TY - JOUR A1 - Rieger, J. A1 - Colla, V. A1 - Matino, I. A1 - Branca, T. A. A1 - Stubbe, G. A1 - Panizza, A. A1 - Brondi, C. A1 - Falsafi, M. A1 - Hage, J. A1 - Wang, X. A1 - Voraberger, B. A1 - Fenzl, T. A1 - Masaguer, V. A1 - Faraci, E. L. A1 - di Sante, L. A1 - Cirilli, F. A1 - Loose, Florian A1 - Thaler, C. A1 - Soto, A. A1 - Frittella, P. A1 - Foglio, G. A1 - di Cecca, C. A1 - Tellaroli, M. A1 - Corbella, M. A1 - Guzzon, M. A1 - Malfa, E. A1 - Morillon, A. A1 - Algermissen, D. A1 - Peters, K. A1 - Snaet, D. T1 - Residue Valorization in the Iron and Steel Industries: Sustainable Solutions for a Cleaner and More Competitive Future Europe JF - Metals N2 - The steel industry is an important engine for sustainable growth, added value, and high-quality employment within the European Union. It is committed to reducing its CO2 emissions due to production by up to 50% by 2030 compared to 1990′s level by developing and upscaling the technologies required to contribute to European initiatives, such as the Circular Economy Action Plan (CEAP) and the European Green Deal (EGD). The Clean Steel Partnership (CSP, a public–private partnership), which is led by the European Steel Association (EUROFER) and the European Steel Technology Platform (ESTEP), defined technological CO2 mitigation pathways comprising carbon direct avoidance (CDA), smart carbon usage SCU), and a circular economy (CE). CE ap-proaches ensure competitiveness through increased resource efficiency and sustainability and consist of different issues, such as the valorization of steelmaking residues (dusts, slags, sludge) for internal recycling in the steelmaking process, enhanced steel recycling (scrap use), the use of secondary carbon carriers from non-steel sectors as a reducing agent and energy source in the steelmaking process chain, and CE business models (supply chain analyses). The current paper gives an overview of different technological CE approaches as obtained in a dedicated workshop called “Resi4Future—Residue valorization in iron and steel industry: sustainable solutions for a cleaner and more competitive future Europe” that was organized by ESTEP to focus on future challenges toward the final goal of industrial deployment. KW - Circular economy KW - Steelmaking residues KW - Clean steel PY - 2021 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-530350 DO - https://doi.org/10.3390/met11081202 VL - 11 IS - 8 SP - 1202 PB - MDPI AN - OPUS4-53035 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Smol, M. A1 - Adam, Christian A1 - Krüger, O. T1 - Use of nutrients from wastewater for the fertilizer industry - approaches towards the implementation of the circular economy (CE) JF - Desalination and Water Treatment N2 - More sustainable waste management practices are an important element in the Transformation towards a circular economy (CE). Activities in this area should be dedicated to all groups of waste, including those generated in the water and sewage sector. This paper presents the characteristics of sewage sludge ash (SSA) coming from Polish municipal waste incineration plants. Due to the high content of nutrients such as phosphorus (8.01% P2O5), calcium (5.11% CaO) and magnesium (2.75% MgO), the analyzed SSA may constitute a valuable source of raw materials for the fertilizer industry. Despite the good fertilizing properties of the SSA, in some cases the presence of heavy metals such as cadmium (0.74–1.4 mg/kg dry matter), lead (49.8–99 mg/kg dry matter), mercury (3.93 mg/kg dry matter) and arsenic (4.23–4.43 mg/kg dry matter) and poor bioavailability of P from SSA disqualifies this waste from direct use as a fertilizer. Therefore, it is necessary to look for methods that will allow the municipal SSA to be processed, for example, technologies for the extraction of phosphorus and the production of phosphate fertilizer. This way of SSA management is in the line with the CE assumptions, in which waste becomes a valuable source of secondary raw materials. Fertilizer produced from waste meeting quality, safety and labelling requirements and limits of organic, microbiological and physical contaminants will be able to be traded freely within the European Union (EU) and receive the CE marking. The idea of use of SSA for fertilizer purposes is consistent not only with the objectives of the CE but also with the Polish National Waste Management Plan 2022 and the Municipal Sewage Sludge Strategy 2019–2022, which emphasizes the necessity to maximize the use of biogenic substances contained in wastewater. Therefore, sustainable management of SSA, in particular its storage in a way enabling the recovery of phosphorus, should be promoted. KW - Wastewater KW - Circular economy KW - Fertilizer KW - Sewage sludge KW - Phosphorus PY - 2020 DO - https://doi.org/10.5004/dwt.2020.25113 VL - 1 SP - 1 EP - 9 PB - Desalination Publications CY - Hopkinton, MA 01748, USA AN - OPUS4-50646 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Abis, M. A1 - Bruno, M. A1 - Kuchta, K. A1 - Simon, Franz-Georg A1 - Grönholm, R. A1 - Hoppe, M. A1 - Fiore, S. T1 - Assessment of the Synergy between Recycling and Thermal Treatments in Municipal Solid Waste Management in Europe JF - Energies N2 - In 2018, the production of Municipal SolidWaste (MSW) in EU-28 reached 250.6 Mt, with the adoption of different management strategies, involving recycling (48 wt %), incineration and thermal valorization (29 wt %) and landfilling (23 wt %). This