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sector:ippu:other_solvent_and_product_use:other_solvent_use:start [2021/04/15 10:31] – [Recalculations] kotzullasector:ippu:other_solvent_and_product_use:other_solvent_use:start [2022/10/17 12:52] (current) – Fix links tarakji
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 In source category //2.D.3.i - Other Solvent Use//, emissions from various product groups and processes and also from lubricants use in stationary and mobile applications are reported. Relevant pollutants are NMVOC and some heavy metals. In source category //2.D.3.i - Other Solvent Use//, emissions from various product groups and processes and also from lubricants use in stationary and mobile applications are reported. Relevant pollutants are NMVOC and some heavy metals.
  
-^ Category Code                                                                                              Pollutants                                   ||^  Method                    |||^  AD                          |||^  EF                           |||| +^ Category Code                                                                                              Pollutants                                                ||^  Method                                                        |||^  AD                       |||^  EF                        |||| 
-| [[#Other solvent use|2.D.3.i - Other solvent use]]                                                        |  NMVOC                                        |||  T2                        ||||  NS                          ||||  CS                           |||| +| [[#Other solvent use|2.D.3.i - Other solvent use]]                                                        |  NMVOC                                                     |||  T2                                                            ||||  NS                       ||||  CS                        |||| 
-| [[#Use of lubricants in stationary applications|2.D.3.i - Use of lubricants in stationary applications]]  |  NMVOC                                        |||  T2                        ||||  NS                          ||||  CS                           |||| +| [[#Use of lubricants in stationary applications|2.D.3.i - Use of lubricants in stationary applications]]  |  NMVOC                                                     |||  T2                                                            ||||  NS                       ||||  CS                        |||| 
-| [[#Use of lubricants in mobile applications|2.D.3.i - Use of lubricants in mobile applications]]          |  Cd, Cr, Cu, Ni, Pb, Se and Zn                |||  T1                        ||||  NS, M                       ||||  D                            |||| +| [[#Use of lubricants in mobile applications|2.D.3.i - Use of lubricants in mobile applications]]          |  Cd, Cr, Cu, Ni, Pb, Se and Zn                             |||  T1                                                            ||||  NS, M                    ||||  D                         |||| 
-^  Key Category                                                                                             ^  SO₂                            ^  NOₓ   NH₃  ^  NMVOC    CO  ^  BC  ^  Pb  ^  Hg     ^  Cd  ^  Diox  ^  PAH  ^  HCB  ^  TSP  ^  PM₁₀  ^  PM₂ ₅  ^ +^                                                                                                           ^  NO<sub>x</sub>                 ^  NMVOC  ^  SO<sub>2</sub>   NH<sub>3</sub>  ^  PM<sub>2.5</sub>  ^  PM<sub>10</sub>  ^  TSP  ^  BC     ^  CO  ^  PB  ^  Cd  ^  Hg  ^  Diox  ^  PAH  ^  HCB  ^ 
-2.D.3.i                                                                                                   |  -                              |        |  L/T     |  -   |  -   |  -   |  -      |  -       |  -    |  -    |  -    |  -     |  -      |+Key Category:                                                                                             |  -                              |  L/T                  |  -               |  -                 |  -                |  -    |  -      |  -     |  -   |  -   |  -     |  -    |  -    |
  {{page>general:Misc:LegendEIT:start}}  {{page>general:Misc:LegendEIT:start}}
 \\ \\
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 === General procedure === === General procedure ===
  
