{"id":16563,"date":"2023-08-15T16:14:50","date_gmt":"2023-08-15T14:14:50","guid":{"rendered":"https:\/\/2025.mining-report.de\/english\/?page_id=16563"},"modified":"2024-01-31T14:30:02","modified_gmt":"2024-01-31T13:30:02","slug":"environmental-pressures-of-current-mining-in-germany-a-critical-comment","status":"publish","type":"page","link":"https:\/\/mining-report.de\/english\/environmental-pressures-of-current-mining-in-germany-a-critical-comment\/","title":{"rendered":"Environmental Pressures of Current Mining in Germany: a Critical Comment"},"content":{"rendered":"<span class=\"tie-dropcap \">M<\/span>ines interfere with the environment. However, active mining in Germany in its various forms causes only small overall environmental pressures, based on data from the Federal Statistical Office of Germany, due to its limited land use, waste production, water extraction as well as particulate matter and greenhouse gas emissions. Therefore, federal politics should acquire and present to the public strategies, key issue papers, writings and websites on German mining that reflect these scientific facts. In future, it is important for the German mining sector to remain a global role model for environmental stewardship and land restoration and to move from individual examples of excellence to normality.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n\n\t\t<div class=\"one_third tie-columns\"><a href=\"\/wp-content\/uploads\/_pda\/2023\/08\/MRG_2304_Umweltbelastungen_Bergbau_Lottermoser_230816.pdf\" target=\"_blank\" class=\"shortc-button small white\">Download article as PDF<\/a>\n\t\t<\/div>\n\t\n\n\t\t<div class=\"two_third tie-columns last\"><strong>Author\/Autor:\u00a0<\/strong>Univ.-Prof. PhD Bernd G. Lottermoser, Lehrstuhl f\u00fcr nachhaltige Rohstoffgewinnung, Institute of Mineral Resources Engineering (MRE), RWTH Aachen University (RWTH), Aachen\/Germany \n\t\t<\/div>\n\t\t<div class=\"clearfix\"><\/div>\n\t\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>1\u00a0 Introduction<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>A recognition of the German mining sector in its own country as an important factor for a flourishing economy and its responsible environmental stewardship and nature conservation is missing. Despite its economic performance and the rehabilitation of mining legacies at the highest international level (1), mines and mining companies have a rather poor image among the many facets of German politics and the general public and especially among nature conservationists and environmental groups. Despite world-leading environmental protection measures and standards, German mining is neither accepted nor appreciated in politics or society. Especially in ideologically and politically motivated narratives or poorly researched articles, it is repeatedly pointed out that the mining of raw materials is associated with dramatic consequences for the environment. Such articles, reports, media contributions and websites are limited to purely qualitative and general statements and thus only represent opinions, like the one of the Federal Environment Agency on the responsible supply of raw materials in Germany (2): \u201cActive mining in its diverse manifestations leads to considerable impacts to the environment, in particular to nature and water balances\u201d. Such impotent statements are made without quantitative analyses and robust methods and without a presentation of scientific data. However, documentation and evaluation of quantitative data correspond to good scientific practice and internationally accepted standards, especially in the environmental sciences.<\/p>\n<p>The above opinions on mining are also in stark contrast to international scientific studies, which show that, e.\u2009g., in the global context metal mining causes only minor environmental impacts through land use, water abstraction and greenhouse gas emissions (3). It is therefore necessary to clarify the relative contribution and magnitude of environmental pressures caused by the German mining sector.<\/p>\n<p>This article firstly outlines the fundamental factors that determine environmental impacts of mines in general. Subsequently, the pressures of active German mining on the environment are presented using the DPSIR model (Driving Forces, Pressures, States, Impacts, Responses) (4, 5). This contribution thereby refers to publicly available data from the Federal Statistical Office, which, due to data availability, had to be limited to aspects such as land use, waste production, water withdrawal as well as greenhouse gas and particulate matter emissions. The environmental pressures caused by active German mining are compared with other anthropogenic activities, while the environmental impacts of historic and closed mining operations are not considered here. As a result, this article contributes to the scientific discourse on the pressures, impacts, and effects of active German mining on the environment.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>2\u00a0 Effects and impacts of mining on landscapes and the environment<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>2.1 \u00a0Controlling parameters<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>Mining effects the environment, because mineral extraction processes occur in the Earth&#8217;s natural spheres and they interact with these subsystems, i.