Report - DCE - Nationalt Center for Miljø og Energi

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Ã The last three sources that were considered are all presented in mass emission per mass burned. For the calculation of these emission factors to a unit that matches the activity data, the building masses are estimated using the same methodology as Hansen (2000) and stated in Table 7.19 for 2010. ÃÃÃÃÃÃÃÃÃ Ã Ã ÃÃÃ Ã ÃÃÃÃÃ Ã ÃÃÃ Ã ÃÃÃ Ã Ã Ã Ã Ã Ã Ã Emission factors for particulate matter are available from the EMEP/EEA Guidebook (EEA, 2009) (hereafter the Guidebook), EIIP (2001), Claire (1999) and NAEI (2009), giving four emission factors that vary from 0.14-51.4 kg PM per full scale fire of a detached house. The best reliable source in this case is believed to be the Guidebook which states both the PM10 and the PM2.5 to be equal to the TSP. There is however the quite questionable relationship between the different building types that is claimed by the Guidebook. Comparing with the average floor areas shown in Table 7.18 and 7.19, it seems illogical that a fire in a detached house will cause more than twice the emission of a fire in an undetached house. That a full scale fire in an apartment building is expected to cause less than a third of the emission of that in a detached house, and that a large fire in an industrial building should cause less than a fifth of the emission from a detached house, even keeping in mind an expected difference in the composition of the interior. The Guidebook is the only found source of emission factors for the heavy metals arsenic, cadmium, cobber, chrome, lead and mercury, no emission factors were found for Ni, Se and Zn. For the emission factor of dioxins and furans there are three sources. Hansen (2000) and UNEP toolkit provides data that are very similar with 50-1000 and 400 g per Mg respectively. In addition the Guidebook gives an emission factor of 0.0014 mg per fire. Hansen (2000) is chosen as the best reliable source with an average of 475 g per Mg, translating to 3.05 mg per fire for full scale detached house fires. NAEI (2009) is the only source that provides data for PAHs, and that gives an emission factor for NMVOC. The total PAH emission factor sums the emissions of: benzo(b)flouranthene, benzo(k)flouranthene, benzo(a)pyrene, indeno(1,2,3-c,d)pyrene and benzo(ghi)perylene. Being that Persson et al. (1998) and Blomqvist et al. (2002) are the only sources to a SO2 emission factor, Blomqvist et al. (2002) is the best available source as this provides a more recent and more detailed method. Emission factors for NOx and CO are provided by several sources EIIP (2001), Persson et al. (1998), Blomqvist et al. (2002), Claire (1999) and NAEI (2009). In the case of both compounds there is a good compliance between the emission factors provided by EIIP (2001), Claire (1999) and NAEI (2009). And in both cases the more recent factors of NAEI (2009) are selected. No data was available for HCB and PCB. NH3 is assumed not to be emitted.
Ã &NJTTJPOT Table 7.20 shows the total national emissions from building fires. The entire time series 1980-2010 is shown in Annex 2D Table 2D-13. ÃÃÃÃÃÃÃÃÃ 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 Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã ÉÃ Ã Ã ÉÃ Ã Ã ÉÃÃÃ Ã Ã ÉÃ Ã Ã ÉÃ 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 Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã ÉÃ Ã Ã ÉÃ Ã Ã ÉÃÃÃ Ã Ã ÉÃ Ã Ã ÉÃ Ã Ã "DDJEFOUBM WFIJDMF GJSFT Emissions that escape from accidental vehicle fires include SO2, NOx, NMVOC, CO, particulate matter, heavy metals (As, Cd, Cr, Cu, Ni, Pb, Zn), dioxins/furans and PAHs.
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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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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 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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ÃÉÃ ÃÉÃ Passenger cars 69% 2-
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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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For all vehicle categories/technolo
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Ã
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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 EEvap,fueling, = hydrocarbon
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For gasoline, the DEA residential s
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ICAO Annex 16: "International stand
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Wismann, T. 2001: Energiforbrug og
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