TY - RPRT A1 - Bandow, Nicole A1 - Jürgens, Frederike A1 - Schoknecht, Ute T1 - Beregnete Bauteile und Bauprodukte: Entwicklung von Vergabekriterien für den Blauen Engel mit Hilfe von Auslaugtests N2 - Auslaugversuche wurden mit verschiedenen Bauprodukten durchgeführt, die unter Anwendungsbe-dingungen mit Niederschlägen in Kontakt kommen können. In das Testprogramm wurden Lacke für Außenanwendungen, Wärmedämmverbundsysteme, Dachziegel und polymere Dachfolien einbezogen. Mit diesen Produkten wurden der von CEN TC 351 entwickelte dynamische Oberflächenauslaugtest (DSLT) und Immersionstests nach EN 16105 durchgeführt. Emissionsverläufe wurden sowohl für an-organische Komponenten als auch für organische Substanzen in den Eluaten ermittelt. Auslaugbare organische Substanzen wurden zuvor in Screeningtests identifiziert. Um die mögliche Freisetzung von Stoffen aus Bauprodukten beurteilen zu können, ist es erforderlich, Emissionsverläufe zu beschreiben. Dazu sind die verwendeten Testverfahren geeignet. Um Baupro-dukte mit einem Blauen Engel als „Produkte mit geringer Auslaugung“ auszuloben, müssen die aus-laugbaren Substanzen komplett bekannt sein. Für organische Verbindungen ist das noch eine Heraus-forderung. Außerdem erfordert die Bewertung der Testergebnisse sowohl Übertragungsmodelle, die Vorhersagen über freisetzbare Stoffmengen unter Anwendungsbedingungen ermöglichen, als auch Vorgaben zu tolerierbaren Umweltkonzentrationen. Hier besteht noch Handlungsbedarf. N2 - Leaching tests were performed on different construction products that can be exposed to precipitation during service life. Varnishes for outdoor application, exterior thermal insulation systems, roof tiles and polymeric roof membranes were included in the test program. Leaching tests according to the dynamic surface leaching test (DSLT) as developed by CEN TC 351 and the immersion test according to EN 16105 were performed using these products. Emission curves were determined for inorganic as well as organic substances in the eluates. Leachable organic sub-stances in the eluates were identified by screening tests prior to the leaching tests. It is necessary to describe emission curves to be able to evaluate possible release of substances from construction products. The applied leaching tests are suitable to describe leaching processes. All leach-able substances need to be known in order to award the ecolabel ‘Blue Angel’. This is still challenging in case of organic substances. In addition, evaluation of the test results requires transfer models to predict leachable amounts under service conditions as well as requirements on concentrations that can be tolerated in environmental compartments. There is still need for action to solve these topics. KW - Bauprodukte KW - Auslaugtests KW - Blauer Engel KW - Construction Products KW - Leaching PY - 2018 SN - 1862-4359 VL - 67/2018 SP - 1 EP - 89 CY - Dessau-Rosslau AN - OPUS4-45799 LA - deu AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CONF A1 - Kalbe, Ute A1 - Simon, Franz-Georg A1 - Bandow, Nicole T1 - Potential use of incineration bottom ash in construction – Evaluation of environmental impact N2 - Around 5 million tonnes of MSWI bottom ash (BA) are generated per year in Germany. The incineration itself serves for metals as a concentrating and cleaning process. However, due to the almost exclusive wet extraction out of the furnace chamber the various metals are integrated in a heterogeneous and instable matrix. The metal recovery is therefore still a challenge relating the recovery rate and the purity, respectively. With state of the art treatment trains in Germany around 7.7% of ferrous metals and 1.3% of non-ferrous metals can be recovered out of MSWI BA. Large quantities of the mineral fraction are reused for sub-base material in road construction. A three month ageing period has been established as the common practice of further treatment of bottom ash before reuse applications. In the course of this aging the pH value of bottom ash decreases and contaminants are immobilized by processes like carbonation, hydration and oxidation. In particular leaching of heavy metals may be reduced to environmentally acceptable levels. However, the aging results in fixing of other valuable resources such as metals. Two laboratory scale lysimeters (30 cm in diameter) are being operated for more than three years aiming at the investigation of the long-term leaching behavior of a 0.25/45 mm mineral material obtained by treatment of MSWI bottom ash directly after incineration by a wet processing technology. Artificial rainwater is used as leachant (pH ≈ 6, ingredients NO32-, Cl-, SO42-, Na+, K+, Ca2+, Mg2+). The lysimeters are irrigated related to an average annual precipitation rate of 600 mm/a leading to a liquid to solid ratio (L/S) of about 0.7 per year of operation. Lysimeter tests are more adequate to simulate field scenarios and long-term leaching behavior in contrast to laboratory column tests particularly due to the unsaturated conditions and realistic