\u2009e., lithosphere, hydrosphere, biosphere, pedosphere, atmosphere. Mines may emit, e.\u2009g., greenhouse gases, particulate matter, pollutants and noise, cause vibrations, produce waste, and have an impact on the individual spheres, e.\u2009g., deforestation, loss of biodiversity, water, sediment, soil and air pollution, mine subsidence and hazards. Consequently, mining influences the natural flow of materials and energy in the Earth\u2019s spheres. The extraction of primary raw materials is therefore inevitably accompanied by interventions of the natural Earth systems. Mining may cause a variety of effects on the geospheres, with each mine having its own unique set of challenges.<\/p>\n<p>Possible environmental hazards and pollution at terrestrial mining sites are diverse, varied, and site-specific. The fundamental parameters that determine the impact of mining on landscapes and the environment have been known for some time (6). Mineral deposits are accumulations of primary raw materials in the Earth&#8217;s crust and result from various geological processes. During these processes, the deposits acquire specific geological characteristics, including the amount and type of elements enriched in the deposits, the type of minerals formed and their grain size, and the rock types associated with the deposits. Such fundamental geological aspects of mineral deposits have important and predictable environmental impacts. The geology of a mineral deposit, e.\u2009g., can affect the chemistry of local ground and surface waters and the properties of dusts, soils and sediments. Such effects and impacts of mineral deposits on the environment may also occur naturally. Alternatively, they can be exacerbated or even caused by improper mining practices.<\/p>\n<p>Local climate, hydrology and topography also play an important role in the type and extent of environmental hazards and pressures at a mine site (6). At a steep topographic location, e.\u2009g., contaminants can be transported faster and further than at a mine location that is not so steep. At a humid location, contaminants can be widely distributed via an aqueous transport mode. At an arid location, dust emissions may be the main transport mode of contaminants.<\/p>\n<p>The type and size of the mining and processing operations and their practices also determine the type and size of environmental impacts of a mine. Thus, deposit geology as well as local climate, hydrology and topography, together with mining and mineral processing practices (including crushing), control the nature and magnitude of environmental hazards and pressures at mine sites. Ultimately, the implementation of environmental regulations by the legislator influences the effectiveness of all environmental protection measures. Here, the precautionary principle, the elimination of environmental pressures at their source and the polluter pays principle support the effectiveness of environmental regulations.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>2.2 \u00a0Environmental indicators<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>Environmental analyses are routine tasks of the environmental management at active mine sites (5). Such monitoring provides information on the current state of the environment at individual locations. In general, environmental analyses aim to track changes in the quality and condition of the Earth&#8217;s spheres at different geographic and temporal scales. At mine sites, such data provides information about conditions and processes that may exist or develop during the life-of-mine from exploration to closure.<\/p>\n<p>An environmental indicator is based on a parameter, or a value derived from parameters, that describes the state of the environment and its impact on people, ecosystems and materials, the pressures on the environment, the drivers and the responses that control that system (European Environment Agency, Glossary). The DPSIR model is widely used to relate human activities to the state of the environment (4, 5). Within a DPSIR analysis, indicators are assigned to the individual components of the environmental system under consideration to provide information about<\/p>\n<p>(i)\u00a0\u00a0\u00a0\u00a0 driving forces;<br \/>\n(ii)\u00a0\u00a0 resulting environmental pressures;<br \/>\n(iii)\u00a0 the state of the environment;<br \/>\n(iv)\u00a0\u00a0 impacts resulting from changes in environmental quality; and<br \/>\n(v)\u00a0\u00a0\u00a0 responses to these changes in the environment (5).<\/p>\n<p>In mining, pressure indicators describe, e.\u2009g., the land use of a mine, the amount of mine waste produced, the extraction of ground and surface water, or the emission of particulate matter and greenhouse gases. By contrast, state indicators provide information on the current exposure, e.\u2009g., water quality and noise (Table 1). Impact indicators, on the other hand, communicate the effect on the spheres with their consequences, e.\u2009g., loss of biodiversity. Response indicators refer to responses and attempts to prevent, compensate, improve, or adapt to changes in the state of the environment, e.\u2009g., through investments in environmental protection.<\/p>\n<figure id=\"attachment_16566\" aria-describedby=\"caption-attachment-16566\" style=\"width: 1417px\" class=\"wp-caption alignnone\"><a href=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren.jpg\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-16566 size-full\" src=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren.jpg\" alt=\"\" width=\"1417\" height=\"174\" srcset=\"https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren.jpg 1417w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren-300x37.jpg 300w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren-1024x126.jpg 1024w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren-768x94.jpg 768w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_tab1_umweltindikatoren-600x74.jpg 600w\" sizes=\"auto, (max-width: 1417px) 100vw, 1417px\" \/><\/a><figcaption id=\"caption-attachment-16566\" class=\"wp-caption-text\">Table 1. Examples of environmental indicators describing the interactions between mining and the environment according to the DPSIR framework (Driving Forces, Pressures, States, Impacts, Responses) (5). \/\/ Tabelle 1. Beispiele f\u00fcr Umweltindikatoren zur Beschreibung der Wechselwirkungen zwischen Bergbau und Umwelt gem\u00e4\u00df DPSIR-Framework (Driving Forces, Pressures, States, Impacts, Responses). Source\/Quelle: MRE<\/figcaption><\/figure>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>2.3 \u00a0Environmental pressures of mining in Germany<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>This article refers to data which, as indicators, mainly allow statements to be made about the environmental pressures of active mining in Germany, i.\u2009e. land use, waste production, water withdrawal, greenhouse gas and particulate matter emissions. On the other hand, there is no comprehensive national data on the state and impact of mining on the environment for certain environmental media and impacts, e.\u2009g., loss of biodiversity, water quality. Due to the data situation, the focus of this article is on pressure indicators, while no quantitative statements on status and impact indicators are possible (state and impact indicators). As a result, the following indicators are particularly relevant for assessing the environmental pressures of active mining in Germany.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p><strong>2.3.1\u00a0 Land use<\/strong><\/p>\n<p>The area required by German mining (mining operations, opencast mines, pits, quarries) is only a fraction of the land area of the Federal Republic of Germany (2021: 1,407\u00a0km<sup>2<\/sup>, approximately 0.4\u2009%) (7). This is a tiny fraction compared to the vast tracts of land used for agriculture and forestry (180,590\u00a0km<sup>2<\/sup>, 50.5\u2009%; 106,699\u00a0km<sup>2<\/sup>, 29.8\u2009%, respectively) and compared to the area of wind power plants, which is increase from currently 0.8\u2009% to 2\u2009%. Mining areas, on the other hand, are areas of temporary land use because closed and rehabilitated areas become once again available for industrial, agricultural or other subsequent uses. Therefore, the area of mining land in Germany calculated annually by the Federal Statistical Office does not increase any further. It has even been declining continuously for decades (1992: 1,878\u00a0km<sup>2<\/sup>; 2000: 1,796\u00a0km<sup>2<\/sup>; 2010: 1,623\u00a0km<sup>2<\/sup>; 2021: 1,407\u00a0km<sup>2<\/sup>) (7, 8). Since 1992, the mining area in Germany has decreased by 471\u00a0km<sup>2<\/sup> or 25\u2009%.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p><strong>2.3.2\u00a0 Emissions<\/strong><\/p>\n<p>The extraction of mineral raw materials and coal, especially in opencast mines, is associated with emissions of greenhouse gases, coarse and fine dust as well as noise. The greenhouse gas and fine dust emissions in the extraction of stone and aggregate, coal and ores decreased between 2000 and 2020 (Figures 1, 2, 3). The greenhouse gas emissions of the mining sector are only a small fraction (2020: 4.5 Mt\u00a0CO<sub>2<\/sub>\u00a0equivalent, approximately 0.5\u2009%) compared to the total emissions from all German economic sectors and private households (824 Mt\u00a0CO<sub>2<\/sub>\u00a0equivalent, according to Kyoto-Protocol) (9).<\/p>\n<figure id=\"attachment_16567\" aria-describedby=\"caption-attachment-16567\" style=\"width: 1181px\" class=\"wp-caption alignnone\"><a href=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020.jpg\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-16567 size-full\" src=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020.jpg\" alt=\"\" width=\"1181\" height=\"843\" srcset=\"https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020.jpg 1181w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020-300x214.jpg 300w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020-1024x731.jpg 1024w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020-768x548.jpg 768w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_01_co2_emissionen_bergbau_2000_2020-600x428.jpg 600w\" sizes=\"auto, (max-width: 1181px) 100vw, 1181px\" \/><\/a><figcaption id=\"caption-attachment-16567\" class=\"wp-caption-text\">Fig. 1. Total greenhouse gas emissions (CO<sub>2<\/sub>, CH<sub>4<\/sub>, N<sub>2<\/sub>O, HFC, PFC, SF<sub>6<\/sub>, NF<sub>3<\/sub>) (1,000 t CO<sub>2<\/sub> equivalent) for the German mining sector over the years 2000 to 2020, including CO<sub>2<\/sub> emissions from biomass (9). \/\/ Bild 1. Treibhausgas-Emissionen (CO<sub>2<\/sub>, CH<sub>4<\/sub>, N<sub>2<\/sub>O, HFC, PFC, SF<sub>6<\/sub>, NF<sub>3<\/sub>) insgesamt (1.000 t CO<sub>2<\/sub>-\u00c4quivalent) f\u00fcr den deutschen Bergbausektor \u00fcber die Jahre 2000 bis 2020 (9), einschlie\u00dflich CO<sub>2<\/sub>-Emissionen aus Biomasse (9).