Report - DCE - Nationalt Center for Miljø og Energi

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0 Ã The major GNFR source to NOx emissions is RoadRail followed by Shipping, OffRoadMob, PublicPower and IndustrialComb contributing 36 %, 16 %, 15 %, 15 % and 11 %, respectively. The pattern of the gridded NOx emissions reflect the major road and rail network located in the eastern part of Jutland and across Funen and Zealand to Copenhagen (figure 8.2). Further, large emissions from PublicPower and IndustrialComb are allocated to areas around the major cities. /70$ The major source of NMVOC is Solvents followed by SmallComb, RoadRail, OffRoadMob and Fugitive contributing 31 %, 18 %, 15 %, 11 % and 11 %, respectively. Both emissions from Solvents, SmallComb and OffRoadMob are to a large degree allocated according to population density and location of one-storey settlements. Part of the fugitive emissions is located offshore due to extraction of oil and gas on the North Sea. 40 The major sources of SO2 are PublicPower and IndustrialComb followed by SmallComb and Shipping contributing 27 %, 26 %, 19 %, and 13 %, respectively. Even though the SO2 emission has decreased over the years due to implementation of techniques for reduction of sulphur in the flue gas, it still produces a distinct pattern reflecting the localisation of large power plants in Denmark. The allocation of emissions from IndustrialComb and SmallComb reflect the location of a large number of CHP plants not reported as LPS due to no plant specific emission factors, and the areas with high population density and mainly one-storey settlements. For the ferries operating between Copenhagen and Bornholm part of the route is outside the Danish EEZ. The emissions from all these ferries are included in Shipping and distributed on the part of the straight line between Copenhagen and Bornholm inside the Danish EEZ. This leads to an aggregation of the emissions in few EMEP cells, and thereby artificial high emissions at the part of the route inside EEZ. /) The agricultural sector is by far the major contributor to the NH3 emission. 81 % of the national emissions excluding civil aviation and international navigation derive from AgriLivestock and another 15 % from AgriOther. Emission of NH3 is mainly related to livestock farming and especially to manure management. Emissions are distributed according to very detailed data on animals and fields, and the geographical pattern is in good agreement with the localisation of the major Danish livestock farming in Jutland. 1 The major source of PM2.5 emissions is SmallComb contributing 73 %. Road- Rail is the second largest source contributing 10 % of the PM2.5 emission. Emissions from SmallComb are allocated rather evenly on the land area as a major source is residential wood combustion. Emissions from the residential sector are distributed on municipality level leading to equal emissions for larger areas. Further emissions from CHP plants are located in all parts of the country, also leading to a rather even distribution. 1")T Emissions of PAHs are the sum of benzo(b)flouranthene, benzo(k)flouranthene, benzo(a)pyrene and indeno(1,2,3-c,d)pyrene. The ma-
Ã jor source to PAH emissions in Denmark is SmallCombustion and hereof the all-important source is residential wood combustion. As described for PM2.5 the distribution are made on municipality level leading to a rather even distribution on the land area. 'JHVSF BQ PG %FONBSL JODMVEJOH OBNFT PG SFHJPOT BOE UIF &YDMVTJWF &DPOPNJD ;POF 3FGFSFODFT EMEP/EEA, 2009: EMEP/EEA air pollutant emission inventory guidebook 2009. Technical guidance to prepare national emission inventories. EEA Technical Report 9/2009. Available at: http://www.eea.europa.eu/publications/emep-eea-emissioninventoryguidebook-2009 (10-02-2011). Plejdrup, M.S. & Gyldenkærne, S. 2011: Spatial distribution of emissions to air – the SPREAD model. National Environmental Research Institute, Aarhus University, Denmark. 72 pp. – NERI Technical Report no. FR823. Available at: http://www.dmu.dk/Pub/FR823.pdf UNECE (2009). Guidelines for estimating and reporting emission data under the Convention on Long-range Transboundary Air Pollution (ECE/EB.AIR/97). Available at http://www.ceip.at/fileadmin/inhalte/emep/reporting_2009/Rep_Guideli nes_ECE_EB_AIR_97_e.pdf
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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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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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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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6 5 4 Ã Ã 3 2 É 1 0 6
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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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5SBOTQPSU BOE PUIFS NPCJMF TPVSDFT
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Ã 160 140 120 100 80 60 40 20 0
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Ã Ã Gasoline PC 36% Gasoline LDV
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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 7RQQHV 8000 7000 6000 5000 4000
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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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Ã Ã Ã Ã 7RQQHV 250000 200000 15
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Ã Ã Ã Residential (1A4b) 2% Rail
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Ã 1200 1000 Ã 800 Ã 600 Ã
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Ã 2000 1600 Ã Ã 1200 Ã 800
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Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ
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For all vehicle categories/technolo
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For catalyst vehicles the cold extr
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Ã '($ 1(5, IXHO UDWLR 1,30 1,25 1,
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(EMEP/EEA, 2009) for air traffic, o
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Agricultural tractors (diesel) < 80
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Ã ÃÃ No. 12000 10000 8000 6000 4
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Ã ÃÃÃÉÃÃÃ The 1985-2010 sto
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Ã
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Ã 1R RI URXQG WULSV 1R RI URXQG WU
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Ã &NJTTJPO MFHJTMBUJPO For non-roa
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total emissions (in grams) from the
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Ã Further, the Marine Environment
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European measurement programmes; se
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Where FC = fuel consumption (kg), m
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Where EEvap,fueling, = hydrocarbon
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For gasoline, the DEA residential s
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The time series of emissions for mo
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ICAO Annex 16: "International stand
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Wismann, T. 2001: Energiforbrug og
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where EMFreloading is the emission
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Ã Number of platforms 60 50 40 30
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Flaring in gas treatment and storag
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• Check of units for fuel rate, e
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Fenhann, J. & Kilde, N.A. 1994: Inv
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Ã ÃÃÃÃÃÃÃÃÃÃÃÃÉÃÃÃ
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emission factor based on 2000 figur
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Danish Foundries. The emission of T
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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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ased on EMEP/EEA guidebook. All unc
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ANNUAL DANISH INFORMATIVE INVENTORY
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