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sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:fishing [2021/01/17 18:39] – created kotzullasector:energy:fuel_combustion:small_combustion:mobile_small_combustion:fishing [2023/05/17 07:44] (current) – [Planned improvements] kotzulla
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 ====== 1.A.4.c iii - Agriculture/Forestry/Fishing: National Fishing ====== ====== 1.A.4.c iii - Agriculture/Forestry/Fishing: National Fishing ======
 +
 +===== Short description =====
 +
 +In NFR sub-category //1.A.4.c iii// fuel consumption and emissions of Germany's maritime fishing fleet are reported. 
 +
 +^  Method  ^  AD      EF                ^  Key Category Analysis  ^
 +|  T1, T2  |  NS, M  |  D, M, CS, T1, T2  |  //no key category//    |
 +
 +
 +===== Methodology =====
 +
 +====Activity Data ====
 +
 +Primary fuel delivery data for national fishing is included in NEB lines 6 ('International Deep-Sea Bunkers') and 64 ('Coastal and Inland Navigation') for IMO-registered and unregistered ships respectively.
 +
 +The actual annual amounts used are therefore calculated within (Deichnik (2022)), where ship movement data (AIS signal) allows for a bottom-up approach providing the needed differentiation.[(DEICHNIK2022)]
 +
 +__Table 1: Annual fuel consumption, in terajoules__
 +|                    ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^
 +^ Diesel oil            305 |    240 |    238 |    226 |    227 |    213 |    209 |    214 |    227 |    284 |    298 |    293 |    356 |    322 |    359 |    265 |
 +^ Heavy fuel oil       33,3 |   26,0 |   26,0 |   24,4 |   24,5 |  23,0  |  22,6  |  16,8  |  13,8  |  NO    |  NO    |  NO    |  NO    |  NO    |  NO    |  NO    |
 +| **Ʃ 1.A.4.c iii**  ^    338 ^    266 ^    264 ^    250 ^    251 ^    236 ^    232 ^    231 ^    241 ^    284 ^    298 ^    293 ^    356 ^    322 ^    359 ^    265 ^
 +
 +The strong increase after 2015 cannot be conclusively explained at the moment. However, even if the over-all fuel quantities delivered to the navigation sector would be somehow misallocated between the specific nautical acitivities, there would be no over- or under-estimation of over-all emissions. 
 +
 +==== 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 the BSH model [(DEICHNIK2020)] 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, in kg/TJ__
 +|                      1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^
 +| **DIESEL OIL**                                                                                                                                      |||||||||||||||||
 +^ NH<sub>3</sub>      |   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 |   0.32 |   0.32 |   0.32 |
 +^ NMVOC                 50.2 |   50.2 |   50.2 |   50.2 |   50.2 |   50.2 |   50.2 |   49.5 |   46.4 |   45.6 |   45.2 |   46.4 |   46.3 |   46.3 |   46.6 |   45.5 |
 +^ NO<sub>x</sub>      |  1,139 |  1,139 |  1,139 |  1,139 |  1,139 |  1,139 |  1,139 |  1,139 |  1,172 |  1,172 |  1,174 |  1,164 |  1,172 |  1,170 |  1,171 |  1,181 |
 +^ SO<sub>x</sub>      |    466 |    419 |    233 |    186 |   69.8 |   65.2 |   55.5 |   53.6 |   50.8 |   37.2 |   37.2 |   37.2 |   37.2 |   37.2 |   37.2 |   37.2 |
 +^ BC <sup>2</sup>       83.7 |   75.3 |   41.8 |   33.5 |   12.5 |   11.7 |   11.7 |   12.3 |   12.3 |   12.5 |   12.7 |   12.4 |   12.2 |   12.0 |   11.6 |   11.5 |
 +^ PM <sub>2.5</sub>      270 |    243 |    135 |    108 |   40.5 |   37.8 |   37.8 |   39.8 |   39.5 |   40.4 |   41.1 |   40.0 |   39.4 |   38.8 |   37.5 |   37.2 |
 +^ PM <sub>10</sub>    |    289 |    260 |    144 |    115 |   43.3 |   40.4 |   40.4 |   42.6 |   42.3 |   43.2 |   43.9 |   42.8 |   42.1 |   41.5 |   40.1 |   39.8 |
 +^ TSP                    289 |    260 |    144 |    115 |   43.3 |   40.4 |   40.4 |   42.6 |   42.3 |   43.2 |   43.9 |   42.8 |   42.1 |   41.5 |   40.1 |   39.8 |
