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--- sector:energy:fuel_combustion:other_including_military:military_transport:military_navigation [2021/01/17 18:25] – kotzulla
+++ sector:energy:fuel_combustion:other_including_military:military_transport:military_navigation [2023/02/10 09:50] (current) – kotzulla
@@ Line 5: / Line 5: @@
 In sub-category //1.A.5.b iii - Other, Mobile (including Military)// emissions from military navigation are reported.
-^  Method  ^  AD     ^  EF                ^  Key Category                                                                                              ^
+^  Method  ^  AD     ^  EF                ^  Key Category Analysis                                                                                             ^
 |  T1, T2  |  NS, M  |  D, M, CS, T1, T3  |  see [[sector:energy:fuel_combustion:other_including_military:military_transport| superordinate chapter]]  |
-===== Method =====
+===== Methodology =====
-===Activity Data ===
+==== Activity Data ====
-Primary fuel data for national military waterborne activities is included in NEB lines 6 ('International Deep-Sea Bunkers') and 64 ('Coastal and Inland Navigation') for IMO and non-IMO ships respectively.
+Primary fuel data for national military waterborne activities is included in NEB lines 6 ('International Deep-Sea Bunkers') and 64 ('Coastal and Inland Navigation') for IMO-registered and not registered ships respectively.
-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. (2022)) [(DEICHNIK2022)], where ship movement data (AIS signal) allows for a bottom-up approach providing the needed differentiation.
 __Table 1: Annual fuel consumption, in terajoules__
-|                    |  **1990**  |  **1995**  |  **2000**  |  **2005**  |  **2006**  |  **2007**  |  **2008**  |  **2009**  |  **2010**  |  **2011**  |  **2012**  |  **2013**  |  **2014**  |  **2015**  |  **2016**  |  **2017**  |  **2018**  | **2019**  |
+|                    ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^ 2019  ^ 2020  ^  2021  ^
-^ Diesel Oil         |        983 |        665 |        563 |        410 |        383 |        366 |        360 |        349 |        347 |        330 |        313 |        302 |        332 |        273 |        359 |        489 |        423 |           |
+^ Diesel Oil         |    380 |    263 |    228 |    171 |    150 |    144 |    138 |    111 |    104 |    154 |    141 |    156 |    133 |   164 |   195 |    118 |
-^ Biodiesel          |          0 |          0 |          0 |          9 |         11 |         16 |         18 |         24 |         22 |         21 |         20 |         18 |         19 |         14 |         11 |         11 |         11 |           |
+^ Heavy Fuel Oil     |    152 |    104 |   90.4 |   67.4 |   59.0 |   56.5 |   54.0 |   43.9 |   60.5 |      0 |      0 |      0 |      0 |     0 |     0 |      0 |
-^ Heavy Fuel Oil     |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |          0 |           |
+| **Ʃ 1.A.5.b iii**  ^    532 ^    366 ^    318 ^    239 ^    209 ^    200 ^    192 ^    155 ^    165 ^    154 ^    141 ^    156 ^    133 ^   164 ^   195 ^    118 ^
-| **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. (2022): BSH model 2022
-source: Deichnik, K. (2019): BSH model [((bibcite 1))]
-[[gallery size="medium"]]
+{{ :sector:energy:fuel_combustion:other_incl_military:1a5biii_AD.png?700 | Annual liquid fuels consumption }}
-: 1A5biii_AD.png
-: 1A5biii_AD_bio.png
-[[/gallery]]
-=== Emission factors ===
+==== Emission factors ====
 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 (2022)) 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 implied emission factors<sup>1</sup> for diesel fuels, in kg/TJ__
-|		|	**1990**	|	**1995**	|	**2000**	|	**2005**	|	**2006**	|	**2007**	|	**2008**	|	**2009**	|	**2010**	|	**2011**	|	**2012**	|	**2013**	|	**2014**	|	**2015**	|	**2016**	|	**2017**	|	**2018**	|
+|                     ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^
-^	NH<sub>3</sub>      |	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.33	|	0.32	|	0.33	|	0.33	|	0.33	|
+| **DIESEL OIL**      |        |        |        |        |        |        |        |        |        |        |        |        |        |        |        |        |
-^	NMVOC	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.4	|	41.6	|	41.1	|	47.7	|	37.4	|	38.0	|	39.1	|
+^ NH<sub>3</sub>      |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |
-^	NO<sub>x</sub>	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,106	|	1,105	|	1,098	|	1,011	|	1,119	|	1,124	|	1,117	|
+^ NMVOC               |   39.6 |   39.6 |   39.6 |   39.6 |   39.6 |   39.6 |   39.6 |   40.0 |   39.4 |   34.2 |   34.1 |   34.1 |   36.2 |   35.5 |   36.6 |   36.6 |
-^	SO<sub>x</sub>	|	466	|	419	|	233	|	186	|	186	|	186	|	140	|	69.8	|	69.8	|	65.2	|	59.4	|	55.9	|	53.4	|	40.0	|	38.7	|	38.8	|	39.3	|
+^ NO<sub>x</sub>      |  1,228 |  1,228 |  1,228 |  1,228 |  1,228 |  1,228 |  1,228 |  1,221 |  1,227 |  1,286 |  1,294 |  1,298 |  1,252 |  1,265 |  1,274 |  1,274 |
-^	BC	|	109	|	98.3	|	54.6	|	43.7	|	43.7	|	43.7	|	32.8	|	16.4	|	16.4	|	15.3	|	15.3	|	15.3	|	16.1	|	19.6	|	16.3	|	15.2	|	15.8	|
+^ SO<sub>x</sub>      |    466 |    419 |    233 |    186 |   69.8 |   65.2 |   60.3 |   56.7 |   53.7 |   37.2 |   37.2 |   37.2 |   37.2 |   37.2 |   37.2 |   37.2 |
-^	PM<sub>2.5</sub>	|	352	|	317	|	176	|	141	|	141	|	141	|	106	|	52.9	|	52.9	|	49.3	|	49.3	|	49.3	|	51.9	|	63.2	|	52.6	|	49.0	|	51.0	|
+^ BC                  |    111 |   99.8 |   55.4 |   44.3 |   16.6 |   15.5 |   15.5 |   15.5 |   15.8 |   15.9 |   15.2 |   14.8 |   16.1 |   15.3 |   13.1 |   13.1 |
-^	PM<sub>10</sub>	|	377	|	339	|	189	|	151	|	151	|	151	|	113	|	56.6	|	56.6	|	52.8	|	52.8	|	52.7	|	55.5	|	67.7	|	56.3	|	52.4	|	54.6	|
+^ PM<sub>2.5</sub>    |    358 |    322 |    179 |    143 |   53.6 |   50.1 |   50.1 |   50.1 |   51.0 |   51.2 |   49.1 |   47.8 |   51.9 |   49.3 |   42.2 |   42.2 |
-^	TSP	|	377	|	339	|	189	|	151	|	151	|	151	|	113	|	56.6	|	56.6	|	52.8	|	52.8	|	52.7	|	55.5	|	67.7	|	56.3	|	52.4	|	54.6	|
+^ PM<sub>10</sub>     |    383 |    344 |    191 |    153 |   57.4 |   53.6 |   53.6 |   53.6 |   54.6 |   54.8 |   52.5 |   51.1 |   55.5 |   52.7 |   45.1 |   45.1 |
-^	CO	|	136	|	136	|	136	|	136	|	136	|	136	|	136	|	136	|	136	|	136	|	136	|	136	|	142	|	158	|	148	|	139	|	142	|
+^ TSP                 |    383 |    344 |    191 |    153 |   57.4 |   53.6 |   53.6 |   53.6 |   54.6 |   54.8 |   52.5 |   51.1 |   55.5 |   52.7 |   45.1 |   45.1 |
+^ CO                  |    140 |    140 |    140 |    140 |    140 |    140 |    140 |    139 |    142 |    148 |    144 |    141 |    148 |    142 |    127 |    127 |
+| **HEAVY FUEL OIL**  |        |        |        |        |        |        |        |        |        |        |        |        |        |        |        |        |
+^ NH<sub>3</sub>      |   0.34 |   0.34 |   0.34 |   0.34 |   0.34 |   0.34 |   0.34 |   0.34 |   0.35 |  NA                                                    |||||||
+^ NMVOC               |   28.0 |   28.0 |   28.0 |   28.0 |   28.0 |   28.0 |   28.0 |   27.0 |   28.6 |  NA                                                    |||||||
+^ NO<sub>x</sub>      |  1,468 |  1,468 |  1,468 |  1,468 |  1,468 |  1,468 |  1,468 |  1,488 |  1,496 |  NA                                                    |||||||
+^ SO<sub>x</sub>      |  1,319 |  1,332 |  1,323 |  1,336 |    496 |    496 |    496 |    495 |    506 |  NA                                                    |||||||
+^ BC                  |   42,3 |   42,7 |   42,4 |   42,9 |   15,9 |   15,9 |   15,9 |   14,9 |   16,3 |  NA                                                    |||||||
+^ PM<sub>2.5</sub>    |    353 |  356,0 |    354 |    357 |    132 |    133 |    133 |    124 |    136 |  NA                                                    |||||||
+^ PM<sub>10</sub>     |    388 |    392 |    389 |    393 |    146 |    146 |    146 |    137 |    150 |  NA                                                    |||||||
+^ TSP                 |    388 |    392 |    389 |    393 |    146 |    146 |    146 |    137 |    150 |  NA                                                    |||||||
+^ CO                  |    154 |    154 |    154 |    154 |    154 |    154 |    154 |    148 |    157 |  NA                                                    |||||||
 <sup>1</sup> due to lack of better information: similar EF are applied for fossil and biodiesel \\
-<sup>2</sup> ratio PM<sub>2.5</sub> : PM<sub>10</sub> : TSP derived from the tier1 default EF as provided in [((bibcite 2))]
+<sup>2</sup> ratio PM<sub>2.5</sub> : PM<sub>10</sub> : TSP derived from the tier1 default EF as provided in [(EMEPEEA2019)]   \\
-<sup>3</sup> 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
+<sup>3</sup> estimated from a BC-fraction of 0.31 as provided in [(EMEPEEA2019)], chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Table 3-2
