Addendum to TSAP report #13. Markus Amann, Jens Borken-Kleefeld, Janusz Cofala, Zig Klimont, June 13, 2014
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1 Addendum to report #13 Markus Amann, Jens Borken-Kleefeld, Janusz Cofala, Zig Klimont, June 13,
2 Table 1: Comparison of 2005 total national emission inventories for SO2. submission of as of March 1, (kilotons) missing (-) in AT S content of fuels used in residential/commercial sector BE Industrial combustion and processes - waste flaring and non ferrous metals underestimated in BG Recently installed FGD not fully included in HR Power sector - underestimates progress in implementation of emission control measures CY CZ No submission DK Industrial combustion and processes - underestimates the emissions EE underestimates the emissions from oil shale production and use FI Industrial combustion and processes - consistent with national experts' estimates; compared with NAT emissions overestimated FR Emissions from industrial processes overestimated in DE update of emissions from the power sector not (yet) included in GR underestimates emissions form liquid fuels combustion in industry HU No submission IE IT NAT - higher estimate of emissions from industry LT No submission LU NAT - higher S content of fuels used in residential/commercial sector MT Power sector - NAT - higher S content of heavy fuel oil NL underestimates emissions from industrial combustion PL overestimates S content of coal used in residential/commercial sector
3 Table 1, ctd.: Comparison of 2005 total national emission inventories for SO2. submission of as of March 1, (kilotons) missing (-) in PT Recent improvement of fuel quality (S content) not fully included in RO Recent improvement of fuel quality (S content) not fully included in SK SI ES SE UK Power sector - faster improvement in fuel quality than assumed in Emissions from fuel input to blast furnaces need correction in
4 Table 2: Comparison of 2005 total national emission inventories for NO x. submission of as of March 1, (kilotons) missing (-) in AT Emissions from agricultural soils BE BG Very high emission factor for industrial processes in national inventory Road: Based on consultations in, assumes a higher share of old cars (without catalyst) HR 75.9 Emissions from agricultural soils Road: HR assumes older car fleet compared with COPERT CY 21.2 Emissions from agricultural soils CZ No submission DK Road: higher, assuming older fleet/higher shares of NOC FI Power sector: consistent with national experts' estimates; compared with NAT emissions overestimated FI Road: higher. Differences in details of control shares, but also activity data. FR Power sector (emissions factors and implementation of control measures) FR NAT: Different composition of fleet and age structure compared with COPERT DE Emissions from agricultural soils NAT - lower emissions from iron and steel industry GR Road: Different composition of fleet in NAT compared with COPERT GR No emissions in NAT from off-road (or different allocation) HU No submission. replaced with IE Road: higher. Differences in age structure and inventory approach. IT NAT - lower emission factors in power sector, different classification of industrial CHP plants LV LT 61.9 No submission 62.5 LU 47.4 Emissions from agricultural soils Road: Different LDV - HDV allocation of diesel
5 Table 2, ctd.: Comparison of 2005 total national emission inventories for NO x. submission of as of March 1, (kilotons) missing (-) in MT Road: higher, because based on fuel sold. NAT based on fuel used. NL Emissions from agricultural soils Road: higher, because based on fuel sold. NAT based on fuel used. PL NAT - higher fuel use and emissions from agricultural tractors PT Road: lower, because based on fuel sold, different LDV HDV allocation of diesel, and less older cars. RO Emissions from agricultural soils Road: lower, but higher for NON-RD. Possibly issue of fuel allocation SK Road: lower, possibly because of age structure or LDV HDV diesel fuel allocation. SI NAT: lower emissions from off-rd ES Emissions from agricultural soils Road: higher, because based on fuel sold. NAT based on fuel used. SE Road; higher, because higher share of NOC cars, and different allocation LDV-HDV diesel fuel. UK Off-rd - higher activities and emissions in NAT
6 Table 3: Comparison of 2005 total national emission inventories for PM2.5. submission of as of March 1, (kilotons) missing (-) in AT Small combustion (stoves and boilers) - differences in emission factors BE 28.4 Smoking, barbecues, fireworks Small combustion (stoves and boilers) - activities in too low (statistics do not include real consumption), Belgium uses Tier 1 methodology to estimate the emissions Open burning of agricultural waste 0.3 Road NAT estimate according to fuel used, not sold BG 34.5 Smoking, barbecues, fireworks Small combustion (stoves and boilers) - BG uses Tier methodology Open burning of agricultural waste 5.4 Combustion and process emissions in industry Open burning of municipal waste 0.5 HR 15.0 Smoking, barbecues, fireworks Small combustion (stoves and boilers) - HR uses Tier methodology Open burning of agricultural waste 2.5 Road: different assumptions about the age of car fleet and different emissions factors compared with COPERT HR assumes older car fleet compared with COPERT Open burning of municipal waste 0.4 CY 2.7 Smoking, barbecues, fireworks Combustion and process emissions in industry - emission factor in cement industry needs modification CZ 42.9 No submission, Inventory incomplete. DK Different emission factors for combustion and processes in industry Open burning of municipal waste 0.1 EE 20.0 Smoking, barbecues, fireworks Small combustion (stoves and boilers) Open burning of agricultural waste 0.8 Open burning of municipal waste 0.1 FI Small combustion (stoves and boilers) Road: Gains - lower non-exhaust, different mileage assumptions FR Smoking, barbecues, fireworks Small combustion (stoves and boilers) Road: lower. Differences in details of control shares, but also activity data.
7 Table 3, ctd.: Comparison of 2005 total national emission inventories for PM2.5. submission of as of March 1, (kilotons) missing (-) in DE Open burning of agricultural waste Small combustion (stoves and boilers) Open burning of municipal waste 1.9 GR 61.9 No and submissions HU 29.4 No submission. IE 13.3 Smoking, barbecues, fireworks Small combustion (stoves and boilers) higher in IE Open burning of municipal waste 0.3 Combustion and process emissions in industry higher in NAT IT Smoking, barbecues, fireworks Small combustion (stoves and boilers) higher in NAT Different assessment of emissions from waste burning (agricultural and municipal) LV 18.6 No submission LT 15.0 No submission LU 3.3 No submission. 3.3 MT 0.7 Smoking, barbecues, fireworks Road: NAT higher, older structure of vehicles assumed NL 24.2 Open burning of agricultural waste Small combustion (stoves and boilers) NAT - tier 1 methodology Smoking, barbecues, fireworks; higher 1.7 Road: higher, because based on fuel sold. PL Smoking, barbecues, fireworks Small combustion (stoves and boilers): hifgher, includes combustion of coal of poor quality Different assessment of emissions from waste burning (agricultural and municipal) - NAT higher PT 62.7 Smoking, barbecues, fireworks Open burning of municipal waste 1.1 RO Smoking, barbecues, fireworks Small combustion (stoves and boilers) - NAT higher, Tier 1 methodology
8 Table 3, ctd.: Comparison of 2005 total national emission inventories for PM2.5. submission of as of March 1, (kilotons) Sectors systematically included (+) or missing (-) in SK 32.1 Smoking, barbecues, fireworks Small combustion (stoves and boilers); NAT higher, Tier 1 methodology Open burning of agricultural waste 0.4 Open burning of municipal waste 0.4 SI 9.3 Smoking, barbecues, fireworks Small combustion (stoves and boilers); NAT higher, Tier 1 methodology Open burning of agricultural waste 0.5 Open burning of municipal waste 0.2 ES Smoking, barbecues, fireworks Small combustion (stoves and boilers); NAT lower, Tier 1 methodology Open burning of agricultural waste 26.7 Road: higher, because based on fuel sold. SE 31.2 Open burning of agricultural waste Smoking, barbecues, fireworks (different assessment); higher Combustion and process emissions in industry higher in UK 87.0 Open burning of agricultural waste Smoking, barbecues, fireworks (different assessment); higher Off-road - higher activities and emissions in NAT
9 Table 4: Comparison of 2005 total national emission inventories for NH 3. submission of as of March 1, (kilotons) missing (-) in AT 63.0 Pets and humans BE 74.2 Pets and humans Difference in estimates from Open burning of waste (agri. and municipal) 0.1 waste disposal BG 65.2 Pets and humans Difference in estimates from waste disposal Tier 1 for livestock in national inventory gives higher estimate HR 29.3 Pets and humans Difference in estimates from waste disposal Open burning of waste (agri. and municipal) 0.5 Tier 1 for livestock in national inventory gives higher estimate Industrial combustion and process sources CY 6.2 Pets and humans Tier 1 for livestock in inventory gives higher estimate CZ 79.9 Missing submission, report incomplete DK 73.4 Pets and humans Difference in assumptions on Emissions from crops -5.3 livestock mitigation measures EE 11.8 Pets and humans Difference in estimates from waste disposal Open burning of waste (agri. and municipal) 0.2 Differences in estimates for livestock and mineral fertilizers FI 33.9 Pets and humans Differences in estimates for livestock FR Pets and humans DE Pets and humans Differences in estimates for livestock and mineral fertilizers GR 56.8 Missing submission HU 77.6 Missing submission, report incomplete IE Pets and humans Differences in estimates for livestock and mineral fertilizers IT Pets and humans Open burning of waste (agri. and municipal) 1.1 LV 13.0 Pets and humans Difference in estimates from waste disposal Open burning of waste (agri. and municipal) 0.2 inventory uses Tier 1 IPCC method for mineral fertilizers LT 44.2 Missing submission 39.1 LU 6.2 Pets and humans Differences in estimates for livestock includes emissions from chemical industry
