Outline. Poplar culture for speedy Carbon Sequestration in India: A case study from terai region of Uttarakhand. Forest sector and the CDM

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culture for speedy Carbon Sequestration in India: A case study from terai region of Uttarakhand 31 st Oct 2012 24 th session of IPC, Dehradun Dr. Mohit Gera, IFS Additional Professor, IGNFA P.O. New Forest, Dehradun - 248006 Outline Introduction and CDM requirements Study site and methodology Carbon sequestration potential & costeffectiveness Challenges before A&R projects Agroforestry in REDD-plus E mail: mohitgera87@gmail.com Carbon Sequestration in Forests Forest sector and the CDM CDM forestry projects are limited to Afforestation and Reforestation (A&R). Afforestation Planting with trees, the areas that have not been a forest for the last 50 years. Afforestation Reforestation Important elements of Carbon Sequestration: Reforestation Planting with trees the areas, that have not been a forest since 31 st Dec 1989. Fast growth Rotation period Kinds of wood products Contd. 1

Forest sector and the CDM A/R CDM project activities may include: Afforestation of wastelands Reforestation of degraded forests Agroforestry / Farm forestry contd Plantation models in s CERs (1CER = 1 tco2) from forest sector are nonpermanent (two kinds tcer & lcer) Crediting period 20x1, 20x2, 20x3, 30 years (fixed) Approved methodologies - 12 large scale & 7 small scale Registered projects in forest sector - 40 (7 from India) Block plantation on farm lands (Agri-silviculture) Plantation models in s contd Plantation models in s contd Bund plantation Inter-cropping on farm lands (Agrisilvipastoral) 2

Whether meets CDM requirement on Forest definition? Indian definition of Forest & agro/farm forestry bund plantation - small farm (Spacing 2 m, crown dia. 5.8 m*) 0.05 ha Crown cover 45.47 % 20 m The definition accepted by India is: Minimum area 0.05 ha Minimum tree ht. at maturity 2 m Crown cover 15% 25 m *Source: Dr. R.C. Dhiman bund plantation - large farm (Spacing 2 m, crown dia. 5.8 m) 0.375 ha 75m Crown cover - 18.44 % Gera Mohit, 2007 50m bund plantation: Farm size Vs Crown cover (Crown dia. at 6 year 5.8 m) Farm size (ha) Spacing (m) Crown cover (%) 0.05 2 45.47 0.10 2 34.34 0.13 2 30.14 0.30 2 20.15 0.375 2 18.43 0.45 2 16.65 0.50 2 15.77 (Source: Gera, Mohit, 2007) 3

Carbon Pools eligible under A&R CDM Projects AGB & BGB - One year old block plantation of, Vikrampur, Uttarakhand A sample of woody litter Collection of a soil sample 4

Case study on estimation of Carbon Sequestration potential in Harvested wood products not eligible for first commitment period (Photosource: Presentation from Dr. D.R. Ramesh Singh) Study site Location of selected villages District Nainital Block - Ramnagar Name of the village Gram Panchayat Latitude Longitude Altitude (m) Kanchanpur Choi Choi 29 21 46 79 08 52 369 Nandpur Khempur 29 20 13 79 11 30 314 Kyaribandobasti Kyari 29 21 59 79 11 30 361 Source : GPS readings Uttarakhand (Study period: 2005-06) 5

Brief silvicultural details of selected plantation Plantation Spacing intervention (m) Trees/ ha Survi val (%) Rotat ion (yrs) Planting material Harvest and planting ETP of Uprooted and G3, G48 planted afresh on 5 4 500 100* 6 & other completion of every block clones rotation during the CDM project period. ETP of Uprooted and G3, G48 planted afresh on 2m 384** 100* 6 & other completion of every bund clones rotation during the CDM project period. * All failed plants assumed to be replanted ** For bund plantation, a farm size of 0.25 ha was assumed. Biomass (t/ha) plantation/harvest cycle 2008 2014 2020 2026 2032 2038 Year Methodology - Biomass Selected representative plantation for measurements of AGB, Woody litter and Soil Organic Carbon (SOC). Randomly laid out 3 quadrats (25x20 m) in 3 different age classes for biomass estimation. Measured girth, height of all trees within a quadrat. AGB calculated using standard volume equation. AGB = stem volume x BEF x wood density BGB was calculated by AGB x 0.27. Carbon calculated by multiplying biomass value by 0.45. Woody litter samples (3No.) were also taken randomly from with in the selected plots on 1x1m area. Methodology - SOC 3 soil samples were taken from with in the quadrats laid out for biomass estimation. Dug out a pit of 45 cm and collected the entire soil and made a representative sample for analysis from each quadrat/plantation. Analyzed the sample for SOC. Estimated the SOC in t/ha using standard methods. 6

