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

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162 • Review of existing methods - Complete and detailed overview of applied methods in a schematic and transparent way • Review of the uncertainty calculation • Modifying data structure • Filling up methodological gaps • Setting up control measurements As a response to the recommendations from ERT the uncertainties estimate is improved (Table 6.28) based on Tier1 approach. The further work concerning the uncertainties will focus on the possibilities to improve by using a Monte Carlo simulation, which can increase the outcome from the uncertainty analysis. In the Danish inventory national data is used for N-excretion, ammonia emission, feed intake, stable type, nitrogen and dry matter content in crops. It is important to focus on documentation, especially on the national data and methodology used in the inventory. This year, in co-operation with the Danish Institute of Agricultural Science, a detailed description of the methodology used to calculate the emission of both the ammonia and greenhouse gases has been published (Mikkelsen et al. 2005). Presently, this report is only available in Danish, but will be translated into English. It is planned to review the report by external agricultural experts. This should, ideally, be in co-operation with another member states with agricultural conditions similar to the Danish. This review procedure could be useful for all involved countries to exchange knowledge and to identify the most important inventory improvements. Comparison between the Danish emission inventory and a calculation based on IPCC Tier1 approach could be a tool to improve the comparability, the transparency and the documentation. Further, it is planned to re-estimate the N 2 O from cultivation of histosols and this emission will, in the next reporting, be included in the LULUCF sector. 6.10 References Bussink, D.W. 1994: Relationship between ammonia volatilisation and nitrogen fertilizer application rate, intake and excretion of herbage nitrogen by cattle on grazed swards. Fertil. Res. 38, 111- 121. Børgesen, C.D. & Grant, R. 2003: Vandmiljøplan II – modelberegning af kvælstofudvaskning på landsplan, 1984 til 2002. Baggrundsnotat til Vandmiljøplan II - slutevaulering. December 2003, Danmarks Jordbrugsforskning og Danmarks Miljøundersøgelser. (In Danish). CFR, Common Reporting Format: (http://cdr.eionet.eu.int/dk/Air_Emission_Inventories/Submission_EU) DEA, 2004: DEA – Danish Energy Authority, S. Tafdrup. Pers. Comm., 2004 Djurhuus, J. & Hansen, E.M. 2003: Notat vedr. tørstof og kvælstof i efterladte planterester for landbrugsjord – af 21. maj 2003. Forskningscenter Foulum, Tjele. (In Danish). Fenhann, J. & Kilde, N.A. 1994: Inventory of Emissions to the Air from Danish Sources 1972-1992. System Analysis Department – Risø National Laboratory.
Husted, 1994: Waste Management, Seasonal Variation in Methane Emission from Stored Slurry and Solid Manures. J. Environ. Qual. 23:585-592 (1994). Høgh-Jensen, H., Loges, R., Jensen, E.S., Jørgensen, F.V. & Vinther, F.P. 1998: Empirisk model til kvantificering af symbiotisk kvælstoffiksering i bælgplanter. – Kvælstofudvaskning og –balancer i konventionelle og økologiske produktionssystemer (Red. Kristensen E.S. & Olesen, J.E.) s. 69-86, Forskningscenter for Økologisk Jordbrug. (In Danish). Gyldenkærne, Steen. Researcher at NERI, Departement of Policy Analysis. Pers. Comm., 2004 Illerup, J.B., Nielsen, M., Winther, M., Mikkelsen, M.H., Lyck, E., Hoffmann, L. & Fauser, P. 2004: Annual Danish Emissions Inventory Report to UNECE. Inventories 1990-2002. National Environmental Research Institute. - Research Notes from NERI 202: 490 pp. (electronic). http://www2.dmu.dk/1_viden/2_Publikationer/3_arbrapporter/rapporter/AR202.pdf IPCC, 1996: IPCC Guidelines for National Greenhouse Gas Inventories: Reference Manual. IPCC, 2000: IPCC Good Practice Guidance and Uncertainty Management in National Greenhouse Gas Inventories. Jarvis, S.C., Hatch, D.J. & Roberts, D.H., 1989a: The effects of grassland management on nitrogen losses from grazed swards through ammonia volatilization; the relationship to extral N returns from cattle. J. Agric. Sci. Camb. 112,205-216. Jarvis, S.C., Hatch, D.J. & Lockyer, D.R., 1989b: Ammonia fluxes from grazed grassland annual losses form cattle production systems and their relation to nitrogen inputs. J. Agric. Camp. 113, 99- 108. Kristensen, I.S. 2003: Indirekte beregning af N-fiksering - draft, not published. Danmarks JordbrugsForskning. (In Danish). Kyllingsbæk, 2000: Kvælstofbalancer og kvælstofoverskud i dansk landbrug 1979-1999. DJF rapport nr. 36/markbrug, Dansk Jordbrugsforskning. Massé, D.I., Croteau, F., Patni, N.K. & Masse, L. 2003: Methane emissions from dairy cow and swine slurries stored at 10ºC and 15ºC. Agriculture and Agri-Food Canada, Canadian Biosystem Engineering, Volume 45 p. 6.1-6.6 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 arbejdsrapport nr. 204/2005. Danmarks Miljøundersøgelser og Danmarks JordbrugsForskning. (In Danish). Nielsen, L.H., Hjort-Gregersen, K., Thygesen, P. & Christensen, J. 2002: Socio-economic analysis of centralised Biogas Plants - with technical and corporate economic analysis, Rapport nr. 136, Fødevareøkonomisk Institut, Copenhagen, pp 130. Olesen, J.E., Fenhann, J.F., Petersen, S.O., Andersen, J.M. & Jacobsen, B.H. 2001: Emission af drivhusgasser fra dansk landbrug. DJF rapport nr. 47, markbrug, Danmarks Jordbrugsforskning, 2001. (In Danish) Poulsen, H.D., Børsting, C.F., Rom, H.B. & Sommer, S.G. 2001: Kvælstof, fosfor og kalium i husdyrgødning – normtal 2000. DJF rapport nr. 36 – husdyrbrug, Danmarks Jordbrugsforskning. (In Danish) 163
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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
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
Page 121 and 122: The time-series for emission of CO
Page 123 and 124: 4.2.5 Recalculations No source spec
Page 125 and 126: 4.4 Metal production (2C) 4.4.1 Sou
Page 127 and 128: 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
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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: • This years data delivery agreem
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 and 180: Table 7.8 Agricultural areas in Den
Page 181 and 182: 7.3.2.1 Emission from mineral soils
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
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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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