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Organisationseinheit der BAM
- 1 Analytische Chemie; Referenzmaterialien (2)
- 1.3 Instrumentelle Analytik (2)
- 4 Material und Umwelt (2)
- 4.2 Material-Mikrobiom Wechselwirkungen (2)
- 6 Materialchemie (2)
- 1.1 Anorganische Spurenanalytik (1)
- 1.4 Prozessanalytik (1)
- 5 Werkstofftechnik (1)
- 5.4 Multimateriale Fertigungsprozesse (1)
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Formation Mechanism of a Nano-Ring of Bismuth Cations and Mono-Lacunary Keggin-Type Phosphomolybdate
(2022)
A new hetero-bimetallic polyoxometalate (POM) nano-ring was synthesized in a one-pot procedure. The structure consists of tetrameric units containing four bismuth-substituted monolacunary Keggin anions including distorted [BiO8] cubes. The nano-ring is formed via self-assembly from metal precursors in aqueous acidic medium. The compound (NH4)16[(BiPMo11O39)4] ⋅ 22 H2O; (P4Bi4Mo44) was characterized by single-crystal X-ray diffraction, extended X-ray absorption fine structure spectroscopy (EXAFS), Raman spectroscopy, matrix-assisted laser desorption/ionisation-time of flight mass spectrometry (MALDI-TOF), and thermogravimetry/differential scanning calorimetry mass spectrometry (TG-DSC-MS). The formation of the nano-ring in solution was studied by time-resolved in situ small- and wide-angle X-ray scattering (SAXS/WAXS) and in situ EXAFS measurements at the Mo−K and the Bi−L3 edge indicating a two-step process consisting of condensation of Mo-anions and formation of Bi−Mo-units followed by a rapid self-assembly to yield the final tetrameric ring structure.
This paper presents the results of an interlaboratory study of the rheological properties of cement paste and ultrasound gel as reference substance. The goal was to quantify the comparability and reproducibility of measurements of the Bingham parameters yield stress and plastic viscosity when measured on one specific paste composition and one particular ultrasound gel in different laboratories using different rheometers and measurement geometries.
The procedures for both in preparing the cement paste and carrying out the rheological measurements on cement paste and ultrasound gel were carefully defined for all of the study’s participants. Different conversion schemes for comparing the results obtained with the different measurement setups are presented here and critically discussed. The procedure proposed in this paper ensured a reasonable comparability of the results with a coefficient of variation for the yield stress of 27% and for the plastic viscosity of 24%, despite the individual measurement series’ having been performed in different labs with different rheometers and measurement geometries.
Microstrain distributions were acquired in functional thin films by high-resolution X-ray microdiffraction measurements, using polycrystalline CuInSe2 thin films as a model system. This technique not only provides spatial resolutions at the submicrometre scale but also allows for analysis of thin films buried within a complete solar-cell stack. The microstrain values within individual CuInSe2 grains were determined to be of the order of 10^-4. These values confirmed corresponding microstrain distribution maps obtained on the same CuInSe2 layer by electron backscatter diffraction and Raman microspectroscopy.
The investigation of the microstructure in functional, polycrystalline thin films is an important contribution to the enhanced understanding of structure–property relationships in corresponding devices. Linear and planar defects within individual grains may affect substantially the performance of the device. These defects are closely related to strain distributions. The present work compares electron and X-ray diffraction as well as Raman microspectroscopy, which provide access to microstrain distributions within individual grains. CuInSe₂ thin films or solar cells are used as a modelsystem. High-resolution electron backscatter diffraction and X-ray microdiffraction as well as Ramanmicrospectroscopy were applied for this comparison. Consistently, microstrain values were determined of the order of 10⁻⁴ by these three techniques. However,only electron backscatter diffraction, X-ray microdiffraction exhibit sensitivities appropriate for mapping local strain changes at the submicrometer level within individual grains in polycrystalline materials.
