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sector:energy:fuel_combustion:transport:navigation:international_maritime_navigation [2021/01/15 16:22] – kotzulla | sector:energy:fuel_combustion:transport:navigation:international_maritime_navigation [2021/12/15 20:00] (current) – external edit 127.0.0.1 | ||
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===== Short description ===== | ===== Short description ===== | ||
- | Under NFR category **1.A.3.d i (i)**, emissions from international maritime navigation fuelling in and starting form German harbours are reported. | + | Under NFR category **1.A.3.d i (i)**, emissions from international maritime navigation fuelling in and starting form German harbours are reported. |
- | + | ^ Category Code ^ Method | |
- | ^ Method | + | | 1.A.3.d i (i) |
- | | T1, T2, T3 | NS, M | CS, M | //not included in key category analysis// | + | ^ Key Category |
+ | | 1.A.3.d i (i) | ||
{{page> | {{page> | ||
+ | \\ | ||
- | The source category includes international deep sea fishery and international marine transport. | + | ===== Methodology ===== |
- | Emissions from fuel consumption for international transports of ocean-going ships are not reported as part of total national inventories. | + | |
- | ===== Method ===== | + | ==== Activity data ==== |
- | ===Activity data === | + | Primary fuel delivery data (primary activity data, PAD) for // |
- | + | ||
- | Primary fuel delivery data (primary activity data, PAD) for // | + | |
The AD applied for // | The AD applied for // | ||
- | [[math]] | + | | <WRAP left round info 100%> |
- | AD_\text{ | + | |
- | [[/math]] | + | |
__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** | | + | | | **1990** |
- | | Diesel Oil | 12,748 | 12,919 | 13,664 | 11,993 | 15,817 | 17,524 | 13,105 | 14,412 | 16,662 | 15,370 | 12,594 | 12,414 | 13,674 | 33,088 | 28,093 | 22,924 | 15,419 | | + | ^ Diesel Oil |
- | | Heavy | + | ^ Heavy fuel oil | |
- | | **Ʃ 1.A.3.d | + | | **Ʃ 1.A.3.d |
- | source: own estimates based on [((bibcite 2))] | + | source: own estimates based on underlying BSH model (Deichnik, K. (2020)) [(DEICHNIK2020)] |
- | + | ||
- | [[gallery size=" | + | |
- | : 1A3di_AD.png | + | |
- | [[/gallery]] | + | |
Consumption of heavy oil has been increasing since 1984 as a result of high petroleum prices, global increases in transports and increasing maritime use of diesel engines that can run on heavy oil. The emissions fluctuations that occurred in the navigation sector in 1992 and 1996 were caused by trade and oil crises. | Consumption of heavy oil has been increasing since 1984 as a result of high petroleum prices, global increases in transports and increasing maritime use of diesel engines that can run on heavy oil. The emissions fluctuations that occurred in the navigation sector in 1992 and 1996 were caused by trade and oil crises. | ||
- | ++ Emission factors | + | Furthermore, |
+ | |||
+ | {{ : | ||
+ | |||
+ | ==== Emission factors | ||
- | For **main pollutants** and **particulate matter**, modelled emission factors are available from (Deichnik, K. (2019)) [((bibcite 2))]. | + | For **main pollutants** and **particulate matter**, modelled emission factors are available from (Deichnik, K. (2020)) [(DEICHNIK2020)]. |
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 SO< |
__Table 2: Annual country-specific emission factors, in kg/TJ__ | __Table 2: Annual country-specific emission factors, in kg/TJ__ | ||
- | || ||= **1990** ||= **1995** ||= **2000** ||= **2005** ||= **2006** ||= **2007** ||= **2008** ||= **2009** ||= **2010** ||= **2011** ||= **2012** ||= **2013** ||= **2014** ||= **2015** ||= **2016** ||= **2017** ||= **2018** ||= | + | | |
