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sector:ippu:mineral_industry:quarrying_mining:start [2023/10/30 10:52] – [Activity Data] kludt | sector:ippu:mineral_industry:quarrying_mining:start [2025/04/29 13:29] (current) – [Planned improvements] kotzulla | ||
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====== 2.A.5.a - Quarrying & Mining - Other Than Coal ====== | ====== 2.A.5.a - Quarrying & Mining - Other Than Coal ====== | ||
- | ^ Category Code ^ Method | + | ^ Category Code ^ Method |
- | | 2.A.5.a | + | | 2.A.5.a |
- | ^ ^ NO<sub>x</ | + | | |
- | | Key Category: | | + | |
- | {{page> | + | ---- |
- | \\ | + | | NO< |
+ | | NA | ||
+ | | {{page> | ||
+ | |||
+ | Quarrying & Mining is the main source for particulate matter emissions within the entire **Mineral industries sub-sector (2.A)**. | ||
- | For particulate emissions, Mining is the main emissions source in the Mineral industries. | ||
- | In Germany we use two approaches - one for Sands and rocks, one for salts. | ||
===== Short description ===== | ===== Short description ===== | ||
- | The mining | + | Generally, |
+ | |||
+ | **NFR 2.A.5.a - Quarrying and mining of minerals | ||
- | Salt production is a sub-category of the mining | + | Due to the country-specific approach applied, the production |
===== Methodology ===== | ===== Methodology ===== | ||
- | With the use of the 2019 GB method [(EMEP/EEA, 2019: EEA Report No 13/2019 EMEP EEA air pollutant | + | Withi the German |
- | In particular, this concerns input variables on humidity | + | **Sands |
- | No area information from the Corine land cover before 2010 is used (consistent data sets). In addition, information from CLC category 131 (Mineral extraction sites [(Copernicus 2019: CLC-classes; | + | By applying the 2023 GB method [(EMEPEEA2023)], |
+ | the German federal states. Here, as the three German city-states (Berlin, Hamburg, and Bremen) do not represent average weather conditions, | ||
+ | and Niedersachsen). | ||
+ | Parameters on weather as well as on areas can thus be improved in the model mentioned above. | ||
+ | In a first approach, this was done by using weather data from the German Weather Service (DWD), which can be obtained as daily station data from (DWD, 2024) [(DWD2024)]. | ||
+ | No area information from the Corine land cover before 2010 is used (consistent data sets). In addition, information from CLC category 131 (Mineral extraction sites) had to be adjusted for areas of active open-pit lignite mines. | ||
- | For salt production currently | + | **Salts** |
+ | |||
+ | Salt mining represents only a minor portion (less than 4%, depending on the PM fraction) of the particulate-matter emissions reported for NFR 2.A.5.a. | ||
+ | |||
+ | With respect to this limited scale of both activity and emissions, salt mining | ||
+ | Therefore, in contrast to the mining/ | ||
===== Activity Data ===== | ===== Activity Data ===== | ||
- | As provided in the Guidebook model, specific AD for hard rock, sand, and recycled material are applied. | + | **Sands |
- | Because of incomplete national statistics, these AD are taken from nationals and international association information [(European Industry Association data are published annually at https:// | + | |
- | For time series concsistency, | + | |
- | The data from national statistics includes production of potash and rock salt. Potash salt is dominating, nevertheless gaps of statistics are filled | + | As provided in the calculation model presented with the EMEP/EEA Guidebook, specific activity |
+ | Here, due to incomplete national | ||
- | ===== Emission factors ===== | + | Within the framework of technical consultations, |
- | The calculation of emissions takes into account national circumstances | + | However, additional information |
- | With the help of the GB tools, IEFs are estimated on an annual basis, which are used for the inventory method AR x EF. The emission factors are virtual, but the calculation of this is modified by national circumstances on the parameters. So we would name the EF as country-specific. | + | Therefore, for time series consistency, data gaps are closed via interpolation or expert adjustments. |
- | ===== Trend discussion ===== | + | |
- | Trends in emissions follow the shrinking mining activities. | + | **Salts** |
- | [{{sector: | + | Production data for potash and rock salt are included |
+ | Here, as potash salt is dominating, all reported emissions are modelled as resulting from potash salt. | ||
- | ===== Recalculations ===== | ||
- | <WRAP center round info 60%> | + | ===== Emission |
- | With **activity data and emission | + | |
- | </ | + | |
- | =====Planned improvements ===== | + | **Sands and Rocks** |
- | At the moment, it is planned evaluate further Country | + | As described above, |
- | ===== Short description - Salt Production ===== | + | The calculations are available in from of more than ten MS Excel files (individual years since 1990, annually from 2010). |
+ | Since the GB tool in principle calculates emissions for exactly one year [(EMEPEEA2023)], | ||
+ | In case of data gaps, intermediate years are interpolated . | ||
- | Salt production is a sub-category of the mining activities in respect | + | With the help of the GB tools, annual implied EFs are estimated which are used for the inventory method (EM = AR x EF). |
+ | As the calculation | ||
- | ===== Method ===== | + | **Salts** |
- | ==== Activity data ==== | + | |
- | The data from national statistics includes production of potash and rock salt. Potash salt is dominating, nevertheless gaps of statistics are filled and emissions are modelled as potash salt only. | + | |
- | ==== Emission factors ==== | + | The emission factors |
- | The emission factors are based on analogy to bulk product handling by an UBA expert judgement: | + | |
- | __Table 2: Overview of applied | + | __Table 2: Overview of emission factors |
- | ^ |^ | + | ^ |^ value |^ trend || |
- | ^ TSP || 0.031 | + | ^ TSP || 0.031 || constant |
- | ^ PM< | + | ^ PM< |
- | ^ PM< | + | ^ PM< |
+ | ===== Trend discussion ===== | ||
+ | |||
+ | Trends in emissions follow the shrinking mining activities. | ||
+ | |||
+ | [{{sector: | ||
+ | |||
+ | note: small change for 2023 | ||
+ | |||
+ | As mentioned above, emissions from salt mining represent only a small portion (less than 4%) of the total emissions allocated to NFR sub-sector 2.A.5.a, depending on the specific pm fraction. | ||
+ | |||
+ | [{{: | ||
===== Recalculations ===== | ===== Recalculations ===== | ||
- | <WRAP center round info 60%> | + | Recalculations were necessary due to updated production figures for the most recent year. |
- | With **activity data and emission | + | |
+ | <WRAP center round info 65%> | ||
+ | For **pollutant-specific information on recalculated | ||
</ | </ | ||
+ | =====Planned improvements ===== | ||
- | ===== Planned improvements ===== | + | <WRAP center round info 45%> |
+ | It is planned to further evaluate country-specific conditions. | ||
+ | </ | ||
- | At the moment, no category-specific improvements are planned. | ||
+ | [(EMEPEEA2023> | ||
+ | [(DWD2024> | ||
+ | [(COPERNICUS2019> | ||
+ | [(UEPG2024> | ||
+ | [(BVMIRO2024> | ||
+ | [(BGR> BGR - Bundesanstalt für Geowissenschaften und Rohstoffe (Federal Institute for Geosciences and Natural Resources): https:// | ||