 <WRAP center round info 100%>
-With respect to the emission factors applied for particulate matter, given the circumstances during test-bench measurements, condensables are most likely included at least partly.[[footnote]] During test-bench measurements, temperatures are likely to be significantly higher than under real-world conditions, thus reducing condensation. On the contrary, smaller dillution (higher number of primary particles acting as condensation germs) together with higher pressures increase the likeliness of condensation. So over-all condensables are very likely to occur but different to real-world conditions. [[/footnote]]
+With respect to the emission factors applied for particulate matter, given the circumstances during test-bench measurements, condensables are most likely included at least partly. ((During test-bench measurements, temperatures are likely to be significantly higher than under real-world conditions, thus reducing condensation. On the contrary, smaller dillution (higher number of primary particles acting as condensation germs) together with higher pressures increase the likeliness of condensation. So over-all condensables are very likely to occur but different to real-world conditions.))
 </WRAP>
+<WRAP center round info 100%>
-<WRAP center round info 60%>
+For information on the **emission factors for heavy-metal and POP exhaust emissions**, please refer to Appendix 2.3 - Heavy Metal (HM) exhaust emissions from mobile sources and Appendix 2.4 - Persistent Organic Pollutant (POP) exhaust emissions from mobile sources.
-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>
-[!--
 ===== Discussion of emission trends =====
-> This sub-category is **not considered separately in the key category analysis**.
+<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 sub-sector is not considered separately.
-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.
+</WRAP>
-Therefore, the fuel-consumption dependend trends in emission estimates are only influenced by the annual fuel mix.
-++ Selected main pollutants: NO,,x,,
-[[gallery size="medium"]]
-: 1A5biii_EM(NOx).png
-[[/gallery]]
-++ 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.
-[[gallery size="medium"]]
-: 1A5biii_EM(SOx).png
-: 1A5biii_EM(PM).png
-[[/gallery]]
---]
 ===== Recalculations =====
-The small changes in the **activity data** applied result solely from a revised biofuel share for biodiesel in 2017:
+<WRAP center round info 60%>
+For information on revised inventory data, please see the [[sector:energy:fuel_combustion:other_including_military:military_transport| superordinate chapter]].
+</WRAP>
-__Table 4: Revised fuel consumption data 2017, in terajoules__
+===== Uncertainties =====
-||		||=	 **TOTAL**	||=	 **Diesel Oil**	||=	 **Biodiesel**	||=
-||~	Submission 2020	||>	500.2	||>	489.3	||>	10.9 	||=
-||~	Submission 2019	||>	500.6	||>	489.3	||>	11.3 	||=
-||~	absolute change	||>	-0.40	||>	0.00  	||>	-0.40	||=
-||~	relative change	||>	-0.08%	||>	0.00%	||>	-3.57%	||=
-In contrast, all (annual) country-specific **emission factors** remain unaltered.
 <WRAP center round info 60%>
-For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following chapter [[general:recalculations:start | 8.1 - Recalculations]].
+For uncertainty information, please see the [[sector:energy:fuel_combustion:other_including_military:military_transport| superordinate chapter]].
 </WRAP>
-===== Uncertainties =====
-See [[sector:energy:fuel_combustion:other_including_military:military_transport| superordinate chapter]] on NFR 1.A.5.b.
 ===== Planned improvements =====
 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, 2019.
+[(DEICHNIK2022> Deichnik (2022): 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, 2022.)]
-: 2 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, Copenhagen, 2019.
+[(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, Copenhagen, 2019.)]
-: 3 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, FKZ 205 67 444, UBA Texte | 01/2008, January 2008 - URL: http://www.umweltbundesamt.de/en/publikationen/nationaler-durchfuehrungsplan-unter-stockholmer
+[(RENTZ2008> Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, FKZ 205 67 444, UBA Texte | 01/2008, January 2008 - URL: http://www.umweltbundesamt.de/en/publikationen/nationaler-durchfuehrungsplan-unter-stockholmer )]
-[[/bibliography]]

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