Capacity Development Workshop “Understanding National Inventories for LULUCF Sector: The experience of Annex-I Countries” 05-07 Nov., Berlin, Germany National.

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Presentation transcript:

Capacity Development Workshop “Understanding National Inventories for LULUCF Sector: The experience of Annex-I Countries” Nov., Berlin, Germany National System and National Inventory Report of Germany for LULUCF Karsten Dunger Institute for forest ecology and forest inventory

Outline -german reporting commitments -organisation of responsibilities -actual methodology of reporting -areas and activities -emission factors, emissions and stock changes -actual issues -planned improvements

German reporting commitments  annual reporting under UNFCCC –years from 1990 until actual year, anually –all Land use classes incl. transition classes –all relevant gases –all relevant pools  reporting and accounting under KP 3.3 and 3.4 –afforestation, (reforestation), deforestation –forest management –

Organisation of responsibilities (historical) FAL BMUBMELV UBA BFH, Inst. VII Agriculture + LULUCF Forest parts of LULUCF 3.4 KP Agriculture LULUC 3.3 KP Reviews: institutional arrangements needed

Institutional Arrangements  starting point: –benefits by accounting for „forest sink“ expected –additional needs by Kyoto reporting identified  Federal ministry of Food, Agriculture and Consumer Protection responsible for: –agriculture –LULUCF (incl. Kyoto ARD and FM)  in place since 2007  connected with financial ressources for reporting (capacity building!)

Organisation of responsibilities (current) UBA: „national system“ for emission reporting (NASE) vTI-AK: calculations and archiving Destatis: activity data KTBL: data, knowledge, emission factors vTI-AK, WG emission inventories: coordination, QC/QK agriculture vTI-AK: calculations, archiving LULUC BGR/AdV ATKIS… vTI-WOI: calculations, archiving, projections forestry vTI-WFW, vTI-HTB, vTI-OEF: Uncertainties, harvested wood products, add. studies vTI-LR, KTBL: projections, migitation costs

Separate reporting system on LULUC and F  historical reasons for separation to forests reporting  LULUC: –including all LUC except forests –based on Land use statistics and maps –most important pool: soils  F: –including forests and tansition classes from and to forests –based on statistical (plot-based) forest inventories  continuous development of methodology  process of integration in developement

Prequisites for reporting of activities  activites in LUCUCF are mostly areas  needed: definitions of land use classes –references: IPCC GPG Marakesh Accords (forests) –adaptions for national circumstances –analysis of differences between national definitions and references

Example: forest definition German NFI Reference = Marrakesh Accords (FCCC/CP/2001/13/Add.1, p.58.) Forest is any ground area covered by forest vegetation with an area more than 0,1 ha and a width more than 10 m. Watercourses up to 5 m wide do not break the continuity of a forest area. Succession areas (swamp, moorland, pastures) are considered to be forests, if they have reached an average age of five years and if at least 50% of the area is covered by forest vegetation. Forests also include openings (areas of wooded ground temporarily without forest cover) and non-wooded ground (forest tracks, rides and firebreaks over 5 m, wide, landings, tree nurseries, seed and plant nurseries, wood-pastures and fields for game, the areas of yards and buildings used for forestry purposes, recreational facilities linked to the forest and rocks, boulders, gravel and water located in the forest). Cultivation of Christmas trees and parkland attached to urban areas are not forests. minimum area of land of hectares -with tree crown cover (or equivalent stocking level) of more than per cent -with trees with the potential to reach a minimum height of 2-5 metres at maturity in situ. A forest may consist either of -closed forest formations where trees of various storeys and undergrowth cover a high proportion of the ground -or open forest. Young natural stands and all plantations which have yet to reach -a crown density of per cent or -tree height of 2-5 metres are included under forest, -as are areas normally forming part of the forest area which are o temporarily unstocked o as a result of human intervention such as  harvesting or  natural causes o but which are expected to revert to forest; land use vs. land cover

Impact of forest definition parameters Definition of Forest: tree crown cover: at least 10 % (≠ NFI) minimum area: 0.1 ha (= NFI) potential minimum height of trees: 5 meters (≠ NFI) Differences to NFI definition (example for sensitivity analysis): min. height of 5 m Only 3 species in the German NFI species list, which (under some circumstances) not reach a potential height of 5m Alnus viridis (green alder) Pinus mugo (dwarf mountain pine) Ilex aquifolium (Holly) area is lower than 0,05 % of the forest area (within forest area error estimation).

