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| appendices:appendix2.4_pops_from_mobile_sources [2026/03/24 09:30] – [Aircraft in 1.A.3.a and 1.A.5.b ii] kotzulla | appendices:appendix2.4_pops_from_mobile_sources [2026/04/08 14:21] (current) – [Maritime Vessels] kotzulla | ||
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| This appendix chapter provides additional information regarding the approaches applied for estimating exhaust POP emissions from mobile sources in: | This appendix chapter provides additional information regarding the approaches applied for estimating exhaust POP emissions from mobile sources in: | ||
| - | * [[#Road Transport]] (1.A.3.b i - iv) | + | * [[#Road Transport]] (in 1.A.3.b i - iv) |
| - | * [[#Non-road Mobile Machinery in 1.A.2.g vii, 1.A.4.a ii/b ii/c ii, and 1.A.5.b | + | * [[#Non-road Mobile Machinery |
| * [[# | * [[# | ||
| - | * [[# | + | * [[#inland_vessels | Inland vessels and ships ]] (in 1.A.3.d ii) |
| - | * [[#Aircraft in 1.A.3.a and 1.A.5.b]] | + | * [[# |
| + | * [[#Aircraft]] (in 1.A.3.a and 1.A.5.b) | ||
| =====Road Transport===== | =====Road Transport===== | ||
| - | For **exhaust emissions of Benzo[a]Pyrene, | + | For **exhaust emissions of Benzo[a]Pyrene, |
| {{ general: | {{ general: | ||
| Line 25: | Line 26: | ||
| + | ===== Non-road Mobile Machinery ===== | ||
| - | ===== Non-road Mobile Machinery in 1.A.2.g vii, 1.A.4.a.ii, 1.A.4.b.i, 1.A.4.c.ii and 1.A.5.b | + | Table 1 provides the emission factors applied for POPs from non-road mobile machinery as covered as part of NFR categories |
| __Table 1: Tier1 default emission factors applied to NRMM__ | __Table 1: Tier1 default emission factors applied to NRMM__ | ||
| Line 34: | Line 36: | ||
| ^ 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) | ^ LPG (1.A.4.a ii only) | ||
| | < | | < | ||
| | < | | < | ||
| - | | < | + | | < |
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| - | =====Inland Vessels | + | =====Inland Vessels ===== |
| - | __Table | + | The following table provides the emission factors applied for POPs from inland vessels as covered as part of NFR category 1.A.3.d ii - National Navigation (Shipping). Please note that these energy input related emssion factors have been derived from mass-related values taking into account the NCVs of the fuels used. |
| + | |||
| + | __Table | ||
| | | | | ||
| | | | | ||
| Line 64: | Line 68: | ||
| | < | | < | ||
| + | \\ | ||
| - | ===== Maritime Vessels and Ships in 1.A.3.d i, 1.A.3.d | + | <WRAP center round important 80%> |
| + | The specific tier1 default emission factors available from the latest (2023) version of the EMEP/EEA Guidebook have not yet been implemented | ||
| + | </ | ||
| - | The following table provides the tier1 EF applied for POPs from ships and vessels in both civil and military operation in NFR categories 1.A.3.d i -International | + | ===== Maritime |
| - | __Table | + | The following table provides the emission factors applied for POPs 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 - Fishery and 1.A.5.b iii - Other: Military Navigation. Please note that these energy input related emssion factors have been derived from mass-related values taking into account the NCVs of the fuels used. |
| + | |||
| + | __Table 3: Tier1 default emission factors applied to maritime ships and vessels__ | ||
| | | | | ||
| | | | | ||
| Line 83: | Line 92: | ||
| | < | | < | ||
| - | ===== Aircraft | + | \\ |
| + | |||
| + | <WRAP center round important 80%> | ||
| + | The specific tier1 default emission factors available from the latest (2023) version of the EMEP/EEA Guidebook have not yet been implemented | ||
| + | </ | ||
| + | ===== Aircraft | ||
| The EMEP/EEA Guidebook 2023 does not provide specific defaults for POP emissions from the combustion of jet kerosene and aviation gasoline, stating that for for aviation gasoline these emissions are //not estimated// (NE). Therefore, the inventory compiler decided to apply the tier1 EF for **PAHs** from gasoline fuel used in non-road mobile machinery here. | The EMEP/EEA Guidebook 2023 does not provide specific defaults for POP emissions from the combustion of jet kerosene and aviation gasoline, stating that for for aviation gasoline these emissions are //not estimated// (NE). Therefore, the inventory compiler decided to apply the tier1 EF for **PAHs** from gasoline fuel used in non-road mobile machinery here. | ||
| - | Furthermore, | + | Furthermore, |
| As the Party assumes that POP emissions from the combustion of jet kerosene are unlikely to occur, these emissions are reported as //not applicable// | As the Party assumes that POP emissions from the combustion of jet kerosene are unlikely to occur, these emissions are reported as //not applicable// | ||
| - | __Table | + | Tabel 4 provides the emission factors applied for PAH emissions from aircaft in 1A.3.a and 1.A.5.b ii as derived from tier1 EF for **PAHs** from gasoline fuel used in non-road mobile machinery: |
| - | | | **B[a]P** | **B[b]F** | + | |
| - | ^ Kerosene | NA | NA | NA | NA | NA | NA | | + | __Table 4: Tier1 default emisison factors applied to aircraft, in mg/TJ__ |
| - | ^ Aviation gasoline | 126 | 182 | 90 | 205 | 602 | NE | | + | | |
| - | + | ^ Kerosene | |
| - | ------ | + | ^ Aviation gasoline |
| [(EMEPEEA2019> | [(EMEPEEA2019> | ||
| - | [(EMEPEEA2023> | + | [(EMEPEEA2023> |
| [(RENTZ2008> | [(RENTZ2008> | ||