-NMVOC emissions are calculated in keeping with a product-consumption-oriented approach. In this approach, solvent-based products or solvents are allocated to the source category, and then the relevant NMVOC emissions are calculated from those solvent quantities via specific emission factors. Thus, the use of this method is possible with the following valid input figures for each product group:+NMVOC emissions are calculated in accordance with a product-consumption-oriented approach. In this approach, solvent-based products or solvents are allocated to the source category, and then the relevant NMVOC emissions are calculated from those solvent quantities via specific emission factors. Thus, the use of this method is possible with the following valid input figures for each product group:
   * Quantities of VOC-containing (pre-) products and agents used in the report year,   * Quantities of VOC-containing (pre-) products and agents used in the report year,
   * The VOC concentrations in these products (substances and preparations),   * The VOC concentrations in these products (substances and preparations),
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 ==== Discussion of emission trends ==== ==== Discussion of emission trends ====
 === General information === === General information ===
-Since 1990, so the data, NMVOC emissions from use of solvents and solvent-containing products in general have decreased by nearly 38%. The main emissions reductions have been achieved in the years since 1999. This successful reduction has occurred especially because of regulatory provisions such as the 31st Ordinance on the execution of the Federal Immissions Control Act (Ordinance on the limitation of emissions of volatile organic compounds due to the use of organic solvents in certain facilities – 31. BImSchV), the 2nd such ordinance (Ordinance on the limitation of emissions of highly volatile halogenated organic compounds – 2. BImSchV) and the TA Luft.+Since 1990, so the data, NMVOC emissions from use of solvents and solvent-containing products in general have decreased by nearly 55%. The main emissions reductions have been achieved in the years since 1999. This successful reduction has occurred especially because of regulatory provisions such as the 31st Ordinance on the execution of the Federal Immissions Control Act (Ordinance on the limitation of emissions of volatile organic compounds due to the use of organic solvents in certain facilities – 31. BImSchV), the 2nd such ordinance (Ordinance on the limitation of emissions of highly volatile halogenated organic compounds – 2. BImSchV) and the TA Luft.
  
 === Specific information === === Specific information ===
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 ==== Recalculations ==== ==== Recalculations ====
-There are no recalculations+ 
 +As the emission data for the 2021 reporting could not be completely revised due to staff constraints and for these reasons the emission data for 2018 had to be updated in last year's reporting, a complete recalculation of the emission data for 2019 and 2020 was carried out for this year's reporting. In doing so, it was also possible to take into account the current changes in the systematics of the national production statistics and the foreign trade statistics
  
 <WRAP center round info 60%> <WRAP center round info 60%>
-For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following [[general:recalculations:start|chapter 8.1 - Recalculations]].+For pollutant-specific information on recalculated emission estimates for Base Year and actual year, please see the pollutant specific recalculation tables following [[general:recalculations:start|chapter 8.1 - Recalculations]].
 </WRAP> </WRAP>
 ==== Planned improvements ==== ==== Planned improvements ====
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 Sub-category //2.D.3.i - Other product use: Use of lubricants in stationary applications// comprises the entire use phase including the process stages of input and output. The products or lubricants covered here, are: Sub-category //2.D.3.i - Other product use: Use of lubricants in stationary applications// comprises the entire use phase including the process stages of input and output. The products or lubricants covered here, are:
  
-  * Automotive and industrial gear oils 
   * Compressor oils   * Compressor oils
   * Turbine oils   * Turbine oils
 +  * Gear oils (automotive oils including automatic transmission fluids, industrial-gear oils)
   * Hydraulic oils   * Hydraulic oils
-  * Electro insulating oils+  * Insulating oils
   * Machine oils   * Machine oils
   * Process oils   * Process oils
   * Other industrial oils not for lubricating purposes   * Other industrial oils not for lubricating purposes
-  * Metal working fluids+  * Metal working fluids fluids (hardening oils, water-miscible and not water-miscible metal working fluids, anticorrosive oils)
   * Greases   * Greases
   * Base oils   * Base oils
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 \\  \\ 
  
-The consumption of lubricants in Germany has remained at a relatively constant level since 1990, apart from a sharp decrease in 2009 that was related to the overall economic situation.+The consumption of lubricants in Germany has remained at a relatively constant level since 1990, apart from a sharp decrease in 2009 and in 2020.
  
 === Emission factors === === Emission factors ===
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 Along the life cycle of the different lubricant types, different kinds of losses occur. Only some types of losses are of relevance with regard to air emissions and the different lubricants types differ significantly from each other. Relevant emitted pollutants identified for lubricants are NMVOC and CO<sub>2</sub>. But only for engine oils used in machinery and in vehicles emission of both could be accounted for due to combustion of a small fraction of lubricating oils directly resulting in CO<sub>2</sub> emissions. Along the life cycle of the different lubricant types, different kinds of losses occur. Only some types of losses are of relevance with regard to air emissions and the different lubricants types differ significantly from each other. Relevant emitted pollutants identified for lubricants are NMVOC and CO<sub>2</sub>. But only for engine oils used in machinery and in vehicles emission of both could be accounted for due to combustion of a small fraction of lubricating oils directly resulting in CO<sub>2</sub> emissions.
  
-For Electro insulating oils <sup>**[[#Bibliography| [Lit. 3, 5]]]**</sup>, Process oils <sup>**[[#Bibliography| [Lit. 4, 10, 11]]]**</sup>, Greases <sup>**[[#Bibliography| [Lit. 10, 11]]]**</sup> and Extracts from lubricant production <sup>**[[#Bibliography| [Lit. 2, 10, 11]]]**</sup> no emissions expected.+For Insulating oils <sup>**[[#Bibliography| [Lit. 3, 5]]]**</sup>, Process oils <sup>**[[#Bibliography| [Lit. 4, 10, 11]]]**</sup>, Greases <sup>**[[#Bibliography| [Lit. 10, 11]]]**</sup> and Extracts from lubricant production <sup>**[[#Bibliography| [Lit. 2, 10, 11]]]**</sup> no emissions expected.
  
-All emission factors are determined in a research project (UBA, 2018)<sup>**[[#Bibliography| [Lit. 14]]]**</sup>.+All emission factors are are constant in the entire time series. They were determined in a research project (UBA, 2018)<sup>**[[#Bibliography| [Lit. 14]]]**</sup>.
  
  
-__Table 1: Tier 2 emission factor for source category 2.D.3.i, 2.G Other solvent and product use, Other__+__Table 1: Tier 2 emission factors for specific lubricant-type groups in percent__
  
 |                                                |                                              |  ** NMVOC **              ||                | |                                                |                                              |  ** NMVOC **              ||                |
 ^ Lubricant-type group                            Proportion range of total sales since 1990  ^  Default      ^      Range ^  Reference     ^ ^ Lubricant-type group                            Proportion range of total sales since 1990  ^  Default      ^      Range ^  Reference     ^
-| ** Automotive gear oils **                      5 - 10 %                                    |  1 %          |  0 - 2 %   | <sup>**[[#Bibliography| [Lit. 2 - 7]]]**</sup>  | 
-| ** Industrial gear oils **                      2 - 3 %                                      1.5 %        |  1 - 2 %   | <sup>**[[#Bibliography| [Lit. 3, 4, 8]]]**</sup>     | 
 | ** Compressor oils **                          |  =< 1 %                                      |  1.5 %        |  1 - 2 %   | <sup>**[[#Bibliography| [Lit. 2 - 7]]]**</sup>   | | ** Compressor oils **                          |  =< 1 %                                      |  1.5 %        |  1 - 2 %   | <sup>**[[#Bibliography| [Lit. 2 - 7]]]**</sup>   |
 | ** Turbine oils **                              < 1 %                                        0.5 %        |  0 - 1 %   | <sup>**[[#Bibliography| [Lit. 2, 3, 5]]]**</sup>   | | ** Turbine oils **                              < 1 %                                        0.5 %        |  0 - 1 %   | <sup>**[[#Bibliography| [Lit. 2, 3, 5]]]**</sup>   |
 +| ** Automotive gear oils **                                5 - 10 %                          |  1 %          | 0 - 2 %                                                      |
 +| ** Industrial gear oils **                                2 - 3 %                            1.5 %        |  1 - 2 %                                                      |
 | ** Hydraulic oils **                            6 - 15 %                                    |  1.5 %        |  1 - 2 %   |:::     | | ** Hydraulic oils **                            6 - 15 %                                    |  1.5 %        |  1 - 2 %   |:::     |
 | ** Machine oils **                              1 - 7 %                                      2.5 %        |  0 - 5 %   | <sup>**[[#Bibliography| [Lit. 2, 5, 9]]]**</sup>   | | ** Machine oils **                              1 - 7 %                                      2.5 %        |  0 - 5 %   | <sup>**[[#Bibliography| [Lit. 2, 5, 9]]]**</sup>   |
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 | ** Base oils **                                |  4 - 16 %                                    |  10 %          5 - 15 %  | <sup>**[[#Bibliography| [Lit. 14]]]**</sup>   | | ** Base oils **                                |  4 - 16 %                                    |  10 %          5 - 15 %  | <sup>**[[#Bibliography| [Lit. 14]]]**</sup>   |
  