 +^ CO                  |    102 |    102 |    102 |    102 |    102 |    102 |    102 |    107 |    107 |    110 |    112 |    109 |    107 |    106 |    103 |    103 |
 +| **HEAVY FUEL OIL**                                                                                                                                  |||||||||||||||||
 +^ NH<sub>3</sub>      |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |   0.33 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ NMVOC                 36.4 |   36.4 |   36.4 |   36.4 |   36.4 |   36.4 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ NO<sub>x</sub>      |  1,258 |  1,258 |  1,258 |  1,258 |  1,258 |  1,258 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ SO<sub>x</sub>      |  1,319 |  1,332 |  1,323 |  1,336 |    496 |    496 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ BC <sup>2</sup>       64.9 |   65.5 |   65.1 |   65.7 |   24.4 |   24.4 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ PM <sub>2.5</sub>      541 |    546 |    542 |    548 |    203 |    203 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ PM <sub>10</sub>    |    595 |    601 |    597 |    602 |    224 |    224 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ TSP                    595 |    601 |    597 |    602 |    224 |    224 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +^ CO                  |    200 |    200 |    200 |    200 |    200 |    200 |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |  NA    |
 +<sup>1</sup> ratios PM<sub>2.5</sub> : PM<sub>10</sub> : TSP derived from the tier1 default EF as provided in [(EMEPEEA2019)] \\
 +<sup>2</sup> estimated from f-BCs as provided in [(EMEPEEA2019)]: f-BC (HFO) = 0.12, f-BC (MDO/MGO) = 0.31, chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii \\
 +Navigation, Table 3-2 and Table A1 - BC fractions of PM emissions from relevant studies
 +
 +> **NOTE:** 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**, 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.
 +
 +
 +===== Trend discussion for Key Sources =====
 +
 +> **NFR 1.A.4.c iii - National Fishing** is **no key source**.
 +
 +===== Recalculations =====
 +
 +With both **activity data and emission factors unaltered**, no recalculations occur against last year's submission. 
 +
 +
 +<WRAP center round info 65%>
 +For **pollutant-specific information on recalculated emission estimates for Base Year and 2020**, please see the recalculation tables following [[general:recalculations:start|chapter 8.1 - Recalculations]].
 +</WRAP>
 +
 +===== Uncertainties =====
 +
 +Uncertainty estimates for **emission factors** were adopted from NFR 1.A.3.d i as a comparable emission source.
 +
 +=====Planned improvements =====
 +
 +Besides a routine revision of the underlying BSH model, further focus will be put on the correct allocation of actvity data to the different navigation activities covered in different NFR sub-sectors.
 +
 +With respect to the strong increase in activity data from 2015 to 2016: This issue is under discussion with the BSH Hamburg as the agency in charge of the underlying model. However, these activity data are based on ship movement data showing a correspondingly increasing trend. Nonetheless, the model is under steady revision and erroneous calculations and results will be corrected whenever they are determined. 
 +
 +
 +[(DEICHNIK2022> Deichnik (2022): 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.)]
 +[(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook – 2019; Chapter 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation; URL: https://www.eea.europa.eu/publications/emep-eea-guidebook-2019/part-b-sectoral-guidance-chapters/1-energy/1-a-combustion/1-a-3-d-navigation )]
 +[(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: https://www.umweltbundesamt.de/en/publikationen/nationaler-durchfuehrungsplan-unter-stockholmer )]