TY - CONF A1 - Simon, Franz-Georg T1 - Rückgewinnung von Aluminium aus Abfällen N2 - Abtrennung von Nichteisenmetallen aus Müllverbrennungsaschen T2 - IFAT, Messe für Wasser-, Abwasser-, Abfall- und Rohstoffwirtschaft CY - München, Germany DA - 16.05.2018 KW - Rostasche KW - Kumulierter Energieaufwand KW - Sekundärrohstoffe PY - 2018 AN - OPUS4-44939 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - GEN A1 - Abis, M. A1 - Bruno, M. A1 - Simon, Franz-Georg A1 - Grönhom, R. A1 - Kuchta, K. A1 - Fiore, S. ED - Medici, F. T1 - A Novel Dry Treatment for Municipal Solid Waste Incineration Bottom Ash for the Reduction of Salts and Potential Toxic Elements N2 - The main obstacle to bottom ash (BA) being used as a recycling aggregate is the content of salts and potential toxic elements (PTEs), concentrated in a layer that coats BA particles. This work presents a dry treatment for the removal of salts and PTEs from BA particles. Two pilotscale abrasion units (with/without the removal of the fine particles) were fed with different BA samples. The performance of the abrasion tests was assessed through the analyses of particle size and moisture, and that of the column leaching tests at solid-to-liquid ratios between 0.3 and 4. The results were: the particle-size distribution of the treated materials was homogeneous (25 wt % had dimensions <6.3 mm) and their moisture halved, as well as the electrical conductivity of the leachates. A significant decrease was observed in the leachates of the treated BA for sulphates (44%), chlorides (26%), and PTEs (53% Cr, 60% Cu and 8% Mo). The statistical analysis revealed good correlations between chloride and sulphate concentrations in the leachates with Ba, Cu, Mo, and Sr, illustrating the consistent behavior of the major and minor components of the layer surrounding BA particles. In conclusion, the tested process could be considered as promising for the improvement of BA valorization. KW - Bottom ash KW - Dry treatment KW - Municipal solid waste PY - 2022 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-552161 SN - 978-3-0365-3063-5 DO - https://doi.org/10.3390/ma14113133 SP - 57 EP - 71 PB - MDPI CY - Basel AN - OPUS4-55216 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - GEN A1 - Simon, Franz-Georg A1 - Scholz, Philipp A1 - Gleis, Markus ED - Thiel, Stephanie ED - Thome-Kozminesky, Elisabeth ED - Quicker, Pater ED - Gosten, Alexander ED - Stengler, Ella T1 - Einstufung von Aschen und Schlacken aus der Abfallverbrennung im Hinblick auf die weitere Verwertung N2 - There are two mirror entries in the European Waste Catalogue for bottom ash and slag from waste incineration: 19 01 11* and 19 01 12. Entry 19 01 11* describes a waste material containing hazardous substances. It was shown that only the hazardous property HP14 (ecotoxic) is of relevance for the classification. If substances with the hazard statement code (HSC) H400, H410, H411, H412 and H413 are present in incineration bottom ash (IBA) above certain level the waste is classified as hazardous, otherwise it is non-hazardous (in this case 19 01 12). It was further shown that only Cu, Zn and Pb compounds have an impact on the classification using a summation rule: 100xΣ c(H410) + 10xΣ c(H411) + Σ c(H412). Limit value is 25 percent. It is obvious that H410 substances have the highest impact. Therefore, the knowledge of the elemental composition of IBA is not sufficient because the content of distinct chemical compounds (with the respective molecular weight) is needed. When the exact speciation is not known a worst-case approach has to be applied. A practical guideline for the estimation of HP14 was developed based on the definition of 4 substance groups: 1. Metals and alloys, 2. Water-soluble substances, 3. Oxides and carbonates and 4. Substances not soluble in weak acids. In substance group 1 only fine Zn powder has the HSC H410. Water-soluble substances are assumed to be H410 substances. Their concentrations are, however, regularly below the cut-off value of 0.1 %. The amount of substance group 3 is estimated by a selective extraction with maleic acid. According to the worst-case approach it is assumed that CuCO3xCu(OH)2 and ZnO represent the respective Cu and Zn species in IBA because these substances have the highest stochiometric factor. Even with this worst-case approach results from operators of IBA treatment plant showed that the limit value of 25 % is not exceeded. The requirements for utilization of IBA in Germany are defined in the Secondary Building Materials Decree (Ersatzbaustoffverordnung EBV) which was set into force in August 2023. Leaching methods (batch test or column test) with a liquid-to-solid ratio of 2 l/kg are applied. IBA fulfills the requirements for class HMVA-2. Actually, even a classification of IBA as hazardous (i.e 19 01 11*) would not affect utilization but handling and transport. KW - Rostasche KW - Ökotoxizität KW - Ersatzbaustoffverordnung KW - XANES-Spektroskopie PY - 2024 SN - 978-3-944310-90-9 VL - 1 SP - 402 EP - 414 PB - TK-Verlag CY - Neuruppin ET - 1 AN - OPUS4-59465 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CHAP A1 - Syc, M. A1 - Simon, Franz-Georg A1 - Biganzoli, L. A1 - Grosso, M. A1 - Hyks, J. ED - Holm, O. ED - Thome-Kozmiensky, E. T1 - Resource recovery from incineration bottom ash: Basics, concepts, principles N2 - Waste-to-energy (WtE) is one of the leading technologies for municipal solid waste (MSW) treatment in Europe. According to Eurostat data, in 2015, 27 % of MSW was utilized in WtE plants, which represents more than 80 million tons per year. Therefore, the European annual production of incineration bottom ash (IBA) is about 20 million tons, as it is about 25 wt% of input MSW. In the European List of Waste, IBA is listed as mirror entry (i.e. waste materials which should be classified as either non-hazardous or hazardous, depending on its hazardous properties and/or content of hazardous substances) under codes 19 01 11 and 19 01 12. Recent trends indicate that WtE allows, apart from utilization of the energy content of waste, also the recovery of various valuable components. Hence, WtE can be included in the key technologies that can put the circular economy concept into practice. Secondary raw materials in the case of WtE are solid residues, especially IBA, as it is a secondary source, particularly of ferrous metals (Fe) and non-ferrous metals (NF) and glass. Moreover, the residual mineral fraction can be used for various applications in the construction industry, i.e. as aggregates substitute for bound or unbound applications, in cement manufacturing or, as indicated by recent research, also in more sophisticated applications, e.g. for ceramics production. Recovery of these metals can also cause huge greenhouse gas savings. Alone in Europe, metal recovery from IBA reduces greenhouse gas emissions by approximately 3.2 million tonnes of CO2 equivalent. KW - Bottom ash KW - Recovery PY - 2018 SN - 978-3-944310-44-2 VL - 1 SP - 1 EP - 10 PB - Thomé-Kozmiensky Verlag GmbH CY - Neuruppin ET - 1 AN - OPUS4-46146 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - GEN ED - Simon, Franz-Georg ED - Kalbe, Ute T1 - Measurement of the Environmental Impact of Materials N2 - Throughout their life cycles—from production, usage, through to disposal—materials and products interact with the environment (water, soil, and air). At the same time, they are exposed to environmental influences and, through their emissions, have an impact on the environment, people, and health. Accelerated experimental testing processes can be used to predict the long-term environmental consequences of innovative products before these actually enter the environment. We are living in a material world. Building materials, geosynthetics, wooden toys, soil, nanomaterials, composites, wastes and more are research subjects examined by the authors of this book. The interactions of materials with the environment are manifold. Therefore, it is important to assess the environmental impact of these interactions. Some answers to how this task can be achieved are given in this Special Issue. KW - Leaching KW - Recycling KW - Emissions PY - 2023 UR - https://www.mdpi.com/books/book/6546 SN - 978-3-0365-5983-4 SN - 978-3-0365-5984-1 DO - https://doi.org/10.3390/books978-3-0365-5983-4 SP - 1 EP - 264 PB - MDPI CY - Basel ET - 1 AN - OPUS4-56770 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Simon, Franz-Georg A1 - Scholz, Philipp A1 - Ling, Ruisi A1 - Koralewska, Ralf A1 - Gleis, Markus T1 - Aschen und Schlacken aus der Abfallverbrennung im Lichte der Ersatzbaustoffverordnung N2 - Aschen und Schlacken aus der thermischen Abfallbehandlung stellen mit rund 25% Massenanteil die größte Reststofffraktion dar. In Deutschland fallen pro Jahr rund 6 Millionen Tonnen an. Während sich die Verwertung der metallischen Anteile problemlos gestaltet, werden an die mineralische Fraktion Anforderungen bezüglich der möglichen Freisetzung von Schwermetallen sowie Chlorid und Sulfat gestellt. In der Ersatzbaustoffverordnung sind für Aschen und Schlacken aus der Abfallverbrennung zwei Materialklassen mit unterschiedlich hohen Anforderungen an die Umweltverträglichkeit definiert. Im Rahmen eines Forschungsprojekts wurde untersucht, ob mit Abtrennung der Feinfraktion von 0–2mm die höhere Materialklasse HMVA-1 erreicht werden kann. Im Ergebnis wurde eine Verbesserung des Auslaugverhaltens erzielt, doch nicht in dem Maß, dass eine Qualität nach HMVA-1 erreicht wird. Rostaschen halten aber die Anforderungen zur Deponierung auf einer DK I-Deponie sowie die Anforderungen zur Verwertung gemäß HMVA-2 sicher ein. KW - Rostasche KW - Auslaugtest KW - Ersatzbaustoff PY - 2024 DO - https://doi.org/10.37307/j.1863-9763.2024.07.08 SN - 1863-9763 VL - 56 IS - 7 SP - 407 EP - 411 PB - Erich Schmidt Verlag GmbH & Co. KG CY - Berlin AN - OPUS4-60601 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - GOVDOC A1 - Simon, Franz-Georg A1 - Wöhlecke, Andreas T1 - 8. Nachtrag zum Zulassungsschein 12/BAM IV.3/09/00 