 +In 1995 four categories fell away/ceased to exist (Table 2) and three type groups were newly introduced due to modifications/changes in the Mineral Oil Statistics concerning lubricants. A slight adjustment of the procedure for the years 1990-1994 was needed. Table 2 shows the affected categories as well as the ways in which they were handled in the calculation procedure.
  
 +__Table 2: Handling of categories in the Mineral Oil Statistics, 1990-1994__
 +
 +^  Category                              ^  Remarks concerning the procedure                                                                                                                                        NMVOC emission factor  ^
 +| Other lubricating oils, specialty and other lubricating oils, non-specialty    | These are handled like the “machine oils” group, which is lacking in the 1990-1994 period. This group includes various specialty and non-specialty libricationg oils.   | 2.5 %                   |
 +| Other mineral oils for special applications           | This category contains no lubricating oils. It is handled like the category “Other industrial oils not used for lubrication” which is lacking in the 1990-1994 period.  | 25 %                    |
 +| Light-coloured plasticisers and extender oils  | Extender oils and plasticisers are classified with the process oils. They are handled accordingly.                                                                      | 0 %                     |
 ==== Uncertainties ==== ==== Uncertainties ====
  
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 The emission factors are based on a broad review of literature and results from relevant research projects and have been discussed with senior lubricant experts. The experts suggested using ranges which are provided in the emission factor table 1. The emission factors are based on a broad review of literature and results from relevant research projects and have been discussed with senior lubricant experts. The experts suggested using ranges which are provided in the emission factor table 1.
  
 +The modifications of the Mineral Oil Statistics in 1995 show no impact of overall amount of lubricants. Only a reclassification of lubricants from unspecified application categories to specified application categories was made. The emissions for the years 1990-1994 could therefore be just up to 25% to high.
 ==== Recalculations ==== ==== Recalculations ====
  
-Recalculation of NMVOC emissions in the year 2011 due to correction of emission factor (wrong decimal point). +Recalculations of NMVOC emissions were done for the entire time series because of the integration of automotive gear oils.
  
 +<WRAP center round info 65%>
 +For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the recalculation tables following chapter [[general:recalculations:start | 8.1 - Recalculations]].
 +</WRAP>
 ==== Planned improvements ==== ==== Planned improvements ====
  
