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ÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃ ÃÃ Ã ÃÃÃÃÃ ÃÃÃ ÃÃÃÃÃ ÃÃÃÃÃ Ã ÉÃÃÃ ÃÃÃÃÃ ÃÃÃÃÉÃ ÃÃÃÃÃ ÃÃÃ ÃÃÃÃÉÃ ÃÃÃÃÉÃ ÃÃÃÃÃ ÉÃÃÃ ÃÃÃÃÃ Ã ÃÃÃÃÃ ÉÃ (SJEEFE FNJTTJPO EBUB ÃÃÃÃÃ ÃÃÃÃ ÃÃÃÃÃ ÃÃÃ ÃÃÃ ÃÃÃÃÃÃÃ ÃÃÃÉÃÃ ÃÃÃÃ Ã ÃÃÃÃÃÃÃ Ã ÃÃÃÃÃ ÃÃÃÃ ÃÃÃÃÃ ÃÃÃÃ ÃÃÃÃ ÃÃÃÃÃÃÃ ÃÃÃÃÃ ÃÃÃÃ ÃÃÃÉÃ ÃÃÃ ÃÃ ÃÃÃÃÃÃÃ ÃÃÃÃÃÃ ÃÃÃÃÉÃ ÃÃÃ Ã ÃÃ ÃÃÃÃ ÃÃÃÃ ÃÃÃ ÃÃÃÃÃ ÃÃÃÃÃ ÃÃÃÃ ÃÃÃÃ ÃÃÃÃÃ ÃÃÃ ÃÃÃ ÃÃÃ ÃÃÃÉÃ ÃÃÃ ÃÃ Ã ÃÃÃÃ ÃÃÃÃÃ ÃÃÃ ÃÃÃ ÃÃ ÃÃÃÃÃ ÃÉÃÃÃ Ã ÃÃÃÃ ÃÃÃÃ ÃÃÃÃÃ ÃÃÃ ÃÃÃÃ ÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃ ÃÃ ÃÃÃÃ ÃÃÃÃÃ ÃÃ ÃÃÃ ÃÃÃÃÃÃ ÃÃÃÃ ÃÃÃÃÃ ÃÃÃÃÃÃ Ã ÃÃÃÃ ÃÃ ÃÃÃÃÃÃ ÃÃ ÃÃÃÃÃÃ ÃÃÃÃÃÃ ÃÃÃ In this section selected maps of gridded emission is presented, all referring to the emission year 2010. The selected maps in Figure 9.1 illustrate the
Ã emissions included in the national total in the NFR table (all emissions excluding Civil Aviation - Domestic and International Cruise, and international Maritime Navigation). All figures illustrate the sum of all included GNFR sectors. The Danish high resolution gridded emissions are aggregated on the 50 km x 50 km EMEP grid for reporting to CLRTAP. The share of each 1 km x 1 km grid cell located in the relevant EMEP grid cells are calculated and the aggregated emissions are calculated as the weighted sum of emissions in the 1 km grid cells intersecting each EMEP grid cell being partial or fully part of the Danish Exclusive Economic Zone, EEZ. B C $ E F ' ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃÃ Ã ÃÃÃÃÃÃÃÃÉÃÃÃÉÃÉÃÉÃÃ ÉÃÃÃÃÃÃ Even on the 50 km x 50 km aggregated level spatial patterns from the major sectors are recognisable for different pollutants.
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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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Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã
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4VNNBSZ * #BDLHSPVOE JOGPSNBUJPO PO
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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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#SJFG EFTDSJQUJPO PG NFUIPEPMPHJFT
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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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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 Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃ
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7RQQHV 600000 500000 400000 300000
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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 Ã 763 HPLVVLRQV LQWHUQDWLRQDO E
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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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ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã
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Ã Ã Ã Ã Ã Ã Ã Ã Ã ÉÃ Ã
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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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ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ
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Flaring in gas treatment and storag
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Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã
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Ã Ã ÃÃÃÃÃÃÃÃÃ Ã Ã Ã
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Ã ÃÃÃÃÃÃÃÃÃ Ã Ã
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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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Ã ÃÃÃÃÃÃÃÃÃÃÃÃÉÃÃÃ
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Ã 4PVSDF TQFDJGJD SFDBMDVMBUJPOT P
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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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ÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã Ã
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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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Ã In 2010 the PM emission from hou
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ÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã
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EEA guidebook (EMEP/EEA, 2009) defa
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Page 276 and 277: Ã Ã ity from these facilities. Th
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on information from the Danish Plan
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ANNUAL DANISH INFORMATIVE INVENTORY
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