<\/figcaption><\/figure>\n<figure id=\"attachment_16568\" aria-describedby=\"caption-attachment-16568\" style=\"width: 1181px\" class=\"wp-caption alignnone\"><a href=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020.jpg\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-16568 size-full\" src=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020.jpg\" alt=\"\" width=\"1181\" height=\"813\" srcset=\"https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020.jpg 1181w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020-300x207.jpg 300w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020-1024x705.jpg 1024w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020-768x529.jpg 768w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_02_feinstaub_pm10_emissionen_bergbau_2000_2020-600x413.jpg 600w\" sizes=\"auto, (max-width: 1181px) 100vw, 1181px\" \/><\/a><figcaption id=\"caption-attachment-16568\" class=\"wp-caption-text\">Fig. 2. Total particulate matter emissions (PM10, tonnes) for the German mining sector over the years 2000 to 2020 (9). \/\/ Bild 2. Feinstaub-Emissionen (PM10, Tonnen) insgesamt f\u00fcr den deutschen Bergbausektor \u00fcber die Jahre 2000 bis 2020 (9).<\/figcaption><\/figure>\n<figure id=\"attachment_16569\" aria-describedby=\"caption-attachment-16569\" style=\"width: 1181px\" class=\"wp-caption alignnone\"><a href=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020.jpg\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-16569 size-full\" src=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020.jpg\" alt=\"\" width=\"1181\" height=\"635\" srcset=\"https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020.jpg 1181w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020-300x160.jpg 300w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020-1024x551.jpg 1024w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020-768x413.jpg 768w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_03_feinstaub_pm2_5_emissionen_bergbau_2000_2020-600x323.jpg 600w\" sizes=\"auto, (max-width: 1181px) 100vw, 1181px\" \/><\/a><figcaption id=\"caption-attachment-16569\" class=\"wp-caption-text\">Fig. 3. Total particulate matter emissions (PM2.5, tonnes) for the German mining sector over the years 2000 to 2020 (9). \/\/ Bild 3. Feinstaub-Emissionen (PM2,5, Tonnen) insgesamt f\u00fcr den deutschen Bergbausektor \u00fcber die Jahre 2000 bis 2020 (9).<\/figcaption><\/figure>\n<p>Particulate matter emissions from the mining sector also only represent fractions (2020: approximately 9.3\u2009% PM10, approximately 3.4\u2009% PM2.5) compared to the particulate matter emissions of all German economic sectors and private households (180,138 t PM10 and 81,181 t PM2.5 emissions in total, according to the Kyoto Protocol) (Figures 2, 3). In a whole year (2020), coal mining produced the same magnitude of PM10 fine dust (2,978 t) (9), as the burning of fireworks on New Year\u2019s Eve (2,050 t) (10). Nevertheless, innovations in dust suppression at mine sites are still needed. Recent research at RWTH Aachen University, Aachen\/Germany, has shown by-products and wastes from food processing to be potentially environmentally friendly alternatives to traditional dust suppressants (11, 12).<\/p>\n<p>In the Federal Immission Control Act (BImschG), open-cast mines are classified as \u201cinstallations not requiring approval\u201d. The noise limit values for opencast mines are therefore only guideline values, which have been set at 60 dB(A) during day time and 45\u00a0dB(A) at night for commercial centers, villages and mixed housing and commercial areas around opencast mines (13). Operators must also set up and operate systems in such a way that harmful environmental effects are prevented, and unavoidable harmful environmental effects are reduced to a minimum. In the Rhenish lignite mining area, emission measurements have shown, e.\u2009g., that these have been below the guideline values in almost all cases for years (14). On the other hand, significantly lower environmental standards apply to a state-owned company such as the Deutsche Bahn, since there is a 18,500 km DB route network with &gt; 57\u00a0dB(A), i.\u2009e. 18,500\u00a0km of DB route network are at least twice as loud as the nightly reference values for opencast mines. These gigantic DB noise emission routes are not to be rectified until 2050 (15).<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p><strong>2.3.3 \u00a0Waste production<\/strong><\/p>\n<p>Depending on the characteristics of a deposit and the extraction and processing practices, large amounts of waste can be produced at mine sites. In the German mining sector, non-hazardous waste predominates (&gt; 99\u2009%), and the amount of waste from the mining sector is a small proportion (2020: 28.6 Mt; approximately 6.9\u2009%) of the total waste generated in Germany (413 Mt) (16). In addition, the amount of hazardous and non-hazardous waste generated during extraction and treatment of mineral resources fell continuously between 1996 and 2020 in Germany (Figure 4).