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appendices:appendix2.3-hm-from-mobile-sources [2021/04/14 23:26] – [Railways] kotzulla | appendices:appendix2.3-hm-from-mobile-sources [2024/11/06 14:56] (current) – external edit 127.0.0.1 | ||
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For heavy-metal exhaust emissions (other then lead from leaded gasoline), tier1 values have been derived from tier1 default values provided in the 2019 EMEP/EEA Guidebook. | For heavy-metal exhaust emissions (other then lead from leaded gasoline), tier1 values have been derived from tier1 default values provided in the 2019 EMEP/EEA Guidebook. | ||
- | __Table 1: Tier1 default emisison factors applied to road vehicles, in [g/TJ]__ | + | __Table 1: Tier1 default emisison factors applied to road vehicles, in g/TJ__ |
| ^ **Pb** | | ^ **Pb** | ||
^ Diesel oil | ^ Diesel oil | ||
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//(Note: Until submission 2017, the EMEP/EEA default EFs provided for NRMM were used in the German inventory. As these EFs do not differentiate between fuel combustion and lubricant co-incineration, | //(Note: Until submission 2017, the EMEP/EEA default EFs provided for NRMM were used in the German inventory. As these EFs do not differentiate between fuel combustion and lubricant co-incineration, | ||
- | __Table 2: Tier1 default emission factors applied to NRMM, in [g/TJ__ | + | __Table 2: Tier1 default emission factors applied to NRMM, in g/TJ__ |
| ^ **Pb** | | ^ **Pb** | ||
^ Diesel oil | ^ Diesel oil | ||
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===== Railways ===== | ===== Railways ===== | ||
- | __Table 3: Tier1 default emission factors applied to railway vehicles, in [g/TJ]__ | + | __Table 3: Tier1 default emission factors applied to railway vehicles, in g/TJ__ |
| ^ **Pb** | | ^ **Pb** | ||
^ Diesel oil | ^ Diesel oil | ||
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As the EMEP/EEA GB 2019 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. | As the EMEP/EEA GB 2019 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**. | ||
+ | Here, a country-specific approach is applied with emissions of (i) chromium and nickel being estimated as part of the particle emissions from brake wear whereas emissions of copper (ii) copper are estimated as part of the PM emissions from the contact line. | ||
+ | |||
+ | __Table 4: Country-specific emission factors for abrasive emissions, in g/km__ | ||
+ | ^ | ||
+ | ^ Contact line < | ||
+ | ^ Tyres on rails < | ||
+ | ^ Braking system < | ||
+ | ^ Current collector < | ||
+ | < | ||
+ | < | ||
+ | < | ||
+ | < | ||
+ | |||
+ | |||
===== Inland Vessels and Ships in 1.A.3.d ii ===== | ===== Inland Vessels and Ships in 1.A.3.d ii ===== | ||
- | __Table | + | __Table |
| ^ **Pb** | | ^ **Pb** | ||
^ Diesel oil | 1.21 | 0.233 | ^ Diesel oil | 1.21 | 0.233 | ||
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The following table provides the tier1 EF applied for HMs from ships and vessels in both civil and military operation in NFR categories 1.A.3.d i -International Maritime Navigation, 1.A.3.d ii - National Navigation (Shipping), 1.A.4.c iii -Fisheryand 1.A.5.b iii - Other: Military Navigation. | The following table provides the tier1 EF applied for HMs from ships and vessels in both civil and military operation in NFR categories 1.A.3.d i -International Maritime Navigation, 1.A.3.d ii - National Navigation (Shipping), 1.A.4.c iii -Fisheryand 1.A.5.b iii - Other: Military Navigation. | ||
- | __Table | + | __Table |
| | | | ||
^ Heavy Fuel oil< | ^ Heavy Fuel oil< | ||
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The EMEP/EEA GB 2019 does not provide specific defaults for HM emissions from the combustion of jet kerosene and aviation gasoline, stating that for for aviation gasoline these emissions are //not estimated// (NE): | The EMEP/EEA GB 2019 does not provide specific defaults for HM emissions from the combustion of jet kerosene and aviation gasoline, stating that for for aviation gasoline these emissions are //not estimated// (NE): | ||
- | |||
- | [[gallery size=" | ||
- | : GB2016(July2017)_EF_NA+NE_Avgas.PNG | ||
- | [[/ | ||
Therefore, the inventory compiler decided to apply the tier1 EF from gasoline fuel used in non-road mobile machinery here, too. | Therefore, the inventory compiler decided to apply the tier1 EF from gasoline fuel used in non-road mobile machinery here, too. | ||
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 HM emission from jet kerosene are reported as //not estimated// (NE). | ||
- | __Table | + | __Table |
| ^ **Pb** | | ^ **Pb** | ||
^ Kerosene | ^ Kerosene | ||
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< | < | ||
- | [(EMEPEEA2019> | + | [(EMEPEEA2019> |