work was based on the analysis of the baseline situation of MSW management in EU-28 in 2018, considering its progress in 2008–2018, and discussed the possible improvement perspectives based on a framework involving incineration and recycling as the only possible alternatives, specifically evaluating the capability of already-existing incineration plants to fulfill the EU needs in the proposed framework. The results of the assessment showed two main crucial issues that could play a pivotal role in the achievement of Circular Economy action plan targets: the need to increase the recycling quotas for specific MSW fractions through the separate collection, and therefore the improvement of definite treatment process chains; the optimization of the recovery of secondary raw materials from incineration bottom ash, involving the Recycling of ferrous and nonferrous metals and the mineral fraction. Both issues need to find an extensive application across all member states to decrease the actual differences in the adoption of sustainable MSW management options. KW - Bottom ash KW - Circular economy KW - Waste treatment KW - Recycling PY - 2020 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-520285 DO - https://doi.org/10.3390/en13236412 SN - 1996-1073 VL - 13 IS - 23 SP - 6412 EP - 6412 PB - MDPI CY - Basel AN - OPUS4-52028 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Pienkoß, Fabian A1 - Abis, M. A1 - Bruno, M. A1 - Grönholm, R. A1 - Hoppe, M. A1 - Kuchta, K. A1 - Fiore, S. A1 - Simon, Franz-Georg T1 - Heavy metal recovery from the fine fraction of solid waste incineration bottom ash by wet density separation JF - Journal of Material Cycles and Waste Management N2 - This work is aimed at exploring the recovery of heavy metals from the fine fraction of solid waste incineration bottom ash. For this study, wet-discharged bottom ash fine-fraction samples from full-scale treatment plants in Germany and Sweden were analyzed. The potential for the recovery of heavy metal compounds was investigated through wet density-separation with a shaking table. The feed materials were processed without any pre-treatment and the optimum processing conditions were determined by means of design of experiments. Tilt angle and stroke frequency were identified as the most relevant parameters, and the optimum settings were − 7.5° and 266 rpm, respectively. The obtained balanced copper enrichments (and yields) were 4.4 (41%), 6.2 (28%) and 2.4 (23%). A maximum copper enrichment of 14.5 with 2% yield was achieved, providing a concentrate containing 35.9 wt.% relevant heavy metal elements. This included 26.3 wt.% iron, 4.3 wt.% zinc and 3.8 wt.% copper. In conclusion, density separation with shaking tables can recover heavy metals from bottom ash fine fractions. Medium levels of heavy metal enrichment (e.g., for Cu 2.7–4.4) and yield (Cu: 26–41%) can be reached simultaneously. However, the separation performance also depends on the individual bottom ash sample. KW - Bottom ash KW - Density separation KW - Circular economy KW - Design of experiments PY - 2021 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-538569 DO - https://doi.org/10.1007/s10163-021-01325-1 SN - 1438-4957 SN - 1611-8227 VL - 24 SP - 364 EP - 377 PB - Springer Nature CY - Heidelberg AN - OPUS4-53856 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Maisels, A. A1 - Hiller, A. A1 - Simon, Franz-Georg T1 - Chemical Recycling for Plastic Waste: Status and Perspectives JF - ChemBioEng Reviews N2 - Industrial-scale mechanical recycling of plastics has been established for years, but has technical and economic limits. Chemical recycling processes lead back to monomers or to the raw materials, so that in the end new goods can be produced for all areas of application of plastics. The variety of chemical recycling processes is large. The capacities of the plants are still low today. The profitability of the plants is strongly influenced by the price of oil; the profitability limit is currently between 50 and 60 US $ per barrel. KW - Chemical recycling KW - Plastic waste KW - Circular economy KW - Pyrolysis KW - Solvolysis PY - 2022 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-565700 DO - https://doi.org/10.1002/cben.202200024 SN - 2196-9744 VL - 9 IS - 6 SP - 541 EP - 555 PB - Wiley-VCH GmbH CY - Weinheim AN - OPUS4-56570 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - JOUR A1 - Simon, Franz-Georg A1 - Kalbe, Ute T1 - Case Study on Secondary Building Materials for a Greener Economy JF - Applied Sciences N2 - Half of global material consumption involves mineral material. The circularity is still low so that the 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 placed 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, and soil-like material and IBA were characterized with respect to their material composition. Their environmental compatibilities in particular were 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 two. 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 regulations. Improved levels of utilization might be achievable with better treatment technologies. KW - Incineration bottom ash KW - Soil-like material KW - Leaching KW - Circular economy PY - 2023 UR - https://nbn-resolving.org/urn:nbn:de:kobv:b43-576343 DO - https://doi.org/10.3390/app13106010 SN - 2076-3417 VL - 13 IS - 10 SP - 1 EP - 13 PB - MDPI CY - Basel AN - OPUS4-57634 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER -