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Table 2.2.7.2: Information on Source Category 2H2 'Food and Beverages Industry' (Alcoholic Beverages) - NMVOC
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Statistical data regarding bread making and other food in the RM within 1990-2019 time periods (see Table 4-186 from the National Inventory Report: 1990-2019. Greenhouse Gas Sources and Sinks in the Republic of Moldova) are available in the Statistical Yearbooks of the Republic of Moldova for 1994 (pages 289-290), 1999 (pages 304-306), 2003 (pages 393-394), 2006 (pages 309-310), 2010 (pages 301-303), 2014 (pages 299-301); Statistical Reports PRODMOLD-A Total production, as a natural expression, in the Republic of Moldova, by product type, for 2006-2019"; as well as in the Statistical Yearbooks of the ATULBO for 1998 (page 177), 2000 (page 100), 2002 (page 104), 2006 (page 94), 2007 (page 90), 2009 (page 93), 2011 (page 95), 2014 (page 89), 2017 (page 102), 2020 (page 103).
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See the 95% confidence interval in the table above (in the brackets, lower-upper).
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Table 2.3.1.1: Information on Source Category 3A 'Enteric Fermentation' (Dairy Cattle, Non-Dairy Cattle, Sheep, Goat) - CH₂
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Relevant information on categories comprised within the inventory, including description of each category allocated to Sector 3 'Agriculture' is provided below.
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Chapter 2: Methods and Data Documentation
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Table 2.3.1.2: Information on Source Category 3A 'Enteric Fermentation' (Swine, Horses, Asses and Mules, Rabbits) - CH,
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Table 2.3.2.1: Information on Source Category 3B "Manure Management' (Dairy Cattle, Non-Dairy Cattle, Swine) - CH₂
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Tables 2.3.2.1-2.3.2.4 below comprise relevant information on source categories comprised within the inventory, including description of each source by gas allocated to category 3B 'Manure Management'.
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Methane is produced in herbivores as a by-product of enteric fermentation, a digestive process by which carbohydrates are broken down by microorganisms into simple molecules for absorpion into the bloodstream. The amount of methane that is released depends on the type of digestive tract, age, and weight of the animal, and the quality and quantity of the feed consumed. Following definition in the 2006 IPCC GL, the mature swine include sows in gestation, sows which have farrowed and are nursing young and boars that are used for breeding purposes, while the growing swine include nursery, finishing, gits that will be used for breeding purposes and growing boars that will be used for breeding purposes. Methodology: Tier 1
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Total CH, enteric-total CH, emissions from Enteric Fermentation, ktCH,/yr. Ei-is the emissions for the i livestock categories and sub-categories EF-emission factor for the defined livestock population, kg CH,headlyr. N-the number of head of livestock species/category T in the country. T-species/category of livestock.
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Due to the importance of this source the Tier 2 methodology has been used
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Animal population (thousand heads)-data are provided by the National Bureau of Statistics through Statistical Annual Report No. 24-agr Animal Breeding Sector". The Number of Livestock and Poultry in all Households Categories as of 1st of January (Annual Reports for 1990-2019) and the Basic Indicators of Animal Breeding Sector Development in all Households Categories in the Republic of Moldova (Annual Reports for 1990-2019). Statistical Yearbooks of Administrative-Territorial Units on Left Bank of Dniester River (ATULBD) for 1998 (page 224), 2002 (page 118), 2006 (page 109), 2010 (page 110), 2014 (page 104), 2017 (page 117), 2020 (page 118).
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IPCC Default EF for developed countries from 2006 IPCC GL, page 10.28, Table 10.10: for Swine-1.5 kg CH /headlyr, Horses-18 kg CH /head/lyr, Mules and Asses-10 kg CH/headly Coun try Specific (Russian Federation) EF for Rabbits-0.59 kg CH headlyr (National Inventory Report of Russian Federation for 1990-2016 period, Chapter 5, Table 5.6, Page 188).
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Type and source of EF and OF
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Uncertainty of AD and source Uncertainty of EF and source Potential Improvements
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2.3.2. Category 3B 'Manure Management'
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± 30% for Tier 1, 2006 IPCC GL, page 10.33, chapter 10.3.4 'Uncertainty assessment
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No potential improvements are planned to be implemented in the next inventory cycle for these animal categories under 3A Enteric Fermentation category.