<\/p>\n<figure id=\"attachment_16570\" aria-describedby=\"caption-attachment-16570\" style=\"width: 1181px\" class=\"wp-caption alignnone\"><a href=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020.jpg\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"wp-image-16570 size-full\" src=\"https:\/\/2025.mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020.jpg\" alt=\"\" width=\"1181\" height=\"640\" srcset=\"https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020.jpg 1181w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020-300x163.jpg 300w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020-1024x555.jpg 1024w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020-768x416.jpg 768w, https:\/\/mining-report.de\/english\/wp-content\/uploads\/sites\/3\/2023\/08\/rwth_04_bergematerial_bergbau_1996_2020-600x325.jpg 600w\" sizes=\"auto, (max-width: 1181px) 100vw, 1181px\" \/><\/a><figcaption id=\"caption-attachment-16570\" class=\"wp-caption-text\">Fig. 4. Mining wastes and wastes from the extraction and treatment of mineral resources (1,000 t) in the years 1996 to 2020 (16). \/\/ Bild 4. Bergematerial aus dem Bergbau bzw. Abf\u00e4lle aus Gewinnung und Behandlung von Bodensch\u00e4tzen (1.000 t) in den Jahren 1996 bis 2020 (16).<\/figcaption><\/figure>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p><strong>2.3.4 \u00a0Ground and surface waters<\/strong><\/p>\n<p>At many sites, the extraction of mineral raw materials and coal using open pits requires pumping of groundwater. This is where the German mining sector is having a major impact on the Earth&#8217;s spheres, with over 1,288 M\u00a0m<sup>3<\/sup> of water being extracted in 2019 (17). However, water abstraction by the mining sector is only a fraction (approximately 6.2\u2009%) of the total amount of abstraction by the public and non-public water supply and sanitation (total water extraction ca. 20,716 M\u00a0m<sup>3<\/sup>) (17). Most of the water withdrawn is returned back into receiving waters and aquifers via seepages and direct discharges (approximately 1,079 M\u00a0m<sup>3<\/sup>) (17). The most significant pumping and reintroduction of groundwater takes place in opencast lignite mining (approximately 1,000 M\u00a0m<sup>3<\/sup>, so the remaining water withdrawal from other mining operations is only a fraction of the total water withdrawal in Germany (approximately 209 M\u00a0m<sup>3<\/sup>, 1\u2009%).<\/p>\n<p>Until recently, Germany was spared mining-related, sudden environmental catastrophes. Yet in August 2022, the river Oder was affected by severe environmental damage over a length of around 500 km, in which fish, mussels, crabs and snails died on an unprecedented scale (18). Toxic algae blooms caused by low water levels, low oxygen levels, high water temperatures and the rapid discharge of large amounts of saline mine water from operations in Poland are likely to blame (18). In order to prevent such accidents in the future, mobile and lab-based measuring devices, online availability of the monitoring data, and official reporting chains are required, as they already exist in other mining regions of the world, e.\u2009g., Hunter River Salinity Trading Scheme, Australia. Moreover, innovations in determining mine water quality are needed. Recent research at RWTH has shown portable devices to be potentially low-cost methods compared to traditional laboratory approaches (19, 20).<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p><strong>2.3.5 \u00a0Biodiversity<\/strong><\/p>\n<p>The decline in terrestrial biodiversity is mainly attributed to land use changes. The fact that agriculture is a driving force behind the loss of biodiversity in Germany has been acknowledged for some time (21). Mines also have a land use, albeit a small one, are connected to the biosphere and can therefore have an impact on biodiversity. In this context, however, it has been established that mining contributes to less than 1\u2009% of the total land-use-related biodiversity loss worldwide (22).<\/p>\n<p>Active and disused mine sites have a high ecological value and offer opportunities as \u201cwandering biotopes\u201d (23). Half of all Bavarian owls, e.\u2009g., breed in quarries (24). During recultivation, former mine sites can contribute to the development of biodiversity due to their diverse terrain types, because site diversity favors species diversity and the rich structure allows the development of a wide variety of small-scale habitats. In addition, German post-mining landscapes offer great potential as wilderness areas. These locations often consist of different ecosystems and developing into different ecosystems and, as large, (largely) undivided, use-free areas, which allow the (re)development of biodiversity (25).<\/p>\n<p>Despite the above facts, descriptions of the various threats to biodiversity in Germany repeatedly and extensively refer to mining (26). However, the Federal Environment Agency does not point out to the public other and far greater causes of biodiversity loss. The largest global human-related loss of birds and mammals, e.