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

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The emission/sink from mineral soils are not reported this year, but will be reported from next year. The carbon dioxide emission factor from the organic soils is based on emission data from Denmark, UK, Sweden, Finland and Germany, adjusted for differences in annual mean temperature to the average Danish climate (Svend E. Olesen, DIAS, 2005). E.g. data from southern Finland are adjusted with a factor of 2 and data from central Germany with a factor of 0.6. The emission factors for organic soils are shown in Table 7.12 Negative values indicates a built up of organic matter. Wet organic soils are defined as having a water table between 0 and 30 centimetres. Table 7.12 Emission factors for organic soils. Negative values indicates a built up. Emissions of nitrous oxide from organic soils are estimated from degradation of organic matter and the C:N-ratio in the organic matter. Figure 7.3 shows the C:N-ratio for 160 different soils. Hence for organic soils are used a C:N-ratio of 20. As emission factor is used the IPCC Tier 1 value of 1.25%. 178 % organic soils 1 % with deep organic soils % wet soils Dry shallow Emission factor, t C ha -1 y -1 Dry deep Wet shallow Annual crops 3.8 38 0 5 8 0 0 Grass in rotation 11.2 38 0 5 8 0 0 Set-a-side 10.4 38 26 3 4 -0.5 -0.5 Permanent grass (drained) 19.5 38 26 3 4 -0.5 -0.5 1 Percentage of the total area from the annual survey from Statistics Denmark classified as organic 65,00 60,00 55,00 50,00 45,00 40,00 35,00 30,00 25,00 20,00 15,00 10,00 y = 0,3575x + 15,448 5,00 0,00 Organiske jorde Spagnumarealer 0 5 10 15 20 25 30 35 40 45 50 55 60 65 Figure 7.3 C:N-ratio in organic soils in relation to soil carbon content (Olesen 2004) ÈÃ Wet deep
7.3.2.1 Emission from mineral soils The removals/sinks from mineral soils are not reported this year due to methodological issues, but will be reported next year when a clarification of the methodology has been made. 7.3.2.2 Horticulture Permanent horticultural plantations are reported separately under Cropland (Table 5.B). Permanent horticulture is only a minor production in Denmark. The total area for different main classes is given in Table 7.13. Due to the limited area and small changes between years the CO re- 2 moval/emission is calculated without a growth model for the different tree categories. Instead the average stock figures is used in Table 7.14 multiplied with changes in the area to estimate the annual emissions/removals. Perennial horticultural crops account for approximately 0.07% of the standing C-stock. The factors for estimating the C-stock in perennial horticulture are given in Table 7.14. Expansion factors and densities are the same as used in forestry (Section 7.2). Table 7.13 Area with perennial fruit trees and – bushes, C stock and stock changes from 1990-2003. 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 Apples, ha 2726 2462 3006 2209 2061 1658 1854 1697 1660 1623 1679 1783 1574 1624 Pears, ha 351 497 436 438 328 545 469 430 555 431 441 469 420 457 Cherries and Plumes, ha 2200 2200 2200 2222 2641 2854 3023 2794 2791 2956 3002 2903 2871 2967 Black currant, ha 1269 1486 2091 1919 2351 1827 1783 1531 1280 1411 1492 1850 1939 2028 Other, ha 250 250 250 449 337 348 343 323 235 272 412 376 384 448 Total, ha 6796 6895 7983 7237 7718 7232 7472 6775 6521 6693 7026 7381 7188 7524 Ct, stock, Gg 64.846 62.530 70.859 60.303 62.637 59.485 63.356 58.079 57.540 58.381 60.135 61.368 58.121 60.316 Stock change, -1 Gg y 0.406 -2.316 8.329 -10.557 2.334 -3.152 3.871 -5.277 -0.540 0.842 1.754 1.233 -3.247 2.195 CO2-emission, -1 Gg y 1.489 -8.492 30.541 -38.708 8.558 -11.556 14.194 -19.348 -1.978 3.086 6.430 4.519 -11.905 8.048 Table 7.14 Parameters used to estimate the C-stock in perennial horticulture (Gyldenkærne et al. 2005). Apples, old Apples, new Pears, old Pears, new Cherries and Plumes Black currant Other fruits bushes Stem diameter, m 0.09 0.07 0.07 0.05 0.09 0,042 0,042 Height, m 3.00 3.00 3.00 3.00 4.00 1,00 1,50 Numbers, ha -1 1905 2700 1250 2300 1000 4500 3000 Form figure 1.20 1.20 1.20 1.20 1.20 1,00 1,00 Volume, m 3 ha -1 43.63 37.41 17.32 16.26 30.54 6,23 6,23 Expansion factor 1.20 1.20 1.20 1.20 1.20 1,20 1,20 Density, t m -3 0.56 0.56 0.56 0.56 0.56 0,56 0,56 Biomass, t ha -1 29.32 25.14 11.64 10.93 20.52 4,19 4,19 C content, t C t -1 biomasse -1 0.50 0.50 0.50 0.50 0.50 0,50 0,50 C, t ha -1 14.66 12.57 5.82 5.46 10.26 2,09 2,09 C, t ha -1 (average) 13.61 5.64 10.26 2.09 2.09 7.3.2.3 Hedgerows Since the beginning of the early 1970s governmental subsidiaries has been given to increase the area with hedgerows to reduce soil erosion. Annually financial support is given to approximately 179
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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
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Som beskrevet i rapportens kapitel
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1 Introduction 1.1 Background infor
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The role of the European Union The
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Table 1.1 List of current data stru
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1.4 Brief general description of me
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1A2f (Industry-other), 1A3a (Civil
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is calculated. It is found that tha
