Report - DCE - Nationalt Center for Miljø og Energi

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Ã ÃÃÃÃÃÃÃÃÃ ÃÃÃÆÃÃÉÃÇÃÃÃ Ã Ã ÃÃÉ ÃÃÃÃ ÃÃÃÆÃ ÃÃ Ã Ã ÃÃ Ã ÃÃÃ ÃÃÃ ÃÃÃ ÃÃÃ ÃÃ ÃÃ ÃÃÃÃÃ ÃÃÃ Ã ÃÃÃÃ Ã Ã ÃÃÃÃÃ Ã Ã Ã ÃÃÃÃÃÃÃÃ ÃÃ ÃÃÃÃ ÃÃ ÃÃÃÃ ÃÃÃÃ The use of air pollution control devices, and activated carbon, for the removal of Hg is expected to also reduce the flue gas concentration of dioxins, PAHs and odour. Existing knowledge on the reduction efficiencies justifies that no emission limits are necessary (Schleicher & Gram, 2008). "DUJWJUZ EBUB Table 7.3 shows the development in total number of nationally deceased persons (Statistics Denmark, 2011), number of cremations and the development in the fraction of cremated corpses from the total number of deceased (DKL, 2011). Annex 2D Table 2D-1 presents data for the entire time series. ÃÃÃÃÃÃÃÉÃÃÃÃÃ ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÆÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÆÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÆÃ Ã Ã Ã Ã Ã
Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃÃÃÃÃÃÃÉÃÃÃÃÃÃ ÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃÃÃ Even though the total number of yearly cremations is fluctuating, the cremation percentage has been steadily increasing since 1984, and is likely to continue to increase. The average body weight of cremated corpses is assumed to be 65 kg. Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃ Figure 7.2 presents the trend of the national number of deceased persons together with the activity data for human cremation. The figure shows a direct connection between the number of deceased and the activity of human cremation as the two trends are quite similar. Figure 7.2 also shows the effect of the increasing fraction of cremated bodies, as the number of cremations is not decreasing along with the number of deceased. The cremation fraction has increased from 67 % in 1990 to 77 % in 2010; the trend of this fraction is shown in Figure 7.1, Table 7.3 and Annex 2D Table 2D-1. &NJTTJPO GBDUPST For crematoria, emissions are calculated by multiplying the total number of cremations by the emission factors. Since there are no measurements available of the yearly emission from Danish crematoria, the estimation of emis-
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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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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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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 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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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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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 4PVSDF TQFDJGJD SFDBMDVMBUJPOT P
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ANNUAL DANISH INFORMATIVE INVENTORY
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