TY - CONF A1 - Simon, Franz-Georg T1 - Economic and legal aspects of secondary resource management N2 - Direct and indirect effects (DIERec) of the recovery of secondary resources are in the range of 500 million tonnes per year in Germany; energy savings are 1.4 million TJ. These savings are between 10 and 20% of the total. The effects of materials recovery exceed those of energy recovery by far with the exception of secondary plastic material where DIERec from energy recovery is higher by factor of 2.7. Untapped potential for the recovery of secondary resources exist in the fine fraction of bottom ash from municipal solid waste incineration, mainly Cu and precious metals and in urban mining. T2 - Travelling Conference Resource efficiency and environmental compatibility in waste management (REECO-WM) CY - Seoul, Ho-Chi-Minh-City, Perth DA - 29.01.2018 KW - Waste management KW - Materials flow KW - Secondary resources PY - 2018 AN - OPUS4-44942 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CONF A1 - Simon, Franz-Georg A1 - Barqawi, Haitham A1 - Chubarenko, B. A1 - Esiukova, E. A1 - Putna-Nimane, I. A1 - Barda, I. A1 - Strode, E. A1 - Purina, I. ED - Köppen, S. ED - Reckermann, M. T1 - EI‐GEO environmental impact of geosynthetics in aquatic systems N2 - EI‐GEO is a multinational research project (Germany, Latvia, Russia) funded under the ERA.Net RUS Plus Call 2017. Aim of the project is the investigation whether geosynthetics in hydraulic engineering applications could be a source of microplastics (MPs) and other contaminants to the aquatic environment causing negative effects to aquatic organisms. Whereas the behavior of geosynthetics in landfill engineering is well studied and documented since decades, little is known on application in applications such as coastal protection or ballast layers for wind energy plants. However, due to the rapid expansion of offshore wind energy, rising water levels and more extreme weather conditions as a result of climate change more and more hydraulic engineering projects will be realized in the future. Applied methods are artificial ageing of geosynthetics in environmental simulation chambers, storage of samples under environmental condition for comparison with laboratory simulation, sample characterization by microscopic methods and ecotoxicological testing of water in contact with geosynthetics. In parallel a case study at the Baltic Sea shore at Kaliningrad Oblast (Russia) will be performed. The aim of study is to estimate the level of pollution of the beaches by geosynthetic debris and identify the possible sources. T2 - 3rd Baltic Earth Conference CY - Online meeting DA - 02.06.2020 KW - Geosynthetics KW - Micro plastic KW - Hydraulic engineering PY - 2020 UR - https://www.baltic-earth.eu/hel2020/material/3rd_BalticEarth_Conference_Proceedings.pdf SN - 2198-4247 SP - 151 EP - 152 PB - International Baltic Earth Secretariat Publications CY - Geesthacht AN - OPUS4-50881 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CHAP A1 - Simon, Franz-Georg A1 - Meggyes, Tamas ED - Meyers, Robert A. T1 - Sustainable remediation methods for metals and radionuclides N2 - Since it was realized that sites contaminated with metals and radionuclides needed treatment, various remediation methods have been and are being developed. Depending on the size of the contaminated site and urgency of intervention, conventional or recently introduced techniques have been used. Conventional techniques include excavation and removal for treatment of soil and contaminants, or the so-called “pump-and-treat” method, in which contaminated groundwater is removed from the ground by pumping and treated in a treatment plant on the surface. It has the advantage of using proven techniques and is easy to control, and the treated groundwater can be reinjected into the ground or discharged in rivers or lakes. Novel methods include permeable reactive barriers, biomineralization, and electrokinetic remediation. KW - Permeable reactive barriers KW - Groundwater KW - Uranium PY - 2019 SN - 978-1-4939-2493-6 U6 - https://doi.org/10.1007/978-1-4939-2493-6_63-3 SP - 1 EP - 37 PB - Springer Science+Business Media, LLC CY - Heidelberg ET - 1 AN - OPUS4-48816 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CONF A1 - Kalbe, Ute A1 - Vogel, Christian A1 - Simon, Franz-Georg T1 - Antimony in incineration bottom ash – Leaching behavior and conclusions for treatment processes N2 - Antimony (Sb) is used in industrial products mainly as flame retardant in plastic material. Due to such additives in plastics, about a half of Sb ends up in municipal solid waste incineration at the end-of-life and consequently in relevant amounts in the generated bottom ash. In contact with water, the initial leachability is low, as antimonates form sparingly soluble compounds with Ca2+. Following the carbonation of the incineration bottom ash (IBA) during the proceeding ageing the pH in the leachates decreases. With decreasing concentration of Ca in the eluate the solution equilibrium changes and antimonates dissolve. In Germany it