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appendices:appendix2.3-hm-from-mobile-sources [2021/04/14 21:08] – [Table] kotzullaappendices:appendix2.3-hm-from-mobile-sources [2024/11/06 13:50] (current) – external edit 127.0.0.1
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 For heavy-metal exhaust emissions (other then lead from leaded gasoline), tier1 values have been derived from tier1 default values provided in the 2019 EMEP/EEA Guidebook. For heavy-metal exhaust emissions (other then lead from leaded gasoline), tier1 values have been derived from tier1 default values provided in the 2019 EMEP/EEA Guidebook.
  
-__Table 1: Tier1 default emisison factors applied to road vehicles, in [g/TJ]__+__Table 1: Tier1 default emisison factors applied to road vehicles, in g/TJ__
 |                        ^  **Pb**  ^  **Cd**  ^  **Hg**  ^  **As**  ^  **Cr**  ^  **Cu**  ^  **Ni**  ^  **Se**  ^  **Zn**  ^ |                        ^  **Pb**  ^  **Cd**  ^  **Hg**  ^  **As**  ^  **Cr**  ^  **Cu**  ^  **Ni**  ^  **Se**  ^  **Zn**  ^
 ^ Diesel oil             |  0.012   |  0.001   |  0.123   |  0.002   |  0.198   |  0.133   |  0.005   |  0.002   |  0.419   | ^ Diesel oil             |  0.012   |  0.001   |  0.123   |  0.002   |  0.198   |  0.133   |  0.005   |  0.002   |  0.419   |
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 <sup>1</sup> values differ from EFs applied for fossil diesel oil to take into account the specific NCV of biodiesel <sup>1</sup> values differ from EFs applied for fossil diesel oil to take into account the specific NCV of biodiesel
  
-In contrast to the 2013 GB, the July 2017 version of the 2016 GB provides separate values for Hm from fuel combustion (icluding engine wear) and the unintended co-incineration of lube oil.+The 2019 GB provides separate values for Hm from fuel combustion (icluding engine wear) and the unintended co-incineration of lube oil.
 The latter are reported in NFR 2.D as emissions from product use. (//Note: This country-specific approach has been discussed and accepted at both the 2018 TFEIP meeting and the 2018 NEC review.//) The latter are reported in NFR 2.D as emissions from product use. (//Note: This country-specific approach has been discussed and accepted at both the 2018 TFEIP meeting and the 2018 NEC review.//)
  
-__Screenshot of EMEP/EEA GB 2016 (2013), chapter 1.A.3.b, Table 3-104: Heavy metal emission factors for all vehicle categories in mg/kg fuel:__ +{{ :general:appendices:emepeea2019_1a3b_table3.78_ef_hm_fuel.png ?700 }} 
-[[gallery size="medium"]] +{{ :general:appendices:emepeea2019_1a3b_table3.78_ef_hm_lubricant.png ?700 }}
-: GB2016(2013)_default-EF(HM).JPG  +
-[[/gallery]] +
- +
-Unfortunately, the July 2017 version of the 2016 GB does no longer include default values for HM emissions from CNG and LPG. Furthermore, no such values are available for biogas. +
- +
-__Screenshot of EMEP/EEA GB 2016 (July 2017), chapter 1.A.3.b, Table 3.77: Heavy metal emission factors for all vehicle categories in ppm/wt fuel:__ +
-[[gallery size="medium"]] +
-: GB2016(July2017)_default-EF(HM)_from_fuels.JPG  +
-[[/gallery]] +
- +
-__Screenshot of EMEP/EEA GB 2016, chapter 1.A.3.b, Table 3.78: Heavy metal emission factors for all vehicle categories in ppm/wt lubricant__ +
-[[gallery size="medium"]] +
-: GB2016(July2017)_default-EF(HM)_from_lubricants.JPG +
-[[/gallery]]+
  
 ===== Non-road Mobile Machinery in 1.A.2.g vii, 1.A.4.a.ii,1.A.4.b.i, 1.A.4.c.ii and 1.A.5.b i ===== ===== Non-road Mobile Machinery in 1.A.2.g vii, 1.A.4.a.ii,1.A.4.b.i, 1.A.4.c.ii and 1.A.5.b i =====
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 Without country-specific information, tier1 values are applied.  Without country-specific information, tier1 values are applied. 
  