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 **Lit.  6:** Kline & Company. Lubricant Consumption and Used Oil Generation in California: A Segmented Market Analysis: Part II: Collectable Used Oil Availability in California, 2000-2011. published 03/03/2015: Sacramento, CA, USA, 2012.) \\  **Lit.  6:** Kline & Company. Lubricant Consumption and Used Oil Generation in California: A Segmented Market Analysis: Part II: Collectable Used Oil Availability in California, 2000-2011. published 03/03/2015: Sacramento, CA, USA, 2012.) \\ 
 **Lit.  7:** UNEP. Compendium of Recycling and Destruction Technologies for Waste Oils: Osaka, Japan, 2012.) \\  **Lit.  7:** UNEP. Compendium of Recycling and Destruction Technologies for Waste Oils: Osaka, Japan, 2012.) \\ 
-**Lit.  8:** VSI. Getriebeöle; http://www.vsi-schmierstoffe.de/schmierstoffe/technische-information/getriebeoele.html.) \\ +**Lit.  8:** VSI. Getriebeöle; https://www.vsi-schmierstoffe.de/index.php.) \\ 
 **Lit.  9:** Vidal-Abarca, G. C.; Kaps, R.; Oliver, W.; Escamilla, M.; Josa, J.; Riera, M. R.; Benedicto, E. Revision of European Ecolabel Criteria for Lubricants. Preliminary Report: Sevilla, 2016.) \\  **Lit.  9:** Vidal-Abarca, G. C.; Kaps, R.; Oliver, W.; Escamilla, M.; Josa, J.; Riera, M. R.; Benedicto, E. Revision of European Ecolabel Criteria for Lubricants. Preliminary Report: Sevilla, 2016.) \\ 
 **Lit. 10:** Möller, U. J. Altölentsorgung durch Verwertung und Beseitigung; Kontakt & Studium Bd. 253; Expert Verlag: Renningen, 2004.) \\  **Lit. 10:** Möller, U. J. Altölentsorgung durch Verwertung und Beseitigung; Kontakt & Studium Bd. 253; Expert Verlag: Renningen, 2004.) \\ 
 **Lit. 11:** Bartz, W. J.; Springer, G.; Blanke, H.-J. Expert Praxislexikon Tribologie Plus: 2010 Begriffe für Studium und Beruf, 2., völlig neubearb. Aufl. des Lexikons der Schmierungstechnik von G. Vögtle; Expert Verlag: Renningen, 2000.) \\  **Lit. 11:** Bartz, W. J.; Springer, G.; Blanke, H.-J. Expert Praxislexikon Tribologie Plus: 2010 Begriffe für Studium und Beruf, 2., völlig neubearb. Aufl. des Lexikons der Schmierungstechnik von G. Vögtle; Expert Verlag: Renningen, 2000.) \\ 
-**Lit. 12:** VSI. Grundöle; http://www.vsi-schmierstoffe.de/schmierstoffe/technische-information/grundoele.html.) \\ +**Lit. 12:** VSI. Grundöle; https://www.vsi-schmierstoffe.de/index.php.) \\ 
 **Lit. 13:** Kolshorn, K.-U.; Wiesert, P.; Götz, R.; Rippen, G. Ermittlung von Altölvermeidungspotentialen: UBA-Forschungsvorhaben Nr. 103 60 111; Trischler und Partner GmbH: Darmstadt, 1996.) \\  **Lit. 13:** Kolshorn, K.-U.; Wiesert, P.; Götz, R.; Rippen, G. Ermittlung von Altölvermeidungspotentialen: UBA-Forschungsvorhaben Nr. 103 60 111; Trischler und Partner GmbH: Darmstadt, 1996.) \\ 
 **Lit. 14:** UBA, 2018: Zimmermann, T.; Jepsen, D. (2018) Entwicklung von Methoden zur Berechnung von Treibhausgas- und Luftschadstoffemissionen aus der Verwendung von Schmierstoffen und Wachsen.) \\  **Lit. 14:** UBA, 2018: Zimmermann, T.; Jepsen, D. (2018) Entwicklung von Methoden zur Berechnung von Treibhausgas- und Luftschadstoffemissionen aus der Verwendung von Schmierstoffen und Wachsen.) \\ 
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 Basically, the amounts of lubricants unintentionally co-incinerated in engines other than 2-strokes is estimated from the annual amounts of fuels used in these engines, excluding the amounts of fuels used for international aviation and navigation.  Basically, the amounts of lubricants unintentionally co-incinerated in engines other than 2-strokes is estimated from the annual amounts of fuels used in these engines, excluding the amounts of fuels used for international aviation and navigation. 
  
-Here, the majority of lubricant co-incineration takes place in road vehicles. These related amounts of co-incinerated lubricants are calculated directly within TREMOD [((bibcite 1))].+Here, the majority of lubricant co-incineration takes place in road vehicles. These related amounts of co-incinerated lubricants are calculated directly within TREMOD [(KNOERR2021a)].
  
 __Table 1: Annual amounts of lubricants co-incinerated in mobile vehicles and machinery - excluding 2-stroke engines, in terajoules__ __Table 1: Annual amounts of lubricants co-incinerated in mobile vehicles and machinery - excluding 2-stroke engines, in terajoules__
-^  1990    1995    2000    2005    2006    2007    2008    2009    2010    2011    2012    2013    2014    2015    2016    2017    2018    2019   ^ +^  1990    1995    2000    2005    2006    2007    2008    2009    2010    2011    2012    2013    2014    2015    2016    2017    2018    2019   ^  2020  
-|  1,415   1,606   1,710   1,747  |  1,755   1,769   1,762   1,776   1,791   1,824   1,822   1,838   1,877   1,915   1,956   1,980   1,759   1,769  |+|  1,400   1,602   1,714   1,747  |  1,796   1,826   1,825   1,841   1,881   1,914   1,941   1,963   1,965   1,983   1,771   1,400   1,602   1,714  |  1,747 |
  
-source: own estimations and TREMOD [(KNOERR2020a)]+source: own estimations and TREMOD [(KNOERR2021a)]
  
-The **emission factors** are derived from chapter //1.A.3.b.i-iv Road transport 2019//, Table 3-80 of the EMEP/EEA air pollutant emission inventory guidebook 2019 [(EMEPEEA2019)].+The **emission factors** are derived from chapter //1.A.3.b.i-iv Road transport 2019//, Table 3-87 of the EMEP/EEA air pollutant emission inventory guidebook 2019 [(EMEPEEA2019)].
  
-These default EF in [ppm HM /wt lubricant] have been transferred into [g HM/kg lubricant] via a NCV of 0.03985 GJ/kg into the following values:+{{sector:ippu:other_product_use:emep2019_1.a.3.bi-iv_table3-87_hm_from_lubricants.png?nolink&700}} 
 + 
 +These default values were transferred via a NCV of 0.03985 GJ/kg into the following energy-related values:
  