für eine Schutzschicht bestehend aus einer sandgefüllten Schutzbahn für Kunststoffdichtungsbahnen in Deponieabdichtungen N2 - 8. Nachtrag zum Zulassungsschein 12/BAM IV.3/09/00 für eine Schutzschicht bestehend aus einer sandgefüllten Schutzbahn für Kunststoffdichtungsbahnen in Deponieabdichtungen der Fa. G quadrat GmbH, Krefeld. KW - Zulassung KW - Deponie KW - Schutzschicht KW - Kunststoffdichtungsbahn PY - 2024 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-604877 SP - 1 EP - 29 PB - Bundesanstalt für Materialforschung und -prüfung (BAM) CY - Berlin AN - OPUS4-60487 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - RPRT A1 - Holm, Olaf T1 - ATR Aufschluss, Trennung und Rückgewinnung von ressourcenrelevanten Metallen aus Rückständen thermischer Prozesse mit innovativen Verfahren N2 - Ziel des Vorhabens war die Steigerung der Rückgewinnung von Metallen aus Aschen und Schlacken durch Aufschluss aus den mineralischen Verbunden. Durch das innovative Prallzerkleinerungsverfahren (Hochgeschwindigkeits-Rotations-Beschleuniger) des Projektpartners TARTECH, sollten die Verunreinigungen an den metallischen Anteilen praktisch vollständig abgeschlagen werden. Diese Aufbereitungstechnik sollte im Rahmen des Projektes so verfeinert und angepasst werden, dass metallische Partikel von 0,5 bis 5 mm aufgeschlossen werden, damit sie anschließend über Wirbelstromscheider in elementarer Form abgetrennt werden können. KW - Rostasche KW - Prallzerkleinerungsverfahren KW - Aufbereitungstechnik PY - 2021 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-521571 UR - https://edocs.tib.eu/files/e01fb21/1748479865.pdf DO - https://doi.org/10.2314/KXP:1748479865 SP - 1 EP - 516 AN - OPUS4-52157 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - RPRT A1 - Simon, Franz-Georg A1 - Scholz, Philipp A1 - Barqawi, Haitham T1 - Einfluss von Geokunststoffen auf die aquatische Umwelt N2 - Im Rahmen des Projekts konnte gezeigt werden, dass Geokunststoffe bei ausreichender Stabilisierung Einsatzdauern von über 100 Jahren besitzen. Es werden keine Stoffe freigesetzt, die für Wasserorganismen schädlich sind. An den Ostseestränden im Gebiet Kaliningrad werden nennenswerte Mengen von Kunststoffresten gefunden, die zum Teil aus Küstenschutzbauwerken stammen. Ursache ist hier jedoch eine verfehlte Materialauswahl. Hauptsächlich stammen die Kunststoffreste am Strand jedoch aus unsachgemäße Abfallbehandlung. KW - Geokunststoffe KW - Mikroplastik KW - Autoklaventest KW - Ökotoxtests PY - 2022 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-556431 DO - https://doi.org/10.2314/KXP:1813230285 SP - 1 EP - 15 AN - OPUS4-55643 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CHAP A1 - Wünsch, Christoph A1 - Simon, Franz-Georg ED - Maletz, Roman ED - Dornack, Christina ED - Ziyang, Lou T1 - The reduction of greenhouse gas emissions through the source-separated collection of household waste in Germany N2 - The production of secondary materials from waste materials requires, in most cases, significantly lower energy amounts than the primary material production of raw materials. Along with lower energy demand, the greenhouse gas emissions produced are also lower. The duty of a modern waste management system should therefore be to collect and sort the waste materials in a way that the highest amounts of single material fractions with the highest qualities can be generated. In this contribution, the greenhouse gas balances of the theoretical treatment of the household waste, if collected as mixed waste in sanitary landfills, in waste incineration plants, or in mechanical-biological treatment plants, are compared to the existing separate waste collection and treatment in Germany in 2014. The results show that the treatment of the mixed collected household waste in sanitary landfills would lead to a significant release of greenhouse gases. The treatment in MBTs with the recovery of valuables and the further disposal of the biologically stabilized fraction on landfills, as well as the treatment of the high calorific fraction (also called refuse derived fuel – RDF) in RDF plants, coal-fired power plants, or cement kilns, would lead to small amounts of avoided greenhouse gas emissions. The thermal treatment in waste incineration plants would lead to moderate amounts of avoided greenhouse gases. Only with the actually practiced separate collection and treatment of household waste were significant amounts of greenhouse gas emissions avoided. In total, this is approximately 5.5 million tons of carbon dioxide equivalents for approximately 45.5 million tons of separate collected and treated household waste in Germany in 2014. KW - Greenhouse gas accounting KW - Greenhouse gas mitigation KW - Household waste KW - Material recycling KW - Separate collection PY - 2018 SN - 978-3-319-69071-1 DO - https://doi.org/10.1007/698_2017_35 VL - 63 SP - 269 EP - 287 PB - Springer International Publishing CY - Berlin ET - 1 AN - OPUS4-44937 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER -