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sector:energy:fuel_combustion:transport:navigation:national_navigation [2021/04/10 09:10] – [Table] kotzullasector:energy:fuel_combustion:transport:navigation:national_navigation [2021/12/15 20:00] (current) – external edit 127.0.0.1
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 ==== Activity data ==== ==== Activity data ====
  
-As described for the over-all sector 1.A.3.d and all other navigational activities [[[1-a-3-d-navigation | here ]]], specific fuel consumption data for NFR 1.A.3.d ii  is included in the primary fuel deliveries data provided in NEB lines 6 ('International Maritime Bunkers') and 64 ('Coastal and Inland Navigation') [(AGEB2020)]. +As described for the over-all sector 1.A.3.d and all other navigational activities in the superordinate chapter, specific fuel consumption data for NFR 1.A.3.d ii is included in the primary fuel deliveries data provided in NEB lines 6 ('International Maritime Bunkers') and 64 ('Coastal and Inland Navigation') [(AGEB2020)]. 
  
 Here, the annual fuel consumption for domestic //maritime// navigation are modelled within [(DEICHNIK2020)] based on AIS data and deduced from NEB lines 6 and 64 respectively, depending on whether or not a certain ship is registered by the International Maritime Organization (IMO). Here, fuels consumed by large, IMO-registered and sea-going ships and vessels are included in NEB line 6 whereas fuels consumed by smaller ships without IMO-registration are included in NEB line 64. After these deductions, the amounts of fuels remaining in NEB 64 are allocated to domestic //inland// navigation. Here, the annual fuel consumption for domestic //maritime// navigation are modelled within [(DEICHNIK2020)] based on AIS data and deduced from NEB lines 6 and 64 respectively, depending on whether or not a certain ship is registered by the International Maritime Organization (IMO). Here, fuels consumed by large, IMO-registered and sea-going ships and vessels are included in NEB line 6 whereas fuels consumed by smaller ships without IMO-registration are included in NEB line 64. After these deductions, the amounts of fuels remaining in NEB 64 are allocated to domestic //inland// navigation.
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 ^ Heavy fuel oil    |     11,723 |      8,041 |      8,577 |      7,172 |      6,114 |      5,961 |      6,410 |      6,376 |      6,046 |       50,0 |       7,05 |       7,01 |        190 |       358 | ^ Heavy fuel oil    |     11,723 |      8,041 |      8,577 |      7,172 |      6,114 |      5,961 |      6,410 |      6,376 |      6,046 |       50,0 |       7,05 |       7,01 |        190 |       358 |
 | **Ʃ 1.A.3.d ii**  ^     48,326 ^     37,896 ^     27,224 ^     25,768 ^     22,297 ^     22,916 ^     23,011 ^     23,200 ^     24,578 ^     22,831 ^     24,174 ^     22,407 ^     24,037 ^    21,914 ^ | **Ʃ 1.A.3.d ii**  ^     48,326 ^     37,896 ^     27,224 ^     25,768 ^     22,297 ^     22,916 ^     23,011 ^     23,200 ^     24,578 ^     22,831 ^     24,174 ^     22,407 ^     24,037 ^    21,914 ^
- 
- 
  
 __Table 2: Specific fuel consumption data for domestic maritime and inland navigation, in terajoule__ __Table 2: Specific fuel consumption data for domestic maritime and inland navigation, in terajoule__
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 ^ Diesel Oil                        |     20.664 |     18.597 |      6.788 |      8.634 |      7.497 |      8.466 |      7.556 |      7.777 |      8.567 |      9.422 |      7.873 |      7.179 |      7.511 |     7.595 | ^ Diesel Oil                        |     20.664 |     18.597 |      6.788 |      8.634 |      7.497 |      8.466 |      7.556 |      7.777 |      8.567 |      9.422 |      7.873 |      7.179 |      7.511 |     7.595 |
 | **Ʃ 1.A.3.d ii**                  ^     48.326 ^     37.896 ^     27.224 ^     25.768 ^     22.297 ^     22.916 ^     23.011 ^     23.200 ^     24.578 ^     22.831 ^     24.174 ^     22.407 ^     24.037 ^    21.914 ^ | **Ʃ 1.A.3.d ii**                  ^     48.326 ^     37.896 ^     27.224 ^     25.768 ^     22.297 ^     22.916 ^     23.011 ^     23.200 ^     24.578 ^     22.831 ^     24.174 ^     22.407 ^     24.037 ^    21.914 ^
 +
 +{{ :sector:energy:fuel_combustion:transport:navigation:1a3dii_ad.png?700 }}
 +
 +==== Emission factors====
  
 The emission factors applied for **national maritime navigation** are derived from different sources and therefore are of very different quality. The emission factors applied for **national maritime navigation** are derived from different sources and therefore are of very different quality.
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 Here, for **sulphur dioxide** and **particulate matter**, annual values are available representing the impact of fuel sulphur legislation. Here, for **sulphur dioxide** and **particulate matter**, annual values are available representing the impact of fuel sulphur legislation.
-In addition, regarding SO,,x,,, the increasing operation of so-called scrubbers in order to fullfil emission limits especially within SECA areas is reflected for heavy fuel oil.+In addition, regarding <sub>2</sub>, the increasing operation of so-called scrubbers in order to fullfil emission limits especially within SECA areas is reflected for heavy fuel oil.
  
 __Table 3: Country-specific emission factors applied for fuels used in domestic maritime navigation, in [kg/TJ]__ __Table 3: Country-specific emission factors applied for fuels used in domestic maritime navigation, in [kg/TJ]__
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 ^ NMVOC                     48,7 |       48,7 |       48,7 |       48,7 |       48,7 |       48,7 |       48,7 |       48,4 |       48,0 |       44,8 |       44,7 |       45,0 |       45,2 |      45,2 | ^ NMVOC                     48,7 |       48,7 |       48,7 |       48,7 |       48,7 |       48,7 |       48,7 |       48,4 |       48,0 |       44,8 |       44,7 |       45,0 |       45,2 |      45,2 |
 ^ NO<sub>x</sub>      |      1.070 |      1.070 |      1.070 |      1.070 |      1.069 |      1.069 |      1.069 |      1.073 |      1.077 |      1.151 |      1.132 |      1.157 |      1.128 |     1.128 | ^ NO<sub>x</sub>      |      1.070 |      1.070 |      1.070 |      1.070 |      1.069 |      1.069 |      1.069 |      1.073 |      1.077 |      1.151 |      1.132 |      1.157 |      1.128 |     1.128 |
-^ SO<sub>x</sub>      |      465,5 |      419,0 |      232,8 |      186,2 |       69,8 |      65,18 |      54,53 |      52,56 |      50,48 |      40,74 |      40,61 |      40,74 |      40,76 |     40,76 |+^ SO<sub>2</sub>      |      465,5 |      419,0 |      232,8 |      186,2 |       69,8 |      65,18 |      54,53 |      52,56 |      50,48 |      40,74 |      40,61 |      40,74 |      40,76 |     40,76 |
 ^ BC<sup>1</sup>      |      109,2 |       98,6 |       54,7 |       43,8 |       16,4 |       15,4 |       15,3 |       15,2 |       15,2 |       16,3 |       16,9 |       16,9 |       16,5 |      16,5 | ^ BC<sup>1</sup>      |      109,2 |       98,6 |       54,7 |       43,8 |       16,4 |       15,4 |       15,3 |       15,2 |       15,2 |       16,3 |       16,9 |       16,9 |       16,5 |      16,5 |
 ^ PM<sub>2.5</sub>    |      352,4 |      318,0 |      176,5 |      141,2 |       53,0 |       49,6 |       49,5 |       49,1 |       49,1 |       52,7 |       54,5 |       54,5 |       53,1 |      53,1 | ^ PM<sub>2.5</sub>    |      352,4 |      318,0 |      176,5 |      141,2 |       53,0 |       49,6 |       49,5 |       49,1 |       49,1 |       52,7 |       54,5 |       54,5 |       53,1 |      53,1 |
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 ^ TSP<sup>2</sup>            526 |        532 |        528 |        533 |        198 |        198 |        198 |        203 |        206 |        166 |        226 |        168 |        135 |       135 | ^ TSP<sup>2</sup>            526 |        532 |        528 |        533 |        198 |        198 |        198 |        203 |        206 |        166 |        226 |        168 |        135 |       135 |
 ^ CO                  |        162 |        162 |        162 |        162 |        162 |        162 |        162 |        162 |        167 |        165 |        198 |        167 |        134 |       134 | ^ CO                  |        162 |        162 |        162 |        162 |        162 |        162 |        162 |        162 |        167 |        165 |        198 |        167 |        134 |       134 |
-<sup>1</sup> estimated from f-BCs as provided in [(EMEPEEA2019)]: f-BC (HFO) = 0.12, f-BC (MDO/MGO) = 0.31 as provided in [((bibcite 2))], chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Tables 3-1 & 3-2 \\+<sup>1</sup> estimated from f-BCs as provided in [(EMEPEEA2019)]: f-BC (HFO) = 0.12, f-BC (MDO/MGO) = 0.31 as provided in [(EMEPEEA2019)], chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Tables 3-1 & 3-2 \\
 <sup>2</sup> ratio of PM<sub>2.5</sub> : PM<sub>10</sub> : TSP derived from the tier1 default EF as provided in [(EMEPEEA2019)], chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Tables 3-1 & 3-2 <sup>2</sup> ratio of PM<sub>2.5</sub> : PM<sub>10</sub> : TSP derived from the tier1 default EF as provided in [(EMEPEEA2019)], chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Tables 3-1 & 3-2
  
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 </WRAP> </WRAP>
    
- +For main pollutants and particulate matter from **national inland navigation**, modelled emission factors are available from TREMOD (Knörr et al. (2020a)) [(KNOERR2020a)].  
-For main pollutants and particulate matter from **national inland navigation**, modelled emission factors are available from TREMOD (Knörr et al. (2019a)) [((bibcite 5))].  +Here, for //SO<sub>2</sub>,// and //PM//, annual values reflect the impact of fuel-sulphur legislation.
-Here, for //SO,,2,,// and //PM//, annual values reflect the impact of fuel-sulphur legislation.+
  
 __Table 4: Country-specific emission factors for diesel fuels used in domestic inland navigation, in [kg/TJ]__ __Table 4: Country-specific emission factors for diesel fuels used in domestic inland navigation, in [kg/TJ]__
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 ^ PM<sup>2</sup>  |       56,5 |       51,7 |       45,6 |       39,3 |       32,5 |       31,8 |       31,0 |       30,5 |       29,8 |       29,2 |       28,6 |       28,0 |       27,5 |      27,5 | ^ PM<sup>2</sup>  |       56,5 |       51,7 |       45,6 |       39,3 |       32,5 |       31,8 |       31,0 |       30,5 |       29,8 |       29,2 |       28,6 |       28,0 |       27,5 |      27,5 |
 ^ CO              |        417 |        387 |        337 |        307 |        277 |        272 |        266 |        261 |        256 |        251 |        246 |        241 |        236 |       236 | ^ CO              |        417 |        387 |        337 |        307 |        277 |        272 |        266 |        261 |        256 |        251 |        246 |        241 |        236 |       236 |
-<sup>1</sup> calculated from f-BC as provided in [((bibcite 3))], Chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii, Table 3-2: f-BC (MDO/MGO) = 0.31 \\ +<sup>1</sup> calculated from f-BC as provided in [(EMEPEEA2019)], Chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii, Table 3-2: f-BC (MDO/MGO) = 0.31 \\ 
-<sup>2</sup> EF(PM,,2.5,,) also applied for PM,,10,, and TSP (assumption: > 99% of TSP from diesel oil combustion consists of PM,,2.5,,)+<sup>2</sup> EF(PM<sub>2.5</sub>) also applied for PM<sub>10</sub> and TSP (assumption: > 99% of TSP from diesel oil combustion consists of PM<sub>2.5</sub>)
  