 __Table 2: tier1 emission factors for heavy-metal emissions from co-incinerated lubricants, in g/TJ__ __Table 2: tier1 emission factors for heavy-metal emissions from co-incinerated lubricants, in g/TJ__
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 __Table 3: Annual heavy-metal emissions from co-incinerated lubricants, in metric tonnes__ __Table 3: Annual heavy-metal emissions from co-incinerated lubricants, in metric tonnes__
-|      ^  1990  ^  1995  ^  2000  ^  2005  ^  2006  ^  2007  ^  2008  ^  2009  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^ +|      ^  1990  ^  1995  ^  2000  ^  2005  ^  2006  ^  2007  ^  2008  ^  2009  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019   2020  ^ 
-^  As  |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 | +^  As  |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 | 
-^  Cd  |   0,16 |   0,18 |   0,20 |   0,20 |   0,20 |   0,20 |   0,20 |   0,20 |   0,20 |   0,21 |   0,21 |   0,21 |   0,21 |   0,22 |   0,22 |   0,23 |   0,20 |   0,20 | +^  Cd  |   0.16 |   0.18 |   0.20 |   0.20 |   0.20 |   0.20 |   0.20 |   0.20 |   0.21 |   0.21 |   0.21 |   0.21 |   0.22 |   0.22 |   0.22 |   0.22 |   0.22 |   0.23 |   0.20 | 
-^  Cr  |   0,68 |   0,77 |   0,82 |   0,84 |   0,85 |   0,85 |   0,85 |   0,86 |   0,86 |   0,88 |   0,88 |   0,89 |   0,90 |   0,92 |   0,94 |   0,95 |   0,85 |   0,85 | +^  Cr  |   0.67 |   0.77 |   0.83 |   0.84 |   0.85 |   0.86 |   0.85 |   0.86 |   0.87 |   0.88 |   0.88 |   0.89 |   0.91 |   0.92 |   0.94 |   0.95 |   0.95 |   0.96 |   0.85 | 
-^  Cu  |  27,62  31,35  33,38  34,10  34,26  34,53  34,41  34,68  34,97 |  35,61  35,57  35,89  36,65  37,38 |  38,19  38,66  34,34 |  34,54 +^  Cu  |   27.3   31.3   33.5   34.1   34.4   34.8   34.6   34.8   35.1   35.6   35.6   36.0   36.7 |   37.4 |   37.9 |   38.3   38.4   38.7   34.6 
-^  Hg  |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 | +^  Hg  |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 | 
-^  Ni  |   1,13 |   1,28 |   1,37 |   1,40 |   1,40 |   1,42 |   1,41 |   1,42 |   1,43 |   1,46 |   1,46 |   1,47 |   1,50 |   1,53 |   1,57 |   1,58 |   1,41 |   1,42 | +^  Ni  |   1.12 |   1.28 |   1.37 |   1.40 |   1.41 |   1.43 |   1.42 |   1.43 |   1.44 |   1.46 |   1.46 |   1.47 |   1.51 |   1.53 |   1.55 |   1.57 |   1.57 |   1.59 |   1.42 | 
-^  Pb  |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 |   0,00 | +^  Pb  |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 |   0.00 | 
-^  Se  |   0,16 |   0,18 |   0,19 |   0,20 |   0,20 |   0,20 |   0,20 |   0,20 |   0,20 |   0,21 |   0,21 |   0,21 |   0,21 |   0,22 |   0,22 |   0,23 |   0,20 |   0,20 | +^  Se  |   0.16 |   0.18 |   0.20 |   0.20 |   0.20 |   0.20 |   0.20 |   0.20 |   0.20 |   0.21 |   0.21 |   0.21 |   0.21 |   0.22 |   0.22 |   0.22 |   0.22 |   0.23 |   0.20 | 
-^  Zn  |  15,98  18,14  19,32  19,73  19,83  19,98  19,91  20,07  20,24  20,61  20,59  20,77  21,21 |  21,63  22,10  22,37  19,87  19,99 |+^  Zn  |   15.8   18.1   19.4   19.7   19.9   20.1   20.0   20.1   20.3   20.6   20.6   20.8   21.2 |   21.6   21.9   22.2   22.2   22.4   20.0 | 
 + 
 ===== Recalculations===== ===== Recalculations=====
  
 **Activity data** (annual amounts of unintentionally co-incinerated lubricants) have been revised slightly for the entire time series. **Activity data** (annual amounts of unintentionally co-incinerated lubricants) have been revised slightly for the entire time series.
-Here, for 2018 only, larger changes occur due to the finalisation of this year's National Energy Balance.+Here, for 2019, larger changes occur due to the finalisation of this year's National Energy Balance, whereas for 2018 the erronous over-all amount of co-incinerated lubricants has been corrected.
  
