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sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry [2022/12/20 13:35] – kotzulla | sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry [2024/02/27 12:13] (current) – old revision restored (2023/04/11 12:29) kotzulla | ||
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__Table 2: Annual percentual contribution of NFR 1.A.4.c ii to the primary fuel delivery data provided in NEB line 67__ | __Table 2: Annual percentual contribution of NFR 1.A.4.c ii to the primary fuel delivery data provided in NEB line 67__ | ||
| | | | ||
- | | **DIESEL FUELS** | + | | **DIESEL FUELS** |
- | ^ 1.A.4.c ii (i) | 47.6% | 45.6% | 43.9% | 46.2% | 47.5% | 47.2% | 47.3% | 48.0% | 47.8% | 48.3% | 48.5% | 48.5% | 48.4% | 48.4% | 48.3% | | | + | ^ 1.A.4.c ii (i) | 47.5% | 45.6% | 43.8% | 46.2% | 47.4% | 47.2% | 47.2% | 48.0% | 47.8% | 48.2% | 48.4% | 48.5% | 48.4% | 48.4% | 48.2% | |
- | ^ 1.A.4.c ii (ii) | + | ^ 1.A.4.c ii (ii) |
- | | **GASOLINE FUELS**< | + | | **GASOLINE FUELS**< |
- | ^ 1.A.4.c ii (ii) | + | ^ 1.A.4.c ii (ii) |
source: own estimations based on Knörr et al. (2022b) [(KNOERR2022b)] | source: own estimations based on Knörr et al. (2022b) [(KNOERR2022b)] | ||
< | < | ||
__Table 3: Annual mobile fuel consumption in agriculture and forestry, in terajoules__ | __Table 3: Annual mobile fuel consumption in agriculture and forestry, in terajoules__ | ||
- | | | + | | |
- | ^ Diesel oil | 55,958 | 45,954 | 43,747 | 40,309 | 44,606 | 45,576 | 44,609 | 47,090 | 48,977 | 51,836 | 53,891 | 55,585 | 52,399 | 53,310 | | + | ^ Diesel oil | 55,882 | 45,884 | 43,681 | 40,258 | 44,553 | 45,522 | 44,555 | 47,035 | 48,921 | 51,776 | 53,829 | 55,520 | 52,338 | 53,249 | |
- | ^ Biodiesel | + | ^ Biodiesel |
- | ^ Gasoline | + | ^ Gasoline |
- | ^ Biogasoline | + | ^ Biogasoline |
- | | **Ʃ 1.A.4.c ii** ^ | + | | **Ʃ 1.A.4.c ii** ^ |
- | {{: | + | {{ : |
==== Emission factors ==== | ==== Emission factors ==== | ||
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For all unregulated pollutants, emission trends directly follow the trend in fuel consumption. | For all unregulated pollutants, emission trends directly follow the trend in fuel consumption. | ||
- | {{: | + | {{ : |
Here, exemplary for cadmium, the extreme steps in emission estimates result from two effects: | Here, exemplary for cadmium, the extreme steps in emission estimates result from two effects: | ||
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In addition, in contrast to the main pollutants, all heavy-metal and POP emissions are calculated based on default EF from [(EMEPEEA2019)]. | In addition, in contrast to the main pollutants, all heavy-metal and POP emissions are calculated based on default EF from [(EMEPEEA2019)]. | ||
- | {{: | + | {{ : |
- | {{: | + | |
__Table 4: Development of gasoline consumption in NFR 1.A.4.c ii, in terajoules__ | __Table 4: Development of gasoline consumption in NFR 1.A.4.c ii, in terajoules__ | ||
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For all regulated pollutants, emission trends follow not only the trend in fuel consumption but also reflect the impact of fuel-quality and exhaust-emission legislation. | For all regulated pollutants, emission trends follow not only the trend in fuel consumption but also reflect the impact of fuel-quality and exhaust-emission legislation. | ||
- | {{: | + | {{ : |
- | {{: | + | |
+ | Here, emissions of sulphur oxides follow the step-by-step reduction of sulphur contents in liquid fuels, resulting in a reduction of over 99% since 1990: | ||
+ | |||
+ | {{ : | ||
=== Particulate matter & Black carbon=== | === Particulate matter & Black carbon=== | ||
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Additional contributors such as the impact of TSP emissions from the use of leaded gasoline (until 1997) have no significant effect onto over-all emission estimates. | Additional contributors such as the impact of TSP emissions from the use of leaded gasoline (until 1997) have no significant effect onto over-all emission estimates. | ||
- | {{: | + | {{ : |
===== Recalculations ===== | ===== Recalculations ===== | ||
- | Revisions in **activity data** result from revised activity data for gasoline used in military vehicles (entire timeseries; see NFR 1.A.5.b) as well as the implementation of primary activity data from the now finalised NEB 2019. | + | Revisions in **activity data** result from revised activity data for gasoline used in military vehicles (entire timeseries; see NFR 1.A.5.b) as well as the implementation of primary activity data from the now finalised NEB 2020. |
__Table 6: Revision of annual activity data, in terajoules__ | __Table 6: Revision of annual activity data, in terajoules__ | ||
- | | ^ 1990 | + | | ^ 1990 |
- | | **DIESEL FUELS** | + | | **DIESEL FUELS** |
- | ^ Submission 2022 | + | ^ current submission |
- | ^ Submission 2021 | + | ^ previous submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **GASOLINE FUELS** | + | | **GASOLINE FUELS** |
- | ^ Submission 2022 | + | ^ current submission |
- | ^ Submission 2021 | + | ^ previous submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **OVER-ALL FUEL CONSUMPTION** | + | | **OVER-ALL FUEL CONSUMPTION** |
- | ^ Submission 2022 | + | ^ current submission |
- | ^ Submission 2021 | + | ^ previous submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
In contrast, all **emission factors** remain unrevised compared to last year's susbmission. | In contrast, all **emission factors** remain unrevised compared to last year's susbmission. | ||
<WRAP center round info 65%> | <WRAP center round info 65%> | ||
- | For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the recalculation tables following [[general: | + | For **pollutant-specific information on recalculated emission estimates for Base Year and 2020**, please see the recalculation tables following [[general: |
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