\u2009g., is caused by the domestic cat Felis catus, ranging from domestic to feral domestic cats (27). In Germany, the approximately 15 million domestic cats and 2 million feral cats are responsible for the loss of approximately 1 million birds, mammals and reptiles per day (28). However, only 9\u2009% of all German cities and municipalities are currently following the Paderborn model (registration and castration of domestic cats). Ultimately, many governments, including Germany&#8217;s, are failing to meet their international obligations to prevent, reduce or eliminate the impact of free-roaming and feral domestic cats on biodiversity (27).<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>3 \u00a0Ecological approach to domestic mining<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>The existing German raw materials strategy, the key issues paper on raw material supply and the coalition agreement of the federal government repeatedly emphasize that domestic raw material extraction in Germany should be ecologically oriented (29, 30, 31). The term \u201cecological\u201d was (un)consciously not defined in these strategic policy documents. Here, it is assumed that an ecological orientation of domestic mining means an ecological industrial policy according to the definition of the Federal Environment Agency, i. e. a strategic orientation of the industrial policy instruments to the central challenges of climate protection, global environmental destruction, scarcity of resources.<\/p>\n<p>The German mining sector has made phenomenal progress in its ability to observe, measure and describe mining environments. This also includes best practice environmental protection protocols, standards and remediation technologies for waste management, sewage management, noise and vibration protection, air pollution control, species and landscape protection, protection and remediation of soil, groundwater and surface water, avoidance and reduction of greenhouse gases, use of renewable energies, energy efficiency and energy savings. Germany is a global leader here and German mining companies invested comparatively more in environmental protection in 2020 (805 M \u20ac) than many other manufacturing industries such as the textile, clothing and furniture industries (32), which generate higher gross added values. However, investment in environmental protection by the mining sector is only a fraction (approximately 0.9\u2009%) of the total investment by the manufacturing industry excluding construction (a total of 89,734 M \u20ac) (32). The comparatively low investments in environmental protection could also be due to the fact that, as explained, only minor environmental pressures are caused by active mining and &gt; 99\u2009% of mine waste can be classified as non-hazardous (16).<\/p>\n<p>From a scientific point of view, political strategies on domestic mining should take into account the relatively low environmental pressures of active mining, illustrated by the pressure indicators mentioned above, and the progress in climate and environmental protection as well as resource efficiency. Here, the German mining industry has individual examples of excellence that have been accepted internationally. The European Aggregate Association, e.\u2009g., has repeatedly awarded sustainability prizes to German companies, and the Federal German Agency for Nature Conservation has recognized RWE&#8217;s recultivation of open-cast lignite mining for its biodiversity as part of the UN Decade on Biological Diversity. When formulating the German raw materials policy, it is also not taken into account that the domestic mining industry is committed to climate protection, e.\u2009g., by reducing energy consumption with the help of continuous conveyor belts. It has also proven itself as an energy producer by installing renewable energy systems on its properties.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>4\u00a0 Conclusion<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>Mines interfere with the natural spheres, and individual mines can cause significant impacts to the environment. However, environmental indicators based on a DPSIR model and derived from data from the Federal Statistical Office show that overall active mining in Germany<\/p>\n<ul>\n<li>causes only small percentages of the total environmental pressures through land use, waste production, water extraction and greenhouse gas and particulate matter emissions; and<\/li>\n<li>causes smaller environmental pressures than many other public and non-public activities.<\/li>\n<\/ul>\n<p>Global mining contributes less than 1\u2009% of total land-use-related biodiversity loss, and in terms of biodiversity threats, mines and their post-mining activities provide opportunities for biodiversity, biotopes and habitats for many threatened and rare animals and plants. In addition, the German mining sector has proven for some time through individual examples of excellence and international recognition that environmental protection, nature conservation, species protection, renewable energies and resource efficiency can be combined with mining. In future, the German mining industry will have to remain a global role model for environmental stewardship and land restoration in the raw materials sector and move from individual examples of excellence to normality.