Report - DCE - Nationalt Center for Miljø og Energi

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Ã &NJTTJPO MFHJTMBUJPO For non-road working machinery and equipment, and recreational craft and railway locomotives/motor cars, the emission directives list specific emission limit values (g pr kWh) for CO, VOC, NOx (or VOC + NOx) and TSP, depending on engine size (kW for diesel, ccm for gasoline) and date of implementation (referring to engine market date). For diesel, the directives 97/68 and 2004/26 relate to non-road machinery other than agricultural and forestry tractors and the directives have different implementation dates for machinery operating under transient and constant loads. The latter directive also comprises emission limits for railway machinery. For tractors the relevant directives are 2000/25 and 2005/13. For gasoline, the directive 2002/88 distinguishes between hand-held (SH) and not hand-held (NS) types of machinery. For engine type approval, the emissions (and fuel consumption) are measured using various test cycles (ISO 8178). Each test cycle consists of a number of measurement points for specific engine loads during constant operation. The specific test cycle used depends on the machinery type in question and the test cycles are described in more details in the directives. ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃ ÃÃ Ã ÃÃ ÃÃ Ã Ã ÃÃÃ ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã
Ã Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã Ã Ã ÃÃÃÃÃ ÃÃ ÃÃ Ã ÃÃ Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃ Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã For recreational craft, Directive 2003/44 comprises the emission legislation limits for diesel engines, and for 2-stroke and 4-stroke gasoline engines, respectively. The CO and VOC emission limits depend on engine size (kW) and the inserted parameters presented in the calculation formulas in Table 3.33. For NOx, a constant limit value is given for each of the three engine types. For TSP, the constant emission limit regards diesel engines only. ÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã ÃÃÃ Ã ÃÃ ÃÃÃÃÃ ÃÃ ÃÃ Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃ ÃÃÃÃ Ã Ã Ã Ã ÃÃ Ã Ã ÃÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Aircraft engine emissions of NOx, CO, VOC and smoke are regulated by ICAO (International Civil Aviation Organization). The engine emission certification standards are contained in Annex 16 — Environmental Protection, Volume II — Aircraft Engine Emissions to the Convention on International Civil Aviation (ICAO Annex 16, 1993). The emission standards relate to the
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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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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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Page 120 and 121: Ã 160 140 120 100 80 60 40 20 0
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 150 and 151: For all vehicle categories/technolo
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Page 156 and 157: (EMEP/EEA, 2009) for air traffic, o
Page 158 and 159: Agricultural tractors (diesel) < 80
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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
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Page 184 and 185: ICAO Annex 16: "International stand
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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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Ã Ã Ã Ã 232 ÃÃÃÃÃÃÃÃÃ
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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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Ã The implied emission factors rel
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EEA guidebook (EMEP/EEA, 2009) defa
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ased on EMEP/EEA guidebook. All unc
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The emission of NMVOC from crops ha
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ANNUAL DANISH INFORMATIVE INVENTORY
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