Annual Danish informative inventory report to UNECE. Emission ...

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288 Data Storage level 2 The full documentation for the correct connection exists through the yearly model file, its output and report files made by the CollectER database system. Data Storage level 2 This check is performed, comparing model output and report files made by the CollectER database system, refer to DS.2.5.1. 6RXUFH VSHFLILF UHFDOFXODWLRQV No recalculations have been performed 6RXUFH VSHFLILF SODQQHG LPSURYHPHQWV There are currently no planned improvements for this section 6RXUFH VSHFLILF SHUIRUPHG LPSURYHPHQWV Source-specific QA/QC and verification is now included in this section. 5HIHUHQFHV 5.Correctness DS.2.5.1 Documentation of a correct connection between all data types at level 2 to data at level 1 5.Correctness DS.2.5.2 Check if a correct data import to level 2 has been made CANA, 1993: European Environmental Agency, Emission Inventory Guidebook 2007, SNAP 090901, December 2006. Available at: http://reports.eea.europa.eu/EMEPCORINAIR5/en/B991vs1.1.pdf Chen, S.-J., Hsieh, L.-T. & Chiu, S.-C., 2003: Emission of polycyclic aromatic hydrocarbons from animal carcass incinerators. The Science of the Environment 313 (2003) 61-76, Elsevier. Available at: http://www.sciencedirect.com/science?_ob=MImg&_imagekey=B6V7 8-48S4NWY-1- D&_cdi=5836&_user=642076&_pii=S0048969703002560&_orig=search& _coverDate=09%2F01%2F2003&_sk=996869998&view=c&wchp=dGLbV lz-zSkzk&md5=cf9b977d597c037b8bc5ad9e2427c553&ie=/sdarticle.pdf Chen, S.-J., Hung, M.-C., Huang, K.-L. & Hwang, W.-I. 2004: Emission of heavy metals from animal carcass incinerators in Taiwan. Chemosphere 55 (2004) 1197-1205, Elsevier. Available at: http://www.sciencedirect.com/science?_ob=MImg&_imagekey=B6V7 4-4BRSD1W-1- 8&_cdi=5832&_user=642076&_pii=S0045653504000463&_orig=search&_ cover- Date=06%2F30%2F2004&_sk=999449990&view=c&wchp=dGLbVlzzSkWz&md5=35a40c3da06e8bdb4ff9ff826fb51fa7&ie=/sdarticle.pdf Danmarks Statistik, 2009: Statistikbanken, Population and elections, Births and deaths. Available at: http://www.statistikbanken.dk DKL, 2009: Danske krematoriers landsforening, statistisk materiale. Available at: http://www.dkl.dk/statistik_1990_1999.aspx and http://www.dkl.dk/statistik_2000_2009.aspx (Danish).
Eisaku TODA, 2006: POPs and heavy metals emission inventory of Japan, Ministry of the Environment, Japan. Available at: http://espreme.ier.unistuttgart.de/homepage_old/workshop/papers/ Toda %20 %20POPs %20and %20heavy %20metals %20emission %20inventory %20of %20Japan.pdf Fontelle, J.-P., Allemand, N., Andre, J.-M., Beguier, S., Chang, J.-P., Gueguen, C., Jacquier, G., Martinet, Y., Mathias, E., Nguyen, V., Oudart, B., Serveau, L. & Vincent, J., 2008: Organisation et méthodes des inventaires nationaux des émissions atmosphériques en France, 5 ème édition, Available at: http://www.citepa.org/publications/OMINEA_5e_edition_fev2008.zi p (French). Guidebook, 2007: EMEP/Corinair Emission Inventory Guidebook 2007, Technical report No 16/2007. Available at: http://www.eea.europa.eu/publications/EMEPCORINAIR5/B991vs1. 1.pdf Guidebook, 2009: EMEP/EEA air pollutant emission inventory guidebook – 2009, Technical report No 6/2009. Available at: http://www.eea.europa.eu/publications/emep-eea-emissioninventory-guidebook-2009/part-b-sectoral-guidance-chapters/6waste/6-c/6-c-d-cremation-tfeip-endorsed-draft.pdf Heldstab, J. & Kasser, F., 2008: Switzerland’s Informative Inventory Report 2008. Submission under the UNECE Convention on Long-range Transboundary Air Pollution. Available at: http://webdab.umweltbundesamt.at/download/submissions2008/CH _IIR2008.zip?cgiproxy_skip=1 Henriksen, T.C., Illerup, J.B. & Nielsen, O.-K., 2006: Dioxin Air Emission Inventory 1990-2004. National Environmental Research Institute, Denmark. 90 pp. – NERI Technical report no 602. Available at: http://www.dmu.dk/Pub/FR602.pdf KM, 2006: Arbejdsgruppe foreslår, at der skal være færre krematorier Ministry of Ecclesiastical Affairs, december 2006. Available at: http://www.km.dk/generelle-sider/nyheder/singlenews/arbejdsgruppe-foreslaar-at-der-skal-vaere-faerrekrematorier/2.html (Danish). Kriegbaum, M. & Jensen, E., 2005: Input til branchebilag for krematorieanlæg, Kommentarer og begrundelser, Dato 23. september 2005. Available at: www.mst.dk/NR/rdonlyres/926C2D8E-5B8A-4828-86E9- BF3B672184F9/0/060116Inputkrematorieanlæg.doc (Danish). NAEI, 2007: National Atmospheric Emission Inventory Website of the UK, Available at: http://www.sciencedirect.com/science?_ob=MImg&_imagekey=B6V7 4-4BRSD1W-1- 8&_cdi=5832&_user=642076&_pii=S0045653504000463&_orig=search&_ cover- 289
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ANNUAL DANISH INfORMATIVE INVENTORY
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AU ANNUAL DANISH INfORMATIVE INVENT
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&RQWHQWV 6XPPDU\ , %DFNJURXQG LQIRU