<\/p>\n<p>Federal politics is currently pursuing an ecological focus for domestic mining, although very high environmental standards already exist for German mining operations. Federal politics and especially the Federal Environment Agency should rather<\/p>\n<ul>\n<li>comply with Germany&#8217;s international obligations for species protection;<\/li>\n<li>design exemplary environmental standards for state-owned enterprises and use them as pioneers and leaders in an exemplary manner; and<\/li>\n<li>develop and present to the public strategies, key issues papers, publications and websites on the environmental impact of active German mining that reflect scientific facts.<\/li>\n<\/ul>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<h4>Acknowledgements<\/h4>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n<p>Aspects of this contribution were presented at the 15th Deutschen Naturschutzrechtstag 2023.<\/p>\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<div class=\"toggle tie-sc-close\">\n\t\t\t<h3 class=\"toggle-head\"><strong>References \/ Quellenverzeichnis<\/strong> <span class=\"fa fa-angle-down\" aria-hidden=\"true\"><\/span><\/h3>\n\t\t\t<div class=\"toggle-content\">\n<p>(1) Brock, A. (2020): Securing accumulation by restoration \u2212 Exploring spectacular corporate conservation, coal mining and biodiversity compensation in the German Rhineland. In: Environment and Planning E: Nature and Space 0(0), pp 1\u2009\u2212\u200932.<\/p>\n<p>(2) Umweltbundesamt (2020): Politikempfehlungen f\u00fcr eine verantwortungsvolle Rohstoffversorgung Deutschlands als Beitrag zur nachhaltigen Entwicklung. Teil I \u2212 Handlungsvorschl\u00e4ge f\u00fcr eine umwelt- und ressourcenschonende Rohstoffgewinnung in Deutschland. 44 S.<\/p>\n<p>(3) Tost, M.; Bayer, B.; Hitch, M.; Lutter, S.; Moser, P.; Feiel, S. (2018): Metal mining\u2019s environmental pressures: a review and updated estimates on CO<sub>2<\/sub>\u00a0emissions, water use, and land requirements. In: Sustainability 10(8), pp 2881.<\/p>\n<p>(4) EEA (1999): Environmental indicators: typology and overview. Technical Report No. 25, 19 pp.<\/p>\n<p>(5) Lottermoser, B. G. (2017): Environmental Indicators in Metal Mining. Springer Nature, Springer International Publishing \u00adSwitzerland, 413 pp.<\/p>\n<p>(6) Lottermoser, B. G. (2010): Mine Wastes: Characterization, Treatment and Environmental Impacts. 3rd edition. Springer-Verlag, Berlin Heidelberg, 400 pp.<\/p>\n<p>(7) Statistisches Bundesamt (Destatis) (2022): Fl\u00e4chennutzung \u2212 Bodenfl\u00e4che insgesamt nach Nutzungsarten in Deutschland am 31.12.2021. 1 S.<\/p>\n<p>(8) BGR (2022): Deutschland \u2212 Rohstoffsituation 2021. 162 S.<\/p>\n<p>(9) Statistisches Bundesamt (Destatis) (2022): Umwelt\u00f6konomische Gesamtrechnungen. Anthropogene Luftemissionen. Berichtszeitraum 2000 \u2212 2020. 65 S.<\/p>\n<p>(10) Umweltbundesamt (2022): Zum Jahreswechsel: Wenn die Luft \u201ezum Schneiden\u201c ist. Hintergrund \/\/ November 2022. 16 S.<\/p>\n<p>(11) Freer, J.; L\u00fcbeck, M.; Sieger, J.; Lottermoser, B.G.; Braun,\u00a0M. (2022): Effectiveness of food processing by-products as dust suppressants for exposed mine soils: results from \u00adlaboratory experiments and field trials. In: Applied Sciences 12(22), pp\u00a011551.<\/p>\n<p>(12) Sieger, J.; Lottermoser, B. G.; Freer, J. (2023): Effectiveness of protein and polysaccharide biopolymers as dust suppressants on mine soils: results from wind tunnel and penetrometer testing. In: Applied Sciences 13(7), pp 4158.<\/p>\n<p>(13) Technische Anleitung zum Schutz gegen L\u00e4rm (TA L\u00e4rm) (2017): www.verwaltungsvorschriften-im-internet.de\/bsvwvbund_26081998_IG19980826.htm<\/p>\n<p>(14) Bezirksregierung Arnsberg (2023): Messwerte der L\u00e4rmmessungen im Rheinischen Braunkohlenrevier. <a href=\"https:\/\/www.bra.nrw.de\/energie-bergbau\/umweltschutz-im-bergbau\/laermmessungen-im-rheinischen-braunkohlenrevier\" target=\"_blank\" rel=\"noopener\">www.bra.nrw.de\/energie-bergbau\/umweltschutz-im-bergbau\/laermmessungen-im-rheinischen-braunkohlenrevier<\/a><\/p>\n<p>(15) BMDV (2022): L\u00e4rmschutz im Schienenverkehr. 282 pp.<\/p>\n<p>(16) Statistisches Bundesamt (Destatis) (2022): Umwelt \u2212 Abfallbilanz. (Abfallaufkommen\/-verbleib, Abfallintensit\u00e4t, Abfallaufkommen nach Wirtschaftszweigen). 82 S.<\/p>\n<p>(17) Statistisches Bundesamt (Destatis) (2023): Wasserwirtschaft \u2212 Eigengewinnung und Fremdbezug von Wasser sowie Einleitung von Abwasser und ungenutztem Wasser. 1 S.<\/p>\n<p>(18) IGB (2022): Die Zukunft der Oder. Forschungsbasierte Handlungsempfehlungen nach der menschengemachten Umwelt\u00adkatastrophe. IGB Policy Brief, Leibniz-Institut f\u00fcr Gew\u00e4sser\u00ad\u00f6kologie und Binnenfischerei, Berlin, 9 S.<\/p>\n<p>(19) Knobloch, M; Palmer, L. W.; Roethe, R. G.; Lottermoser, B.\u00a0G. (2022): Infrared thermographic investigation of the oxidation behaviour of sulfide minerals from antimony-bearing rocks exemplified by the Podkozara deposit, Bosnia-Herzegovina. In:\u00a0Applied Geochemistry 137, pp 105181.