Report - DCE - Nationalt Center for Miljø og Energi

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Ã '($ 1(5, IXHO UDWLR 1,30 1,25 1,20 1,15 1,10 1,05 1,00 0,95 )XHO VFDOH IDFWRUV EDVHG RQ IXHO FRQVXPSWLRQ 1985 1987 1989 1991 1993 1995 1997 1999 2001 2003 2005 2007 2009 Gasoline Diesel ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃÃ In the figures 3.85 and 3.86 the COPERT IV:DEA gasoline and diesel fuel use ratios are shown for fuel sales and fuel consumption from 1985-2010. The data behind the figures are also listed in Annex 3.B.8. The fuel consumption figures are related to the traffic on Danish roads by Danish vehicles and foreign trucks. Pr fuel type, all mileage numbers are equally scaled in order to obtain fuel equilibrium, and hence the mileage factors used are the reciprocal values of the COPERT IV:DEA fuel consumption: fuel sales ratio. The reasons for the differences between DEA sales figures and bottom-up fuel estimates are mostly due to a combination of the uncertainties related to COPERT IV fuel consumption factors, allocation of vehicle numbers in subcategories, annual mileage, trip speeds and mileage splits for urban, rural and highway driving conditions. The final fuel consumption and emission factors are shown in Annex 2.B.7 for 1985-2010. The total fuel consumption and emissions are shown in Annex 2.B.8, pr vehicle category and as grand totals, for 1985-2010 (and NFR format in Annex 2.B.16. In Annex 2.B.15, fuel consumption and emission factors as well as total emissions are given in CollectER format for 2010. In Table 3.29, the aggregated emission factors for SO2, NOX, NMVOC and TSP are shown in CollectER format for Danish road transport.
Ã ÃÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃÃÃÃÃÃ ÉÃ ÃÃ Ã ÃÃ Ã ÃÃÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃ /PO FYIBVTU QBSUJDVMBUF FNJTTJPOT GSPN SPBE USBOTQPSU The TSP, PM10 and PM2.5 emissions arising from tyre and brake wear (SNAP 0707) and road abrasion (SNAP 0708) are estimated for the years 2000-2010 as prescribed by the UNECE convention reporting format. The emissions are calculated by multiplying the total annual mileage pr vehicle category with the correspondent average emission factors for each source type. The calculation procedure is consistent with the COPERT IV model approach used to estimate the Danish national emissions coming from exhaust. A more thorough explanation of the calculations is given by Winther and Slentø (2010). Emission factors are taken from EMEP/EEA (2009) and specific Danish tyre wear data are gathered by Winther and Slentø (2010). The emission factors and total emissions for 2010 are shown in Annex 2.B.15. FUIPEPMPHJFT BOE SFGFSFODFT GPS PUIFS NPCJMF TPVSDFT Other mobile sources are divided into several sub-sectors: sea transport, fishery, air traffic, railways, military, and working machinery and materiel in the industry, forestry, agriculture and household and gardening sectors. The emission calculations are made using the detailed method as described in the EMEP/EEA Air Pollutant Emission Inventory Guidebook
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ANNUAL DANISH INFORMATIVE INVENTORY
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AU ANNUAL DANISH INFORMATIVE INVENT
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$POUFOUT "DLOPXMFEHFNFOUT 4VNNBSZ *
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0UIFS BJS QPMMVUBOUT /PO NFUIBOF WP
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Wood combustion in residential plan
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to an error F28 was previously used
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eduction in emission of about 50 %
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elative bidrag for SO2, NOx og NH3
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holdningsanlæg (78 % i 2010). Emis
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tige syn i 2008. Opdaterede oplysni
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*OUSPEVDUJPO #BDLHSPVOE JOGPSNBUJPO
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QA/QC plan (Chapter 1.5), the data
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of round trips per ferry, engine si
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sion. Simple mass balances for calc
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The Other Waste category includes c
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Ã *OEVTUSJBM QSPDFTTFT Categories
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Nielsen, O.-K., Mikkelsen, M.H., Ho
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42 Figure 2.1 Emissions of NH3, NOX
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44 Figure 2.4 NH3 emissions. Distri
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46 Figure 2.8 PM2.5 emissions. Dist
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48 Figure 2.11 Pb emissions. Time s
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&OFSHZ /'3 TFDUPS 0WFSWJFX PG UIF T