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Annex 2A-11 QA/QC for stationary co
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8 ,, 7UHQGV LQ HPLVVLRQV $FLGLI\LQJ
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10 reduced emissions is mainly incr
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12 Danish energy statistics have, f
Page 16 and 17:
14 ,QGXVWULDO SURFHVVHV Recalculati
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16 ,, 8GYLNOLQJHQ L HPLVVLRQHU )RUV
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18 kilde til emission af kobber er
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20 6¡IDUW Brændselsforbrug for sk
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22 en stigning i NH3 emissionen for
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24 UNECE-LRTAP Convention of the An
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26 Table 1.1 List of current data s
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28 A list of all subsectors at the
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30 )XJLWLYH HPLVVLRQV IURP QDWXUDO
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32 Please refer to Chapter 5 for fu
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34 Table 1.2 Danish uncertainty est
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36 NR is used for pollutants prior
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38 ��Ã�� Acid-
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40 ��Ã��
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42 ��Ã��
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44 �� Industrial Processes 1% N
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46 �Ã�� Non-industrial
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48 Table 3.1 NFR source categories
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50 (PLVVLRQ VRXUFH FDWHJRULHV In th
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52 Fuel consumption, PJ Fuel consum
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54 sumption in ,QGXVWU\ in 2009 add
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56 (PLVVLRQV 62� Stationary combu
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58 the reduced emission from electr
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60 NMVOC, Gg 25 20 15 10 5 0 1990 1
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62 The primary sources of PM emissi
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64 PM, Gg PM 2.5, Gg 30 25 20 15 10
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66 Table 3.11 Decrease in heavy met
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68 3$+ Stationary combustion plants
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70 Benzo(a)pyrene Benzo(a)pyrene, M
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72 plants has increased due to incr
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74 Fuel consumption, PJ SO2, Gg____
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As, Mg_____ Cd, Mg_____ Cr, Mg_____
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78 SO2, Gg____ NOx, Gg_____ Fuel co
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82 Fuel consumption, PJ 90 80 70 60
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84 As, Mg_____ 0.00 0.05 0.10 0.15
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86 Fuel consumption, PJ 1A4 Other S
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88 As, Mg Cd, Mg Cr, Mg Cu, Mg Hg,
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94 software for inventories. The me
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96 Both traded and non-traded fuels
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98 ƒ Christiansen et al. (1997).
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100 The emission factors for decent
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102 Table 3.19 Danish uncertainty e
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104 Danish Energy Agency (DEA), 201
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106 Miljøstyrelsen (MST), 2010: An
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108 Table 3.20 SNAP - NFR correspon
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110 sumption development is due to
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112 these types of machinery, the D
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114 � � 5 4,5 4 3,5 3 2,5 2 1,5
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116 Table 3.22 Emissions of SO2, NO
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118 7RQQHV 600000 500000 400000 300
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120 7RQQHV 8000 7000 6000 5000 4000
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122 The TSP emission development fo
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124 Residential (1A4b) 0% Agr./for.
