Report - DCE - Nationalt Center for Miljø og Energi

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ÃÃÃÃÃÃÃÃÃÃ Ã Ã ÃÃ Ã ÃÃ ÃÃ Ã Ã ÃÃÃÃÆÃ ÃÃ Ã ÃÃÃÃ ÃÃÃÃ ÃÃÃÃ ÃÃÃÃ Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃ Ã Ã Ã Ã Ã ÃÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃÃÆÃÃÃÃÃ Ã 4QSFBEJOH JO GJFMET There is no statistical information on how the farmer handling the manure in practice. In calculation of emission from application of manure on the fields is used to different weighted emission factors, which distinguish between solid manure and liquid manure. In 2010 the emission factor for solid manure is estimated to 6 % and liquid manure is estimated to 15 % for cattle and 11% for swine of TAN ex storage. The weighted emission factor will vary from year to year depending on changes in the practice of spreading. The weighted emission factor is based on background estimates of time of spreading, application methods, spreading in growing crops or on bare soil and the time from spreading to ploughing in soil. In table 2C.5 background information for 2010 are given. ÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃÃ Ã ÃÃ Ã Ã ÃÃÃÃÃÃÃÃ Ã Ã Ã ÃÃ ÃÃ ÃÃ Ã ÃÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã 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 ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ Ã Ã Ã ÃÃÃÃÃÃÃÃ ÃÃ Ã ÃÃÃ 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 ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÃÃ ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã
"OOFY $ #BDLHSPVOE JOGPSNBUJPO /) GSPN "HSJDVMUVSBM 4PJMT 4ZOUIFUJD GFSUJMJTFS Since 1985 there has been a significant decrease in use of synthetic fertiliser. This is due to requirements to utilising of nitrogen in manure as outlined for example in the Action Plan on the Aquatic Environment. Further, the use of different fertiliser types has changed. At present, urea constitutes less than 1% of the total nitrogen used as fertiliser (table 2C.6). It is estimated that 1.5 % of the total nitrogen used in synthetic fertiliser is emitted as NH3 in 2010. It means the implied emission factor for 2010 is 1.5 % compared to 10 % in the EMEP/EEA guidebook. Data on the use of synthetic fertiliser is based on the sale estimations collected by the Danish Plant Directorate (2011). Emission factors are based on the values given in EMEP/EEA guidebook (EMEP/EEA, 2009). The use of synthetic fertiliser includes fertiliser used in parks, golf courses and private gardens. Approximately 1-2 percent of the synthetic fertiliser can be related to use out side the agriculture area. ÃÃÃÃÃÃÃÃÃÃÃ Ã ÃÃ Ã ÃÃÃÃÃ Ã ÃÃ ÃÃ Ã Ã ÃÃÃÃÃ Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃÃ Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã ÃÃÃ Ã Ã ÃÃ Ã Ã Ã Ã Ã Ã Ã Ã ÃÃÃÃ Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃÃÃ Ã Ã ÃÃÃÃÃ Ã Ã ÃÃÃÃ ÃÃÉÃ ÃÃÃÃÃ Ã Ã Ã (SB[JOH It is assumed that 5% of the manure from dairy cattle is deposited in the field, which corresponding to 18 days per year. For heifers 36% of the nitrogen in the manure is estimated deposited during grazing, 61% for suckling cows, 50% for horses and 73% for sheep and goats. An emission factor of 7% of the total nitrogen content is assumed to evaporate as NH3 (Jarvis HW DO. 1998a, Jarvis HW DO. 1989b and Bussink 1994). The emission factor is used on all animal categories.
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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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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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Flaring in gas treatment and storag
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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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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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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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Ã sions is based on emission facto
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0 Ã The major GNFR source to NOx e
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craft which cannot represent these
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too high. The addition of the categ
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ANNUAL DANISH INFORMATIVE INVENTORY
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