- | ||||||||||||||||||||||||||||||||||||< | + | | **DIESEL OIL** ||||||||||||||| |
- | ||~ NH,,3,, ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.32 ||> 0.33 ||> 0.32 ||> 0.32 ||> 0.32 ||= | + | ^ NH<sub>3</ |
- | ||~ NMVOC ||> 48.7 ||> 48.7 ||> 48.7 ||> 48.7 ||> 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 ||= | + | ^ NMVOC |
- | ||~ NO,,x,, ||> 1,070 ||> 1,070 ||> 1,070 ||> 1,070 ||> 1,070 ||> 1,070 ||> 1,070 ||> 1,069 ||> 1,069 ||> 1,069 ||> 1,069 ||> 1,073 ||> 1,077 ||> 1,151 ||> 1,132 ||> 1,157 ||> 1,128 ||= | + | ^ NO<sub>x</ |
- | ||~ SO,,x,, ||> 465.5 ||> 419.0 ||> 232.8 ||> 186.2 ||> 186.2 ||> 186.2 ||> 139.7 ||> 69.8 ||> 69.8 ||> 65.2 ||> 54.5 ||> 52.6 ||> 50.5 ||> 40.7 ||> 40.6 ||> 40.7 ||> 40.8 ||= | + | ^ SO<sub>x</ |
- | ||~ PM,,2.5,,^^1^^ ||> 352.4 ||> 318.0 ||> 176.5 ||> 141.2 ||> 141.3 ||> 141.3 ||> 105.9 ||> 53.0 ||> 53.0 ||> 49.6 ||> 49.5 ||> 49.1 ||> 49.1 ||> 52.7 ||> 54.5 ||> 54.5 ||> 53.1 ||= | + | ^ BC< |
- | ||~ PM,,10,, ||> 377.1 ||> 340.3 ||> 188.9 ||> 151.0 ||> 151.2 ||> 151.2 ||> 113.3 ||> 56.7 ||> 56.7 ||> 53.0 ||> 53.0 ||> 52.5 ||> 52.6 ||> 56.4 ||> 58.3 ||> 58.3 ||> 56.9 ||= | + | ^ PM<sub>2.5</ |
- | ||~ TSP ||> 377.1 ||> 340.3 ||> 188.9 ||> 151.0 ||> 151.2 ||> 151.2 ||> 113.3 ||> 56.7 ||> 56.7 ||> 53.0 ||> 53.0 ||> 52.5 ||> 52.6 ||> 56.4 ||> 58.3 ||> 58.3 ||> 56.9 ||= | + | ^ PM<sub>10</ |
- | ||~ BC^^2^^ ||> | + | ^ TSP< |
- | ||~ CO ||> 127 ||> 128 ||> 128 ||> 128 ||> 128 ||> 128 ||> 128 ||> 128 ||> 128 ||> 128 ||> 128 ||> 127 ||> 128 ||> 134 ||> 139 ||> 138 ||> 136 ||= | + | ^ CO | 127 | 128 | 128 | 128 | 128 | 128 | 128 | 128 | 128 | 128 | 128 | 127 | 128 | |
- | ||||||||||||||||||||||||||||||||||||< | + | | **HEAVY FUEL OIL** ||||||||||||||| |
- | ||~ NH,,3,, ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.34 ||> 0.35 ||> 0.33 ||> 0.33 ||> 0.34 ||> 0.35 ||= | + | ^ NH<sub>3</ |
- | ||~ NMVOC ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 36.6 ||> 37.6 ||> 37.8 ||> 30.0 ||> 36.8 ||> 30.4 ||> 28.3 ||= | + | ^ NMVOC |
- | ||~ NO,,x,, ||> 1,379 ||> 1,378 ||> 1,378 ||> 1,378 ||> 1,378 ||> 1,378 ||> 1,378 ||> 1,378 ||> 1,378 ||> 1,377 ||> 1,379 ||> 1,382 ||> 1,393 ||> 1,348 ||> 1,245 ||> 1,360 ||> 1,503 ||= | + | ^ NO<sub>x</ |
- | ||~ SO,,x,, ||> 1,319 ||> 1,332 ||> 1,323 ||> 1,336 ||> 744 ||> 742 ||> 742 ||> 744 ||> 496 ||> 496 ||> 496 ||> 496 ||> 506 ||> 47.5 ||> 49.3 ||> 46.4 ||> 49.8 ||= | + | ^ SO<sub>x</ |
- | ||~ PM,,2.5,,^^1^^ ||> 479 ||> 483 ||> 480 ||> 485 ||> 270 ||> 269 ||> 269 ||> 270 ||> 180 ||> 180 ||> 180 ||> 184 ||> 187 ||> 151 ||> 205 ||> 153 ||> 123 ||= | + | ^ BC< |
- | ||~ PM,,10,, ||> 526 ||> 532 ||> 528 ||> 533 ||> 297 ||> 296 ||> 296 ||> 297 ||> 198 ||> 198 ||> 198 ||> 203 ||> 206 ||> 166 ||> 226 ||> 168 ||> 135 ||= | + | ^ PM<sub>2.5</ |
- | ||~ TSP ||> 526 ||> 532 ||> 528 ||> 533 ||> 297 ||> 296 ||> 296 ||> 297 ||> 198 ||> 198 ||> 198 ||> 203 ||> 206 ||> 166 ||> 226 ||> 168 ||> 135 ||= | + | ^ PM<sub>10</ |
- | ||~ BC^^2^^ ||> | + | ^ TSP< |
- | ||~ CO ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 162 ||> 167 ||> 165 ||> 198 ||> 167 ||> 134 ||= | + | ^ CO | 162 | 162 | 162 | 162 | 162 | 162 | 162 | 162 | 162 | 162 | 162 | 162 | 167 | |
- | ^^1^^ ratios PM,,2.5,, : PM,,10,, : TSP derived from the tier1 default EF as provided in [((bibcite 3))] | + | <sup>1</ |
- | ^^2^^ estimated from f-BCs as provided in [((bibcite | + | < |
- | > **NOTE: | + | <WRAP center round info 100%> |
+ | For the country-specific emission factors applied for particulate matter, no clear indication is available, whether or not condensables are included. | ||
+ | </ | ||
- | > For information on the **emission factors for heavy-metal and POP exhaust emissions**, | + | <WRAP center round info 100%> |
+ | For information on the **emission factors for heavy-metal and POP exhaust emissions**, | ||
