted forests in Vietnam, there are several studies on forestbiomass and carbon sequestration inVietnam These studies have mainly been implemented by theForest Science Institute ofVietnam (FSIV) Detailed biomass and carbonstock data for major plantations species i.e three pine species (Pinus massoniana; P merkusii; and P keysia); three species of acacia (Acacia mangium; A auriculiformis; A hybrid (mangium x auriculiformis); Eucalyptus urophylla; and Mangletia glauca are available (Vu Tan Phuong 2010; Vo Dai Hai et al 2010) A few studies on biomass and carbonstock have also been carried out inthe Central Highlands, focussing on estimation ofbiomass and carbon stocks for evergreen, semi-evergreen and deciduous forests (Bao Huy et al 2012, and Vo Dai Hai et al 2013) Studies to date offer limited information on forestbiomass and carbon stocks in Vietnam’s natural forests Biomass and carbon estimations are mostly based on coarse resolution data resembling Tier 12 approach ofthe IPCC The values applicable inthe Tier approach are generally not specific toVietnam and may not be suitable for drawing inference on forestcarbon stocks for broader forest types because the default values used have large degrees of uncertainty The maps produced by the present study used the most recent publicly available forest cover information, and specific allometric relationships for different forest types in Vietnam, to come up with a Tier 23 level estimate offorestcarbonstock density 2 Tier - approach employs the basic methods and default emission factors provided inthe IPCC Guidelines (Workbook and Reference Manual) A Tier approach uses activity data that are spatially coarse, such as nationally or globally available estimatesof deforestation rates, agricultural production statistics, and global land cover maps (IPCC 2006) 3 Tier - approach can use the same methodological approach as Tier 1, but uses emission factors and activity data that are defined by the country forthe most important land uses/activities Higher resolution activity data are typically used in Tier to correspond with country-defined coefficients for specific regions and specialised land-use categories (IPCC 2006) SNV REDD+ www.snvworld.org/redd Methods 2.1 Overview 2.2 Data availability The first national forest inventory inVietnam was started in 1991, and since then the () has been implemented on a five yearly cycle Therefore, a good forest database exists forthe period of 1990 – 2010 However, the national forest inventory programme inVietnam was not primarily designed forforestbiomasscarbonstock estimation; the focus oftheforest inventory was on merchantable volume of wood and available information may not be available for non-merchantable portion of trees, thus there are challenges in deriving biomasscarbonestimates comparable to a more detailed Tier 34 approach Therefore, forforestbiomasscarbon density mappingin Vietnam, a Tier approach was targeted to maximize the use of country specific data Development ofbiomasscarbonstockfor different forest types can use the national forest inventory data that include mainly wood volume of different forest types It must also be noted that due to unavailability of data, forestbiomasscarbonstock assessment considered only areas covered by trees and excluded areas covered by shrubs, bushes and grasslands 2.2.1 Wood volume estimation Inthe NFIMAP, there are a large number of permanent plots used forforest monitoring For NFIMAP III (2001-2005) the volumes of wood in merchantable tree stems, more commonly known as growing stock volume, for each oftheforest types were estimated from 4,100 sampling plots (Raae et al 2010) The mean values of growing stock volume for each forest type are shown in Table Table Mean value of wood volume (m3 ha-1) by forest strata in 2001-2005 Forest type 10 11 12 Rich evergreen broadleaved forest Medium evergreen broadleaved forest Poor evergreen broadleaved forest Regrowth evergreen broadleaved forest Deciduous forest Bamboo forest* Mixed wood-Bamboo forest Coniferous forest Mixed broadleaved and coniferous forest Mangrove forestForest on rocky mountain Plantation forest Growing Stock Volume (m3 ha-1) 255 157 71 70 100 87 151 137 33 73 67 Source: Adapted from Raae et al 2010 *The estimate ofthe growing stock volume of bamboo was not available 4 Tier – approach uses models and inventory