Report - DCE - Nationalt Center for Miljø og Energi

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Agricultural tractors (diesel) < 80 kW 0 10000 20000 30000 40000 50000 60000 70000 80000 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 No. 37,3 44,7 48,5 52,2 55,9 59,7 63,4 67,1 70,8 Ã Agricultural tractors (diesel) > 80 kW 0 1000 2000 3000 4000 5000 6000 7000 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 No. 85,8 93,2 96,9 100,7 111,9 126,8 130,5 156,6 186,4 Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Harvesters
Ã The tractor and harvester developments towards fewer vehicles and larger engines, shown in Figure 3.90, are very clear. From 1985 to 2010, tractor and harvester numbers decrease by around 20 % and 54 %, respectively, whereas the average increase in engine size for tractors is 32 %, and 175 % for harvesters, in the same time period. ÃÃ No Size No Size ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃÃ The most important machinery types for industrial use are different types of construction machinery and fork lifts. The Figures 3.91 and 3.92 show the 1985-2010 stock development for specific types of construction machinery and diesel fork lifts. Due to lack of data, the construction machinery stock for 1990 is used also for 1985-1989. For most of the machinery types there is an increase in machinery numbers from 1990 onwards, due to increased construction activities. It is assumed that track type excavators/wheel type loaders (0-5 tonnes), and telescopic loaders first enter into use in 1991 and 1995, respectively. Ã Ã
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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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&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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Page 110 and 111: • Research carried out by TNO (Be
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Page 122 and 123: Ã Ã Gasoline PC 36% Gasoline LDV
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Page 132 and 133: Ã Ã Ã Ã ment in emission factor
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Page 140 and 141: Ã Ã Ã Residential (1A4b) 2% Rail
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Page 156 and 157: (EMEP/EEA, 2009) for air traffic, o
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Page 162 and 163: Ã ÃÃÃÉÃÃÃ The 1985-2010 sto
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Page 170 and 171: total emissions (in grams) from the
Page 172 and 173: Ã Further, the Marine Environment
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Page 178 and 179: Where EEvap,fueling, = hydrocarbon
Page 180 and 181: For gasoline, the DEA residential s
Page 182 and 183: The time series of emissions for mo
Page 184 and 185: ICAO Annex 16: "International stand
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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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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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234 ÃÃÃÃÃÃÃÃÃ Ã ÃÃ ÃÃ
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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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ased on EMEP/EEA guidebook. All unc
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Ã sions is based on emission facto
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ANNUAL DANISH INFORMATIVE INVENTORY
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