10 Table 4, ctd: Comparison of 2005 total national emission inventories for NH 3. submission of as of March 1, (kilotons) MT 1.7 Pets and humans NL Pets and humans Difference in estimates from waste disposal PL Pets and humans Difference in estimates from waste disposal Open burning of waste (agri. and municipal) 1.3 Differences in estimates for livestock ( cattle emissions very low) PT 70.9 Pets and humans Difference in estimates from waste disposal RO Pets and humans Tier 1 for livestock in inventory gives higher estimate Open burning of waste (agri. and municipal) 4.8 Difference in estimates from waste disposal SK 28.3 Pets and humans Differences in estimates for Open burning of waste (agri. and municipal) 0.1 livestock and mineral fertilizers SI 19.0 Pets and humans Open burning of waste (agri. and municipal) 0.1 ES Pets and humans SE 53.5 Pets and humans Differences in estimates for livestock and mineral fertilizers UK
11 Table 5: Comparison of 2005 total national emission inventories for VOC. submission of as of March 1, (kilotons) missing (-) in AT Emissions from livestock manures Vehicle structure and emission factors for road transport Assumptions for paint use activities BE Open burning of waste (agri. and municipal) Activities and emission factors for solvent use BG Emissions from livestock manures Activities and emission factors for solvent use Open burning of waste (agri. and municipal) -1.4 High share of old gasoline cars and missing non-road Tier 1 for residential combustion HR 79.1 Open burning of waste (agri. and municipal) Activities and emission factors for solvent use Tier 1 for residential combustion CY 8.8 Emissions from livestock manures Activities and emission factors for solvent use CZ Missing submission, report incomplete DK Emissions from livestock manures Open burning of waste (agri. and municipal) 0.1 Activities and emission factors for solvent use EE 38.4 Emissions from livestock manures Tier 1 for residential combustion Open burning of waste (agri. and municipal) 1.1 FI Emission factors for small combustion Activities and emission factors for solvent use FR Emission factors for small combustion FR Activities and emission factors for solvent use
12 Table 5: Comparison of 2005 total national emission inventories for VOC. submission of as of March 1, (kilotons) DE Open burning of waste (agri. and municipal) Activities and emission factors for solvent use Emission factors for small combustion Tier 1 for residential combustion GR Open burning of waste (agri. and municipal) Inventory incomplete - no emissions from solvents High share of old gasoline cars and missing non-road Tier 1 for residential combustion HU Missing submission IE 63.4 Open burning of waste (agri. and municipal) Activities and emission factors for solvent use IT Emissions from livestock manures Emission factors for small combustion IT Open burning of waste (agri. and municipal) LV 69.0 Open burning of waste (agri. and municipal) Activities and emission factors for solvent use Tier 1 for residential combustion LT 84.5 Missing submission 68.0 LU 12.6 Emissions from livestock manures Activities and emission factors for solvent use MT Activities and emission factors for solvent use NL Emissions from livestock manures (fuel sold basis in ) Open burning of waste (agri. and municipal) 0.2 PL Open burning of waste (agri. and municipal) Tier 1 for residential combustion PT Open burning of waste (agri. and municipal) Emission factors for small combustion RO Emissions from livestock manures Activities and emission factors for solvent use Open burning of waste (agri. and municipal) 30.5 Tier 1 for residential combustion SK 77.1 Emissions from livestock manures High share of old gasoline cars and missing non-road Open burning of waste (agri. and municipal) 0.4 Tier 1 for residential combustion SI 41.2 Open burning of waste (agri. and municipal) Emission factors for small combustion Activities and emission factors for solvent use ES High share of old gasoline cars and non-road differences SE Open burning of waste (agri. and municipal) UK Activities and emission factors for solvent use
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