measurement systems tailored to address national circumstances, repeated over time, and driven by high-resolution activity data and disaggregated at sub-national to local scales These higher order methods provide estimatesof greater certainty than lower tiers and have a closer link between biomass and soil dynamics (IPCC 2006) SNV REDD+ www.snvworld.org/redd 2.2.2 Biomass expansion factors Stem volume is a useful proxy ofbiomass traditionally used in forestry A critical requirement for estimating biomasscarbonstock based on stem volume is to develop biomass expansion factors (BEF) for different forest types The BEF serves as substitute forthe expansion ratios to calculate non-merchantable biomass (limbs, small trees etc.) from tree biomass contained in merchantable stem volume BEFs for different forest types were estimated from BEF and stem biomass relationship developed by Brown (1997) (Eq 2) except for conifers, mixed broadleaved-bamboo forests and bamboo forests For mixed broadleaved and conifer forest, default values provided in IPCC (2003) were used, while BEF was not estimated for bamboo forestThe BEFs used for various forest types inVietnam are shown in Table Table Biomass Expansion Factor for different forest types inVietnam using 2001-2005 inventory data on wood volume Forest types BEF Rich evergreen broadleaved forest Medium evergreen broadleaved forest Poor evergreen broadleaved forest Regrowth evergreen broadleaved forest Deciduous forest Bamboo forest 2.04 2.60 3.89 3.90 3.27 Not Available Mixed wood-Bamboo forest 2.00 10 11 12 Coniferous forest Mixed broadleaved and coniferous forest Mangrove forestForest on rocky mountain Plantation forest 1.20 2.78 5.74 3.84 4.00 Remarks Estimated using equation developed by Brown (1997) IPCC 2003 values (lower limit) IPCC 2003 values (lower limit) Estimated using equation developed by Brown (1997) 2.3 Method used for Tier type forestbiomasscarbon estimation The method to estimate forestbiomasscarbon used in this report is outlined in Figure Thebiomasscarbonstock estimation process starts with the definition ofthe spatial area of interest In this national-level study, the whole ofVietnam was used Once the spatial boundary was defined, a review of available data on biomasscarbonstock density, forest area, forest types, root to shoot ratio, wood density and carbon fraction was conducted SNV REDD+ www.snvworld.org/redd Figure Simple methodological framework used to estimate forestbiomasscarbon densities Rectangles depict process while parallelograms depict specific outputs or inputs to these processes 10 SNV REDD+ www.snvworld.org/redd 2.3.1 Forest stratification and area estimation The estimation offorestbiomasscarbonstockforthe entire forest estate of a country requires two variables, one is forest area and the other is carbonstock per hectare offorest i.e carbonstock density Theforest classifications used over the past four NFIMAP cycles were not consistent Therefore, there was a need to harmonize these systems to have relatively uniform categories offorest strata for analysis The area of each forest type was estimated for 2005 for 12 distinct harmonized forest strata developed by Raae et al (2010) These harmonized forest strata and areas covered by these forest types are shown in Table For each forest stratum, wood densities were derived and applicable root to shoot ratios and stem volumes were estimated Table Forest area by forest stratum in 2005 10 11 12 Total Forest type Rich evergreen broadleaved forest Medium evergreen broadleaved forest Poor evergreen broadleaved forest Regrowth evergreen broadleaved forest Deciduous forest Bamboo forest Mixed wood-Bamboo forest Coniferous forest Mixed broadleaved and coniferous forest Mangrove forestForest on rocky mountain Plantation forest Area (ha) 702,654 1,696,703 1,784,617 2,999,528 701,813 955,321 634,318 210,980 84,866 159,228 356,297 1,630,296 11,916,623 Source: Raae et al (2010) 2.3.2 Estimation offorestbiomassBiomasscarbonstock density in both AGB and BGB pools was estimated for each forest stratum AGB is estimated from the volume and density relationship offorest types using Eq AGB=VOB∙WD∙BEF Eq where, AGB is above-ground biomass (tdm ha-1) (tdm is tonnes of dry matter), VOB is inventoried stem volume over bark (m3 ha-1), BEF is biomass expansion factor (to convert over bark volume