contact time with the leachant. In comparison to the leaching of bottom ash (aged for 3 month and non-treated) in column tests the chloride and sulfate leaching in the lysimeters was reduced as a consequence of the previous wet processing. The sulfate release kept almost constant limited by CaSO4 solubility up to an L/S of about 0.7 l/kg. The chloride concentrations dropped quickly, starting from 7300 mg/l, and are now at an almost constant level of 50 mg/l which is significantly above the chloride concentration in the leachant. After an initial decrease of the pH from about 10.4 to 8 at L/S of 0.2 l/kg, the pH increased again and leveled out around 9.8 up to L/S 2.2 l/kg. At an L/S of about 2.5 l/kg now, Cr, Cu are still released. The Cu and Cr concentrations in the leachates were about 760 µg/l and 90 µg/l respectively at the beginning. For both metals the concentration decreased to about 35 µg/l now. The Mo concentrations dropped steadily from 1300 to 250 µg/l, whereas V and Sb concentrations increased in the course of the tests. Fe and Mn are not detectable anymore. More results of this experimental study will be presented and discussed with a special focus on elements forming oxyanions. T2 - 10th International Conference on the Environmental and Technical Implications of Construction with Alternative Materials, WASCON 2018 CY - Tampere, Finland DA - 06.06.2018 KW - Lysimeter, Antimony KW - MSWI bottom ash KW - Leaching PY - 2018 AN - OPUS4-45263 LA - eng AD - Bundesanstalt fuer Materialforschung und -pruefung (BAM), Berlin, Germany ER - TY - CONF A1 - Simon, Franz-Georg A1 - Kalbe, Ute A1 - Bandow, Nicole T1 - Potential use of incineration bottom ash in construction – Evaluation of environmental impact N2 - The results from a long-term lysimeter experiment with incineration bottom ash irrigated with artificial rain are reported. Whereas chloride concentration dropped significantly, the release of antimony increased during the course of the experiment as a result of aging processes. T2 - 10th International Conference on the Environmental and Technical Implications of Construction with Alternative Materials, WASCON 2018 CY - Tampere, Finland DA - 06.06.2018 KW - Leaching KW - MSWI Bottom Ash KW - Lysimeter KW - Antimony PY - 2018 SN - 978-951-758-631-3 SN - 0356-9403 SP - 108 EP - 110 AN - OPUS4-45416 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 - CONF A1 - Vogel, Christian A1 - Kalbe, Ute A1 - Simon, Franz-Georg T1 - Leaching behavior of Antimony in MSWI bottom ash N2 - Bottom ash (BA) from municipal solid waste incineration (MSWI) contains harmful substances such as heavy metals, chloride and sulfate which are mobilized in contact with water. Standardized leaching tests are used to measure the extent of mobilization. It is known that fresh bottom ash displays elevated concentrations of various heavy metals such as lead or zinc due to the formation of hydroxo complexes as a result of high pH values of 12 and above. Storage of BA is accompanied by ageing processes, mainly the reaction of CaO and Ca(OH)2 with CO2 leading to lower pH values in contact with water around 11. Usually heavy metals concentrations are minimum at these conditions. Knowledge of the long-term leaching behavior of potentially harmful substances is crucial for the assessment of the environmental compatibility of reusing municipal solid-waste incineration bottom ash (MSWI BA) in construction, i.e., as a road base layer. BA fractions obtained from wet-processing aiming at the improvement of environmental quality were used to investigate the mobility of relevant substances. Eluates from laboratory-scaled leaching procedures (column percolation and lysimeters) were analyzed to learn about the long-term release of substances. Unsaturated conditions and artificial rainwater were used in the lysimeter tests to simulate field conditions. In addition, batch test eluates were generated at usual liquid-to-solid ratios (L/S) for compliance testing purposes. A variety of cations and anions was measured in the eluates. The wet treatment reduces the leaching of chloride and particularly sulfate by more than 60%. The release of typical contaminants for the treated MSWI BA such as the heavy metals Cu and Cr was well below 1% in the conducted leaching tests. An increase in the Sb concentration was observed in the lysimeter experiments starting at L/S 0.75 L/kg and in the column experiment at L/S 4 L/kg is assumed to be related to decreasing concentrations of Ca and thus to the dissolution of sparingly soluble calcium antimonate. The same leaching mechanism applies with V, but the concentration levels observed are less critical regarding relevant limit values. However, on the long term the behavior of Sb could be problematic for the application of MSWI BA as secondary building material. T2 - MINEA Final Conference CY - Bologna, Italy DA - 20.02.2020 KW - Antimony KW - Bottom ash KW - Leaching KW - Solubility PY - 2020 AN - OPUS4-50450 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 -