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sector:energy:fugitive:start [2022/03/01 09:57] – [Table] boettchersector:energy:fugitive:start [2024/11/06 14:47] (current) – external edit 127.0.0.1
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-| {{ :sector:energy:fugitive:co_2021.jpg?400 }}   | {{ :sector:energy:fugitive:nmvoc_2021.jpg?400 }}  | +| {{ :sector:energy:fugitive:co_2022.jpg?400 }}   | {{ :sector:energy:fugitive:nmvoc_2022.jpg?400 }}  | 
-|  Carbon Monoxide                                 |  NMVOC                                             | +|  Carbon Monoxide                                |  NMVOC                                            | 
-| | | +|                                                 |                                                   | 
-| {{ :sector:energy:fugitive:sox_2021.jpg?400 }}  | {{ :sector:energy:fugitive:tsp_2021.jpg?400 }}    | +| {{ :sector:energy:fugitive:sox_2022.jpg?400 }}  | {{ :sector:energy:fugitive:tsp_2022.jpg?400 }}    | 
-|  SOx                                             |  Particulate Matter                                |+|  SOx                                            |  Particulate Matter                               |
  
  
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 Recalculations covering the past two years have been carried out as a result of the provisional nature of a number of statistics in this area.   Recalculations covering the past two years have been carried out as a result of the provisional nature of a number of statistics in this area.  
 +In addition to this, the TERT noted in 2021 that the reported total PAHs did not equal the sum of the reported estimates from BaP, Benzo(b) Fluoranthene, benzo(k) Fluoranthene and Indeno (1,2,3-cd) Pyrene (to 4 significant figures) for the years 1990-1993. Germany explained why the emission factors from the guidebook cannot be applied. The proportions of those EMEP factors were taken to generate the missing indicator substance. That led to following approach which was accepted by the ERT:
  
-Furthermore, some minor changes in activity data for distribution of mineral oil products led to marginal changes in NMVOC emissions. 
  
-^ **NMVOC**            ^ **Unit**  |^ **1990**|^ **1995**|^ **2000**|^ **2005**|^ **2010**|^ **2015**|^ **2018**| +| **substance**       | **unit**  | **1990**  | **1991**  | **1992**  | **1993**  | **1994**  | 
-| **2020 Submission**  | kt    | 183,50  | 124,68  | 84,95  | 54,21  | 44,48  | 40,68  | 40,06  | +| **BaP**             | kg        | 2,106     | 1,399     | 946       | 386       | 133       | 
-| **2021 Submission**  | kt    | 183,47  | 124,85  | 84,91  | 54,18  | 44,35  | 40,59  | 39,93  | +| **BbF**             | kg        | 2,633     | 1,749     | 1,183     | 483       | 166       | 
-| **Difference**      | kt    | 0,03    | -0,17   | 0,04   | 0,03   | 0,13   | 0,09   | 0,13   |+| **BkF**             | kg        | 1,316     | 874       | 591       | 241       | 83        | 
 +| **IxP**             | kg        | 921       | 612       | 414       | 169       | 58        | 
 +|                     |           |           |           |           |           |           | 
 +| **Sum**             | kg        | 6,976     | 4,634     | 3,134     | 1,28      | 441       | 
 +|                     |           |           |           |           |           |           | 
 +| **previous total**  | kg        | 42,028    | 27,725    | 18,767    | 7,714     | 2,662     |
  
-In addition to this, the TERT noted in 2021 that the reported total PAHs did not equal the sum of the reported estimates from BaP, Benzo(b) Fluoranthene, benzo(k) Fluoranthene and Indeno (1,2,3-cd) Pyrene (to 4 significant figures) for the years 1990-1993. Germany explained why the emission factors from the guidebook cannot be applied. The proportion of those EMEP factors were taken to generate the missing indicator substance. That led to following approach which was accepted by the ERT: 
  
- +Finally, the emissions from storage of chemical products have been allocated under 2.B.10. 
-| **substance**   | **unit**  | **1990**  | **1991**  | **1992**  | **1993**  | **1994**  | +
-| BaP             | kg        | 2,106     | 1,399     | 946       | 386       | 133       | +
-| BbF             | kg        | 2,633     | 1,749     | 1,183     | 483       | 166       | +
-| BkF             | kg        | 1,316     | 874       | 591       | 241       | 83        | +
-| IxP             | kg        | 921       | 612       | 414       | 169       | 58        | +
-|                 |           |           |           |           |           |           | +
-| Sum             | kg        | 6,976     | 4,634     | 3,134     | 1,28      | 441       | +
-|                 |           |           |           |           |           |           | +
-| previous total  | kg        | 42,028    | 27,725    | 18,767    | 7,714     | 2,662     | +
- +
- +
-Finally, the emissions from storage of chemical products were allocated under 2.B.10. +
  
 <WRAP center round info 60%> <WRAP center round info 60%>
-For **pollutant-specific information on recalculated emission estimates reported for Base Year and 2015**, please see the pollutant specific recalculation tables following chapter [[general:recalculations:start|Chapter 8.1 - Recalculations]]].+For **pollutant-specific information on recalculated emission estimates reported for Base Year and 2019**, please see the recalculation tables following chapter [[general:recalculations:start|Chapter 8.1 - Recalculations]].
 </WRAP> </WRAP>
  
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-  * emissions from storage of refinery products will be divided up to fuels (under 1.B) and chemical products (2.B) +  * emission factors from natural gas will be updated according to results of several measurement programms
-  * emission factors from natural gas transmission will be updated according to results of the UNEP OGMP 2.0 measurement programm (1.B.2.b.iv)+