Methodologies for areas identification

Area identification in LULUC (historical)  official German statistics –„Flächenerhebung“ (Survey of Area by Actual Use) – „Agrarstrukturerhebung“ „Bodennutzungshaupterhebung“ (Main Statistics of Land Use) „Ernteerhebung“ (Main Statistics of Harvests) „Wein- und Obstbauerhebung“ (Main Statistics of Viniculture and Fruitproduction)

Area identification in LULUC (historical) Excerpt from combined Database derived from official German statistics Survey of Area by Actual Use Main Statistics of Land Use Survey of Area by Actual Use & Main Statistics of Land Use

District borders Soil mapLand use Data for german LULUC-inventory (new)

crop forl gras othl sett wetl Forestland crop forl gras othl sett wetl Settlements crop forl gras sett wetl Other land crop forl gras othl sett wetl Grassland crop forl gras othl sett wetl Cropland crop forl gras sett Wetlands Legend Example: Land use changes by map intersection

Application of Emission factors (LULUC) Δ C ms = C f – C i = a * ef * C w – a * C w Δ C ms :Change in soil carbon stocks due to land use change in metric tons / district * report period C f :Final soil carbon stocks in metric tons C i :Initial soil carbon stocks in metric tons a:area of land use change in ha ef:Emission factor (free of dimension) C w. :Weighted (by district and land use) carbon stocks in metric tons/ha Mineral soils: Organic soils: Δ C os = a * ef org. Δ C os :Change in soil carbon stocks due to land use change on organic soils in metric tons / district * report period a:Area of land use change in ha ef org. :Emission factor for organic soils under specific use in metric tons/ha*a

Intersection of soil maps with LUC from CORINE/ATKIS BÜK 1000 LBA 3 LBA 4 LBA 5 LBA 6 LBA 7 LBA 11 LBA 17LBA 22 LBA 28 LBA 31 LBA 33 LBA 70 LBA 7 District border

Application of Emission factors (LULUC) Wetlands LBA 3 LBA 4 LBA 5 LBA 6 LBA 7 LBA 11 LBA 17 LBA 22 LBA 28 LBA 31 LBA 33 LBA 70 Other Land LBA 3 LBA 4 LBA 5 LBA 6 LBA 7 LBA 11 LBA 17 LBA 22 LBA 28 LBA 31 LBA 33 LBA 70 Grasland LBA 3 LBA 4 LBA 5 LBA 6 LBA 7 LBA 11 LBA 17 LBA 22 LBA 28 LBA 31 LBA 33 LBA 70 Forestland LBA 3 LBA 4 LBA 5 LBA 6 LBA 7 LBA 11 LBA 17 LBA 22 LBA 28 LBA 33 LBA 70 Cropland LBA 3 LBA 4 LBA 5 LBA 6 LBA 7 LBA 11 LBA 17 LBA 22 LBA 28 LBA 31 LBA 33 LBA 70 Settlements

Specific emission trends for transitions Time after land use change in years Carbon stock losses in % y=0,3778+(30,0488/x) r 2 =0,936; n=18 Relationship between loss from initial soil carbon content and duration of land use change (grassland, perennial crops, fallow or forest to cropland)

Data sources for forests (incl. area): National Forest Inventory: areas biomass (aboveground and belowground) deadwood National Forest Soil Inventory: (areas) litter soil organic matter NFI sub-sample 2008 (Biomass, Deadwood, esp. for GHG) Dataset on Forest Resources (DFR, new states, until 1993) Additional data (forest fire statistics, remote sensing data)

Data sources details (NFI) : National Forest Inventory: nationwide terrestrial multipurpose inventory regular cluster grid with permanent sample plots sample (cluster) distribution nationwide 4 km x 4 km (intensified in some areas) each cluster a quadrangle with sides of 150 m (4 plots) on plots angle-count sampling and sample circles ca. 50,000 forest plots inventory cycles: 1987 (Old federal states) 2002,2012 (whole country) additional sub-sample 2008 (ca. 2,500 forest plots, whole country)

Data sources details (NFSI): National Forest Soil Inventory: nationwide terrestrial inventory regular grid with permanent sample plots sample distribution nationwide 8 km x 8 km on plots various measurements for evaluation of litter-, soil-, and (stand) parameters ca. 2,000 forest plots inventory cycles:

Reporting on Emissions from forests: concept, data sources and time schedule ABNFI1DFRNFI 2(SS08)NFI3 BBNFI1DFRNFI 2(SS08)NFI3 DWNFI 2(SS08)NFI3 LI……NFSI1…NFSI2 SOM……NFSI1…NFSI2 Year ExtrapolationInterpolation Extrapolation/Recalc.+Interpolation Interpolation Extrapolation/Recalc.+Interpolation InterpolationExtrapolation Interpolation Rev. Extrapol.

Area estimation from NFI  „forest / non forest“ as plot parameter  repeated inventories allow change detection  parameter „land use bevor/after forest use“ allows division by transition classes

Emissions from forests (and related LUC)  data actually only for living biomass available  data on soils, litter and deadwood expected in near future  (carbon) stock data collected together with Land use information in statistical (plot-based) forest inventories –repeated Inventories cause need for interpolation and extrapolation (no annual data)  CO2-Emissions from biomass burning integrated in stock change (study on other gases actually under preparation)

Emission calculation method (forest biomass)  “stock-change-method”  Expansion-/Conversions factors on tree level

Example: forest increment and removals

Example: Biomass stock change in forests

Actual tasks  Forestry: –Inventory subsample 2008 (regarding KP commitments) –Studies: Emissions from forest fires Biomass functions / uncertainties Improvement of Documentation, QA/QC  Other LULUC –Project on emissions from organic soils 2/3 of emissions in LULUC mostly on grassland and cropland High uncertainties

Excurse: Projection models Vorrat \ Altersklassen

Projections for political decision support  Example: FM „sink“ under different accounting scenarios

Thank you for attention.