Report - DCE - Nationalt Center for Miljø og Energi

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Ã ÃÃÃÃÃÃÃÃÃÃÃ Ã Ã Ã ÃÃ ÃÃ Ã ÆÃÃ ÆÃ ÆÃ 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 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 Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã Ã ÉÃ Ã Ã Ã ÉÃ Ã Ã Ã ÉÃ Ã Ã Ã ÉÃ Ã Ã Ã ÃÃÃÃÃÃÃÃÃ 4PVSDF TQFDJGJD 2" 2$ BOE WFSJGJDBUJPO A QA/QC plan for the Danish emission inventories has been implemented. The quality manual (Sørensen et al. 2005) describes the concepts of quality work and definitions of sufficient quality, critical control points and a list of Point for Measuring (PM). Details about the source specific QA/QC is included in Annex 2A-11. Documentation concerning verification of the Danish emission inventories has been published by Fauser et al. (2007). Former editions of the sector report for stationary combustion (Nielsen et al. 2010) has been reviewed by external experts in 2004, 2006 and 2009. 4PVSDF TQFDJGJD JNQSPWFNFOUT BOE SFDBMDVMBUJPOT For stationary combustion plants, the emission estimates for the years 1990- 2009 have been updated according to the latest energy statistics published by the Danish Energy Agency. The update included both end use and transformation sectors as well as a source category update. The disaggregation of emissions in $ 0DQXIDFWXULQJ LQGXVWULHV DQG FRQVWUXF WLRQ has been recalculated based on a new improved methodology. Thus, the estimated emissions in the subsectors are considerable, but the total emissions in sector 1A2 are relatively low.
The emissions from residential wood combustion have been recalculated based on improved technology disaggregation data. In addition the NMVOC emission factor has been improved for new stoves resulting in a decreased emission from this sector. The NOx emission factor for natural gas consumption in large power plants has been updated according to Danish legislation 6 . The NMVOC emission factor for refineries have been included or revised for several years. This results in improved time series but also in large relative changes for some years. The PM10 and PM2.5 emission factors for wood and straw have been recalculated to improve consistency with the TSP emission factor. 4PVSDF TQFDJGJD QMBOOFE JNQSPWFNFOUT A number of improvements are planned for the stationary combustion inventories: 1) Improved documentation for emission factors. The reporting of, and references for, the applied emission factors will be further developed in future inventories. 2) Documentation concerning the HM emission factor update. A report documenting the improved HM emission inventory is expected to be published in 2012. 3) Implementation of emission factors from EEA (2009). Some emission factors still refer to older versions of the EMEP/CORINAIR Guidebook. These emission factors will be updated according to EEA (2009). 4) Improved uncertainty estimate. The current uncertainty estimates are based on SNAP main categories and default uncertainties. The source categories will be changed to NFR categories and country specific uncertainty estimates included for some of the main emission sources. 3FGFSFODFT GPS TUBUJPOBSZ DPNCVTUJPO $IBQUFS Berdowski, J.J.M., Veldt, C., Baas, J., Bloos, J.P.J. & Klein, A.E., 1995: Technical Paper to the OSPARCOM-HELCOM-UNECE Emission Inventory of heavy Metals and Persistent Organic Pollutants, TNO-report, TNO-MEP – R 95/247. CEPMEIP, 2001: The Co-ordinated European Programme on Particulate Matter Emission Inventories, Projections and Guidance. Available at: http://www.air.sk/tno/cepmeip/ (2010-03-03). 6 However, in general plant specific emission data are available.
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ANNUAL DANISH INFORMATIVE INVENTORY
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AU ANNUAL DANISH INFORMATIVE INVENT
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$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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#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
Page 62 and 63: &NJTTJPOT 40 Stationary combustion
Page 64 and 65: emission from electricity and heat
Page 66 and 67: NMVOC, Gg 25 20 15 10 5 0 1985 1986
Page 68 and 69: accounting for 94 % of the PM2.5 em
Page 70 and 71: PM, Gg PM 2.5, Gg 30 25 20 15 10 5
Page 72 and 73: ÃÃÃÃÃÃÃÃÃÃ Ã ÃÃÃÆÃ
Page 74 and 75: Ã Ã 1") Stationary combustion pla
Page 76 and 77: Ã Ã Ã Ã %JPYJO Stationary combu
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Page 80 and 81: 200 180 Ã 160 140 120 100 80 60
Page 82 and 83: Ã 0.025 0.020 Ã 0.015 Ã 0.010
Page 84 and 85: Ã Ã 25 20 Ã Ã 15 10 Ã
Page 86 and 87: The total fuel consumption in indus
Page 88 and 89: 0.4 Ã 0.3 Ã 0.2 0.1 Ã Ã
Page 90 and 91: 0.035 0.030 0.025 Ã 0.020 Ã 0.0
Page 92 and 93: Ã 0.30 Ã Ã 0.25 0.20
Page 94 and 95: Ã 6 Ã Ã 5 4 3 Ã
Page 96 and 97: Ã 60 Ã Ã 50 40 30 Ã
Page 98 and 99: 14 12 Ã 10 8 6 4 2 0 10
Page 100 and 101: 6 5 4 Ã Ã 3 2 É 1 0 6
Page 102 and 103: 120 Ã 100 80 60 Ã 40
Page 104 and 105: 16 Ã 14 12 10 8 Ã 6
Page 106 and 107: • Emission data reported from ind
Page 108 and 109: Due to the scarce data available an
Page 110 and 111: • Research carried out by TNO (Be
Page 114 and 115: Christiansen, B.H., Evald, A., Baad
Page 116 and 117: Danish Environmental Protection Age
Page 118 and 119: 5SBOTQPSU BOE PUIFS NPCJMF TPVSDFT
Page 120 and 121: Ã 160 140 120 100 80 60 40 20 0
Page 122 and 123: Ã Ã Gasoline PC 36% Gasoline LDV
Page 124 and 125: 3- 5 4,5 4 3,5 3 2,5 2 1,5 1 0,5 0
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Page 128 and 129: 7RQQHV 600000 500000 400000 300000
Page 130 and 131: Ã 7RQQHV 8000 7000 6000 5000 4000
Page 132 and 133: Ã Ã Ã Ã ment in emission factor
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Page 136 and 137: ÃÉÃ ÃÉÃ Passenger cars 69% 2-
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Page 140 and 141: Ã Ã Ã Residential (1A4b) 2% Rail
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Page 144 and 145: Ã 1200 1000 Ã 800 Ã 600 Ã
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Page 150 and 151: For all vehicle categories/technolo
Page 152 and 153: For catalyst vehicles the cold extr
Page 154 and 155: Ã '($ 1(5, IXHO UDWLR 1,30 1,25 1,
Page 156 and 157: (EMEP/EEA, 2009) for air traffic, o
Page 158 and 159: Agricultural tractors (diesel) < 80
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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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emission factor based on 2000 figur
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Danish Foundries. The emission of T
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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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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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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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Ã Ã ity from these facilities. Th
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ANNUAL DANISH INFORMATIVE INVENTORY
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