meta data for this page
Differences
This shows you the differences between two versions of the page.
Next revision | Previous revision | ||
sector:energy:fuel_combustion:other_including_military:military_transport:military_navigation [2021/01/15 17:10] – created kotzulla | sector:energy:fuel_combustion:other_including_military:military_transport:military_navigation [2022/03/22 12:12] (current) – [Recalculations] kotzulla | ||
---|---|---|---|
Line 5: | Line 5: | ||
In sub-category //1.A.5.b iii - Other, Mobile (including Military)// emissions from military navigation are reported. | In sub-category //1.A.5.b iii - Other, Mobile (including Military)// emissions from military navigation are reported. | ||
- | ^ Method | + | ^ Method |
- | | T1, T2 | NS, M | D, M, CS, T1, T3 | see [[[1-a-5-b-other-military-mobile-combustion | + | | T1, T2 | NS, M | D, M, CS, T1, T3 | see [[sector: |
- | ===== Method | + | ===== Methodology |
- | ===Activity Data === | + | ==== Activity Data ==== |
Primary fuel data for national military waterborne activities is included in NEB lines 6 (' | Primary fuel data for national military waterborne activities is included in NEB lines 6 (' | ||
- | The annual shares used within NFR 1.A.5.b iii are therefore calculated within (Deichnik, K. (2019)), where ship movement data (AIS signal) allows for a bottom-up approach providing the needed differentiation. | + | The annual shares used within NFR 1.A.5.b iii are therefore calculated within (Deichnik, K. (2021)) [(DEICHNIK2021)], where ship movement data (AIS signal) allows for a bottom-up approach providing the needed differentiation. |
__Table 1: Annual fuel consumption, | __Table 1: Annual fuel consumption, | ||
- | || ||= **1990** ||= **1995** ||= **2000** ||= **2005** ||= **2006** ||= **2007** ||= **2008** ||= **2009** ||= **2010** ||= **2011** ||= **2012** ||= **2013** ||= **2014** ||= **2015** ||= **2016** ||= **2017** ||= **2018** ||= | + | | |
- | ||~ Diesel Oil ||> 983 ||> 665 ||> 563 ||> 410 ||> 383 ||> 366 ||> 360 ||> 349 ||> 347 ||> | + | ^ Diesel Oil |
- | ||~ Biodiesel ||> | + | ^ Heavy Fuel Oil |
- | ||~ Heavy Fuel Oil ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> 0 ||> | + | | **Ʃ 1.A.5.b iii** |
- | || **Ʃ 1.A.5.b iii** ||~ 983 ||~ 665 ||~ 563 ||~ 419 ||~ 394 ||~ 382 ||~ 378 ||~ 373 ||~ 369 ||~ 351 ||~ 334 ||~ 319 ||~ 351 ||~ 286 ||~ 370 ||~ 500 ||~ 434 ||> | + | source: Deichnik, K. (2021): BSH model 2021 |
- | source: Deichnik, K. (2019): BSH model [((bibcite 1))] | + | |
- | [[gallery size=" | + | {{:sector: |
- | : 1A5biii_AD.png | + | |
- | : 1A5biii_AD_bio.png | + | |
- | [[/ | + | |
- | ++ Emission factors | + | ==== Emission factors |
The emission factors applied here, are derived from different sources and therefore are of very different quality. | The emission factors applied here, are derived from different sources and therefore are of very different quality. | ||
- | For the main pollutants, country-specific implied values are used, that are based on tier3 EF included in (Deichnik, K. (2019)) [((bibcite 1))] which mainly relate on values from the EMEP/EEA guidebook 2019 [((bibcite 2))]. These modelled IEFs take into account the ship specific information derived from AIS data as well as the mix of fuel-qualities applied depending on the type of ship and the current state of activity. | + | For the main pollutants, country-specific implied values are used, that are based on tier3 EF included in (Deichnik (2021)) which mainly relate on values from the EMEP/EEA guidebook 2019 [(EMEPEEA2019)]. These modelled IEFs take into account the ship specific information derived from AIS data as well as the mix of fuel-qualities applied depending on the type of ship and the current state of activity. |
- | __Table 2: Annual country-specific emission factors for diesel fuels^^1^^, in kg/TJ__ | + | __Table 2: Annual country-specific |
- | || ||= **1990** ||= **1995** ||= **2000** ||= **2005** ||= **2006** ||= **2007** ||= **2008** ||= **2009** ||= **2010** ||= **2011** ||= **2012** ||= **2013** ||= **2014** ||= **2015** ||= **2016** ||= **2017** ||= **2018** ||= | + | |
- | ||~ NH,, | + | |
- | ||~ NMVOC ||> | + | |
- | ||~ NO,, | + | |
- | ||~ SO,, | + | |
- | ||~ BC ||> | + | |
- | ||~ PM,, | + | |
- | ||~ PM,, | + | |
- | ||~ TSP ||> | + | |
- | ||~ CO ||> | + | |
- | ^^1^^ due to lack of better information: | + | |
- | ^^2^^ ratio PM,,2.5,, : PM,,10,, : TSP derived from the tier1 default EF as provided in [((bibcite 2))] | + | |
- | ^^3^^ estimated from a BC-fraction of 0.31 as provided in [((bibcite 2))], chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Table 3-2 | + | |
- | > **NOTE:** With respect | + | | |
+ | | **DIESEL OIL** |||||||||||||||||||| | ||
+ | ^ NH<sub>3</ | ||
+ | ^ NMVOC | ||
+ | ^ NO< | ||
+ | ^ SO< | ||
+ | ^ BC | 111 | 99.8 | 55.4 | 44.3 | 44.3 | 44.3 | 33.3 | 16.6 | 16.6 | 15.5 | 15.5 | 15.5 | 15.8 | 15.9 | 15.2 | 14.8 | 16.1 | 15.3 | 15.3 | | ||
+ | ^ PM< | ||
+ | ^ PM< | ||
+ | ^ TSP | ||
+ | ^ CO | 140 | 140 | 140 | 140 | 140 | 140 | 140 | 140 | 140 | 140 | 140 | 139 | 142 | 148 | 144 | 141 | 148 | 142 | 142 | | ||
+ | | **HEAVY FUEL OIL** | ||
+ | ^ NH< | ||
+ | ^ NMVOC | ||
+ | ^ NO< | ||
+ | ^ SO< | ||
+ | ^ BC | 42,3 | 42,7 | 42,4 | 42,9 | 23,9 | 23,8 | 23,8 | 23,8 | 15,9 | 15,9 | 15,9 | 14,9 | 16,3 | NA |||||| | ||
+ | ^ PM< | ||
+ | ^ PM< | ||
+ | ^ TSP | ||
+ | ^ CO | 154 | 154 | 154 | 154 | 154 | 154 | 154 | 154 | 154 | 154 | 154 | 148 | 157 | NA |||||| | ||
+ | < | ||
+ | < | ||
+ | < | ||
- | > For information on the **emission factors for heavy-metal and POP exhaust emissions**, please refer to [[[ appendix2.3-HM-from-mobile-sources | Appendix 2.3 - Heavy Metal (HM) exhaust emissions from mobile sources]]] and [[[ appendix2.4-POPs-from-mobile-sources | Appendix 2.4 - Persistent Organic Pollutant (POP) exhaust emissions from mobile sources ]]]. | + | <WRAP center round info 100%> |
+ | With respect to the emission factors | ||
+ | </ | ||
- | [!-- | + | <WRAP center round info 100%> |
+ | For information on the **emission factors for heavy-metal and POP exhaust emissions**, | ||
+ | </ | ||
- | + __Discussion | + | ===== Discussion |
- | > This sub-category | + | <WRAP center round info 60%> |
+ | As only NFR 1.A.5.b as a whole is taken into account within the key category analysis, this country-specific | ||
+ | </ | ||
- | Due to the application of very several tier1 emission factors, most emission trends reported for this sub-category only reflect the trend in fuel deliveries. | + | ===== Recalculations ===== |
- | Therefore, the fuel-consumption dependend trends in emission estimates are only influenced by the annual fuel mix. | + | |
- | ++ Selected main pollutants: NO,,x,, | + | **Activity data** have been revised widely after a correction of the underlying model. |
- | [[gallery size=" | + | | ^ 1990 |
- | : 1A5biii_EM(NOx).png | + | | **DIESEL OIL** |
- | [[/ | + | ^ Submission 2022 | 380 | 263 | 228 | 171 | 161 | 155 | 154 | 150 | 150 | 144 | 138 | 111 | 104 | 154 | 141 | 156 | 133 | 164 | |
+ | ^ Submission 2021 | 983 | 665 | 563 | 410 | 383 | 366 | 360 | 349 | 347 | 330 | 313 | 302 | 332 | 273 | 359 | 489 | 436 | 558 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **HEAVY FUEL OlL** | ||
+ | ^ Submission 2022 | 152 | 104 | 90,4 | 67,4 | 63,4 | 61,0 | 60,5 | 59,0 | 59,0 | 56,5 | 54,0 | 43,9 | 60,5 | | ||
