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Table 3.13 N 2 O emission factors 1990-2003 Ã COAL all all 3 EMEP/Corinair 2004 BROWN COAL BRI. all all 3 EMEP/Corinair 2004 COKE OVEN COKE all all 3 EMEP/Corinair 2004 PETROLEUM COKE all all 3 EMEP/Corinair 2004 WOOD AND SIMIL. 1A1a 010102, 010103, 010104 0,8 Nielsen & Illerup 2003 WOOD AND SIMIL. 1A1a 010105, 010202, 010203 4 EMEP/Corinair 2004 WOOD AND SIMIL. 1A2f, 1A4a, 1A4b, 1A4c all 4 EMEP/Corinair 2004 MUNICIP. WASTES 1A1a 010102, 010103, 010104, 010105 1,2 Nielsen & Illerup 2003 MUNICIP. WASTES 1A1a 010203 4 EMEP/Corinair 2004 MUNICIP. WASTES 1A2f, 1A4a 030102, 0201, 020103 4 EMEP/Corinair 2004 STRAW 1A1a 010102, 010103 1,4 Nielsen & Illerup 2003 STRAW 1A1a 010202, 010203 4 EMEP/Corinair 2004 STRAW 1A2f, 1A4b, 1A4c all 4 EMEP/Corinair 2004 RESIDUAL OIL all all 2 EMEP/Corinair 2004 GAS OIL all all 2 EMEP/Corinair 2004 KEROSENE all all 2 EMEP/Corinair 2004 FISH & RAPE OIL all all 2 EMEP/Corinair 2004, assuming same emission factor as gas oil ORIMULSION 1A1a 010101 2 EMEP/Corinair 2004, assuming same emission factor as residual oil NATURAL GAS 1A1a 0101, 010101, 010102, 010103, 010202, 010203 1 EMEP/Corinair 2004 NATURAL GAS 1A1a, 1A1c, 1A2f, 1A4a, 1A4c NATURAL GAS 1A1a, 1A1c, 1A2f, 1A4a, 1A4b, 1A4c NATURAL GAS 1A1c, 1A2f, 1A4a, 1A4b, 1A4c 68 Gas turbines: 010104, 010504, 030104, 020104, 020303 Gas engines: 010105, 010205, 010505, 030105, 020105, 020204, 020304 010502, 0301, 030103, 030106, 0201, 020103, 0202, 020202, 0203 2,2 Nielsen & Illerup 2003 1,3 Nielsen & Illerup 2003 1 EMEP/Corinair 2004 LPG all all 2 EMEP/Corinair 2004 REFINERY GAS all all 2,2 EMEP/Corinair 2004 BIOGAS 1A1a 010102, 010103, 010203 2 EMEP/Corinair 2004 BIOGAS 1A1a, 1A1c, 1A2f, 1A4a, 1A4c Gas engines: 010105, 010505, 030105, 020105, 020304 BIOGAS 1A2f, 1A4a, 1A4c 0301, 030102, 0201, 020103, 0203 0,5 Nielsen & Illerup 2003 2 EMEP/Corinair 2004 SO , NO , NMVOC and CO 2 X Emission factors for SO , NO , NMVOC and CO including time-series and references are listed in 2 X Annex 3A. The emission factors refer to: • The EMEP/Corinair Guidebook (EMEP/Corinair 2004) • The IPCC Guidelines, Reference Manual (IPCC 1996) • Danish legislation: ° Miljøstyrelsen 2001 (Danish Environmental Protection Agency) ° Miljøstyrelsen 1990 (Danish Environmental Protection Agency) ° Miljøstyrelsen 1998 (Danish Environmental Protection Agency) • Danish research reports including: ° An emission measurement program for decentralised CHP plants (Nielsen & Illerup 2003) ° Research and emission measurements programs for biomass fuels: − Nikolaisen et al., 1998 − Jensen & Nielsen, 1990 − Dyrnum et al., 1990 − Hansen et al., 1994 − Serup et al., 1999 ° Research and environmental data from the gas sector:
− Gruijthuijsen & Jensen 2000 − Danish Gas Technology Centre 2001 • Calculations based on plant-specific emissions from a considerable number of power plants (Nielsen 2004). • Calculations based on plant-specific emission data from a considerable number of municipal waste incineration plants. These data refer to annual environmental reports published by plant operators. • Sulphur content data from oil companies and the Danish gas transmission company. • Additional personal communication. Emission factor time-series have been estimated for a considerable number of the emission factors. These are provided in Annex 3A. SO 2 and NO X emissions from large point sources are often plant specific based on emission measurements. Emissions of CO and NMVOC are also plant specific for some plants. 3.2.2.5 Disaggregation to specific industrial subsectors The national statistics on which the emission inventories are based do not include a direct disaggregation to specific industrial subsectors. However, separate national statistics from Statistics Denmark include a disaggregation to industrial subsectors. This part of the energy statistics is also included in the official energy statistics from the Danish Energy Authority. Every other year Statistics Denmark collects fuel consumption data for all industrial companies of a considerable size. The deviation between the total fuel consumption from the Danish Energy Authority and the data collected by Statistics Denmark is rather small. Thus the disaggregation to industrial subsectors available from Statistics Denmark can be applied for estimating disaggregation keys for fuel consumption and emissions. The industrial fuel consumption is considered in three aspects: − Fuel consumption for transport. This part of the fuel consumption is not disaggregated to subsectors. − Fuel consumption applied in power or district heating plants. Disaggregation of fuel and emissions is plant specific. − Fuel consumption for other purposes. The total fuel comsumption and the total emissions are disaggregated to subsectors. All pollutants included in the Climate Convention reporting have been disaggregated to industrial subsectors. 3.2.3 Uncertainties and time-series consistency Time-series for fuel consumption and emission are shown and discussed in Chapter 3.2.1.2 and 3.2.1.3. Uncertainty estimates include uncertainty with regard to the total emission inventory as well as uncertainty with regard to trends. The GHG emission from stationary combustion plants has been estimated with an uncertainty interval of ±11% and the increase in the GHG emission since 1990 has been estimated to be 11,1% ± 1,7 %-age-points. 69
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National Environmental Research Ins
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National Environmental Research Ins
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Contents Executive summary 9 ES.1.
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4.3 Chemical industry (2B) 122 4.3.
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8.3.6 Recalculations 209 8.3.7 Plan
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Executive summary ES.1. Background
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electricity. Also lower outdoor tem
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• The GHG emission inventories fo
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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 and 44: The uncertainty on N 2 O from stati
Page 45 and 46: 1.8 General assessment of the compl
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: Table 3.12 CH 4 emission factors 19
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
Page 95 and 96: Ã Ã Ã Ã Ã Ã
Page 97 and 98: age the emissions from catalyst car
Page 99 and 100: Where S C is the soak emission, l t
Page 101 and 102: 3.3.2.2 Methodologies and reference
Page 103 and 104: Table 3.26 Fuel specific emission f
Page 105 and 106: Where E = emission, FC = fuel consu
Page 107 and 108: For non-road machinery and working
Page 109 and 110: Emission factors The Danish greenho
Page 111 and 112: A comparison of the national approa
Page 113 and 114: ( , 4 = = ( ; 4 + ( , 4 −2
Page 115 and 116: In the 1990-1999 inventories fugiti
Page 117 and 118: Table 3.38 Uncertainty, CRF sector
Page 119 and 120: 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
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7DEOHV $ ± $ RI WKH *RRG 3UDFWLFH
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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
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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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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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