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

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Table 3.8 CH 4 emission from stationary combustion plants 2003 1) 60 2003 1A1a Public electricity and heat production 15647 Mg 1A1b Petroleum refining 2 Mg 1A1c Other energy industries 58 Mg 1A2 Industry 1485 Mg 1A4a Commercial / Institutional 961 Mg 1A4b Residential 4562 Mg 1A4c Agriculture / Forestry / Fisheries 2094 Mg Total 24809 Mg 1) Only emission from stationary combustion plants in the sectors is included 1A4a Commercial / Institutional 4% 1A2 Industry 6% 1A1c Other energy industries 0% 1A4b Residential 18% 1A1b Petroleum refining 0% 1A4c Agriculture / Forestry / Fisheries 8% 1A1a Public electricity and heat production 64% Figure 3.9 CH 4 emission sources, stationary combustion plants, 2003 The CH 4 emission factor for reciprocating lean-burn gas engines is much higher than for other combustion plants due to the continuous ignition/burn-out of the gas. Lean-burn gas engines have an especially high emission factor as discussed in Chapter 3.2.2.4. A considerable number of leanburn gas engines are in operation in Denmark and these plants account for 75% of the CH 4 emission from stationary combustion plants (Figure 3.10). The engines are installed in CHP plants and the fuel used is either natural gas or biogas. Other stationary combustion plants 25% Gas engines 75% Figure 3.10 Gas engine CH 4 emission share, 2003.
The CH 4 emission from stationary combustion increased by a factor of 4.3 since 1990 (Figure 3.11). This results from the considerable number of lean-burn gas engines installed in CHP plants in Denmark in this period. This increase is also the reason for the increasing IEF (implied emission factor) for gaseous fuels and biomass in CRF sector 1A1, 1A2 and 1A4. Figure 3.12 provides timeseries for the fuel consumption rate in gas engines and the corresponding increase of CH 4 emission. CH 4 [Gg] 30 25 20 15 10 5 0 1990 1991 1992 1993 1994 Total 1995 1996 1997 1998 1999 2000 2001 2002 2003 1A1a Public electricity and heat production 1A1b Petroleum refining 1A1c Other energy industries 1A2 Industry 1A4a Commercial / Institutional 1A4b Residential 1A4c Agriculture / Forestry / Fisheries Figure 3.11 CH 4 emission time-series for stationary combustion plants Fuel consumption [PJ] CH 4 emission [Gg] 40 35 30 25 20 15 10 5 0 30 25 20 15 10 5 0 1990 1990 1991 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 Gas engines, Natural gas Gas engines, Biogas 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 Gas engines Other stationary combustion plants Figure 3.12 Fuel consumption and CH 4 emission from gas engines, time-series. 2002 2002 2003 2003 Total 3.2.1.3.3 N O 2 The N O emission from stationary combustion plants accounts for 5% of the total Danish N O 2 2 emission. Table 3.9 lists the N O emission inventory for stationary combustion plants in the year 2 61
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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
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 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: Table 3.7 CO 2 emission from subsec
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
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
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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
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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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