Report - DCE - Nationalt Center for Miljø og Energi

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Ã Ã Ã Ã Ã Ã Ã Ã Ã ÉÃ ÃÃ Ã Ã Ã Ã ÉÃ ÃÃ Ã Ã Ã Ã ÉÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã ÉÃ ÃÃ Ã Ã Ã Ã ÉÃ ÃÃ Ã Ã Ã Ã ÉÃ ÃÃ Ã Ã Ã Ã ÉÃ ÃÃ Ã ÃÃÃÃÃÃÃÃÃÃ ÃÃÃÃÃ Ã FUIPEPMPHJDBM JTTVFT The following chapters give descriptions on the methods of calculation used in the Danish emission inventory. Further, the activity data and emission factors that form the basis for the calculations are described according to data source and values. 'VHJUJWF FNJTTJPOT GSPN TPMJE GVFMT The emissions of particulate matter from storage of coal are estimated on basis of the imported amount of coal (equation 3.4.1). ( ⋅ , _ = (0) _ where EMFcoal_storage is the emission factor for storage of coal in coal piles and Icoal is the amount of coal imported in the actual year. 'VHJUJWF FNJTTJPOT GSPN PJM The emissions from oil derive from offshore activities, service stations and refineries. Emissions from offshore activities include emissions from extraction, onshore oil tanks and onshore and offshore loading of ships. In the case of service stations emissions from reloading of tankers and refuelling of vehicles are included. The emissions from refineries derive from petroleum products processing (oil refining). Emissions from flaring in refineries are included in the chapters concerning flaring. &R
0GGTIPSF BDUJWJUJFT Fugitive emissions from oil include emissions from offshore extraction, from onshore oil tanks and from onshore and offshore loading of ships. The total emission can be expressed as: ( ( + ( + ( = &R Ã Fugitive emissions from extraction According to the EMEP/EEA Guidebook (EMEP/EEA, 2009) the total fugitive emissions of volatile organic components (VOC) from extraction of oil and gas can be estimated by means of equation 3.4.3. ( = . 2⋅ 1 + 1. 1⋅10 3 + 8. 5⋅10 ⋅ 3 , 40 &R −2 −6 where Eextraction,VOC is the emission of VOC in Mg/year, NP is the number of platforms, Pgas is the production of gas, 10 6 Nm 3 and Poil is the production of oil, 10 6 tonnes. It is assumed that the VOC contains 75 % CH4 and 25 % NMVOC and in consequence the total emission of NMVOC for extraction of oil and gas can be calculated as: ( , 0. 25 ⋅ ( , = &R -PBEJOH PG TIJQT Fugitive emissions of NMVOC from loading of ships include the transfer of oil from storage tanks or directly from the well into ships. The activity also includes losses during transport. When oil is loaded hydrocarbon vapour will be displaced by oil and new vapour will be formed, both leading to emissions. The emissions from ships are calculated by equation 3.4.5. ( (0) , ⋅/ , + (0) , ⋅/ , = &R where EMFships is the emission factor for loading of ships and Loil is the amount of oil loaded. 0JM UBOLT The NMVOC emissions for storage of oil are given in the environmental reports from DONG Oil Pipe for 2010 (DONG Oil Pipe A/S, 2011). An implied emission factor is calculated on the basis of the amount of oil transported in pipelines according to equation 3.4.6. ,() ( ÷ 7 = &R where IEFtanks is the implied emission factor for storage of raw oil in tanks, Etanks is the emission and Toil is the amount of oil transported in pipelines. 4FSWJDF TUBUJPOT NMVOC emissions from service stations are estimated as outlined in equation 3.4.7. Ã ( (0) ⋅7 ) + ( (0) 7 ) ( ⋅ = &R
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ANNUAL DANISH INFORMATIVE INVENTORY
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AU ANNUAL DANISH INFORMATIVE INVENT
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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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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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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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120 Ã 100 80 60 Ã 40
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16 Ã 14 12 10 8 Ã 6
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• Emission data reported from ind
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Due to the scarce data available an
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• Research carried out by TNO (Be
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Ã ÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã
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Christiansen, B.H., Evald, A., Baad
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Danish Environmental Protection Age
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Ã 160 140 120 100 80 60 40 20 0
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3- 5 4,5 4 3,5 3 2,5 2 1,5 1 0,5 0
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Ã Ã Ã Ã ment in emission factor
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ÃÉÃ ÃÉÃ Passenger cars 69% 2-
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Page 156 and 157: (EMEP/EEA, 2009) for air traffic, o
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ANNUAL DANISH INFORMATIVE INVENTORY
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