meta data for this page
Differences
This shows you the differences between two versions of the page.
| Both sides previous revisionPrevious revisionNext revision | Previous revision | ||
| appendices:appendix2.3-hm-from-mobile-sources [2025/09/04 15:25] – [Non-road Mobile Machinery in 1.A.2.g vii, 1.A.4.a ii/b ii/c ii, and 1.A.5.b] kotzulla | appendices:appendix2.3-hm-from-mobile-sources [2026/03/18 14:16] (current) – [Maritime Vessels and Ships in 1.A.3.d i, 1.A.3.d ii, 1.A.4.c iii and 1.A.5.b] kotzulla | ||
|---|---|---|---|
| Line 17: | Line 17: | ||
| From these default values, the following country-specific energy-related tier1 EF were derived via the average NCVs of the fuels used: | From these default values, the following country-specific energy-related tier1 EF were derived via the average NCVs of the fuels used: | ||
| - | __Table 1: Tier1 emission factors derived from EMEPEEA GB 2023 defaults, in g/TJ__ | + | __Table 1: Tier1 emission factors derived from EMEP/EEA Guidebook |
| - | | ^ | + | | |
| - | ^ Diesel oil | + | ^ Diesel oil | 0.0116 |
| - | ^ Biodiesel< | + | ^ Biodiesel< |
| - | ^ Gasoline fuels | + | ^ Gasoline fuels | 0.0367 |
| - | ^ CNG | NE | NE | NE | NE | NE | NE | NE | NE | NE | | + | ^ Natural gas (CNG & LNG) | NE | NE | NE | NE | NE | NE | NE | NE | NE |
| - | ^ LPG | NE | NE | NE | NE | NE | NE | NE | NE | NE | | + | ^ LPG |
| - | ^ Biogas | + | ^ Biomethane |
| - | < | + | | < |
| + | |||
| + | \\ | ||
| Here, biodiesel has a slightly lower NCV compared to fossil diesel resulting in higher emissions per TJ, whereas for biogasoline the same NCV is applied as for fossil gasoline. | Here, biodiesel has a slightly lower NCV compared to fossil diesel resulting in higher emissions per TJ, whereas for biogasoline the same NCV is applied as for fossil gasoline. | ||
| Line 44: | Line 46: | ||
| ...the EF for exhaust HMs from NFR 1.A.3.b.i-iv (see above) are applied in order to assure the separate reporting of emissions from fuel and engine wear and the unintended co-incineration of lube oil: | ...the EF for exhaust HMs from NFR 1.A.3.b.i-iv (see above) are applied in order to assure the separate reporting of emissions from fuel and engine wear and the unintended co-incineration of lube oil: | ||
| - | __Table 2: Tier1 emission factors derived from EMEPEEA | + | __Table 2: Tier1 emission factors derived from EMEPEEA |
| - | | ^ | + | | |
| - | ^ Diesel oil | + | ^ Diesel oil | 0.0116 |
| - | ^ Biodiesel< | + | ^ Biodiesel< |
| - | ^ Gasoline fuels - 4-stroke | + | ^ Gasoline fuels - 4-stroke |
| - | ^ Gasoline fuels - 2-stroke< | + | ^ Gasoline fuels - 2-stroke< |
| - | ^ LPG (1.A.4.a ii only) | NE | NE | NE | NE | NE | NE | NE | NE | NE | | + | ^ LPG (1.A.4.a ii only) |
| - | < | + | | < |
| - | < | + | | < |
| <WRAP center round info 100%> | <WRAP center round info 100%> | ||
| Line 69: | Line 72: | ||
| {{ : | {{ : | ||
| - | __Table 3: Tier1 default emission factors applied to railway vehicles, in g/TJ__ | ||
| - | | ^ **Pb** | ||
| - | ^ Diesel oil | ||
| - | ^ Biodiesel< | ||
| - | ^ Lignite Briquettes | ||
| - | ^ Raw Lignite | ||
| - | ^ Hard Coal | | ||
| - | ^ Hard Coal Coke | ||
| - | < | ||
| - | < | ||
| - | < | ||
| - | (//NOTE: Assuming that biodiesel contains far less HMs than fossil diesel oil, similar values are applied to all mobile sources using this biogenic fuel.//) | ||
| - | |||
| - | As the EMEP/EEA GB 2023 does not provide specific defaults for **Pb, Hg and As**, the EF applied here has been derived from chapter: 1.A.3.b i-iv - Road transport: exhaust emissions: tier1 value for diesel vehicles. | ||
| Besides these emissions from fuel combustion and engine wear, the German inventory also covers **abrasive emissions from brakes, wheels on rail and contact line**. | Besides these emissions from fuel combustion and engine wear, the German inventory also covers **abrasive emissions from brakes, wheels on rail and contact line**. | ||
| Line 88: | Line 77: | ||
| __Table 4: Country-specific emission factors for abrasive emissions, in g/km__ | __Table 4: Country-specific emission factors for abrasive emissions, in g/km__ | ||
| - | ^ | + | ^ ^ PM< |
| - | ^ Contact line < | + | ^ Contact line < |
| - | ^ Tyres on rails < | + | ^ Tyres on rails < |
| - | ^ Braking system < | + | ^ Braking system < |
| - | ^ Current collector < | + | ^ Current collector < |
| - | < | + | | < |
| - | < | + | | < |
| - | < | + | | < |
| - | < | + | | < |
| Line 103: | Line 93: | ||
| __Table 5: Tier1 default emission factors applied to inland ships and vessels, in g/TJ__ | __Table 5: Tier1 default emission factors applied to inland ships and vessels, in g/TJ__ | ||
| - | | ^ | + | | |
| - | ^ Diesel oil | 1.21 | 0.233 | + | ^ Diesel oil | 1.21 |
| - | ^ Biodiesel< | + | ^ Biodiesel< |
| - | < | + | | < |
| ===== Maritime Vessels and Ships in 1.A.3.d i, 1.A.3.d ii, 1.A.4.c iii and 1.A.5.b ===== | ===== Maritime Vessels and Ships in 1.A.3.d i, 1.A.3.d ii, 1.A.4.c iii and 1.A.5.b ===== | ||
| Line 117: | Line 108: | ||
| From these mass-related default emission factors, energy-related tier1 EF were derived via average NCVs for the fuels used: | From these mass-related default emission factors, energy-related tier1 EF were derived via average NCVs for the fuels used: | ||
| - | __Table 6: Tier1 default | + | __Table 6: Tier1 emission factors |
| - | | | + | | ^ Pb ^ Cd ^ Hg ^ As ^ Cr ^ Cu ^ Ni ^ Se ^ Zn ^ |
| - | ^ Heavy Fuel oil< | + | ^ Heavy Fuel oil< |
| - | ^ Diesel oil< | + | ^ Diesel oil< |
| - | ^ LNG | + | ^ LNG | NE ||||||||| |
| - | < | + | | < |
| - | < | + | | < |
| + | \\ | ||
| These " | These " | ||
| Line 131: | Line 123: | ||
| ===== Aircraft in 1.A.3.a and 1.A.5.b ===== | ===== Aircraft in 1.A.3.a and 1.A.5.b ===== | ||
| - | The EMEP/ | + | The EMEP/ |
| - | Therefore, the inventory compiler decided to apply the tier1 EF from gasoline fuel used in non-road mobile machinery | + | Therefore, the inventory compiler decided to adopt the tier1 EF from gasoline fuel used in non-road mobile machinery |
| - | Although the Party assumes that HM emissions are also likely to occur from the combustion of jet kerosene, no gap-filling is carried out for this fuel. Instead, all HM emission from jet kerosene are reported as //not estimated// (NE). | + | Although the Party assumes that HM emissions are also likely to occur from the combustion of jet kerosene, no gap-filling is carried out for this fuel. Instead, all heavy metal emission from jet kerosene are reported as //not estimated// (NE). |
| __Table 7: Tier1 default emisison factors applied to aircraft, in g/TJ__ | __Table 7: Tier1 default emisison factors applied to aircraft, in g/TJ__ | ||
| - | | ^ | + | | ^ Pb |
| - | ^ Kerosene | + | ^ Kerosene |
| - | ^ Aviation gasoline | + | ^ Aviation gasoline |
| - | < | + | | < |
| - | [(EMEPEEA2019> EMEP/ | + | [(EMEPEEA2023> EMEP/ |