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126 Table 3.24 Heavy metal emission
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128 Navigation (1A3d) 79% Navigatio
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130 Table 3.25 Dioxin and PAH emiss
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132 Residential (1A4b) 2% Railways
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134 0HWKRGRORJLFDO LVVXHV The descr
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136 1200 1000 � � Ã � 800 Ã
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138 2000 � 1600 � Ã� Ã� 1
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140 Table 3.28 Overview of the exis
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142 8') 8 ⋅ 07& + 8 = , MTC < UMA
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144 (YDSRUDWLYH HPLVVLRQV IURP JDVR
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146 The final fuel use and emission
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148 Figure 3.87 Most frequent domes
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150 No. No. 30000 25000 20000 15000
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152 [No] 4500 4000 3500 3000 2500 2
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154 ��
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156 Table 3.30 Domestic ferry route
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158 national sea transport in the D
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160 Table 3.32 Overview of the EU E
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Table 3.35 Current certification li
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164 Table 3.37 Current legislation
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166 Table 3.38 Fuel based emission
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168 1RQ URDG ZRUNLQJ PDFKLQHU\ DQG
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170 ( = )& ⋅ () (27) where E = em
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172 tions, transport to Greenland a
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174 5RDG WUDQVSRUW The total mileag
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176 Delvig, P. 2010: Unpublished da
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178 Winther, M. 2005: Kyoto notat -
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180 Table 3.41 Summary of the Danis
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182 2IIVKRUH DFWLYLWLHV Fugitive em
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184 Coal import, Gg . 16000 14000 1
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186 gasoline sales show an increase
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188 Venting in gas treatment and st
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190 and Kilde (1994) for the years
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192 Table 3.48 Emission factors for
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194 Table 3.54 Emissions of NMVOC f
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196 and initialisation of new facil
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198 Table 3.59 Estimated emission u
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200 Extraction of oil and gas: fugi
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202 OleQGU\ QVNL � ' EVNL % 6NR V
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204 Table 4.1 Survey of industrial
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206 Table 4.2 Time-series for pollu
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208 financial crises. During the sa
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210 1 1 1 1 1 0 0 0 0 0 &KHPLFDO LQ
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212 they have not been subject to t
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214 Denmark. The emission of TSP an
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216 Table 4.3 Emission factors for
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218 2WKHU SURGXFWLRQ FRQVXPSWLRQ VW
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220 Nielsen, O.-K., Lyck, E., Mikke
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222 products is derived from Table
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224 kt NMVOC/year 60 50 40 30 20 10
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226 tained from the respective comp
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228 over several years so there wil
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230 8QFHUWDLQWLHV DQG WLPH VHULHV F
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232 powder consists of about 75 % o
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234 Passant et al. (2003) and Fyrve
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236 Table 5.9 Emission from firewor
Page 240 and 241: 238 sumentfyrverkerier, Miljö Göt
Page 242 and 243: 240 $JULFXOWXUH 1)5 VHFWRU 2YHUYLHZ
Page 244 and 245: 242 Another important cause of the
Page 246 and 247: 244 The emissions from agricultural
Page 248 and 249: 246 Table 6.3 Livestock categories
Page 250 and 251: 248 Table 6.4 Livestock production
Page 252 and 253: 250 creasing. This is due to measur
Page 254 and 255: 252 Table 6.7 Activity data used to
Page 256 and 257: 254 Table 6.10 Activity data used t
Page 258 and 259: 256 Table 6.13 Livestock categories
Page 260 and 261: 258 Table 6.16 PM emission from hou
Page 262 and 263: 260 swine production, etc to optimi
Page 264 and 265: 262 ning, as given in the CLRTAP Em
Page 266 and 267: 264 implemented NH3 reduction techn
