Denmark's National Inventory Report 2005 - Submitted under the ...

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Table 1.4 Uncertainty rates for each emission source ÃÃ Ã 42 ÃÃ Ã Ã Gg CO2 eq Gg CO2 eq % % Stationary Combustion, Coal CO2 24077 22609 1 5 Stationary Combustion, BKB CO2 11 0 3 5 Stationary Combustion, Coke CO2 138 108 3 5 Stationary Combustion, Petroleum coke CO2 410 779 3 5 Stationary Combustion, Plastic waste CO2 349 649 5 5 Stationary Combustion, Residual oil CO2 2505 2120 2 2 Stationary Combustion, Gas oil CO2 4564 2918 4 5 Stationary Combustion, Kerosene CO2 366 24 4 5 Stationary Combustion, Orimulsion CO2 0 154 1 2 Stationary Combustion, Natural gas CO2 4330 11152 3 1 Stationary Combustion, LPG CO2 164 74 4 5 Stationary Combustion, Refinery gas CO2 806 942 3 5 Stationary combustion plants, gas engines CH4 6 391 2,2 40 Stationary combustion plants, other CH4 115 130 2,2 100 Stationary combustion plants N2O 398 440 2,2 1000 Transport, Road transport CO2 9351 11864 2 5 Transport, Military CO2 119 92 2 5 Transport, Railways CO2 297 218 2 5 Transport, Navigation (small boats) CO2 67 140 56 5 Transport, Navigation (large vessels) CO2 484 426 2 5 Transport, Fisheries CO2 771 632 2 5 Transport, Agriculture CO2 1318 1219 26 5 Transport, Forestry CO2 5 4 26 5 Transport, Industry (mobile) CO2 778 742 40 5 Transport, Residential CO2 87 82 51 5 Transport, Civil aviation CO2 243 138 10 5 Transport, Road transport CH4 55 62 2 40 Transport, Military CH4 0 0 2 100 Transport, Railways CH4 0 0 2 100 Transport, Navigation (small boats) CH4 1 2 56 100 Transport, Navigation (large vessels) CH4 0 0 2 100 Transport, Fisheries CH4 0 0 2 100 Transport, Agriculture CH4 2 2 26 100 Transport, Forestry CH4 0 0 26 100 Transport, Industry (mobile) CH4 3 3 40 100 Transport, Residential CH4 3 3 51 100 Transport, Civil aviation CH4 0 0 10 100 Transport, Road transport N2O 131 416 2 50 Transport, Military N2O 1 1 2 1000 Transport, Railways N2O 3 2 2 1000 Transport, Navigation (small boats) N2O 1 1 56 1000 Transport, Navigation (large vessels) N2O 9 8 2 1000 Transport, Fisheries N2O 15 12 2 1000 Transport, Agriculture N2O 17 16 26 1000 Transport, Forestry N2O 0 0 26 1000 Transport, Industry (mobile) N2O 10 10 40 1000 Transport, Residential N2O 1 1 51 1000 Transport, Civil aviation N2O 3 3 10 1000 Energy, fugitive emissions, oil and natural gas CO2 263 550 15 5 Energy, fugitive emissions, solid fuels CH4 72 93 2 200 Energy, fugitive emissions, oil and natural gas CH4 38 84 15 50 Energy, fugitive emissions, oil and natural gas N2O 1 3 15 50 6 A. Solid Waste Disposal on Land CH4 1334 1153 10 40,8 6 B. Wastewater Handling CH4 200 244 20 35 6 B. Wastewater Handling N2O 88 61 10 30 2A1 Cement production CO2 882 1370 1 2 2A2 Lime production CO2 138 102 5 5 2A7 Glass and Glass wool CO2 17 13 5 2 2B5 Catalysts/Fertilizers, Pesticides and Sulphuric acid CO2 2 3 5 5 2C1 Iron and steel production CO2 28 0 5 5 2B2 Nitric acid production N2O 1043 895 2 25 2F Consumption of HFC HFC 218 695 10 50 2F Consumption of PFC PFC 1 19 10 50 2F Consumption of SF6 SF6 107 31 10 50 4A Enteric Fermentation CH4 3110 2734 10 8 4B Manure Management CH4 743 972 10 100 4B Manure Management N2O 685 560 10 100 4D Agricultural Soils N2O 8308 5632 7,6 19,6
1.8 General assessment of the completeness The Danish greenhouse gas emission inventory due 15 April 2005 includes all sources identified by the Revised IPPC Guidelines except the following: • Industrial processes: CO 2 emission from use of lime and limestone for flue gas cleaning, sugar production etc., and production of expanded clay will be included in the next submission. These sources are expected to contribute with about 0.2% of the total GHG emissions in 2003. • Agriculture: The methane conversion factor in relation to the enteric fermentation for poultry and fur farming is not estimated. There is no default value recommended in IPCC (Table A-4 in GPG). However, this emission is seen as non-significant compared to the total emission from enteric fermentation. 1.9 References Danish Environmental Protection Agency (2004a): Affaldsstatik 2002 - revideret udgave. Orientering fra Miljøstyrelsen Nr 4. Danish Environmental Protection Agency (2004b): Ozone depleting substances and the greenhouse gases HFCs, PFCs and SF6. Danish consumption and emissions 2002. Tomas Sander Poulsen, PlanMiljø. Environmental Project No 890 2004. http://www.mst.dk/udgiv/publications/2004/87- 7614-123-3/pdf/87-7614-124-1.pdf Danish Environmental Protection Agency (2005): Affaldsstatistik 2002 – revideret udgave. Orientering fra Miljøstyrelsen Nr. 4 2004. http://www.mst.dk/udgiv/publikationer/2004/87-7614-172- 1/pdf/87-7614-174-8.pdf Hutchings, N.J., Sommer, S.G., Andersen, J.M., Asman, W.A.H., 2001. A detail ammonia emission inventory for Denmark. Atmospheric Environment 35 (2001) 1959-1968 Illerup, J. B., Lyck, E., Winther, M., and Rasmussen, E. (2000): Denmark’s National Inventory Report – Submitted under the United Nations Framework Convention on Climate Change. Samfund og Miljø – Emission Inventories. Research Notes from National Environmental Research Institute, Denmark no. 127, 326 pp. http://www.dmu.dk/1_viden/2_Publikationer/3_arbrapporter/rapporter/ar127.pdf Illerup, J.B., Lyck, E., Nielsen, M., Winther, M., Mikkelsen, M.H., Hoffmann, L., Sørensen, P.B., Vesterdal, L. & Fauser, P. 2004. Denmark's National Inventory Report - Submitted under the United Nations Framework Convention on Climate Change, 1990-2002 - Emission Inventories. National Environmental Research Institute. - Research Notes from NERI 196: 1027 pp. http://www2.dmu.dk/1_viden/2_Publikationer/3_arbrapporter/rapporter/AR196.pdf IPCC (1997): Greenhouse Gas Inventory Reporting Instructions. Revised 1996 IPCC Guidelines for National Greenhouse Gas Inventories, Vol 1, 2 and 3. The Intergovernmental Panel on Climate Change (IPCC), IPCC WGI Technical Support Unit, United Kingdom. http://www.ipccnggip.iges.or.jp/public/gl/invs1.htm IPCC (2000): IPCC Good Practice Guidance and Uncertainty Management in National Greenhouse Gas Inventories. http://www.ipcc-nggip.iges.or.jp/public/gp/gpgaum.htm Mikkelsen, M.H., Gyldenkærne, S. Poulsen, H.D., Olesen, J.E. & Sommer, S.G. 2005. Opgørelse og beregningsmetode for landbrugets emissioner af ammoniak og drivhusgasser 1985-2002. DMU 43
Page 1 and 2: National Environmental Research Ins
Page 3 and 4: National Environmental Research Ins
Page 5 and 6: Contents Executive summary 9 ES.1.
Page 7 and 8: 4.3 Chemical industry (2B) 122 4.3.
Page 9 and 10: 8.3.6 Recalculations 209 8.3.7 Plan
Page 11 and 12: Executive summary ES.1. Background
Page 13 and 14: electricity. Also lower outdoor tem
Page 15 and 16: • The GHG emission inventories fo
Page 17 and 18: effekten af de forskellige drivhusg
Page 19 and 20: Som beskrevet i rapportens kapitel
Page 21 and 22: 1 Introduction 1.1 Background infor
Page 23 and 24: The role of the European Union The
Page 25 and 26: Table 1.1 List of current data stru
Page 27 and 28: 1.4 Brief general description of me
Page 29 and 30: 1A2f (Industry-other), 1A3a (Civil
Page 31 and 32: is calculated. It is found that tha
Page 33 and 34: (see the reference list at Chapter
Page 35 and 36: 1 Quality control (QC) Quality plan
Page 37 and 38: The different CCP’s are not indep
Page 39 and 40: When new data are introduced they c
Page 41 and 42: Inventory report for year 3 Invento
Page 43: The uncertainty on N 2 O from stati
Page 47 and 48: 2 Trends in Greenhouse Gas Emission
Page 49 and 50: to change in traditional stable sys
Page 51 and 52: from national fishing and off-road
Page 53 and 54: 3 Energy (CRF sector 1) 3.1 Overvie
Page 55 and 56: Table 3.3 CH 4 emission from the en
Page 57 and 58: Fuel consumption time-series for st
Page 59 and 60: Degree days Fuel consumption adjust
Page 61 and 62: Table 3.7 CO 2 emission from subsec
Page 63 and 64: The CH 4 emission from stationary c
Page 65 and 66: 3.2.1.3.4 SO , NO , NMVOC and CO 2
Page 67 and 68: The fuel consumption of area source
Page 69 and 70: Table 3.12 CH 4 emission factors 19
Page 71 and 72: − Gruijthuijsen & Jensen 2000 −
Page 73 and 74: ues from Pulles & Aardenne 2001. Th
Page 75 and 76: • Disaggregation of fuel consumpt
Page 77 and 78: 3.3.1.1 Fuel consumption Table 3.18
Page 79 and 80: 3-@ 90 80 70 60 50 40 30 20 10 0 19
Page 81 and 82: 1,4 1,2 1,0 0,8 0,6 0,4 0,2 0,0 198
Page 83 and 84: Table 3.19 Emissions of CO 2 , CH 4
Page 85 and 86: Passenger cars 56% Passenger cars 8
Page 87 and 88: WRQV@ 120 100 80 60 40 20 0 1985 19
Page 89 and 90: 70000 60000 50000 40000 30000 20000
Page 91 and 92: The NO X emission trend for Agricul
Page 93 and 94: Bunkers The most important emission
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Ã Ã Ã Ã Ã Ã
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age the emissions from catalyst car
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Where S C is the soak emission, l t
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3.3.2.2 Methodologies and reference
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Table 3.26 Fuel specific emission f
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Where E = emission, FC = fuel consu
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For non-road machinery and working
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Emission factors The Danish greenho
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A comparison of the national approa
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( , 4 = = ( ; 4 + ( , 4 −2
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In the 1990-1999 inventories fugiti
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Table 3.38 Uncertainty, CRF sector
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4 Industrial processes (CRF Sector
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The time-series for emission of CO
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4.2.5 Recalculations No source spec
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4.4 Metal production (2C) 4.4.1 Sou
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Table 4.8 Consumption of HFCs in fo
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The potential emissions have been c
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cedure consisted of a check of the
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Danish Environmental Protection Age
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Table 5.1 Emission of chemicals in
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5.2.2 Methodological issues The emi
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(ii) Collection of data for quantif
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6 The emission of greenhouse gases
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Table 6.2 List of institutes involv
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NERI receives the data from differe
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approximately 6%, which nearly corr
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6.3.2 Methodological issues 6.3.2.1
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Table 6.11 Nitrogen excretion, annu
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Table 6.14 Emissions factor - N 2 O
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153
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Table 6.20 Emissions from crop resi
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Ã Ã Ã Ã Ã 80
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6.5 NMVOC emission Less than 1% of
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• This years data delivery agreem
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Husted, 1994: Waste Management, Sea
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7 The Specific methodologies regard
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In 1990, the forested area with tre
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inventory will be quite similar to
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Table 7.4 Data on gross uptake of C
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place during the first 30 years fol
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7.2.5 Recalculations Since the subm
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Table 7.8 Agricultural areas in Den
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7.3.2.1 Emission from mineral soils
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Table 7.17 C-emission from organic
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Table 7.19 Area classification of t
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The LULUCF sector contributes to a
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Schöne, D. and Schulte, A. (1999).
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Table A2.3 ÃÃÃÃÃÃÃÃÃÃ
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As a result the sectoral total in C
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Since, the Danish SWDSs are well-ma
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Table 8.8. Amounts of waste and CH
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Combustible” and “Other not Com
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which disaggregation level that can
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tion, technical upgrades of the WWT
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assuming that the treatment is 100%
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intermediate of both processes. Dan
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Table 8.19. Uncertainties for main
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In general country-specific TOW val
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Danish Environmental Protection Age
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9 Other (CRF sector 7) Chapter 9 is
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Table 10.1 Recalculation performed
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Table 10.2. Recalculation performed
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For the Industrial Sector uncertain
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Annex 1 Key source analyses Descrip
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7KH UHVXOW RI WKH NH\ VRXUFH DQDO\V
Page 227 and 228:
7DEOHV $ ± $ RI WKH *RRG 3UDFWLFH
Page 229 and 230:
Table 3. Key source analysis 1990-2
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Annex 3 Other detailed methodologic
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1 Introduction The Danish atmospher
Page 235 and 236:
Stationary combustion plants are in
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Emissions from non-energy use of fu
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Coke oven coke The emission factor
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Kerosene The emission factor 72 kg/
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Illerup 2003. The estimated emissio
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The emission factor for CHP plants
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− Fuel consumption for transport.
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tricity trade, fuel consumption and
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Figure 3A-6 depicts the time-series
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1A4a Commercial / Institutional 2%
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CO 2 [Tg] 60 50 40 30 20 10 0 1990
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Other stationary combustion plants
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1A4a Commercial / Institutional 2%
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only accounted for a small portion
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Electricity and heat production is
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The use of wood in residential boil
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straw consumption in residential pl
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• The IPCC reference approach val
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Table 3A-21 Key sources, stationary
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emission are N 2 O emission (all pl
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enewable fuels has increased. The D
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Jørgensen, L. & Johansen, L. P. 20
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Appendix 3A-1 The Danish emission i
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030203 Blast furnace cowpers 1A2a 0
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Table 3A-28 Detailed fuel consumpti
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1A2f 118 SEWAGE SLUDGE 030311 40162
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Appendix 3A-4 Emission factors Tabl
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Table 3A-33 N 2 O emission factors
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7. Bjerrum M., 2002. Danish Technol
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NOX NATURAL GAS 010105 1A1a 276 241
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019 Enstedvaerket 04 010101 204 GAS
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Table 3A-39 Large point sources, pl
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Appendix 3A-6 Uncertainty estimates
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Table 3A-42 Uncertainty estimation,
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Table 3A-47 Uncertainty estimation,
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Table 3A-49 Fuel category correspon
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Appendix 3A-9 Reference approach Ã
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Table 3A-51 Fuel category correspon
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20201 - - - - - - - - - - - - - - -
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Passenger Cars Diesel >2.0 l Euro I
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Passenger Cars Gasoline 2.0 l Euro
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Buses Urban Buses Conventional 0 19
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Sector Subsector Tech FYear LYear 1
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Page 323 and 324:
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Sector Subsector Tech FCu FCr FCh C
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Sector Subsector Tech COu COr COh N
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Sector Subsector Tech COuR COrR COh
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Annex 3B-5: Fuel use factors (MJ/km
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2-wheelers 1999 1.195 1.264 1.578 8
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2-wheelers 1991 6.249 4.379 2.011 6
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2002 Heavy Duty Vehicles 37849451 8
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Annex 3B-7: COPERT III:DEA statisti
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0808 Excavators (wheel type) 1000 1
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0808 Forklifts 5-10 tons (diesel) 0
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0809 Trimmers 60000 0.8 0.5 15 10 1
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1990 80502 Air traffic. other airpo
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2003 80403 Fishing Kerosene 731 4.6
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Year Category Mode SO2 NOx NMVOC CH
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Pollutant CRF ID Unit 1985 1986 198
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Pollutant CRF ID Unit 1985 1986 198
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Uncertainty estimation, CH 4 Gas Ba
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Uncertainty estimation, N 2 O IPCC
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Table. Production of Lime/Hydrated
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Suckling cattle 170.2 Swine Average
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7DEOH 'HWDLOHG LQIRUPDWLRQ UHODWHG
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7DEOH &KDQJHV LQ VWDEOH W\SH ± Liv
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Pullet, consumption, floor (100 pcs
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Annex 3E Solid Waste Disposal on La
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B = Biological N = Nitrification (r
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Table 3E.7. Stabilisation of sludge
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in Table 3E.9. Table 3E.9 Gross emi
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5HFRYHUHG &+ Ã HPLVVLRQV >*J@ 14.
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Annex 3F Solvents National Atmosphe
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83 1-ethyl-2,2,6-trimethylcyclohexa
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191 2-methoxy-2-methylpropane 192 2
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299 acetaldehyde 300 acetic acid 30
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407 cyclopentane 408 cyclopenta-phe
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515 methyl naphthalenes 516 methyl
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624 trans-3-hexene 625 trialkyl pho
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Annex 5 Assessment of completeness
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Annex 6.1 Annex 6.1. Additional inf
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Table A6.1.2 ÃÃÃÃ Kingdom DK Ã
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Table A6.1.4 ÃÃÃÃÃÃÃÃÃ Kin
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Annex 6.2 Additional information to
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Annex 7 Table 6.1 and 6.2 of the IP
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Annex 8 Other annexes - (Any other
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PM 2.2: An explicit description in
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Correctness The data at level 3 has
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Level 6 Transparency The background
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Table A9.1 ÃÃÃÃ Denmark ÃÃÃ
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Table A9.3 ÃÃÃÃ Denmark ÃÃÃ
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