to total volume) and WD is basic wood density (kg m-3) 11 SNV REDD+ www.snvworld.org/redd Here, each variable is calculated as below: • VOB is averaged stem volume (m3 ha-1) taken from NFIMAP III, carried out forthe period 2000–2005 by theForest Planning and Inventory Institute (FIPI) VOB was estimated for each ofthe defined forest types • WD is basic wood density (kg m-3) If available, average wood density corresponding toforest types must be used If wood density values for corresponding forest types are not available an average wood density value can be used An average basic wood density for tropical trees which is 0.55 was used (Reyes et al 1992) • BEFs are calculated for defined forest types using stem volume and wood density data from forest inventory The BEFs were estimated by following the approach of Brown (1997) as Eq where, BEF is biomass expansion factor (to convert over bark volume to total volume), VOB is inventoried stem volume over bark (m3 ha-1) and WD is basic wood density (kg m-3) BGB offorest strata is estimated from ratio of BGB to AGB (R factor) using Eq BGB=AGB∙R Eq Default value for R used for estimation of BGB is 0.275 (FAO 2008) The approach described in Eq was not applicable for bamboo forest as a reliable aboveto-below ground relationship was not available for bamboo species Therefore an empirical biomassstock density estimatesfor above- and below-ground biomassstock density in Vietnam’s bamboo forests reported in Vu Tan Phuong et al (2007) was used 2.3.2 Estimation offorestbiomasscarbonstock density Forestbiomasscarbonstock density is calculated by multiplying the estimated forestbiomassstock density by a carbon fraction The default carbon fraction used for calculating forestbiomasscarbonstock is 0.50 (IPCC 2003) The above- and below-ground carbon are added together to obtain the total biomasscarbon estimate for each ofthe defined forest types Theforest type-specific biomasscarbonstock density is multiplied by the area ofthe respective forest types to obtain total carbonstockin 12 different forest types The total forestbiomasscarbonstockforVietnam is estimated by summing together thecarbonstockof different forest types Finally, the total biomasscarbonstock is divided by the total forest area to obtain an estimate of average biomasscarbonstock density 12 SNV REDD+ www.snvworld.org/redd Results and Discussion The estimated wood volume (Table 1), BEF (Table 2) and default values for wood density of 0.55 (Reyes et al 2010), default carbon fraction of 0.50 and a default AGB-to-BGB ratio (or root-to-shoot ratio) of 0.275 was used to estimate the AGB and BGB Carbonfor 12 forest types (Table ) Table Estimated biomasscarbonstock by forest types in 2005 Forest type 10 11 12 Carbonstock (tC ha-1) Area (ha) AGB BGB AGB+BGB Rich evergreen 143 broadleaved forest Medium evergreen 112 broadleaved forest Poor evergreen 76 broadleaved forest Regrowth evergreen 76 broadleaved forest Deciduous forest 90 Bamboo forest* 34 Mixed wood84 Bamboo forest Coniferous forest 50 Mixed broadleaved 105 and coniferous forest Mangrove forest 52 Forest on rocky 77 mountain Plantation forest 74 Total 39 183 702,654 31 143 1,696,703 Total (tC) 128,248,424 242,655,218 21 97 1,784,617 172,977,432 21 96 2,999,528 289,125,871 25 115 43 701,813 955,321 80,544,098 40,804,148 23 107 634,318 67,755,446 14 64 210,980 13,446,411 29 134 84,866 11,373,690 14 66 159,228 10,559,166 21 98 356,297 34,875,519 20 94 1,630,296 153,760,090 11,916,621 * For bamboo forest, an empirical estimate ofbiomasscarbon made by Vu Tan Phuong et al (2007) was used The 12 different forest types encompassing an area 11,916,621 ofthe Vietnamese forest estate was estimated to store a total of 1,260,811,507 tonnes ofbiomasscarbonThe average biomasscarbonstockof Vietnam’s forests in 2005 was about 105 tC ha-1 The lowest biomasscarbonstock density was found in bamboo forest (43 tC ha-1) and the rich evergreen broadleaved forest contained the highest carbonstock density (183 tC ha-1) The estimated carbonstock density values for each oftheforest types were integrated into the spatial forest type maps in GIS to derive thecarbon maps as used in Mant et al (2013) (Figure 2) Compared totheforestbiomasscarbon per hectare in Southeast Asian countries reported by FAO (FAO 2010), average forestbiomasscarbon density inVietnam is notably lower