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Table 2.3.2.4: Information on Source Category 3B "Manure Management (All Animal Types) - Indirect Emissions - N₂O
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2.3.3. Category 3D 'Agricultural Soils'
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Tables 2.3.3.1-2.3.3.2 below comprise relevant information on source categories comprised within the inventory, including description of each source by gas allocated to category 3D 'Agricultural Soils'.
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Table 2.3.3.1: Information on Source Category 3D 'Agricultural Soils' - Direct Soil Emissions - N₂O
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Table 2.3.3.2: Information on Source Category 3D 'Agricultural Soils' - Indirect Soil Emissions - N₂O
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Table 2.3.4.1: Information on Source Category 3H 'Urea Application' - CO₂
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Table 2.3.4.1 below comprises relevant information on source allocated to category 3H 'Urea Application'.
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In principle, for both stages, the methodologies described in the 2006 IPCC Guidelines are applicable under the conditions of the RM. At the same time, country specific emission/removals factors were used, regarding annual biomass increment, the share of carbon in biomass etc., as well as sectorial activity data (forest land areas by species/categories of species, afforestation, wood mass harvesting etc.).
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Data on the areas of forest land in the Republic of Moldova, in the time series from 1990 through 2019, available into a series of nationalisectorial reports on forestry resources (National Report on Forestry Resources of the Republic of Moldova (2011); General Land Cadasters for 1990-2019 periods; OSC Report on updating basic indicators for forest and other types of forest vegetation in the Republic of Moldova (2016); Land Use and Land Use-Change Matrix for 1970-2019 periods, beginning with 2013, information on the distribution of predominant forest species were taken from Forestry Research and Management Institute (ICAS) database.
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For to estimate annual biomass increments and losses, country specific emission factors were calculated/developed, were used production tables, data on actual productivity of stands, according to the forest planning records (Osadcev.G. Ivankov P.T., Sergovskii P.S. et al. (1955), Guidebook on Woodworking (for Forest Farms Consumer Goods Manufacturing Workshops). Moscow, 1955 (in Russian); Giurgiu V., Decei I., Armasescu S. Biometriy of Trees and Stands in Romania, 1972; Shvidenko A.Z., Savich J.N. (1987), Reference Materials for Evaluation of Forests in Ukraine and Moldova. Kiev, Urozhai, 1987 (in Russian); Kapp G., Velsen-Zerweck M., Horst A., Hom L., Galupa D. Talmaci I. et al.: The Baseline Study for the Soil Conservation Project in Moldova, 2003; Vanin S. I. (1949), Wood Science, Moscow (in Russian).
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4A Forest Land
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Table 2.4.3.1: Information on Category 4C 'Grassland' - CO₂
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Tables 2.4.3.1-2.4.3.2 below comprise relevant information on source and/or sink categories comprised within the inventory, including description of each source and/or sink by gas allocated to category 4C 'Grassland'.
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4C2 Land Converted to Grassland-CO,
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Table 2.4.4.1: Information on Category 4D 'Wetlands'- CO₂
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2.4.4. Category 4D 'Wetlands'
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Table 2.4.4.2: Information on Category 4D 'Wetlands' - CO₂
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402 Land Converted to Wetlands - CO,
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Category 4D2 Land Converted to Wellands" include different land types which were previously covered by a certain amount of biomass and other land without initial vegetation converted to wetlands. The main land categories converted to wetlands are croplands and grasslands.
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Category of biomass loss was establish due to conversion of different land types which were previously covered by a certain amount of biomass (forest vegetation, grassland, perennial plantations etc.). At the same time, were estimated biomass increments due to conversion of different land types without inisal vegetation (other land).
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Methodology: Tier 2. The calculation process of CO, removalslemissions is based on the annual increments in carbon stocks due to current biomass growth, and uses Equation 2.15 from the 2006 IPCC Guidelines (Volume 4, Chapter 2, Page 220):
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AC-annual decrease in biomass carbon stocks on land converted to wetlands, due to grassbiomass harvest, disturbances 1 Clyr.
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