 __Table: Revised annual amounts of unintentionally co-incinerated lubricants, in terajoules__ __Table: Revised annual amounts of unintentionally co-incinerated lubricants, in terajoules__
-|                  ^ 1990    1995    2000  ^  2005  ^  2006  ^  2007  ^  2008  ^  2009  ^  2010  ^  2011   ^  2012   ^  2013   ^  2014  ^  2015  ^  2016    2017  ^  2018   +|                  ^  1990    1995    2000  ^  2005  ^  2006  ^  2007  ^  2008  ^  2009  ^  2010  ^  2011  ^  2012  ^  2013  ^  2014  ^  2015   ^  2016    2017   ^  2018   2019  
-^ Submission 2021   1,413 |   1,611 |  1,723 |  1,754 |  1,767 |  1,789 |  1,780 |  1,789 |  1,802   1,831   1,831   1,847 |  1,887  1,922 |   1,945 |  1,974   1,973 +^ Submission 2022    1,400 |   1,602 |  1,714 |  1,747 |  1,760 |  1,781 |  1,772 |  1,782 |  1,796  1,826  1,825  1,841 |  1,881   1,914 |   1,941 |   1,963 |  1,965  1,983 
-^ Submission 2020   1,413 |   1,611 |  1,722 |  1,751 |  1,760 |  1,782 |  1,776 |  1,788 |  1,802   1,832   1,831   1,848 |  1,881  1,914 |   1,947 |  1,968   1,974 +^ Submission 2021    1,415 |   1,606 |  1,710 |  1,747 |  1,755 |  1,769 |  1,762 |  1,776 |  1,791  1,824  1,822  1,838 |  1,877   1,915 |   1,956 |   1,980 |  1,759  1,769 
-^ absolute change  |   0.18 |   -0.12 |   0.61 |   3.28 |   7.15 |   6.21 |   3.75 |   0.26 |   0.07 |   -0.85 |   -0.76 |   -1.41 |   5.98 |   8.27 |   -1.55 |   5.05 |   -1.30 +^ absolute change  |   -14.|   -3.88 |   3.60 |   0.15 |   5.05 |   12.|   9.98 |   6.02 |   4.96 |   1.53 |   2.51 |   2.98 |   3.52 |   -0.49 |   -14.|   -17.4 |    206 |    214 
-^ relative change  |  0.01% |  -0.01% |  0.04% |  0.19% |  0.41% |  0.35% |  0.21% |  0.01% |  0.00% |  -0.05% |  -0.04% |  -0.08% |  0.32% |  0.43% |  -0.08% |  0.26% |  -0.07% |+^ relative change  |  -1.03% |  -0.24% |  0.21% |  0.01% |  0.29% |  0.71% |  0.57% |  0.34% |  0.28% |  0.08% |  0.14% |  0.16% |  0.19% |  -0.03% |  -0.76% |  -0.88% |  11.7% |  12.1% |
  
 On the other hand, the tier1 **emission factors** applied so far, remain unrevised compared to last year's submission. On the other hand, the tier1 **emission factors** applied so far, remain unrevised compared to last year's submission.
  
 Therefore, the canges in the **emission estimates** reported for this sub-category result solely from the named revisions in activity data. Therefore, the canges in the **emission estimates** reported for this sub-category result solely from the named revisions in activity data.
 +
 +<WRAP center round info 60%>
 +For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the pollutant specific recalculation tables following chapter [[general:recalculations:start | 8.1 - Recalculations]].
 +</WRAP>
  
 ===== Planned improvements =====  ===== Planned improvements ===== 
Line 245: Line 263:
 Although there are no improvements planned for this specific sub-category, several routine model revisions are scheduled for mobile sources with impact on fuel consumption data and, hence, the amounts of  unintentionally co-incinerated lubricants. Although there are no improvements planned for this specific sub-category, several routine model revisions are scheduled for mobile sources with impact on fuel consumption data and, hence, the amounts of  unintentionally co-incinerated lubricants.
  
-[(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. )].+[(KNOERR2021a> Knörr et al. (2021a): 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, 2021. )].
 [(EMEPEEA2019> EMEP, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, URL: https://www.eea.europa.eu/publications/emep-eea-guidebook-2019/part-b-sectoral-guidance-chapters/1-energy/1-a-combustion/1-a-3-b-i/view; Copenhagen, 2019.)] [(EMEPEEA2019> EMEP, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, URL: https://www.eea.europa.eu/publications/emep-eea-guidebook-2019/part-b-sectoral-guidance-chapters/1-energy/1-a-combustion/1-a-3-b-i/view; Copenhagen, 2019.)]