Report - DCE - Nationalt Center for Miljø og Energi

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on information from the Danish Plant Directorate, which is provided on information from the farmers. Is has to be mentioned that data regarding 2010 is the same as 2009 and have to be considered as preliminary estimtate. 2010 data will be implemented when data is available. The structural development in the agricultural sector has an influence in change of housing types. The trend in housing system for dairy cattle goes from older tied-up housings, which is replaced by bigger housings with loose-holding. In 1985 85% of the dairy cattle were kept in tied-up housings and in 2010 the part is reduced to 12%. In loose-holding systems the cattle have more space and more straw bedding and this will in general increase the NH3 emission per animal compared to the tied-up housings. In table 2C.2 the distribution of housing type for dairy cattle and fattening pigs from 1985-2010 is listed. ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃÃ Ã Ã Ã ÃÃ Ã Ã Ã ÃÃ Ã Ã Ã Ã &NJTTJPO PG /) )PVTJOH The emission from housings is thus determined by a number of different conditions that depends on housing type and the different kinds of manure disposal systems placed in these housings. Danish Centre for Food and Agriculture, Aarhus University has carried out a number of emission surveys and estimated emission coefficients for each type of housings (Poulsen et al., 2001 and Poulsen, 2011). In table 2C.3 is shown the emission factors for the most important animal categories; dairy cattle and fattening pigs in different housing systems. For the slurry and liquid manure is given TAN emission factors (TAN ex animal) and for solid and deep litter manure is given N ex animal.
Ã ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ ÃÃ Ã ÃÃ ÃÃ Ã ÃÃÃ ÃÃÃ ÃÃÃ ÃÃÃ ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã ÃÃÃÃÃ Ã Ã ÃÃÃÃÃÃ Ã Ã ÃÃÃÃÃ Ã Ã ÃÃÃÃÃ Ã Ã ÃÃÉÃ Ã Ã Ã ÃÃÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã ÃÃÃ Ã Ã ÃÃÃÉÆÃÃÃ Ã Ã ÃÃÃÉÆÃÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃÃÃÃÃ Ã Ã Ã Ã Ã Ã Ã 4UPSBHF Livestock manure is collected either as solid manure or as slurry depending on housing type. In Table 2C.4 is shown the emission factor used for storage. It is assumed that the part of solid manure taken directly from the housing into the field is 65% from cattle, 25% from pigs, 50% sows, 15% from poultry and 5% from hens (Poulsen et al., 2011). The remaining part of the solid manure is deposited in stock piles in the field before field application. By law all slurry tanks have to be covered by a crust in order to reduce NH3 emission. However, investigations show that slurry tanks were incompletely covered earlier (COWI 2000), which result in a higher NH3 emission. In 2010 it is assumed that 5% of the tanks with pig slurry and 2% of tanks with cattle slurry are incompletely covered. This information has been incorporated in the emission inventory.
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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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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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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 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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14 12 Ã 10 8 6 4 2 0 10
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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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3- 5 4,5 4 3,5 3 2,5 2 1,5 1 0,5 0
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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 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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For all vehicle categories/technolo
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(EMEP/EEA, 2009) for air traffic, o
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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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ICAO Annex 16: "International stand
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Wismann, T. 2001: Energiforbrug og
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emission factor based on 2000 figur
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ased on EMEP/EEA guidebook. All unc
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ANNUAL DANISH INFORMATIVE INVENTORY
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