-However, instead of using the emission factors provided in (EMEP/EEA, 2016) [((bibcite 1))], Table 3-1 Tier 1 emission factors for off-road machinery, EF for exhaust HMs from GB chapter 1.A.3.b.i, 1.A.3.b.ii, 1.A.3.b.iii, 1.A.3.b.iv, page 93 ff are applied here, too in order to allow for the separate reporting of emissions from fuel and enigine wear and the unintended co-incineration of lube oil. +However, instead of using the emission factors provided in (EMEP/EEA, 2019) [(EMEPEEA2019)], Table 3-1 Tier 1 emission factors for off-road machinery, EF for exhaust HMs from GB chapter 1.A.3.b.i, 1.A.3.b.ii, 1.A.3.b.iii, 1.A.3.b.iv, page 93 ff are applied here too to allow for the separate reporting of emissions from fuel and enigine wear and the unintended co-incineration of lube oil. 
 Here, separate tier1 default EFs are provided there in tables 3.77 and 3.78 of the GB chapter for road transport.  Here, separate tier1 default EFs are provided there in tables 3.77 and 3.78 of the GB chapter for road transport. 
  
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 //(Note: Until submission 2017, the EMEP/EEA default EFs provided for NRMM were used in the German inventory. As these EFs do not differentiate between fuel combustion and lubricant co-incineration, the inventory compiler decided to apply the more specific EFs from road transport to NRMM in 1.A.2.g vii, 1.A.4.a ii, b ii and c ii and 1.A.5.b, too. This country-specific approach has been discussed and accepted at both the 2018 TFEIP meeting and the 2018 NEC review.)// //(Note: Until submission 2017, the EMEP/EEA default EFs provided for NRMM were used in the German inventory. As these EFs do not differentiate between fuel combustion and lubricant co-incineration, the inventory compiler decided to apply the more specific EFs from road transport to NRMM in 1.A.2.g vii, 1.A.4.a ii, b ii and c ii and 1.A.5.b, too. This country-specific approach has been discussed and accepted at both the 2018 TFEIP meeting and the 2018 NEC review.)//
  
-__Table 2: Tier1 default emission factors applied to NRMM, in [g/TJ__+__Table 2: Tier1 default emission factors applied to NRMM, in g/TJ__
 |                                        ^  **Pb**  ^  **Cd**  ^  **Hg**  ^  **As**  ^  **Cr**  ^  **Cu**  ^  **Ni**  ^  **Se**  ^  **Zn**  ^ |                                        ^  **Pb**  ^  **Cd**  ^  **Hg**  ^  **As**  ^  **Cr**  ^  **Cu**  ^  **Ni**  ^  **Se**  ^  **Zn**  ^
 ^ Diesel oil                             |  0.012   |  0.001   |  0.123   |  0.002   |  0.198   |  0.133   |  0.005   |  0.002   |  0.419   | ^ Diesel oil                             |  0.012   |  0.001   |  0.123   |  0.002   |  0.198   |  0.133   |  0.005   |  0.002   |  0.419   |
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 ===== Railways ===== ===== Railways =====
  
-__Table 3: Tier1 default emission factors applied to railway vehicles, in [g/TJ]__+__Table 3: Tier1 default emission factors applied to railway vehicles, in g/TJ__
 |                        ^  **Pb**            ^  **Cd**            ^  **Hg**            ^  **As**             ^  **Cr**            ^  **Cu**             ^  **Ni**            ^  **Se**            ^  **Zn**             ^ |                        ^  **Pb**            ^  **Cd**            ^  **Hg**            ^  **As**             ^  **Cr**            ^  **Cu**             ^  **Ni**            ^  **Se**            ^  **Zn**             ^
 ^ Diesel oil             |  1.21<sup>2</sup>  |  0.23<sup>1</sup>  |  0.12<sup>1</sup>  |  0.002<sup>2</sup>  |  1.16<sup>2</sup>  |  39.57<sup>2</sup>  |  1.63<sup>2</sup>  |  0.23<sup>2</sup>  |  23.28<sup>2</sup>  | ^ Diesel oil             |  1.21<sup>2</sup>  |  0.23<sup>1</sup>  |  0.12<sup>1</sup>  |  0.002<sup>2</sup>  |  1.16<sup>2</sup>  |  39.57<sup>2</sup>  |  1.63<sup>2</sup>  |  0.23<sup>2</sup>  |  23.28<sup>2</sup>  |
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 ^ Hard Coal              |   NE                                                                                                                                                                                  ||||||||| ^ Hard Coal              |   NE                                                                                                                                                                                  |||||||||
 ^ Hard Coal Coke         |   NE                                                                                                                                                                                  ||||||||| ^ Hard Coal Coke         |   NE                                                                                                                                                                                  |||||||||
-<sup>1</sup> tier1 default from [((bibcite 1))], chapter: 1.A.3.b i-iv - Road transport: exhaust emissions: tier1 value for diesel vehicles \\ +<sup>1</sup> tier1 default from [(EMEPEEA2019)], chapter: 1.A.3.b i-iv - Road transport: exhaust emissions: tier1 value for diesel vehicles \\ 
-<sup>2</sup> tier1 default from [((bibcite 1))], chapter: 1.A.3.c - Railways \\+<sup>2</sup> tier1 default from [(EMEPEEA2019)], chapter: 1.A.3.c - Railways \\
 <sup>3</sup> values differ from EFs applied for fossil diesel oil to take into account the specific NCV of biodiesel \\ <sup>3</sup> values differ from EFs applied for fossil diesel oil to take into account the specific NCV of biodiesel \\
 (//NOTE: Assuming that biodiesel contains far less HMs than fossil diesel oil, similar values are applied to all mobile sources using this biogenic fuel.//) (//NOTE: Assuming that biodiesel contains far less HMs than fossil diesel oil, similar values are applied to all mobile sources using this biogenic fuel.//)
  
