Report - DCE - Nationalt Center for Miljø og Energi

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Danish Foundries. The emission of TSP and distribution between TSP, PM10 and PM2.5 is obtained from CEPMEIP (2003). The emission of heavy metals from production of secondary lead and allied metal manufacturing is based on average emission factors for Danish producers (Illerup et al., 1999) and activity data from Statistics Denmark. The emission of TSP and distribution between TSP, PM10 and PM2.5 is obtained from CEPMEIP (2003). 6ODFSUBJOUJFT BOE UJNF TFSJFT DPOTJTUFODZ The time series are either based on specific measurements, company-specific emission factors combined with activity data or on standard emission factors combined with public statistics. The same methodology has been applied for the entire time series and, therefore, the time series are considered to be consistent. 4PVSDF TQFDJGJD SFDBMDVMBUJPOT No source specific recalculation has been performed for the sector 0HWDO SUR GXFWLRQ. 4PVSDF TQFDJGJD 2" 2$ BOE WFSJGJDBUJPO Detailed discussion of QA/QC can be found in Nielsen et al. (2008). 4PVSDF TQFDJGJD QMBOOFE JNQSPWFNFOUT The time series will be completed and new emission factors for the latest years will be established, if possible. Especially for secondary aluminium and zinc production, potential emissions of heavy metals will be investigated. 0UIFS QSPEVDUJPO /'3 % 4PVSDF DBUFHPSZ EFTDSJQUJPO The sub-sector 2WKHU SURGXFWLRQ (NFR 2D) covers the following process: • Bread (SNAP 040605). • Beer (SNAP 040607). • Spirits (SNAP 040608). • Sugar production (SNAP 040625). • Meat (fish etc. frying/curing) (SNAP 040627). • Margarine and solid cooking fats (SNAP 040698). • Coffee roasting (SNAP 040699). Table 4.6, 4.7 and presents the emission of NMVOC from production of food, beverage and sugar. The emissions are presented for relevant subsectors.
Ã ÃÃÃÃÃÃÃÃÃÃÃÉÃ Ã Ã Ã ÃÃ Ã Ã Ã Ã ÃÃ Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÉÃ ÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÉÃÃ Ã ÃÃÃÃ ÃÃ Ã Ã Ã Ã Ã ÃÉÃÃÃ ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃ ÃÃÃÃ Ã Ã Ã Ã Ã ÃÃÃÃ ÃÃÃÃ Ã ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ ÃÃ Ã ÃÃÃÃ ÃÃ Ã Ã Ã Ã ÃÉÃÃÃ Ã ÃÃ ÃÃ ÃÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃ ÃÃÃÃ Ã Ã Ã Ã ÃÃÃÃ ÃÃÃÃ Ã ÃÃ ÃÃ Ã ÃÃ Ã ÃÃ Ã Ã Ã Ã ÃÃ Ã ÃÃ ÃÃ ÃÃ ÃÃ Ã ÃÃÃÃÃÃÃÃÃÉÃÃ Ã Ã Ã Ã The emission of NMVOC from production of food and beverage follows the activity as the same emission factors have been used for the entire period. The emission factors are presented in Table 4.9.
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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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1SPKFDUJPOT "HSJDVMUVSF 8BTUF 3FGFS
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Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã
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4VNNBSZ * #BDLHSPVOE JOGPSNBUJPO PO
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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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5SBOTQPSU BOE PUIFS NPCJMF TPVSDFT
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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 Ã 7RQQHV 250000 200000 15
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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
Page 172 and 173: Ã Further, the Marine Environment
Page 174 and 175: European measurement programmes; se
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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
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Page 192 and 193: where EMFreloading is the emission
Page 194 and 195: Ã Number of platforms 60 50 40 30
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Page 220 and 221: emission factor based on 2000 figur
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Page 228 and 229: IPCC, 1997: Revised 1996 IPCC Guide
Page 230 and 231: 228 Emission modelling of solvents
Page 232 and 233: 230 ends in waste water, e.g. ethan
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Page 242 and 243: 240 • Inclusion of NMVOC use and
Page 244 and 245: 242 Oertzen, Bundesanstalt für Mat
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Page 248 and 249: only 18 % and 5 % respectively. Mos
Page 250 and 251: DCE - the Danish Centre for Environ
Page 252 and 253: Ã 100 90 80 70 60 50 40 30 20 10
Page 256 and 257: Ã The implied emission factors rel
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Page 262 and 263: EEA guidebook (EMEP/EEA, 2009) defa
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Ã sions is based on emission facto
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Ã Ã ity from these facilities. Th
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0UIFS XBTUF This category is a catc
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Ã Ã Petersen (2001) and Petersen
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Ã describes the average share of b
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craft which cannot represent these
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ANNUAL DANISH INFORMATIVE INVENTORY
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