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(see the reference list at Chapter
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1 Quality control (QC) Quality plan
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The different CCP’s are not indep
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When new data are introduced they c
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Inventory report for year 3 Invento
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The uncertainty on N 2 O from stati
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1.8 General assessment of the compl
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2 Trends in Greenhouse Gas Emission
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to change in traditional stable sys
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from national fishing and off-road
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3 Energy (CRF sector 1) 3.1 Overvie
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Table 3.3 CH 4 emission from the en
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Fuel consumption time-series for st
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Degree days Fuel consumption adjust
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Table 3.7 CO 2 emission from subsec
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The CH 4 emission from stationary c
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3.2.1.3.4 SO , NO , NMVOC and CO 2
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The fuel consumption of area source
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Table 3.12 CH 4 emission factors 19
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− Gruijthuijsen & Jensen 2000 −
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ues from Pulles & Aardenne 2001. Th
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• Disaggregation of fuel consumpt
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3.3.1.1 Fuel consumption Table 3.18
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3-@ 90 80 70 60 50 40 30 20 10 0 19
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1,4 1,2 1,0 0,8 0,6 0,4 0,2 0,0 198
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Table 3.19 Emissions of CO 2 , CH 4
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Passenger cars 56% Passenger cars 8
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WRQV@ 120 100 80 60 40 20 0 1985 19
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70000 60000 50000 40000 30000 20000
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The NO X emission trend for Agricul
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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
Page 129 and 130: The potential emissions have been c
Page 131 and 132: cedure consisted of a check of the
Page 133 and 134: Danish Environmental Protection Age
Page 135 and 136: Table 5.1 Emission of chemicals in
Page 137 and 138: 5.2.2 Methodological issues The emi
Page 139 and 140: (ii) Collection of data for quantif
Page 141 and 142: 6 The emission of greenhouse gases
Page 143 and 144: Table 6.2 List of institutes involv
Page 145 and 146: NERI receives the data from differe
Page 147 and 148: approximately 6%, which nearly corr
Page 149 and 150: 6.3.2 Methodological issues 6.3.2.1
Page 151 and 152: Table 6.11 Nitrogen excretion, annu
Page 153 and 154: Table 6.14 Emissions factor - N 2 O
Page 155 and 156: 153
Page 157 and 158: Table 6.20 Emissions from crop resi
Page 159 and 160: Ã Ã Ã Ã Ã 80
Page 161 and 162: 6.5 NMVOC emission Less than 1% of
Page 163 and 164: • This years data delivery agreem
Page 165 and 166: Husted, 1994: Waste Management, Sea
Page 167 and 168: 7 The Specific methodologies regard
Page 169 and 170: In 1990, the forested area with tre
Page 171 and 172: inventory will be quite similar to
Page 173 and 174: Table 7.4 Data on gross uptake of C
Page 175 and 176: place during the first 30 years fol
Page 177 and 178: 7.2.5 Recalculations Since the subm
Page 179: Table 7.8 Agricultural areas in Den
Page 183 and 184: Table 7.17 C-emission from organic
Page 185 and 186: Table 7.19 Area classification of t
Page 187 and 188: The LULUCF sector contributes to a
Page 189 and 190: Schöne, D. and Schulte, A. (1999).
Page 191 and 192: Table A2.3 ÃÃÃÃÃÃÃÃÃÃ
Page 193 and 194: As a result the sectoral total in C
Page 195 and 196: Since, the Danish SWDSs are well-ma
Page 197 and 198: Table 8.8. Amounts of waste and CH
Page 199 and 200: Combustible” and “Other not Com
Page 201 and 202: which disaggregation level that can
Page 203 and 204: tion, technical upgrades of the WWT
Page 205 and 206: assuming that the treatment is 100%
Page 207 and 208: intermediate of both processes. Dan
Page 209 and 210: Table 8.19. Uncertainties for main
Page 211 and 212: In general country-specific TOW val
Page 213 and 214: Danish Environmental Protection Age
Page 215 and 216: 9 Other (CRF sector 7) Chapter 9 is
Page 217 and 218: Table 10.1 Recalculation performed
Page 219 and 220: Table 10.2. Recalculation performed
Page 221 and 222: For the Industrial Sector uncertain
Page 223 and 224: Annex 1 Key source analyses Descrip
Page 225 and 226: 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
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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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