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

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200 Extraction of oil and gas: fugitive emissions from extraction are calculated from the standard formula in the EMEP/EEA Guidebook (EMEP/EEA, 2009) based on the number of platforms. In 2009 the number of platforms has been corrected for 2007 and 2008. The NMVOC emission in 2008 has decreased by 20 Mg according to this correction corresponding to 1 %. Gas distribution: distribution amounts have been updated for one of three natural gas distribution companies for the years 2006-2008 due to new data availability. The NMVOC emission has decreased by 4 Mg in 2008 due to this corresponding to 10 %. Flaring in oil and gas extraction: The NMVOC emission in 2008 from flaring in the gas treatment plant has been updated for 2008 according to the environmental report leading to an increase of 2 Mg NMVOC. The increase corresponds to 12 % of the NMVOC emission from flaring in oil and gas extraction including offshore flaring 6RXUFH VSHFLILF SODQQHG LPSURYHPHQWV The following future improvements are suggested. Emissions from storage of fuels in tank facilities: The recent edition of the Danish emission inventory holds emissions from extraction of fuels, combustion of fuels and from service stations. To make the inventory complete emissions from storage of fuels in tank facilities should be included in the future if data is available. Work is going on to locate greater tank facilities in Denmark and collect the available data. In cases where no emission estimates or measurements are available a set of emission factors have to be set up. Emissions from offshore extraction of oil and gas: The fugitive emissions from extraction of oil and gas are based on a standard formula. If a better estimate becomes available it will be implemented. D 5HIHUHQFHV IRU IXJLWLYH HPLVVLRQV &KDSWHU A/S Dansk Shell, 2010: Annual environmental report 2008. Danish Energy Agency, 2010a: Oil and Gas Production in Denmark 2007. Available at: http://ens.dk/da- DK/UndergrundOgForsyning/Olie_og_gas/RapOlieGas/Sider/Forsid e.aspx (17-12-2010). Danish Energy Agency, 2010b: The Danish energy statistics (Energistatistik) (in Danish). Available at: http://www.ens.dk/da- DK/Info/TalOgKort/Statistik_og_noegletal/Aarsstatistik/Sider/Forsi de.aspx (17-12-2010). Danish Environmental Protection Agency, 2008: Emissionsfaktorer for NOx-emissioner fra flaring fra platforme i Nordsøen (in Danish). Not published.
DONG Energy, 2010a: Annual environmental reports from DONG Energy for Nybro gas treatment plant and Stenlille gas storage plants (in Danish). Available at: http://www.dongenergy.com/da/ansvarlighed/rapportering/pages/ gronne_regnskaber.aspx and http://gaslager.energinet.dk/DA/Omgaslageret/Sider/Groent-regnskab.aspx (17-12-2010). DONG Energy, 2010b: Annual environmental reports from DONG Energy for Oil Terminals, Fredericia (in Danish). DONG Energy, 2010c: Annual reports 2009 (in Danish). Available at: http://www.dongenergy.com/SiteCollectionDocuments/Koncernregn skab/2009/Q4/DONG_ENERGY_DK_A4.PDF (17-12-2010). EMEP/EEA, 2009: Air emission inventory guidebook, prepared by the UNECE/EMEP Task Force on Emission Inventories and Projections, 2009 update. Available at: http://www.eea.europa.eu/publications/emep-eea-emissioninventory-guidebook-2009 (17-12-2010). Energinet.dk, 2010a: Annual report 2009 for Lille Torup gas storage plant (in Danish). Available at: http://www.e-pages.dk/energinet/190/ (17-12-2010). Energinet.dk, 2010b: Environmental Report 2009. Available at: http://energinet.dk/EN/KLIMA-OG- MILJOE/Environmental%20reporting/Sider/default.aspx (17-12-2010). Fenhann, J., & Kilde, N.A., 1994: Inventory of Emissions to the Air from Danish Sources 1972-1992. Risø National Laboratory, Roskilde, Denmark. 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 on the internet at: http://www.dmu.dk/Pub/FR602.pdf (17-12-2010). IPCC, 2000: Good Practice Guidance and Uncertainty Management in National Greenhouse Gas Inventories. Available at: http://www.ipccnggip.iges.or.jp/public/gp/english/ (17-12-2010). Karll, B. 2003: Personal communication, e-mail 17-11-2003, Danish Gas Technology Centre. Karll, B. 2005: Personal communication, e-mail 09-11-2005, Danish Gas Technology Centre. Oertenblad, M. 2006: personal communication, e-mail 2006, Danish Gas Technology Centre. Oertenblad, M. 2007: personal communication, e-mail 2007, Danish Gas Technology Centre. 201
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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
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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
Page 152 and 153: 150 No. No. 30000 25000 20000 15000
Page 154 and 155: 152 [No] 4500 4000 3500 3000 2500 2
Page 156 and 157: 154 ��
Page 158 and 159: 156 Table 3.30 Domestic ferry route
Page 160 and 161: 158 national sea transport in the D
Page 162 and 163: 160 Table 3.32 Overview of the EU E
Page 164 and 165: Table 3.35 Current certification li
Page 166 and 167: 164 Table 3.37 Current legislation
Page 168 and 169: 166 Table 3.38 Fuel based emission
Page 170 and 171: 168 1RQ URDG ZRUNLQJ PDFKLQHU\ DQG
Page 172 and 173: 170 ( = )& ⋅ () (27) where E = em
Page 174 and 175: 172 tions, transport to Greenland a
Page 176 and 177: 174 5RDG WUDQVSRUW The total mileag
Page 178 and 179: 176 Delvig, P. 2010: Unpublished da
Page 180 and 181: 178 Winther, M. 2005: Kyoto notat -
Page 182 and 183: 180 Table 3.41 Summary of the Danis
Page 184 and 185: 182 2IIVKRUH DFWLYLWLHV Fugitive em
Page 186 and 187: 184 Coal import, Gg . 16000 14000 1
Page 188 and 189: 186 gasoline sales show an increase
