2.A.5.a - Quarrying & Mining - Other Than Coal

Category Code	Method	AD	EF
2.A.5.a	T1/T2	NS/IS/AS	CS
Method(s) applied D Default T1 Tier 1 / Simple Methodology * T2 Tier 2* T3 Tier 3 / Detailed Methodology * C CORINAIR CS Country Specific M Model * as described in the EMEP/EEA Emission Inventory Guidebook - 2019, in category chapters. (source for) Activity Data NS National Statistics RS Regional Statistics IS International Statistics PS Plant Specific As Associations, business organisations Q specific Questionnaires (or surveys) M Model / Modelled C Confidential (source for) Emission Factors D Default (EMEP Guidebook) CS Country Specific PS Plant Specific M Model / Modelled C Confidential

NOx	NMVOC	SO2	NH3	PM2.5	PM10	TSP	BC	CO	Heavy Metals	POPs
NA	NA	NA	NA	L/-	L/T	L/-	NA	NA	NA	NA
L/- key source by Level only -/T key source by Trend only L/T key source by both Level and Trend -/- no key source for this pollutant IE emission of specific pollutant Included Elsewhere (i.e. in another category) NE emission of specific pollutant Not Estimated (yet) NA specific pollutant not emitted from this source or activity = Not Applicable * no analysis done

Regarding particulate emissions, Mining is the main emissions source in the Mineral industries.

In Germany, two diffrent approaches are applied for sands and rocks, and for salts, respectively.

Short description

The mining process emits relevant amounts of particles. Quarrying and mining of minerals other than coal is subsumed, in particular mining of limestone, hard rock and building Sands, with rising recycled materials.

Salt production is a sub-category of the mining activities in respect of the country specific approach used.

The Tier 1 methodology for the emissions from salt mining represents only a small portion of emissions from this sector - few than 4%, depending on the PM fraction. Considering the limited scale of the activity and emission, the part is considered to be below the significance for higher Tiers. Please see the small relevance of this under trend diskussion.

Methodology

With the use of the 2023 GB method EMEP/EEA, 2023: EEA Report No 06/2023 EMEP EEA air pollutant emission inventory guidebook 2023, Copenhagen, 2023; URL: https://www.eea.europa.eu/publications/emep-eea-guidebook-2023/part-b-sectoral-guidance-chapters/2-industrial-processes-and-product-use/2-a-mineral-products/2-a-5-a-quarrying-1/view, a Tier 2 method is available that can reflect different national conditions.

In particular, this concerns input variables on humidity and wind speed, which are localized according to the administrative states of Germany. Larger city states (Berlin, Hamburg and Bremen) were merged with the respective larger states (Brandenburg, Schleswig-Hollstein, Niedersachsen) as the city states do not neccessarily represent the local weather conditions. Parameters on weather as well as on areas can thus be improved in the model above. In a first this was done by using weather data from the German Weather Service (DWD), which may be obtained as daily station data from the Open Data Portal: ClimateDataCenter (CDC) of the DWD URL: https://opendata.dwd.de/climate_environment/CDC/observations_germany/climate/daily/kl/

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; URL: https://land.copernicus.eu/user-corner/technical-library/corine-land-cover-nomenclature-guidelines/html/index-clc-131.html) had to be adjusted for areas of active open-pit lignite mines.

For salt production currently a Tier 1 method is used: information on production of salts are multiplied with country specific emission factors for TSP and PM. Please see the small relevance of this under trend diskussion.

Activity Data

As provided in the Guidebook model, specific AD for hard rock, sand, and recycled material are applied. Because of incomplete national statistics, these AD are taken from nationals and international association information European Industry Association data are published annually at https://www.aggregates-europe.eu/facts-figures/figures/. Within the framework of technical consultations, historical data were confirmed by the National Association for Mineral Resources https://www.bv-miro.org/. Now we are additionally in contact with Federal Institute for Geosciences and Natural Resources for figures og mineral raw materials https://www.bgr.bund.de/DE/Themen/Min_rohstoffe/Produkte/produkte_node.html. For time series consistency, data gaps are closed via interpolation or expert adjustement.

Data of production of potash and rock salt are included in national statistics. Potash salt is dominating, nevertheless gaps of statistics are filled and emissions are modelled as potash salt only.

Emission factors

The calculation of emissions takes into account national circumstances and reduction measures.The calculations are available in total more than ten Excel files (individual years since 1990, annually from 2010). Since the GB tool in principle calculates emissions for exactly one year EMEP/EEA, 2023: EEA Report No 06/2023 EMEP EEA air pollutant emission inventory guidebook 2023, Copenhagen, 2023; URL: https://www.eea.europa.eu/publications/emep-eea-guidebook-2023/part-b-sectoral-guidance-chapters/2-industrial-processes-and-product-use/2-a-mineral-products/2-a-5-a-quarrying-1/view, files must be available for exactly those years in which input data are available. Intermediate years are interpolated in case of data gaps.

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.

The emission factors for salt production are based on analogy to bulk product handling by an UBA expert judgement:

Table 2: Overview of applied emission factors, in kg/t salt

EF value	EF trend
TSP	0.031	constant
PM10	0.016	constant
PM2.5	0.003	constant

Trend discussion

Trends in emissions follow the shrinking mining activities.

The Tier 1 methodology for the emissions from salt mining represents only a small portion of emissions from this sector - few than 4%, depending on the PM fraction. Considering the limited scale of the activity and emission, the part is considered to be below the significance for higher Tiers.

share-of-salt-in-mining

Recalculations

Recalculations were necessary due to update the most recently year.

For pollutant-specific information on recalculated emission estimates for Base Year and 2022, please see the recalculation tables following chapter 8.1 - Recalculations.

Planned improvements

At the moment, it is planned evaluate further Country specific conditions.