<\/p>\n<p>(20) Schlatter, N.; Lottermoser, B. G. (2023): Quantitative analysis of Li, Na, and K in single element standard solutions using portable laser-induced breakdown spectroscopy (pLIBS). In: Geochemistry: Exploration, Environment, Analysis <a href=\"https:\/\/doi.org\/10.1144\/geochem2023-019\" target=\"_blank\" rel=\"noopener\">https:\/\/doi.org\/10.1144\/geochem2023-019<\/a><\/p>\n<p>(21) Leopoldina \u2212 Nationale Akademie der Wissenschaften, \u00adacatech\u00a0\u2212 Deutsche Akademie der Technikwissenschaften, Union der deutschen Akademien der Wissenschaften (2020): Biodiversit\u00e4t und Management von Agrarlandschaften \u2212 \u00adUmfassendes Handeln ist jetzt wichtig. Halle (Saale) 80 S.<\/p>\n<p>(22) Cabernard, L.; Pfister, S. (2022): Hotspots of mining-related biodiversity loss in global supply chains and the potential for reduction through renewable electricity. In: Environmental \u00adScience &amp; Technology 56(22), pp 16357\u2009\u2212\u200916368.<\/p>\n<p>(23) BGR (2017): Heimische mineralische Rohstoffe \u2212 unverzichtbar f\u00fcr Deutschland. 84 S.<\/p>\n<p>(24) Bayerisches Landesamt f\u00fcr Umwelt (2023): Uhu \u2212 Bestand und Gef\u00e4hrdung. <a href=\"https:\/\/www.lfu.bayern.de\/natur\/artenhilfsprogramme_voegel\/uhu\/bestand_gefaehrdung\/index.htm\" target=\"_blank\" rel=\"noopener\">https:\/\/www.lfu.bayern.de\/natur\/artenhilfsprogramme_voegel\/uhu\/bestand_gefaehrdung\/index.htm<\/a><\/p>\n<p>(25) Schumacher, H.; Finck, P.; Riecken, U.; Klein, M. (2018): More wilderness for Germany: Implementing an important objective of Germany\u2019s National Strategy on Biological Diversity. In: Journal for Nature Conservation 42, pp 45\u2009\u2212\u200952.<\/p>\n<p>(26) Umweltbundesamt (2015): Durch Umweltschutz die biologische Vielfalt erhalten. 100 S.<\/p>\n<p>(27) Trouwborst, A.; McCormack P. C.; Camacho E. M. (2022): \u00adDomestic cats and their impacts on biodiversity: A blind spot in the application of nature conservation law. In: People and Nature 2, pp 235\u2009\u2212\u2009250.<\/p>\n<p>(28) DJV (2020): Freilaufende Katzen bedrohen die weltweite Artenvielfalt. <a href=\"https:\/\/www.jagdverband.de\/freilaufende-katzen-bedrohen-die-weltweite-artenvielfalt\" target=\"_blank\" rel=\"noopener\">https:\/\/www.jagdverband.de\/freilaufende-katzen-bedrohen-die-weltweite-artenvielfalt<\/a><\/p>\n<p>(29) BMWi (2019): Rohstoffstrategie der Bundesregierung \u2212 \u00adSicherung einer nachhaltigen Rohstoffversorgung Deutschlands mit nichtenergetischen mineralischen Rohstoffen. 40 S.<\/p>\n<p>(30) Bundesregierung (2021): Mehr Fortschritt wagen. B\u00fcndnis f\u00fcr Freiheit, Gerechtigkeit und Nachhaltigkeit. Koalitionsvertrag zwischen SPD, B\u00fcndnis 90\/Die Gr\u00fcnen und FDP, 178 S.<\/p>\n<p>(31) BMWK (2023) Eckpunktepapier: Wege zu einer nachhaltigen und resilienten Rohstoffversorgung. 10 S.<\/p>\n<p>(32) Statistisches Bundesamt (Destatis) (2022): Umwelt. Investi\u00adtionen f\u00fcr den Umweltschutz im produzierenden Gewerbe. 71 S.<\/p>\n\n\t\t\t<\/div>\n\t\t<\/div>\n\t\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n\n\t\t<div class=\"one_third tie-columns\"><a href=\"\/wp-content\/uploads\/_pda\/2023\/08\/MRG_2304_Umweltbelastungen_Bergbau_Lottermoser_230816.pdf\" target=\"_blank\" class=\"shortc-button small white\">Download article as PDF<\/a>\n\t\t<\/div>\n\t\n\n\t\t<div class=\"two_third tie-columns last\"><strong>Author\/Autor:\u00a0<\/strong>Univ.-Prof. PhD Bernd G. Lottermoser, Lehrstuhl f\u00fcr nachhaltige Rohstoffgewinnung, Institute of Mineral Resources Engineering (MRE), RWTH Aachen University (RWTH), Aachen\/Germany \n\t\t<\/div>\n\t\t<div class=\"clearfix\"><\/div>\n\t\n\n\t\t<div class=\"clearfix\"><\/div>\n\t\t<hr style=\"margin-top:10px; margin-bottom:10px;\" class=\"divider divider-normal\">\n\t\n","protected":false},"excerpt":{"rendered":"<p>Mines interfere with the environment. However, active mining in Germany in its various forms causes only small overall environmental pressures, based on data from the Federal Statistical Office of Germany, &hellip;<\/p>\n","protected":false},"author":25,"featured_media":0,"parent":0,"menu_order":0,"comment_status":"closed","ping_status":"closed","template":"","meta":{"footnotes":""},"categories":[948,315],"tags":[],"class_list":["post-16563","page","type-page","status-publish","hentry","category-fachartikel-04_2023","category-open-access"],"yoast_head":"<!-- This site is optimized with the Yoast SEO plugin v28.2 - https:\/\/yoast.com\/product\/yoast-seo-wordpress\/ -->\n<title>Environmental Pressures of Current Mining in Germany: a Critical Comment - MINING REPORT<\/title>\n<meta name=\"robots\" content=\"index, follow, max-snippet:-1, max-image-preview:large, max-video-preview:-1\" \/>\n<link rel=\"canonical\" href=\"https:\/\/mining-report.de\/english\/environmental-pressures-of-current-mining-in-germany-a-critical-comment\/\" \/>\n<meta property=\"og:locale\" content=\"en_US\" \/>\n<meta property=\"og:type\" content=\"article\" \/>\n<meta property=\"og:title\" content=\"Environmental Pressures of Current Mining in Germany: a Critical Comment - MINING REPORT\" \/>\n<meta property=\"og:description\" content=\"Mines interfere with the environment. 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