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Table 3.2 SO2, NOx, NMVOC, CO and P
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Ã ÃÃÃÃ 1A1c Manufacture of sol
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Fuel consumption, PJ Fuel consumpti
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creased 6 % since 2009. The biomass
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&NJTTJPOT 40 Stationary combustion
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emission from electricity and heat
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NMVOC, Gg 25 20 15 10 5 0 1985 1986
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accounting for 94 % of the PM2.5 em
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PM, Gg PM 2.5, Gg 30 25 20 15 10 5
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ÃÃÃÃÃÃÃÃÃÃ Ã ÃÃÃÆÃ
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Ã Ã 1") Stationary combustion pla
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Ã Ã Ã Ã %JPYJO Stationary combu
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Ã ÃÃÃÃÃÃÃÃÃÃ Ã ÃÃ Ã
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200 180 Ã 160 140 120 100 80 60
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Ã 0.025 0.020 Ã 0.015 Ã 0.010
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Ã Ã 25 20 Ã Ã 15 10 Ã
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The total fuel consumption in indus
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0.4 Ã 0.3 Ã 0.2 0.1 Ã Ã
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0.035 0.030 0.025 Ã 0.020 Ã 0.0
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Ã 0.30 Ã Ã 0.25 0.20
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Ã 6 Ã Ã 5 4 3 Ã
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Ã 60 Ã Ã 50 40 30 Ã
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14 12 Ã 10 8 6 4 2 0 10
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120 Ã 100 80 60 Ã 40
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Page 106 and 107: • Emission data reported from ind
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Page 110 and 111: • Research carried out by TNO (Be
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Page 114 and 115: Christiansen, B.H., Evald, A., Baad
Page 116 and 117: Danish Environmental Protection Age
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Page 150 and 151: For all vehicle categories/technolo
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Page 158 and 159: Agricultural tractors (diesel) < 80
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Page 162 and 163: Ã ÃÃÃÉÃÃÃ The 1985-2010 sto
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Page 170 and 171: total emissions (in grams) from the
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Page 176 and 177: Where FC = fuel consumption (kg), m
Page 178 and 179: Where EEvap,fueling, = hydrocarbon
Page 180 and 181: For gasoline, the DEA residential s
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• Check of units for fuel rate, e
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4PVSDF TQFDJGJD SFDBMDVMBUJPOT In t
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Fenhann, J. & Kilde, N.A. 1994: Inv
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emission factor based on 2000 figur
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Danish Foundries. The emission of T
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Ã FUIPEPMPHJDBM JTTVFT The emissio
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Ã 0UIFS QSPEVDUJPO DPOTVNQUJPO TUP
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IPCC, 1997: Revised 1996 IPCC Guide
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228 Emission modelling of solvents
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230 ends in waste water, e.g. ethan
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Ã Ã Ã Ã 232 ÃÃÃÃÃÃÃÃÃ
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234 ÃÃÃÃÃÃÃÃÃ Ã ÃÃ ÃÃ
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238 confidentiality or that the amo
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240 • Inclusion of NMVOC use and
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242 Oertzen, Bundesanstalt für Mat
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only 18 % and 5 % respectively. Mos
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DCE - the Danish Centre for Environ
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Ã 100 90 80 70 60 50 40 30 20 10
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Ã The implied emission factors rel
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EEA guidebook (EMEP/EEA, 2009) defa
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ased on EMEP/EEA guidebook. All unc
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The emission of NMVOC from crops ha
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Ã Ã ity from these facilities. Th
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ANNUAL DANISH INFORMATIVE INVENTORY
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