Report - DCE - Nationalt Center for Miljø og Energi

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too high. The addition of the category additional buildings is the main reason for the lowered total emissions from accidental building fires. For accidental vehicle fires, similar changes were made. Last year the damage rate was set to 70 % for all fires, but this year the damage rate was divided in four damage categories according to the measure of fire extinguishing; full, large, medium and small scale fires, corresponding to 100, 75, 30 and 5 % damage rate respectfully. These new damage categories give an average burnout for all vehicle categories in 2007-2010 of 34 % and thereby a reduction in emission of about 50 % compared with the 70 % burnout used in last year’s inventory. Also the activity data now includes other transport, trains, ships, airplanes, bicycles, tractors, combined harvesters and machines. The activity of these eight new categories has a descending trend, whereas activities that were also included in last year’s inventory have an increasing trend. The resulting new total emission from accidental vehicle fires has a relatively constant trend. The joint effect of these two changes in methodology is an increase in emissions for 1980-1991 and a decrease for 1992-2009. The largest increase is 9 % for all pollutants in 1980 and the largest decrease is -33 % for all pollutants in 2007, the changes in 1990 and 2009 data are +4 % and -16 % respectively. The total change in emissions caused by the recalculation of accidental fires is a decrease in 2009 data between 16 % (particles) and 44 % (NMVOC).
1SPKFDUJPOT Projections of emissions are carried out by DCE at irregular time intervals. The most recent projection was made in 2011, projecting the emissions of NOx, SO2, NMVOC, NH3, TSP, PM10 and PM2.5 to 2030. The total projected emissions for these pollutants for 2020 and 2030 are shown in the table below. For further documentation, please refer to Nielsen et al. (2012). ÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã 3FGFSFODFT Nielsen, O.-K., Plejdrup, M., Winther, M., Mikkelsen, M.H., Albrektsen, R., Nielsen, M., Fauser, P., Hoffmann, L., Hjelgaard, K. & Gyldenkærne, S. 2012. Projection of SO2, NOx, NH3 and particle emissions - 2010-2030. Aarhus University, DCE – Danish Centre for Environment and Energy, 122 pp. Technical Report from DCE – Danish Centre for Environment and Energy No. 7 http://www.dmu.dk/Pub/TR7.pdf
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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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The total fuel consumption in indus
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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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Christiansen, B.H., Evald, A., Baad
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Danish Environmental Protection Age
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ÃÉÃ ÃÉÃ Passenger cars 69% 2-
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total emissions (in grams) from the
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ANNUAL DANISH INFORMATIVE INVENTORY
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