Report - DCE - Nationalt Center for Miljø og Energi

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Ã In 2010 the PM emission from housings, given in TSP, is estimated to 11.35 Gg. Of this, 80 % relates to swine production. The emission from cattle and poultry contributes with 11 % and 9 %, respectively and the remainder less than 1 %. FUIPEPMPHJDBM JTTVFT The estimation of PM emission is based on the EMEP/EEA guidebook Chapter B1010, where the scientific data mainly is based on an investigation of PM emission in North European housings (Takai et al. 1998). The PM emission includes primary particles in the form of dust from housings. The inventory operates with PM emission from cattle, swine, poultry, horses, sheep and goats (Table 6.13). Some animal categories are divided into subcategories and for each category it is distinguished between solid and slurry based housing systems. The PM emission is related to the number of annual average population (AAP) and to the time the animal is housed. The PM emission from grazing animals is considered as negligible. ÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃ ÃÃÃÃ Ã Ã ÃÃÃÃ ÃÃÃ Ã Ã ÃÃÃ ÃÃ Ã ÃÃÃ Ã ÃÃÃ Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã ÃÉÃÃÃÃ Ã Ã ÃÉÃ Ã ÃÃ ÃÃÉÃ Ã ÃÃ Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã "DUJWJUZ EBUB Livestock production data is based on Statistics Denmark, Agricultural Statistics (www.dst.dk) – Table 6.14.
Ã ÃÃÃÃÃÃÃÃÃÃÃÃÉÃÃ Ã Ã ÃÃ Ã ÃÃ ÃÃ Ã ÃÃ ÃÃ Ã Ã Ã ÃÃ Ã ÃÃ Ã Ã ÃÃÃ Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã ÃÃ ÃÃ Ã Ã Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã ÃÃ Ã Ã ÃÃ ÃÃ Ã Ã Ã Ã ÃÃ Ã Ã &NJTTJPO GBDUPS Emission factor for TSP, PM10 and PM2.5 is based on the EMEP/EEA guidebook (EMEP/EEA, 2009). However, calves and weaners are not included and therefore guidebook 2005 is used. Emission factors for sheep and goats are based on Fontelle et al., 2009. The same emissions factors are used for all years. In Takai et al. (1998), dust emission from housings is estimated as ”inhalable dust”. This is defined as particles that can be transported into the body via the respiratory system. Approximately, “inhalable dust” equates to TSP (Hinz. T., 2002). Estimation of TSP is based on the transformation factors for the conversion of inhalable dust into PM10 given in inventory guidebook 2005 table B3 in appendix B.
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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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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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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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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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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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ANNUAL DANISH INFORMATIVE INVENTORY
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