Report - DCE - Nationalt Center for Miljø og Energi

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Fuel consumption, PJ "OOFY " 5JNF TFSJFT SO 2, Gg NO x, Gg 800 700 600 500 400 300 200 100 0 1980 450 400 350 300 250 200 150 100 50 0 180 160 140 120 100 80 60 40 20 1980 1982 1984 1986 1988 1990 1992 TOTAL 1994 1A1a Electricity and heat production 1A1b Petroleum refining 1A1c Energy industries 1A2 Industry 1A4a i Commercial/Institutional plants 1A4b i Residential plants 1A4c i Agriculture/Forestry TOTAL 1982 1984 Total 1986 1988 1990 1992 1A1a Public electricity and heat production 1A1b Petroleum refining 1994 1996 1996 1998 1998 2000 2000 1A1c Other energy industries 1A2 Industry 1A4a Commercial / Institutional 1A4b Residential 1A4c Agriculture / Forestry / Fisheries Total 0 Total 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 1A1a Public electricity and heat production 1A1b Petroleum refining 1A1c Other energy industries 1A2 Industry 1A4a Commercial / Institutional 1A4b Residential 1A4c Agriculture / Forestry / Fisheries Total 2002 2002 2004 2004 2006 2006 2008 2008 2010 2010
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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 Ã 763 HPLVVLRQV LQWHUQDWLRQDO E
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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
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Ã Further, the Marine Environment
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European measurement programmes; se
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Where FC = fuel consumption (kg), m
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Where EEvap,fueling, = hydrocarbon
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For gasoline, the DEA residential s
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The time series of emissions for mo
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ICAO Annex 16: "International stand
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Wismann, T. 2001: Energiforbrug og
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ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã
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Ã Ã Ã Ã Ã Ã Ã Ã Ã ÉÃ Ã
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where EMFreloading is the emission
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Ã Number of platforms 60 50 40 30
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ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ
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Flaring in gas treatment and storag
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Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã
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Ã Ã ÃÃÃÃÃÃÃÃÃ Ã Ã Ã
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Ã ÃÃÃÃÃÃÃÃÃ Ã Ã
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• Check of units for fuel rate, e
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4PVSDF TQFDJGJD SFDBMDVMBUJPOT In t
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Fenhann, J. & Kilde, N.A. 1994: Inv
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Ã ÃÃÃÃÃÃÃÃÃÃÃÃÉÃÃÃ
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Ã 4PVSDF TQFDJGJD SFDBMDVMBUJPOT P
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emission factor based on 2000 figur
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Danish Foundries. The emission of T
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Ã FUIPEPMPHJDBM JTTVFT The emissio
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Ã 0UIFS QSPEVDUJPO DPOTVNQUJPO TUP
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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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ÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã Ã
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238 confidentiality or that the amo
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240 • Inclusion of NMVOC use and
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242 Oertzen, Bundesanstalt für Mat
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"HSJDVMUVSF /'3 TFDUPS 0WFSWJFX PG
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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 100 90 80 70 60 50 40 30 20 10
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Ã The implied emission factors rel
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Ã In 2010 the PM emission from hou
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ÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã
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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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Ã 8BTUF /'3 TFDUPS The waste secto
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Ã ÃÃÃÃÃÃÃÃÃ ÃÃÃÆÃÃ
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Ã sions is based on emission facto
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ÃÃÃÃÃÃÃÃÃÃÃ Ã
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Ã Ã ity from these facilities. Th
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Ã ÃÃÃÃÃÃÃÃÃÃÃÃ Ã Ã
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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 ÃÃÃÃÃÃÃÃÃÃ ÃÃ Ã
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Ã describes the average share of b
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Ã ÃÃÃÃÃÃÃÃ Ã Ã Ã Ã Ã
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Ã The last three sources that were
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Ã FUIPEPMPHZ Emissions from vehicl
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Ã &NJTTJPO GBDUPST In the process
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ÃÃÃÃÃÃÃÃ Ã Ã Ã Ã
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Ã ÃÃÃÃÃÃÃÃÃÃÆÃ Ã
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Ã ÃÃÃÃÃÃÃÃÃ Ã ÃÃ ÃÃ
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http://www2.mst.dk/udgiv/publikatio
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Lemieux, P.M., Lutes, C.C. & Santoi
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0UIFS BOE OBUVSBM FNJTTJPOT Denmark
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http://cdr.eionet.europa.eu/dk/Air_
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Ã Ã Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃ
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ÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃ Ã
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0 Ã The major GNFR source to NOx e
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3FDBMDVMBUJPOT BOE *NQSPWFNFOUT In
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craft which cannot represent these
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too high. The addition of the categ
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"OOFY ,FZ DBUFHPSZ BOBMZTJT Due to
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"OOFY " $PSSFTQPOEFODF MJTU GPS 4/"
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492 ÃÃÃ Ã Ã Ã Ã Ã Ã Ã Ã
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496 "OOFY # $01&35 *7 %&" TUBUJTUJD
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500 ÃÃÃÃÃÃÃÃ ÃÃ ÃÃ Ã
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504 ÃÃÃÃÃ ÃÃ ÃÃ Ã Ã Ã
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506 "OOFY # 4UPDL EBUB GPS OPO SPBE
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508 ÃÉÃ ÃÃ Ã Ã Ã Ã Ã Ã
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510 ÃÃÃÃÃÃ ÃÉÃ ÃÃ
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524 ÃÃÃÃÃÃÃÃÃ Ã Ã ÃÃ
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526 "OOFY # 5SBGGJD EBUB BOE EJGGFS
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on information from the Danish Plan
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3FGFSFODFT Andersen, J.M., Sommer,
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ANNUAL DANISH INFORMATIVE INVENTORY
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