 <WRAP center round info 100%> <WRAP center round info 100%>
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 <WRAP center round info 100%> <WRAP center round info 100%>
-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 ]]].+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.
 </WRAP> </WRAP>
- 
  
 ===== Discussion of emission trends ===== ===== Discussion of emission trends =====
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 For **ammonia**, **NMVOC**, and **nitrogen oxides** as well as **carbon monoxide**, emission trends more or less represent the trend in over-all fuel consumption.  For **ammonia**, **NMVOC**, and **nitrogen oxides** as well as **carbon monoxide**, emission trends more or less represent the trend in over-all fuel consumption. 
 +
 +{{ :sector:energy:fuel_combustion:transport:navigation:1a3dii_em_nox.png?700 }}
  
 Nonetheless, for these pollutants, annual emission factors from BSH [(DEICHNIK2020)] and TREMOD [(KNOERR2020a)] have been applied for national //maritime// and //inland// navigation, respectively, reflecting the technical development of the German inland navigation fleet. Nonetheless, for these pollutants, annual emission factors from BSH [(DEICHNIK2020)] and TREMOD [(KNOERR2020a)] have been applied for national //maritime// and //inland// navigation, respectively, reflecting the technical development of the German inland navigation fleet.
  
 Here, the trends in **sulphur dioxide** and **particulate matter** emissions reflect the impact of ongoing fuel-sulphur legislation especially in maritime navigation. Here, the trends in **sulphur dioxide** and **particulate matter** emissions reflect the impact of ongoing fuel-sulphur legislation especially in maritime navigation.
 +
 +{{ :sector:energy:fuel_combustion:transport:navigation:1a3dii_em_so2.png?700 }}
 +{{ :sector:energy:fuel_combustion:transport:navigation:1a3dii_em_pm.png?700 }}
  
 ===== Recalculations ===== ===== Recalculations =====
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 ^ relative change                |      0,00% |      0,00% |      0,00% |    -0,46% |    -1,37% |    -1,38% |     -1,37% |     -1,23% |    -1,29% |    -1,23% |     -0,89% |     -0,87% |      1,55% | ^ relative change                |      0,00% |      0,00% |      0,00% |    -0,46% |    -1,37% |    -1,38% |     -1,37% |     -1,23% |    -1,29% |    -1,23% |     -0,89% |     -0,87% |      1,55% |
  
-Furthermore, the country-specific **emission factors** applied for diesel fuels used in **domestic inland navigation** have been revised within TREMOD [((bibcite 5))]:+Furthermore, the country-specific **emission factors** applied for diesel fuels used in **domestic inland navigation** have been revised within TREMOD [(KNOERR2020a)]:
  
 __Table 6: Revised country-specific emission factors for diesel fuels used in domestic inland navigation, in [kg/TJ]__ __Table 6: Revised country-specific emission factors for diesel fuels used in domestic inland navigation, in [kg/TJ]__
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 Besides the **routine revisions of the models** used for maritime and inland navigation, no specific improvements are scheduled. Besides the **routine revisions of the models** used for maritime and inland navigation, no specific improvements are scheduled.
  
-[(AGEB2020> AGEB, 2020: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; URL: http://www.ag-energiebilanzen.de/7-0-Bilanzen-1990-2018.html, Köln & Berlin, 2020)] +[(AGEB2020> AGEB, 2020: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; URL: http://www.ag-energiebilanzen.de/7-0-Bilanzen-1990-2018.html, (Aufruf: 29.11.2020), Köln & Berlin, 2020)] 
-: 2 : BAFA (2019): Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, BAFA): Amtliche Mineralöldaten für die Bundesrepublik Deutschland;  +[(BAFA2020> BAFA, 2020: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, BAFA): Amtliche Mineralöldaten für die Bundesrepublik Deutschland; 
-URL: https://www.bafa.de/SharedDocs/Downloads/DE/Energie/Mineraloel/moel_amtliche_daten_2018_dezember.xlsx?__blob=publicationFile&v=4, (Aufruf: 29.11.2019), Eschborn, 2019.  +URL: https://www.bafa.de/SharedDocs/Downloads/DE/Energie/Mineraloel/moel_amtliche_daten_2018_dezember.html, Eschborn, 2020.)] 
-: 3 : MWV, 2019: German Petroleum Industry Association (Mineralölwirtschaftsverband, MWV): MWV Jahresberichte: URL: https://www.mwv.de/publikationen/jahresberichte/, Berlin, 2019. +[(MWV2020> MWV (2020)Association of the German Petroleum Industry (Mineralölwirtschaftsverband, MWV): Annual Report 2018, page 65, Table 'Sektoraler Verbrauch von Dieselkraftstoff 2012-2018'; URL: https://www.mwv.de/wp-content/uploads/2020/09/MWV_Mineraloelwirtschaftsverband-e.V.-Jahresbericht-2020-Webversion.pdf, Berlin, 2020.)] 
-[DEICHNIK2020> Deichnik (2020): Deichnik, K.: Aktualisierung und Revision des Modells zur Berechnung der spezifischen Verbräuche und Emissionen des von Deutschland ausgehenden Seeverkehrsfrom Bundesamts für Seeschifffahrt und Hydrographie (BSH); Hamburg, 2020.)] +[(KNOERR2020a> Knörr et al. (2020a): Knörr, W., Heidt, C., Gores, S., & Bergk, F.: ifeu Institute for Energy and Environmental Research (Institut für Energie- und Umweltforschung Heidelberg gGmbH, ifeu): Fortschreibung des Daten- und Rechenmodells: Energieverbrauch und Schadstoffemissionen des motorisierten Verkehrs in Deutschland 1960-2035, sowie TREMOD, im Auftrag des Umweltbundesamtes, Heidelberg & Berlin, 2020.)] 
-: 5 : Knörr et al. (2019a): Knörr, W., Heidt, C., Gores, S., & Bergk, F.: ifeu Institute for Energy and Environmental Research (Institut für Energie- und Umweltforschung Heidelberg gGmbH, ifeu): Fortschreibung des Daten- und Rechenmodells: Energieverbrauch und Schadstoffemissionen des motorisierten Verkehrs in Deutschland 1960-2035, sowie TREMOD, im Auftrag des Umweltbundesamtes, Heidelberg & Berlin, 2019+[(DEICHNIK2020> Deichnik (2020)Aktualisierung und Revision des Modells zur Berechnung der spezifischen Verbräuche und Emissionen des von Deutschland ausgehenden Seeverkehrs. from Bundesamts für Seeschifffahrt und Hydrographie (BSH - Federal Maritime and Hydrographic Agency); Hamburg, 2020.)] 
-6 : EMEP/EEA (2019): EMEP/EEA air pollutant emission inventory guidebook 2019, Copenhagen, 2019. +[(EMEPEEA2019>EMEP/EEA2019: EMEP/EEA air pollutant emission inventory guidebook – 2019, Copenhagen, 2019.)] 
-[(KNOERR2009> Knörr et al. (2009): Knörr, W., Heldstab, J., & Kasser, F.: Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland; final report; URL: https://www.umweltbundesamt.de/sites/default/files/medien/461/publikationen/3937.pdf, FKZ 360 16 023, Heidelberg & Zürich, 2009. )]+[(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 )] 
 +[(KNOERR2009>Knörr et al. (2009): Knörr, W., Heldstab, J., & Kasser, F.: Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland; final report; URL: https://www.umweltbundesamt.de/sites/default/files/medien/461/publikationen/3937.pdf, FKZ 360 16 023, Heidelberg & Zürich, 2009.)]