is intended to regulate Sb in IBA with the planned implementation of the so called Mantelverordnung (MantelVO, containing provisions on the utilisation of mineral waste) in the near future. The limit values set in the draft might be critical for IBA and therefore pose a risk for the utilisation of the mineral fraction of IBA in the well-established recycling routes. T2 - SUM 2020 – 5th Symposium on Urban Mining and Circular Economy CY - Online meeting DA - 18.11.2020 KW - Bottom ash KW - Leaching KW - Antimony PY - 2020 SP - 1 EP - 4 AN - OPUS4-51622 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CHAP A1 - Simon, Franz-Georg A1 - Quicker, P. ED - Elvers, B. T1 - Waste, Evaluation Methods N2 - It is difficult to decide which waste management system fulfills best predefined sustainability goals such as maximum materials and energy recovery, least environmental impact, and lowest societal cost. Such decisions are based on many parameters. However, several evaluation methods exist with different scope and output, and the application of one or more evaluation methods provides an objective comparison of alternatives. KW - Waste treatment KW - Exergy KW - Lfe cycle assessment KW - Eco-efficiency analysis PY - 2019 UR - https://onlinelibrary.wiley.com/doi/abs/10.1002/14356007.o28_o02.pub2 SN - 978-3-52730-673-2 U6 - https://doi.org/10.1002/14356007.o28_o02.pub2 SP - 1 EP - 10 PB - Wiley-VCH Verlag CY - Weinheim ET - 1. AN - OPUS4-49715 LA - eng 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 - CHAP A1 - Simon, Franz-Georg A1 - Meggyes, Tamas ED - Zhang, H. X. T1 - Sustainable Remediation Methods for Metals and Radionuclides N2 - Sustainability has become the conscientious and future-oriented principle of modern resource management and environmental protection because caring for the future is tantamount to providing manageable and healthy surroundings for ourselves. For the foreseeable future, geotechnical and environmental engineers must therefore be concerned with ensuring a healthy balance between extraction, processing, manufacturing, utilization, recycling, and disposal of materials and products. KW - Permeable reactive barriers KW - Uranium mining KW - Groundwater KW - Electrochemical remediation PY - 2023 SN - 978-1-0716-2465-4 U6 - https://doi.org/10.1007/978-1-0716-2466-1_63 SN - 2629-2378 SP - 251 EP - 284 PB - Springer Science+Business Media CY - Berlin, Heidelberg ET - 1 AN - OPUS4-58018 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Simon, Franz-Georg A1 - Haas, Marco A1 - Pienkoß, Fabian A1 - Kwiatkowski, Robert T1 - Wet-mechanical treatment: Processing of bituminous road construction waste in a jigging machine N2 - Jigging machines are used in processing technology in many areas. Examples are the processing of coal, ores, and primary and secondary raw and waste materials. Even small differences in density are offen sufficient for successful sorting. In the work presented here, milled material from road construction waste contaminated with bitumen is to be separated from uncontaminated material. In this way, scarce landfill space could be saved and mineral material be returned to the material cycle. KW - Wet-mechanical treatment KW - Jig KW - Road construction waste PY - 2023 UR - https://www.at-minerals.com/de/artikel/aufbereitung-von-bitumenhaltigem-strassenaufbruch-in-einer-setzmaschine-4037512.html SN - 1434-9302 VL - 64 IS - 12 SP - 46 EP - 51 PB - Bauverlag BV GmbH CY - Gütersloh AN - OPUS4-59160 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CONF A1 - Simon, Franz-Georg T1 - Secondary building materials in a circular economy N2 - Half of the global material consumption is mineral material. The circularity is still low so that enhanced use of secondary building material is required to close loops. Three different secondary building materials are discussed based on exemplary research results: construction and demolition waste (C&D waste), soil-like material and incineration bottom ash (IBA). Focus was laid on the environmental compatibility of the materials examined mainly by standardized leaching tests. C&D waste was investigated after a wet treatment using a jigging machine, soil-like material and IBA were characterized with respect to their material composition. The environmental compatibility in particular was studied using standard leaching tests (batch tests and column tests). It was concluded that soil-like material can mostly be utilized even when the precautionary limit values set are exceeded by a factor of less than 2. For C&D waste the fine fraction below 2 mm and the content of brick material is problematic. IBA fulfills quality level HMVA-2 following German regulation. Higher quality levels of utilization might be achievable with better treatment technologies. T2 - 15th International Conference on Ecomaterials (ICEM15) CY - Iki, Japan DA - 26.11.2023 KW - Secondary building materials KW - Incineration bottom ash KW - Construction and demolition waste KW - Soil-like material PY - 2023 AN - OPUS4-59186 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER -