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

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tional emission inventories in future. The plants will report CO 2 emissions for 2005 according to this legislation. Table 3.11 CO 2 emission factors 2003 Ã Ã Ã Ã Coal 95 kg/GJ Country specific Solid Brown coal briquettes 94,6 kg/GJ IPCC reference manual Solid Coke oven coke 108 kg/GJ IPCC reference manual Solid Petroleum coke 92 kg/GJ Country specific Liquid Wood 102 kg/GJ Corinair Biomass Municipal waste 94,5 17,6 kg/GJ Country specific Biomass / Other fuels Straw 102 kg/GJ Country specific Biomass Residual oil 78 kg/GJ Corinair Liquid Gas oil 74 kg/GJ Corinair Liquid Kerosene 72 kg/GJ Corinair Liquid Fish & rape oil 74 kg/GJ Country specific Biomass Orimulsion 80 kg/GJ Country specific Liquid Natural gas 57,19 kg/GJ Country specific Gas LPG 65 kg/GJ Corinair Liquid Refinery gas 56,9 kg/GJ Country specific Liquid Biogas 83,6 kg/GJ Country specific Biomass CH 4 The CH 4 emission factors applied for 2003 are presented in Table 3.12. In general, the same emission factors have been applied for 1990-2003. However, time-series have been estimated for both natural gas fuelled engines and biogas fuelled engines. The emission factors and references are further discussed in Annex 3A. Emission factors for gas engines, gas turbines and CHP plants combusting wood, straw or municipal waste all refer to emission measurements carried out on Danish plants (Nielsen & Illerup 2003). Most other emission factors refer to the EMEP/Corinair Guidebook (EMEP/Corinair 2004). Gas engines combusting natural gas or biogas contribute much more to the total CH 4 emission than other stationary combustion plants. The relatively high emission factor for gas engines is well documented, based on a very high number of emission measurements on Danish plants. The factor is further discussed in Annex 3A. Due to the considerable consumption of natural gas and biogas in gas engines the IEF (implied emission factor) in CRF sector 1A1, 1A2 and 1A4, fuel categories Gaseous fuels and Biomass is relatively high. The considerable change in IEF is a result of the increasing consumption of natural gas and biogas in gas engines as discussed in Chapter 3.2.1.2. 66
Table 3.12 CH 4 emission factors 1990-2003 Ã COAL 1A1a 010101, 010102, 010103 1,5 EMEP/Corinair 2004 COAL 1A1a, 1A2f, 1A4b, 1A4c 010202, 010203, 0301, 0202, 0203 15 EMEP/Corinair 2004 BROWN COAL BRI. all all 15 EMEP/Corinair 2004, assuming same emission factor as for coal COKE OVEN COKE all all 15 EMEP/Corinair 2004, assuming same emission factor as for coal PETROLEUM COKE all all 15 EMEP/Corinair 2004 WOOD AND SIMIL. 1A1a 010102, 010103, 010104 2 Nielsen & Illerup 2003 WOOD AND SIMIL. 1A4a, 1A4b, 1A4c 0201, 0202, 0203 200 EMEP/Corinair 2004 WOOD AND SIMIL. 1A1a, 1A2f 010105, 010202, 010203, 0301, 030102, 030103 32 EMEP/Corinair 2004 MUNICIP. WASTES 1A1a 010102, 010103, 010104, 010105 0,59 Nielsen & Illerup 2003 MUNICIP. WASTES 1A1a, 1A2f, 1A4a all other 6 EMEP/Corinair 2004 STRAW 1A1a 010102, 010103 0,5 Nielsen & Illerup 2003 STRAW 1A1a, 1A2f, 1A4c 010202, 010203, 020302, 030105 32 EMEP/Corinair 2004 STRAW 1A4b, 1A4c 0202, 0203 200 EMEP/Corinair 2004 RESIDUAL OIL all all 3 EMEP/Corinair 2004 GAS OIL all all 1,5 EMEP/Corinair 2004 KEROSENE all all 7 EMEP/Corinair 2004 FISH & RAPE OIL all all 1,5 EMEP/Corinair 2004, assuming same emission factor as gas oil ORIMULSION 1A1a 010101 3 EMEP/Corinair 2004, assuming same emission factor as residual oil NATURAL GAS 1A1a 0101, 010101, 010102, 010202 6 DGC 2001 NATURAL GAS 1A1a 010103, 010203 15 Gruijthuijsen & Jensen 2000 NATURAL GAS 1A1a, 1Ac, 1A2f, 1A4a, Gas turbines: 010104, 010504, 030104, 1,5 Nielsen & Illerup 2003 1A4c 020104, 020303 NATURAL GAS 1A1a, 1A1c, 1A2f, 1A4a, Gas engines: 010105, 010205, 010505, 1) 520 Nielsen & Illerup 2003 1A4b, 1A4c 030105, 020105, 020204, 020304 NATURAL GAS 1A1c, 1A2f, 1A4a, 1A4b, 1A4c 010502, 0301, 0201, 0202, 0203 6 DGC 2001 NATURAL GAS 1A2f, 1A4a, 1A4b 030103, 030106, 020103, 020202 15 Gruijthuijsen & Jensen 2000 LPG all all 1 EMEP/Corinair 2004 REFINERY GAS 1A1b 010304 1,5 EMEP/Corinair 2004 BIOGAS 1A1a, 1A1c, 1A2f, 1A4a, Gas engines: 010105, 010505, 030105, 1) Nielsen & Illerup 2003 1A4c 020105, 020304 323 BIOGAS 1A1a, 1A2f, 1A4a, 1A4c all other 4 EMEP/Corinair 2004 1) 2003 emission factor. Time-series is shown in Annex 3A N O 2 The N O emission factors applied for the 2003 inventory are listed in Table 3.13. The same emission 2 factors have been applied for 1990-2003. Emission factors for gas engines, gas turbines and CHP plants combusting wood, straw or municipal waste all refer to emission measurements carried out on Danish plants (Nielsen & Illerup 2003). Other emission factors refer to the EMEP/Corinair Guidebook (EMEP/Corinair 2004). 67
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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
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 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: The fuel consumption of area source
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
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
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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
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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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