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1.A.3.d ii - National Navigation

Short description

Under category 1.A.3.d ii - National Navigation emissions from national navigation (both inland and maritime) are reported.

Method AD EF Key Category Analysis
T1, T2, T3 NS, M CS, D, M L&T: PM,,10,, & PM,,2.5,, / L: NO,,x,,

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T = key source by Trend L = key source by Level

Methods
D Default
RA Reference Approach
T1 Tier 1 / Simple Methodology *
T2 Tier 2*
T3 Tier 3 / Detailed Methodology *
C CORINAIR
CS Country Specific
M Model
* as described in the EMEP/CORINAIR Emission Inventory Guidebook - 2007, in the group specific chapters.
AD - Data Source for Activity Data
NS National Statistics
RS Regional Statistics
IS International Statistics
PS Plant Specific data
AS Associations, business organisations
Q specific questionnaires, surveys
EF - Emission Factors
D Default (EMEP Guidebook)
C Confidential
CS Country Specific
PS Plant Specific data

Methodology

Activity data

As described for the over-all sector 1.A.3.d and all other navigational activities 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') 1).

Here, the annual fuel consumption for domestic maritime navigation are modelled within 2) 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.

Table 1: Annual over-all fuel consumption for domestic navigation, in terajoule

1990 1995 2000 2005 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019
Diesel Oil
Heavy fuel oil
Ʃ 1.A.3.d ii

gallery size="medium" : 1A3dii_AD.png gallery

Table 2: Specific fuel consumption data for domestic maritime and inland navigation, in terajoule

1990 1995 2000 2005 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019
NATIONAL MARITIME NAVIGATION
Diesel Oil 15940 11258 11860 9962 8685 8489 9046 9047 9965 13359 16295 15221 16336 13961
Heavy fuel oil 11723 8041 8577 7172 6114 5961 6410 6376 6046 50,0 7,05 7,01 190 358
NATIONAL INLAND NAVIGATION
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 6,636
Ʃ 1.A.3.d ii 48,326 37,896 27,224 26,036 22,988 23,673 23,719 23,846 25,282 23,528 24,635 22,927 23,298

The emission factors applied for national maritime navigation 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 the BSH model 3) which mainly relate on values from the EMEP/EEA guidebook 2019 4). 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.

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.

Table 3: Country-specific emission factors applied for fuels used in domestic maritime navigation, in [kg/TJ]

1990 1995 2000 2005 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019
DIESEL OIL
NH3
NMVOC
NOx
SOx
BC1
PM2.5
PM10
TSP2
HEAVY FUEL OIL
CO
NH3
NMVOC
NOx
SOx
BC1
PM2.5
PM10
TSP2
CO

1 estimated from f-BCs as provided in 5): f-BC (HFO) = 0.12, f-BC (MDO/MGO) = 0.31 as provided in 6), chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Tables 3-1 & 3-2
2 ratios PM,,2.5,, : PM,,10,, : TSP derived from the tier1 default EF as provided in 7), chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation, Tables 3-1 & 3-2

For the country-specific emission factors applied for particulate matter, no clear indication is available, whether or not condensables are included.

For main pollutants and particulate matter from national inland navigation, modelled emission factors are available from TREMOD (Knörr et al. (2019a)) 8). 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]

1990 1995 2000 2005 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019
NH3
NMVOC
NOx
SOx
BC1
PM2
CO

1 calculated from f-BC as provided in 9), 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
2 EF(PM,,2.5,,) also applied for PM,,10,, and TSP (assumption: > 99% of TSP from diesel oil combustion consists of PM,,2.5,,)

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. 1)

NFR 1.A.3.d ii is key category for emissions of NO,,x,,, PM,,2.5,, and PM,,10,,.

For ammonia, NMVOC, and nitrogen oxides as well as carbon monoxide, emission trends more or less represent the trend in over-all fuel consumption.