+ | </ | ||
- | + __Trends of exhaust emissions from international navigation__ | ||
- | > **NFR 1.A.3.d i** is **not considered in the key category analysis**. | + | ===== Discussion of emission trends===== |
- | Emission trends for unregulated pollutants (such as **NH,,3,,**, **NO,,x,,**, **NMVOC** and **CO**, all **HM** and **POPs**) with only slight changes in the annual over-all IEFs applied, follow the trends in fuel consumption and the shares of diesel and heavy fuel oil: | + | **NFR 1.A.3.d i** is **not considered in the key category analysis**. |
- | [[gallery size=" | + | Emission trends for unregulated pollutants (such as **NH< |
- | : EM_1A3di_NH3.png | + | |
- | : EM_1A3di_Cd.png | + | |
- | [[/gallery]] | + | |
- | On the other hand, the emission trends for **SO,,x,,** and **PM**, both depending on the fuel's sulphur content, follow not only the trends in fuel consumption but do also reflect fuel-sulphur legislation: | + | {{ :sector: |
- | [[gallery size=" | + | On the other hand, the emission trends for **SO< |
- | : EM_1A3di_SO2.png | + | |
- | : EM_1A3di_PM.png | + | |
- | [[/ | + | |
- | + __Recalculations__ | + | {{ : |
- | Resulting from changes in the fuel consumption data computed within [((bibcite 2))] for // | + | ===== Recalculations ===== |
- | __Table 3: Revised | + | Resulting from changes in the fuel consumption data computed within [(DEICHNIK2020)] for // |
- | ||= ||= **Diesel oil** ||= **Heavy fuel oil** ||= **over-all consumption** ||= | + | |
- | ||~ Submission 2020 ||> | + | |
- | ||~ Submission 2019 ||> | + | |
- | ||~ absolute change ||> | + | |
- | ||~ relative change ||> | + | |
+ | __Table 3: Revised fuel consumption data 2018, in terajoules__ | ||
+ | | ^ Diesel< | ||
+ | ^ Submission 2021 | | ||
+ | ^ Submission 2020 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | < | ||
In contrast, all country-specific and default **emission factors applied remain unrevised** compared to last year's submission. | In contrast, all country-specific and default **emission factors applied remain unrevised** compared to last year's submission. | ||
- | > For more information on **recalculated emission estimates for Base Year and 2017**, please see the pollutant-specific recalculation tables following chapter [[[recalculations | 8.1 - Recalculations]]]. | + | <WRAP center round info 60%> |
+ | For more information on recalculated emission estimates for Base Year and 2018, please see the pollutant-specific recalculation tables following chapter [[general:recalculations: | ||
+ | </ | ||
- | + __Uncertainties__ | + | ===== Uncertainties ===== |
- | Uncertainty estimates for **activity data** of mobile sources derive from research project FKZ 360 16 023: " | + | Uncertainty estimates for **activity data** of mobile sources derive from research project FKZ 360 16 023: " |
- | + __Planned improvements__ | + | ===== Planned improvements ===== |
Besides routine maintenance and further development of the BSH model, no improvements are planned. | Besides routine maintenance and further development of the BSH model, no improvements are planned. | ||
- | ------ | + | ===== FAQs ===== |
- | [[bibliography]] | + | [(AGEB2020> |
- | : 1 : AGEB, 2019: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; | + | [(DEICHNIK2020> |
- | : 2 : Deichnik, K. (2019): 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, | + | [(EMEPEEA2019> |
- | : 3 : EMEP/EEA (2019): EMEP/EEA air pollutant emission inventory guidebook 2019, URL: https:// | + | [(RENTZ2008> |
- | : 4 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, | + | [(KNOERR2009> |
- | : 5 : 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; | + | |
- | [[/ | + |