Plantation intervention Key input data on carbon pools Mean annual increment (t/ha/yr) Baseline AGB (t/ha) Baseline soil carbon (t/ha) Soil carbon uptake (t/ha/yr) Woody litter (t/ha) block 19.35 0 29.60 0.93 (6)* 0.26 (2.94)** bund 14.86 0 33.75 0.56 (6)* 0.21 (2.94)** * Accumulation period in years ** Decomposition period in years Key input data on wood products Plantation Wood product as % of MAI intervention Chip logs Veneer logs Fuel wood block 20 (30)* 60 (30)* 18 (0)* bund 20 (30)* 60 (30)* 18 (0)* * Product life in years PRO - COMAP MODEL Comprehensive Mitigation Assessment Process (COMAP) for project activities (spread sheet model). The model is used to analyze potential and cost effectiveness of C- sequestration projects. It takes into account 5 C-pools Above Ground Biomass Below Ground Biomass Woody litter Soil carbon Harvested Wood Products PRO - COMAP contd A broad framework Identify and screen potential options Assess current and future forest and agriculture land use patterns Assess current and future wood product demand Determine land area and wood production scenarios by option (Source: Sathaye et al., 1995) Estimate net carbon sequestratio n per ha by options (vegetation, soils, understory, litter and wood product) Estimate unit costs and benefits per ha by option Develop scenarios of total cost and carbon sequestrati on by option Discuss barriers to and policies needed for implementation Assess macroeconomic effects of scenarios (jobs, capital, exports, GDP, etc.) Evaluate costeffectiveness indicators for ranking options 7

Annual incremental carbon, total carbon sequestered, and likely annual carbon benefits Plantation intervention Initial cost^ (Rs/ha) Incremental carbon Annual (tc/ha/yr) Annual sequestration (tco 2 /ha/yr)* block 13,700 39.76 (72.17) 1.33 (2.41) 4.86 (8.83) 7,450 31.48 1.05 3.85 bund (53.86) (1.80) (6.61) ^ Includes all costs incurred for establishment of plantations. * 1tC = 3.67tCO 2 ** 1$ = Rs. 55/- (Figures in parenthesis refer to values for with wood products case.) Benefit @$5/t CO 2 (Rs/ha/yr)** Per unitarea (tc/ha) 1337/- (2428/-) 1060/- (1817/-) Total C density (tc) 60 50 40 30 20 10 block plantation Changes in carbon pools per ha 0 2008 2018 2028 2038 2048 2058 2068 2078 2088 2098 Vegetation stock Below ground biomass Woody litter Soil Stock Wood products Internal rates of returns under different carbon price scenarios Internal Rate of Return (IRR %) Plantation Without carbon with carbon benefits intervention benefits Scenario I Scenario II Scenario III block 61.20 69.5 (69.8)* 70.9 (71.5) 74.3 (75.4) bund 52.20 58.3 (58.6) 59.6 (60.2) 62.7 (63.9) Scenario I - Carbon price $5, 1US $ = Rs. 55/- Scenario II - Carbon price $5 + 2% annual increase (backstop price $50/tCO 2 ) Scenario III - Carbon price $5 + 5% annual increase (backstop price $50/tCO 2 ) (* Figures in parentheses show values for the with wood products case.) Carbon sequestration potential of poplar as reported by different researchers S. No. Nature of plantation 1. Block Bund C- sequestration potential tc/ha/yr 2.54 (4.42)* 1.42 (2.46) Reference Gera et al., 2006 2. Block 1.98 (3.33) Hooda et al., 2007 3. Block 1.33 (2.41) Gera et al., 2011a 4. Block Bund Average Block Bund 2.20 (3.83) 1.23 (2.13) 2.01 (3.50) 1.33 (2.30) Gera et al., 2011b * Figures in parenthesis are for with wood products 8

Annual carbon sequestration by Populus deltoides at national level Total area 312,000 ha Ratio of block and bund plantation 60% : 40% Carbon sequestration (without wood products) 542,240 tc/ha Carbon sequestration (with wood products) 942,240 tc/ha Challenges before forestry CDM projects Competing land uses Complex modalities & procedures under CDM Higher transaction costs Non-permanence (low price of tcer or lcer) Limited demand for CERs from forest sector Addressing additionality may be difficult. Non-inclusion of HWP pool. Agroforestry in REDD-plus Indian s definition of 'forest' favour agroforestry Plays key role in preventing deforestation and forest degradation Enormous scope for increasing removals Need for enabling legal and policy environment for Tree rights and ownership Security of investment Market reforms Thanks for your kind attention 9