Page 268 and 269: 266 :DVWH 1)5 VHFWRU The waste sect
Page 270 and 271: 268 0HWKRGRORJ\ +XPDQ FUHPDWLRQ The
Page 272 and 273: 270 Even though the total number of
Page 274 and 275: 272 statistic data show an increase
Page 276 and 277: 274 an emission factor of 28 µg pr
Page 278 and 279: 276 Table 7.8 Emission factors for
Page 280 and 281: 278 Table 7.9b Total national emiss
Page 282 and 283: 280 Table 7.10a Total national emis
Page 284 and 285: 282 Table 7.11 Estimated uncertaint
Page 286 and 287: 284 Table 7.13 Overview of yearly s
Page 288 and 289: 286 Data Processing level 1 1. Accu
Page 292 and 293: 290 Date=06%2F30%2F2004&_sk=9994499
Page 294 and 295: 292 Amount composted, Gg 1200 1000
Page 296 and 297: 294 • 50 kg waste pr year will in
Page 298 and 299: 296 Affaldsstatistik 2007 og 2008 (
Page 300 and 301: 298 and 5 % of a large fire respect
Page 302 and 303: 300 for fire-fighting and will typi
Page 304 and 305: 302 Table 7.21 Different types of n
Page 306 and 307: 304 Table 7.22 Average vehicle mass
Page 308 and 309: 306 Table 7.23 Emission factors bui
Page 310 and 311: 308 material estimated in Persson e
Page 312 and 313: 310 Table 7.26 Emission factors veh
Page 314 and 315: Table 7.27a National emissions from
Page 316 and 317: 314 Table 7.28b National emissions
Page 318 and 319: 316 UNEP toolkit, 2005: United Nati
Page 320 and 321: 318 4$ 4& DQG YHULILFDWLRQ 4$ 4& SU
Page 322 and 323: 320 These references exist in the d
Page 324 and 325: 322 Data Processing level 1 For the
Page 326 and 327: 324 2WKHU DQG QDWXUDO HPLVVLRQV Den
Page 328 and 329: 326 similar methodology was used fo
Page 330 and 331: 328 the localisation of the Danish
Page 332 and 333: 330 • The national energy statist
Page 334 and 335: 332 the Energy Statistics for 2009
Page 336 and 337: 334 $QQH[ ± �H\ FDWHJRU\ DQDO\VL
Page 338 and 339: 336 $QQH[ $ ,3&& 61$3 VRXUFH FRUUHV
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338 $QQH[ $ )XHO UDWH Table 2A-2.1
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340 Table 2A-2.2 Detailed fuel cons
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342 ��Ã
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344 ��Ã
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346 ��Ã
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348 ��Ã
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Table 56 Time-series for calorific
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$QQH[ $ (PLVVLRQ IDFWRUV Table 2A-4
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14. Danish Gas Technology Centre 20
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pollutant fuel_type fuel nfr nfr_na
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Table 2A-4.4a PM emission factors,
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Table 2A-4.5 HM emission factors (m
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378 Ã ÃÃ ÃÃ ÃÃ ÃÃ Benzo(a)
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Table 2A-4.9a PAH emission factors
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Table 2A-4.9b PAH emission factors
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Table 2A-4.10 Dioxin and HCB emissi
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Table 2A-4.11a Dioxin and HCB emiss
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Table 2A-4.12 NH3 emission factors
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$QQH[ $ /DUJH SRLQW VRXUFHV Table 2
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02 MUNICIP. WASTES 44 STRAW 25 Hade
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396 national emissions in year t du
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398 ��Ã S
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400 ��Ã S
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402 ��Ã S
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406 • Monthly reporting by e-mail
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408 ��Ã��Ã �
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410 ��Ã��Ã �
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412 $QQH[ $ 7LPH VHULHV Fuel consum
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Table 6.1 List of external data sou
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416 however, included in the refere
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418 Data Processing level 1 3.Compl
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420 Some automated checks have been
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Annual working hours, load factors
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Stock data for household and garden
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Stock data for small boats and plea
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Ferry data: Sailing time (single tr
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Uncertainty estimation, Chromium. 5
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Uncertainty estimation, Lead. 582 G
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Uncertainty estimation, Flouranthen
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Uncertainty estimation, Benzo(g,h,i
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588 Table 2C.1a Nitrogen excretion
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590 (PLVVLRQ RI 1+ � +RXVLQJ The
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592 $QQH[ & %DFNJURXQG LQIRUPDWLRQ
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594 $QQH[ & %DFNJURXQG LQIRUPDWLRQ
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598 Emissions from clinical, indust
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