+ | ^ Submission 2021 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **OVER-ALL FUEL CONSUMPTION** | ||
+ | ^ Submission 2022 | 532 | 366 | 318 | 239 | 225 | 216 | 214 | 209 | 209 | 200 | 192 | 155 | 165 | 154 | 141 | 156 | 133 | 164 | | ||
+ | ^ Submission 2021 | 983 | 665 | 563 | 410 | 383 | 366 | 360 | 349 | 347 | 330 | 313 | 302 | 332 | 273 | 359 | 489 | 436 | 558 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
- | ++ Sulphur dioxide and particulate matter | ||
- | As fuel sulphur content underlies strict legislation, the trends of these directly related emissions reflect the outcome of ever lower fuel sulphur contents. | + | In addition, several **emission factors** for diesel oil have been revised within |
- | [[gallery size=" | + | | |
- | : 1A5biii_EM(SOx).png | + | | **AMMONIA** |
- | : 1A5biii_EM(PM).png | + | ^ Submission 2022 |
- | [[/ | + | ^ Submission 2021 |
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **NMVOC** | ||
+ | ^ Submission 2022 | ||
+ | ^ Submission 2021 | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **NITROGEN OXIDES** | ||
+ | ^ Submission 2022 | ||
+ | ^ Submission 2021 | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **SULPHUR OXIDES** | ||
+ | ^ Submission 2022 | ||
+ | ^ Submission 2021 | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **BLACK CARBON** | ||
+ | ^ Submission 2022 | ||
+ | ^ Submission 2021 | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **PARTICULATE MATTER** | ||
+ | ^ Submission 2022 | ||
+ | ^ Submission 2021 | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **CARBON MONOXIDE** | ||
+ | ^ Submission 2022 | ||
+ | ^ Submission 2021 | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
- | --] | ||
- | + __Recalculations__ | + | <WRAP center round info 65%> |
+ | For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the recalculation tables following [[general: | ||
+ | </ | ||
- | The small changes in the **activity data** applied result solely from a revised biofuel share for biodiesel in 2017: | + | ===== Uncertainties ===== |
- | __Table 4: Revised fuel consumption data 2017, in terajoules__ | + | See [[sector:energy: |
- | || ||= **TOTAL** ||= **Diesel Oil** ||= **Biodiesel** ||= | + | |
- | ||~ Submission 2020 ||> | + | |
- | ||~ Submission 2019 ||> | + | |
- | ||~ absolute change ||> | + | |
- | ||~ relative change ||> | + | |
- | In contrast, all (annual) country-specific **emission factors** remain unaltered. | + | ===== Planned improvements ===== |
- | + | ||
- | + | ||
- | > For more pollutant-specific information on **recalculated emission estimates for Base Year and 2017**, please see the pollutant specific recalculation tables following chapter [[[recalculations | 8.1 - Recalculations]]]. | + | |
- | + | ||
- | + __Uncertainties__ | + | |
- | + | ||
- | See [[[1-a-5-b-other-military-mobile-combustion | superordinate chapter]]] on NFR 1.A.5.b. | + | |
- | + | ||
- | + __Planned improvements__ | + | |
A **routine revision** of the underlying model is planned for the next annual submission. | A **routine revision** of the underlying model is planned for the next annual submission. | ||
- | ------ | ||
- | [[bibliography]] | ||
- | : 1 : Deichnik (2019): Deichnik, K.: Aktualisierung und Revision des Modells zur Berechnung der spezifischen Verbräuche und Emissionen des von Deutschland ausgehenden Seeverkehrs. from Bundesamts für Seeschifffahrt und Hydrographie (BSH); Hamburg, | + | [(DEICHNIK2021> |
- | : 2 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, Copenhagen, 2019. | + | [(EMEPEEA2019> |
- | : 3 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, | + | [(RENTZ2008> |
- | [[/ | + |