Report - DCE - Nationalt Center for Miljø og Energi

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ÃÃ Ã Ã ÃÃÃÃÃÃÃ ÃÃ ÃÃÃÃÃÃÃÃ ÃÃÃÃ See Table 61 for general references. Much documentation already exists. However, some of the information used is classified and therefore not publicly available. ÃÃ ÃÃ Ã Ã ÃÃÃÃÃÃÃ See Table 61. Data processing, level 1 Ã Ã ÃÃ ÃÃ Ã ÃÃÃÃÃ ÃÃÃÃÃÃÃÃÃ ÃÃÃÃÃÉÃÃ ÃÃÃÃÃÃÃ Ã The uncertainty assessment of activity data and emission factors are discussed in the chapter concerning uncertainties. Ã Ã ÃÃ ÃÃ Ã ÃÃÃÃÃ ÃÃÃÃÃÃÃÃÃ ÃÃÃÃÃÉÃÃ ÃÃ The uncertainty assessment of activity data and emission factors are discussed in the chapter concerning uncertainties. Ã Ã ÃÃ ÃÃ Ã ÃÃÃÃÃ ÃÃÃ The methodological approach is consistent with international guidelines. Tier 2 or tier 3 methodologies are used. Ã Ã ÃÃ ÃÃ Ã ÃÃÃÃÃ ÃÃ Calculated emission factors are compared with guideline emission factors to ensure that they are within reason. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃÃ ÃÃÃÃ ÃÃÃ The calculations follow the principle in international guidelines. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃ ÃÃÃÃÃÃ
Regarding the distribution of energy consumption for industrial sources (CRF sector 1A2), a more detailed and frequently updated data material would be preferred. There is ongoing work to increase the accuracy and completeness of this IPCC source category. It is not assessed that this has any influence on the overall emission level of greenhouse gases. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃ ÃÃÃÃÃÃ ÃÃÃÃÃ ÃÃ There is no missing accessibility to critical data sources. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃ ÃÃÃÃÃÃÃ ÃÃ A change in calculation procedure would entail that an updated description would be elaborated. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃ ÃÃÃÃÃÃ Ã During data processing it is checked that calculations are done correctly. This is to a wide degree documented in the data processing spreadsheets. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃ Ã Time-series for activity data on SNAP level and sectoral level (see main report) are used to identify possible errors in the calculation procedure. Timeseries for emission factors and fuel consumption are also scrutinized. Ã Ã ÃÃ Ã Ã ÃÃÃÃÃÃ Ã The IPCC reference approach validates the fuel consumption rates and CO2 emissions of fuel combustion. Fuel consumption rates and CO2 emissions differ by less than 2.0 % (1990-2009). The reference approach is further discussed in the main report. Ã Ã ÃÃ Ã Ã ÃÃÃÃ ÃÃÃÃÃÃÃ ÃÃÃÃ There is a direct line between the external datasets, the calculation process and the input data used to Data Storage level 2. During the calculation process numerous controls are conducted to ensure correctness, e.g. sum checks of the various stages in the calculation procedure.
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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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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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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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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 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 &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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Fenhann, J. & Kilde, N.A. 1994: Inv
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emission factor based on 2000 figur
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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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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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Ã In 2010 the PM emission from hou
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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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ANNUAL DANISH INFORMATIVE INVENTORY
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