Page 190 and 191: 188 Venting in gas treatment and st
Page 192 and 193: 190 and Kilde (1994) for the years
Page 194 and 195: 192 Table 3.48 Emission factors for
Page 196 and 197: 194 Table 3.54 Emissions of NMVOC f
Page 198 and 199: 196 and initialisation of new facil
Page 200 and 201: 198 Table 3.59 Estimated emission u
Page 204 and 205: 202 OleQGU\ QVNL � ' EVNL % 6NR V
Page 206 and 207: 204 Table 4.1 Survey of industrial
Page 208 and 209: 206 Table 4.2 Time-series for pollu
Page 210 and 211: 208 financial crises. During the sa
Page 212 and 213: 210 1 1 1 1 1 0 0 0 0 0 &KHPLFDO LQ
Page 214 and 215: 212 they have not been subject to t
Page 216 and 217: 214 Denmark. The emission of TSP an
Page 218 and 219: 216 Table 4.3 Emission factors for
Page 220 and 221: 218 2WKHU SURGXFWLRQ FRQVXPSWLRQ VW
Page 222 and 223: 220 Nielsen, O.-K., Lyck, E., Mikke
Page 224 and 225: 222 products is derived from Table
Page 226 and 227: 224 kt NMVOC/year 60 50 40 30 20 10
Page 228 and 229: 226 tained from the respective comp
Page 230 and 231: 228 over several years so there wil
Page 232 and 233: 230 8QFHUWDLQWLHV DQG WLPH VHULHV F
Page 234 and 235: 232 powder consists of about 75 % o
Page 236 and 237: 234 Passant et al. (2003) and Fyrve
Page 238 and 239: 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
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250 creasing. This is due to measur
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252 Table 6.7 Activity data used to
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254 Table 6.10 Activity data used t
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256 Table 6.13 Livestock categories
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258 Table 6.16 PM emission from hou
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260 swine production, etc to optimi
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262 ning, as given in the CLRTAP Em
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264 implemented NH3 reduction techn
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266 :DVWH 1)5 VHFWRU The waste sect
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268 0HWKRGRORJ\ +XPDQ FUHPDWLRQ The
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270 Even though the total number of
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272 statistic data show an increase
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274 an emission factor of 28 µg pr
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276 Table 7.8 Emission factors for
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278 Table 7.9b Total national emiss
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280 Table 7.10a Total national emis
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282 Table 7.11 Estimated uncertaint
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284 Table 7.13 Overview of yearly s
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286 Data Processing level 1 1. Accu
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288 Data Storage level 2 The full d
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290 Date=06%2F30%2F2004&_sk=9994499
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292 Amount composted, Gg 1200 1000
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294 • 50 kg waste pr year will in
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296 Affaldsstatistik 2007 og 2008 (
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298 and 5 % of a large fire respect
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300 for fire-fighting and will typi
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302 Table 7.21 Different types of n
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304 Table 7.22 Average vehicle mass
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306 Table 7.23 Emission factors bui
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308 material estimated in Persson e
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310 Table 7.26 Emission factors veh
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Table 7.27a National emissions from
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314 Table 7.28b National emissions
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316 UNEP toolkit, 2005: United Nati
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318 4$ 4& DQG YHULILFDWLRQ 4$ 4& SU
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320 These references exist in the d
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322 Data Processing level 1 For the
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324 2WKHU DQG QDWXUDO HPLVVLRQV Den
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326 similar methodology was used fo
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328 the localisation of the Danish
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330 • The national energy statist
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332 the Energy Statistics for 2009
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334 $QQH[ ± �H\ FDWHJRU\ DQDO\VL
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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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CH4 shares of VOC for diesel, gasol
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Annual working hours, load factors
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Operational data for the most impor
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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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