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| appendices:appendix2.4_pops_from_mobile_sources [2026/03/18 14:09] – [Table] 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__ | ||
| - | | | **B[a]P** | + | | |
| - | | | [mg/ | + | | |
| - | ^ Diesel oil | + | ^ Diesel oil | 698 | 1.164 | 801 | 184 | 2,847 | 1.62< |
| - | ^ 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) | 4.35 | + | ^ LPG (1.A.4.a ii only) |
| - | < | + | | < |
| - | < | + | | < |
| - | < | + | | < |
| ===== Railways ===== | ===== Railways ===== | ||
| Line 50: | Line 53: | ||
| - | =====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 63: | 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 82: | 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 GB 2016 (July 2017) 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): | + | Furthermore, both **HCB** and **PCBs** |
| - | Therefore, | + | As the Party assumes that POP emissions from the combustion of jet kerosene are unlikely |
| - | Furthermore, | + | |
| - | As the Party assumes that POP emissions from the combustion of jet kerosene are unlikely to occur, these emission are reported as //not applicable// | + | Tabel 4 provides |
| - | __Table | + | __Table |
| - | | | **B[a]P** | **B[b]F** | + | | |
| - | ^ Kerosene | NA | NA | NA | NA | NA | NA | | + | ^ Kerosene |
| - | ^ Aviation gasoline | 126 | 182 | 90 | 205 | 602 | NE | | + | ^ Aviation gasoline |
| - | + | ||
| - | ------ | + | |
| [(EMEPEEA2019> | [(EMEPEEA2019> | ||
| + | [(EMEPEEA2023> | ||
| [(RENTZ2008> | [(RENTZ2008> | ||