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Ã 8BTUF /'3 TFDUPS The waste sector consists of the four main NFR categories 6A Solid waste disposal on land, 6B Waste-Water handling, 6C Waste incineration and 6D Other waste. Table 7.1 below shows the relevant SNAP codes for the waste sector. ÃÃÃÃÃÃÃÃÃÃÃ ÃÃ ÃÃ ÃÃ Ã ÃÃÃÃÃ Ã Ã ÃÃÃÃ Ã Ã Ã Ã Ã ÃÃÃÃÃ Ã Ã Ã Ã Ã ÃÃÃÃÃÃ Ã Ã ÃÃÃÃÃÃ Ã Ã ÃÃÃÃÉÃÃ Ã Ã ÃÃÃÃ Ã Ã ÃÃÃÃÃÃÃ Ã Ã ÃÃÃÃ Ã Ã ÃÃÃÃ Ã Ã ÃÃÃ Ã Ã ÃÃÃ Ã Ã ÃÃÃÃÃÃ Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã ÃÃ Ã Ã ÃÃÃÃÉÃÃÃ Ã Ã ÃÃ Ã Incineration of waste in Denmark is done with energy recovery and therefore the emissions are included under the relevant sectors under NFR sector 1A. The documentation for waste incineration is included in Chapter 3.2. 4PMJE XBTUF EJTQPTBM PO MBOE Major emissions from waste disposal are emissions of greenhouse gases. It is assumed that waste disposal also leads to emission of small quantities of NMVOC, CO, NH3 and NOx. PM emissions are emitted from waste handling as well, but no emission factors are available. For the 2012 submission Denmark has not estimated emissions of air pollutants from solid waste disposal. The draft EMEP/EEA Guidebook contains a default NMVOC emission factor, however due to limited resources it has not been possible to estimate the emissions. 8BTUF XBUFS IBOEMJOH According to the EMEP/EEA Guidebook waste-water handling can be a source for emissions of POPs, NMVOC, NH3 and CO. Of these pollutants only NMVOC is thought to be significant.
For the current submission Denmark has not estimated emissions of air pollutants from waste-water handling. The EMEP/EEA Guidebook contains a default NMVOC emission factor for latrines and waste-water handling, however due to limited resources it has not been possible to estimate the emissions. 8BTUF JODJOFSBUJPO Incineration of municipal, industrial and clinical waste take place with energy recovery, therefore the emissions are included in the relevant subsectors under NFR sector 1A. For documentation please refer to Chapter 3.2. Flaring off-shore and in refineries are included under NFR sector 1B2c, for documentation please refer to Chapter 3.4. No flaring in chemical industry occurs in Denmark. )VNBO DSFNBUJPO The incineration of human bodies is a common practice that is performed on an increasing part of the yearly deceased. All Danish incineration facilities use optimised and controlled combustions, with temperatures reaching 800- 850 °C, secondary combustion chambers, controlled combustion air flow and regulations for coffin materials. However, the emissions of especially Hg caused by cremations can still contribute to a considerable part of the total national emissions. In addition to the most frequently discussed emissions of Hg and PCDD/Fs (dioxins and furans), are the emissions of compounds like SO2, NOx, NMVOC, CO, other heavy metals (As, Cd, Cr, Cu, Ni, Pb, Se, Zn), particulate matter, HCB, PAHs and PCBs. Crematoria are usually located within cities, close to residential areas and normally, their stacks are relatively low. Therefore environmental and human exposure is likely to occur as a result of emissions from cremation facilities. FUIPEPMPHZ There are 31 crematoria in Denmark, some with multiple furnaces, 21 facilities are run by the church and 10 by the local authorities (DKL, 2011, Kirkeministeriet, 2006). During the 1990es all Danish crematoria were rebuilt to meet new standards. This included installation of secondary combustion chambers and in most cases, replacement of old primary incineration chambers (Schleicher et al., 2001). All Danish cremation facilities are therefore performing controlled incinerations with a good burn-out of the gases, and a low production of pollutants. But only a few crematoria are equipped with flue gas cleaning (bag filters with activated carbon). Following the development of new technology, the emission limits for crematoria were lowered again in 1/2011. These new standard terms were originally expected from 1/2009 but have been postponed two years for existing crematoria. Table 7.2 shows a comparison of the emission limits from 2/1993 and the new standard limits.
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ANNUAL DANISH INFORMATIVE INVENTORY
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AU ANNUAL DANISH INFORMATIVE INVENT
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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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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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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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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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ÃÉÃ ÃÉÃ Passenger cars 69% 2-
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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
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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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