Nonetheless, for these pollutants, annual emission factors from BSH 10) and TREMOD 11) have been applied for national maritime and inland navigation, respectively, reflecting the technical development of the German inland navigation fleet.

gallery size="medium" : EM_1A3dii_NH3.png : EM_1A3dii_NMVOC.png : EM_1A3dii_NOx.png : EM_1A3dii_CO.png gallery

Here, the trends in sulphur dioxide and particulate matter emissions reflect the impact of ongoing fuel-sulphur legislation especially in maritime navigation.

gallery size="medium" : EM_1A3dii_SO2.png : EM_1A3dii_PM.png gallery

Recalculations

Major changes in activity data result from the revision of the National Energy Balance 2018. Furthermore, as no biodiesel is blended to marine diesel oil for technical reasons, no more biodiesel is reported for nautical activities. This correction results in additional recalculations for all years as of 2004.

Table 5: Revised fuel consumption data for national maritime navigation, in terajoules

1990 1995 2000 2005 2010 2011 2012 2013 2014 2015 2016 2017 2018
diesel oil
Submission 2021 15940 11258 11860 9962 8685 8489 9046 9047 9965 13359 16295 15221 16336
Submission 2020 15940 11258 11860 9962 8685 8489 9046 9047 9965 13359 16295 15221 15856
absolute change 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 480
relative change 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 3,03%
Biodiesel
Submission 2021 0 0 0 0 0 0 0 0 0 0 0 0 0
Submission 2020 0 0 0 79,2 205 202 215 192 210 167 146 134 135
absolute change 0,00 0,00 0,00 -79,2 -205 -202 -215 -192 -210 -167 -146 -134 -135
relative change -100% -100% -100% -100% -100% -100% -100% -100% -100% -100%
Heavy Fuel Oil
Submission 2021 11723 8041 8577 7172 6114 5961 6410 6376 6046 50,0 7,05 7,01 190
Submission 2020 11723 8041 8577 7172 6114 5961 6410 6376 6046 50,0 7,05 7,01 283
absolute change 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 0,00 -92,4
relative change 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% 0,00% -32,7%
over-all fuel consumption
Submission 2021 27662 19299 20436 17134 14799 14450 15455 15423 16011 13409 16302 15228 16527
Submission 2020 27662 19299 20436 17214 15004 14652 15670 15615 16220 13576 16448 15363 16274
absolute change 0,00 0,00 0,00 -79,2 -205 -202 -215 -192 -210 -167 -146 -134 253
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 12):

Table 6: Revised country-specific emission factors for diesel fuels used in domestic inland navigation, in [kg/TJ]

1990 1995 2000 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018
NON-METHANE VOLATILE ORGANIC COMPUNDS - NMVOC
Submission 2021
Submission 2020
absolute change
relative change
NITROGEN OXIDES
Submission 2021
Submission 2020
absolute change
relative change
SULPHUR OXIDES
Submission 2021
Submission 2020
absolute change
relative change
BLACK CARBON - BC
Submission 2021
Submission 2020
absolute change
relative change
PARTICULATE MATTER - PM
Submission 2021
Submission 2020
absolute change
relative change
CARBON MONOXIDE - CO
Submission 2021
Submission 2020
absolute change
relative change

In contrast, the country-specific emission factors applied for fuels used in national maritime navigation remain unaltered.

For more information on recalculated emission estimates for Base Year and 2018, please see the pollutant-specific recalculation tables following chapter 8.1 - Recalculations.

Uncertainties

Uncertainty estimates for activity data of mobile sources derive from research project FKZ 360 16 023: “Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland” by Knörr et al. (2009) 13).

Planned improvements

Besides the routine revisions of the models used for maritime and inland navigation, no specific improvements are scheduled.


bibliography : 1 : AGEB, 2019: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; URL: http://www.ag-energiebilanzen.de/7-0-Bilanzen-1990-2017.html, Köln & Berlin, 2019. : 2 : BAFA (2019): 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. : 3 : MWV, 2019: German Petroleum Industry Association (Mineralölwirtschaftsverband, MWV): MWV Jahresberichte: URL: https://www.mwv.de/publikationen/jahresberichte/, Berlin, 2019. : 4 : 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. : 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. : 6 : EMEP/EEA (2019): EMEP/EEA air pollutant emission inventory guidebook 2019, Copenhagen, 2019. : 7 : 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. bibliography


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1)
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.