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 U6 - 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 - TY - CHAP A1 - Lübben, S. A1 - Enzner, V. A1 - Holm, Olaf ED - Thiel, S. ED - Thome-Kozmiensky, E. ED - Friedrich, B. ED - Pretz, T. ED - Quicker, P. ED - Senk, D. G. ED - Wotruba, H. T1 - Aufbereitung von Teilströmen der Abfallverbrennungsasche zu hochwertigen Zuschlagstoffen und deren Einsatz als Recyclingprodukte in der Baustoffindustrie T1 - Treatment of Separated Mass Fractions of Waste Incineration Bottom Ashes for the Use as Secondary Construction Material N2 - In the framework of the project OPTIMIN a fractionation of BA in different grain size distributions with an integrated washing step has been carried out. Due to further treatment and measurements of the resulting three fractions 0–0.2 mm, 0.2–2 mm and 2–25 mm, the possible application in asphalt, concrete or cement has been investigated. One option could be the use of fresh BA which has been treated prior to the ageing processes. The preliminary results show the shifting of pollutants to the fine fraction but also components responsible for the ageing processes. Parts of the fine fraction hold the limit values for the cement plant of the project partner. On the other hand, the Contents of copper and zinc exceed the standard values for the process. The coarser fractions are free from mineral coatings and are not agglomerated in the case of the use of fresh BA. A following industrial separation step of glass has been successful. From the physical point of view an application in asphalt or concrete for the coarser fractions seems to be feasible. However, in leaching experiments a high release of different metals, especially copper, could be detected. This is probably due to the poorly conceived washing process but needs to be further investigated. N2 - Im Rahmen des Projekts OPTIMIN wurde eine Fraktionierung von Rostasche in verschiedene Korngrößenverteilungen mit integriertem Waschschritt durchgeführt. Aufgrund der weiteren Behandlung und Analyse der resultierenden drei Fraktionen 0–0,2 mm, 0,2–2 mm und 2–25 mm wurde die mögliche Verwertung in Asphalt, Beton oder Zement untersucht. Eine Option könnte die Verwendung von frischer Rostasche sein, die vor dem Einsetzen von Alterungsprozessen behandelt wird. Die vorläufigen Ergebnisse zeigen die Verlagerung von Schadstoffen in die Feinfraktion, aber auch von Anteilen, die für die Alterungsprozesse verantwortlich sind. Teile der Feinfraktion halten die Grenzwerte für das Zementwerk des Projektpartners ein. Andererseits übersteigen die Gehalte an Kupfer und Zink die Vorgabewerte für den Prozess. Die gröberen Fraktionen sind frei von mineralischen Anhaftungen und agglomerieren bei der Verwendung von frischer Rostasche nicht. Die nachfolgende Abtrennung von Glas war erfolgreich. Aus bauphysikalischer Sicht erscheint eine Anwendung in Asphalt oder Beton für die gröberen Fraktionen möglich. In Auslaugtests konnte jedoch eine hohe Freisetzung verschiedener Metalle, insbesondere Kupfer, nachgewiesen werden. Dies ist wahrscheinlich auf den schlecht konzipierten Waschprozess zurückzuführen, muss jedoch weiter untersucht werden. KW - Ersatzbaustoffe KW - Rostasche PY - 2018 SN - 978-3-944310-41-1 VL - 5 SP - 152 EP - 172 PB - TK Verlag CY - Neuruppin ET - 1 AN - OPUS4-46618 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 -