than that of Malaysia (157 tC ha-1) and Indonesia (138 tC ha-1) But the average forestbiomasscarbonstock per hectare in 13 SNV REDD+ www.snvworld.org/redd this calculation is about 1.4 times higher than the estimate of 72 tC ha-1 provided inthe FRA 2010 report forVietnam One potential reason for underestimation inthe FRA report is assumed growing stock volume of 78 m3 ha-1, a value from the year 2000, while theforest monitoring plot-based estimate of 2001-2005 showed an average growing stock volume of 100 m3 ha-1 Figure Tier 2-type forestbiomasscarbon map for Vietnam, 2001-2005 Source Mant et al 2013 14 SNV REDD+ www.snvworld.org/redd Comparison was also made with an alternative forestbiomasscarbon map (Figure 3): a global map offorestbiomasscarbon stocks in tropical regions (Saatchi et al 2011) which shows an estimated biomasscarbonstock density forVietnamof 257 tC ha-1, which is twice the amount estimated by this study The discrepancy inthe estimate may be attributed to a large degree of uncertainty i.e up to 54% inthe estimate of Saatchi et al (2011), potentially caused by use of coarse imagery at 1-km pixel resolution and use of a different approach for deriving below-ground biomasscarbon (LiDAR) Figure Tier 1-type forestbiomasscarbon map for Vietnam, 2000 (Source: Saatchi et al 2011) 15 SNV REDD+ www.snvworld.org/redd Previous SNV forestbiomasscarbon maps (Figure 4), using a Tier approach, showed thebiomasscarbonstock density was approximately 113 tC ha-1 (Holland and McNally 2009) Figure Average land cover carbon density by km pixel in Vietnam, 2000 Source: Holland and McNally (2009) 16 SNV REDD+ www.snvworld.org/redd While undertaking this study, only limited information was found for growing stock volume or biomasscarbonstock density for bamboo forests In future, as more reliable information is available for bamboo forests, more precise estimatesofbiomasscarbon may be made Theforestbiomasscarbonestimates presented here are only for live biomass and not include carbonin deadwood, litter and soil carbon pools Even though there exist opportunities to refine these estimates by incorporating data from excluded carbon pools and using finer resolution biomass data, the estimates, nevertheless, provide a robust preliminary visualisation ofthe distribution offorestbiomasscarbonstockinVietnam More up-to-date forestbiomasscarbon maps could be produced using the 2006-2010 NFIMAP IV forest cover and standing timber volume data unavailable to this study (Mant et al 2013) Forestbiomasscarbon maps can be further refined by using theforest management units level biomass inventory data as REDD+ activities progress inVietnaminthe future AGB estimations could be further refined by applying improvements in tree allometry at the global level (e.g Chave et al 2005), or better still, at the national level (e.g recently developed allometric equations for estimating forestcarbonforthe major forest ecoregions ofVietnam (Vu Tan Phuong et al 2012) 17 SNV REDD+ www.snvworld.org/redd References Bao Huy, Pham Tuan Anh, Vo Hung and Nguyen Thi Thanh Huong (2012) Report on estimation of CO2 sequestered in evergreen broad leaf forest in Central Highland ofVietnamfor reducing deforestation and forest degradation program Tay Nguyen University, Dak Lac Brown, S., A J R Gillespie and A E Lugo (1989) Biomass estimation methods for tropical forest with application toforest inventory data Forest Science 35: 881-902 Brown, S (1997) Estimating Biomass and Biomass Change of Tropical Forests: a Primer (FAO Forestry Paper - 134) FAO Forestry Paper 134, FAO, Rome Chave, J., Andalo, C., Brown, S., Cairns, M.A., Chambers, J.Q., Eamus, D., Folster, H., Fromard, F., Higuchi, N., Kira, T., Lescure, J.P., Nelson, B.W., Ogawa, H., Puig, H., Rie´ra, B and Yamakura, T (2005) Tree allometry and improved estimation ofcarbon stocks and balance in tropical forests Oecologia 145: 87–99 FAO (2008) Guidelines for Country Reporting totheForest Resource Assessment 2010 Food & Agriculture Organisation ofthe United Nations (FAO), Rome FAO (2010) Global forest resource assessment 2010 FAO forestry paper 163 Food & Agriculture Organisation ofthe United Nations (FAO), Rome Holland, T and McNally, R (2009) MappingPotentialfor REDD inVietnamForest cover, forest cover change, and forestcarbon density SNV - The Netherlands Development Organisation, Vietnam Programme, Hanoi IPCC (2003) Good practice guidance for land use, land use change and forestry Intergovernmental Panel on Climate Change (IPCC), Geneva IPCC (2006) IPCC Guidelines for National Green House Gases Inventory Volume “Agriculture, Forestry and Other Land Use” Intergovernmental Panel on Climate Change (IPCC), Geneva Mant, R., S.R Swan, Hoang Viet Anh, Vu Tan Phuong, Le Viet Thanh, Vo Thanh Son, M Bertzky, C Ravilious, J Thorley, K Trumper, L Miles and B.D Sharma (2013) MappingthePotentialforREDD+toDeliverBiodiversityConservationin Vietnam: a Preliminary Analysis SNV – The Netherlands Development Organisation, Ho Chi Minh City, and United Nations Environment Programme – World Conservation Monitoring Centre, Cambridge MONRE (2003) Vietnam’s first National Communication to United Nation Framework on Climate Change MONRE Hanoi MONRE (2010) Vietnam’s second National Communication to United Nation Framework on Climate Change MONRE Hanoi Raae, K., Christensen, P.C., Vu Tan Phuong and Vu Tien Dien (2010) Technical Report on Technical Assistance inthe Development ofthe National REDD Programme of Vietnam: Component of Collecting Information and Analyzing Trends ofForest Resources and ForestCarbonStockfor Establishment ofthe Interim Baseline Reference Scenarios Vietnam Administration of Forestry, Hanoi Reyes, G., Brown, S., Chapman, J and Lugo, A.E (1992) Wood densities of tropical tree species USDA Forest Service, General Technical Report SO-88, Southern Forest Experiment Station, New Orleans, Louisiana, USA 18 SNV REDD+ www.snvworld.org/redd Ruesch, A and Gibbs, H.K (2008) New IPCC Tier-1 Global BiomassCarbon Map Forthe Year 2000 Available online from theCarbon Dioxide Information Analysis Center [http://cdiac ornl.gov] Saatchi, S., Harris, N., Brown, S., Lefsky, M., Mitchard, E., Salas, W., Zutta, B., Buermann, W., Lewis,S., Hagen, S., Petrova, S., White, L., Silman, M and More, A (2011), Benchmark map offorestcarbon stocks in tropical regions across three continents. Proc Natl Acad Sci U S A., 108: 9899–9904 Scharlemann, J.P.W, Hiederer, R., Kapos, V In prep Global map of terrestrial soil organic carbon stocks UNEP-WCMC & EU-JRC, Cambridge, UK Vo Dai Hai, Dang Thinh Trieu, Nguyen Van Bich and Pham Vien Dien (2010) Carbon sequestration of some plantations inVietnam Agriculture Publishing House, Hanoi Vo Dai Hai, Dang Thinh Trieu, Vu Tan Phuong and Nguyen Van Bich (2013). Report on biomass and carbonstockof evergreen, semi-evergreen and deciduous forests in Central Highland ofVietnam Vietnamese Academy of Forest Sciences, Hanoi Vu Tan Phuong, Nguyen Tien Hung, Tran Thi Thu Ha and Nguyen Viet Xuan (2007) Valuation of economic and environmental values of major forests inthe North ofVietnamForest Science Institute of Vietnam, Hanoi Vu Tan Phuong, Pham Xuan Phuong, Vu Tri Dung, Hoang Lien Son, Tran Thi Thu Ha, Nguyen Viet Xuan, Nguyen Tien Hung, Nguyen Thi Hai and Pham Thi Huong Lan (2010) Forest valuation inVietnam Science and Techniques Publishing House, Hanoi Vu Tan Phuong, Inoguchi, A., Birigazzi, L., Henry, M and Sola, G (2012) Tree Allometric Equation Development for Estimation ofForest Above-Ground Biomassin Viet Nam: Part A -Introduction and Background ofthe Study The United Nations Collaborative Programme on Reducing Emissions from Deforestation and Forest Degradation in Developing Countries (UN-REDD) Viet Nam National Program, Hanoi 19 SNV REDD+ www.snvworld.org/redd SNV Netherlands Development Organisation REDD+ Programme th Floor, Thien Son Office Building, Nguyen Gia Thieu Street, District 3, Ho Chi Minh City, Vietnam Tel./Fax: 84 3930 0668 Email: sswan@snvworld.org This publication was printed with FSC certified paper and vegetable-based ink 20 SNV REDD+ www.snvworld.org/redd ... types to obtain total carbon stock in 12 different forest types The total forest biomass carbon stock for Vietnam is estimated by summing together the carbon stock of different forest types Finally,... added together to obtain the total biomass carbon estimate for each of the defined forest types The forest type-specific biomass carbon stock density is multiplied by the area of the respective forest. .. (2013) Generating Forest Biomass Carbon Stock Estimates for Mapping the Potential of REDD+ to deliver biodiversity conservation in Vietnam SNV – The Netherlands Development Organisation, Ho Chi Minh