-As the EMEP/EEA GB 2016 does not provide specific defaults for **Pb, Hg and As**, the EF applied here has been derived from chapter: 1.A.3.b i-iv - Road transport: exhaust emissions: tier1 value for diesel vehicles.  +As the EMEP/EEA GB 2019 does not provide specific defaults for **Pb, Hg and As**, the EF applied here has been derived from chapter: 1.A.3.b i-iv - Road transport: exhaust emissions: tier1 value for diesel vehicles. 
- +
-[[gallery size="medium"]] +
-: GB2016_EF_NE+NA_1.A.3.c.png +
-[[/gallery]]+
  
 ===== Inland Vessels and Ships in 1.A.3.d ii ===== ===== Inland Vessels and Ships in 1.A.3.d ii =====
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 ^ Diesel oil<sup>2</sup>      |  3.03    |  0.23    |  0.70    |  0.93    |  1.16    |  20.5    |  23.3    |  2.33    |  27.9    | ^ Diesel oil<sup>2</sup>      |  3.03    |  0.23    |  0.70    |  0.93    |  1.16    |  20.5    |  23.3    |  2.33    |  27.9    |
 ^ Biodiesel<sup>3</sup>       |  0.013   |  0.0013  |  0.142   |  0.003   |  0.23    |  0.15    |  0.005   |  0.003   |  0.48    | ^ Biodiesel<sup>3</sup>       |  0.013   |  0.0013  |  0.142   |  0.003   |  0.23    |  0.15    |  0.005   |  0.003   |  0.48    |
-<sup>1</sup> tier1 defaults from [((bibcite 1))], Chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation: Table 3-1 \\ +<sup>1</sup> tier1 defaults from [(EMEPEEA2019)], Chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation: Table 3-1 \\ 
-<sup>2</sup> tier1 defaults from [((bibcite 1))], Chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation: Table 3-2 \\+<sup>2</sup> tier1 defaults from [(EMEPEEA2019)], Chapter: 1.A.3.d.i, 1.A.3.d.ii, 1.A.4.c.iii Navigation: Table 3-2 \\
 <sup>3</sup> similar EF for biodiesel applied for all mobile sources <sup>3</sup> similar EF for biodiesel applied for all mobile sources
 (//NOTE: Assuming that biodiesel contains far less HMs than fossil diesel oil, similar values are applied to all mobile sources using this biogenic fuel.//) (//NOTE: Assuming that biodiesel contains far less HMs than fossil diesel oil, similar values are applied to all mobile sources using this biogenic fuel.//)
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 ===== Aircraft in 1.A.3.a and 1.A.5.b ii ===== ===== Aircraft in 1.A.3.a and 1.A.5.b ii =====
  
-The EMEP/EEA GB 2016 (July 2017) does not provide specific defaults for HM emissions from the combustion of jet kerosene and aviation gasoline, stating that for for aviation gasoline these emissions are //not estimated// (NE):  +The EMEP/EEA GB 2019 does not provide specific defaults for HM emissions from the combustion of jet kerosene and aviation gasoline, stating that for for aviation gasoline these emissions are //not estimated// (NE): 
- +
-[[gallery size="medium"]] +
-: GB2016(July2017)_EF_NA+NE_Avgas.PNG +
-[[/gallery]]+
  
 Therefore, the inventory compiler decided to apply the tier1 EF from gasoline fuel used in non-road mobile machinery here, too. Therefore, the inventory compiler decided to apply the tier1 EF from gasoline fuel used in non-road mobile machinery here, too.
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 <sup>1</sup> estimated from average lead content of AvGas 100 LL (see also: 1.A.3.a ii (i) and FAQs) of 0.56 g Pb/liter <sup>1</sup> estimated from average lead content of AvGas 100 LL (see also: 1.A.3.a ii (i) and FAQs) of 0.56 g Pb/liter
  
------- +[(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019; Chapter 1.A - Combustion; URL: https://www.eea.europa.eu/publications/emep-eea-guidebook-2019/part-b-sectoral-guidance-chapters/1-energy/1-a-combustion, Copenhagen, 2019.)]
- +
-[[bibliography]] +
-: 1 : EMEP/EEA, 2016: EMEP/EEA air pollutant emission inventory guidebook 2016; Copenhagen, July 2017. +
-[[/bibliography]]+