Electrochemical water splitting is an environmentally friendly technology to store renewable energy in the form of chemical fuels. Among the earth-abundant first-row transition metal-based catalysts, mixed Ni-Fe oxides have shown promising performance for effective and low-cost catalysis of the oxygen evolution reaction (OER) in alkaline media, but the synergistic roles of Fe and Ni cations in the OER mechanism remain unclear. In this work, we report how addition of Ni changes the reactivity of a model iron oxide catalyst, based on Ni deposited on and incorporated in a magnetite Fe3O4(001) single crystal, using a combination of surface science techniques in ultra-high vacuum such as low energy electron diffraction (LEED), x-ray photoelectron spectroscopy (XPS), low-energy ion scattering (LEIS), and scanning tunneling microscopy (STM), as well as atomic force microscopy (AFM) in air, and electrochemical Methods such as cyclic voltammetry (CV) and electrochemical impedance spectroscopy (EIS) in alkaline media. A significant improvement in the OER activity is observed when the top surface presents an iron fraction among the cations in the range of 20-40%, which is in good agreement with what has been observed for powder catalysts. Furthermore, a decrease in the OER overpotential is observed following surface aging in electrolyte for three days. At higher Ni load, AFM shows the growth of a new phase attributed to an (oxy)-hydroxide phase which, according to CV measurements, does not seem to correlate with the surface activity towards OER. EIS suggests that the OER precursor species observed on the clean and Ni-modified surfaces are similar and Fe-centered, but form at lower overpotentials when the surface Fe:Ni ratio is optimized. We propose that the well-defined Fe3O4(001) surface can serve as a model System for understanding the OER mechanism and establishing the structure-reactivity relation on mixed Fe-Ni oxides.
The wireless high-frequency technology requires a robust, cost-effective, and highly integrated substrate technology offering the capability for areas of tailored permittivity. The wet-chemical porosification of low temperature co-fired ceramics (LTCC) substrates offers such an approach by locally embedding air. Porosification of LTCC in both extremely acidic and alkaline media has been investigated in previous works. However, for improving the available knowledge on the porosification of LTCC with H3PO4 as a standard and a widely used etching solution, the impact of solution concentration was systematically investigated and a substantial improvement in the etching performance was achieved. Moreover, in the present study, for the first time, the intermediate pH values, and the impact of pH as a key parameter on the etching process have been investigated. For this purpose, the applicability of phosphate buffer solution (PBS) as a prospective novel etchant mixture for the porosification of a commercially available LTCC tape (Ceramtape GC) was explored. Valuable information about surface morphology, crystalline composition, and the pore structure of the etched LTCCs was gathered employing scanning electron microscopy, transmission electron microscopy, X-ray diffraction analysis, and mercury porosimetry measurements. Based on these findings, the performance of PBS-based etchant systems towards the generation of porous LTCCs combining high depths of porosification with acceptable surface characteristics for subsequent metallization is demonstrated. Based on the obtained results, by application of a 0.2 mol L−1 solution of PBS, the effective relative permittivity of test samples with a thickness of approximately 600 µm and a porosification depth of 186 µm from each side, could be reduced up to 10% of its initial “as fired” value. Also, based on the measurement results and by measuring the depth of porosification, the permittivity of the etched layer was estimated to show a reduction of up to 22% compared to the initial “as fired” value.
The study, dedicated to Beautiful Pietàs conserved in South Tyrol (Northern Italy), aims to establish, for the first time, a connection between Austroalpine raw materials and the high-fired gypsum mortars constituting the Gothic figure groups in question. The origin and chronology of this stylistically and qualitatively differing ensemble have been subject of art historical debate for nearly a century. The discourse is dominated by three main hypotheses: itinerary of an Austrian artist versus itinerary of the work of art created in an artist’s workshop in Austria versus itinerary of the stylistic vocabulary via graphical or three-dimensional models. The comparison of the δ34S values and the 87Sr/86Sr ratios of the gypsum mortars and Austroalpine sulphate deposits (in a compilation of own reference samples and literature data) points to the exploitation of sediments in the Salzkammergut and possibly also in the evaporite district of the Eastern Calcareous Alps, thus evidencing the import of the sculptures and not the activities of local South Tyrolean or itinerant artists. Two geochronological units are distinguishable: The Pietà in the Church St. Martin in Göflan can be assigned to Upper Permian raw material, whereas the metrologically consistent sculptures in the Church of Our Lady of the Benedictine Abbey Marienberg and in the Chapel St. Ann in Mölten correlate with deposits of the Early Triassic (or the Lower-Middle Triassic transition). The medieval gypsum mortars also differ in their mineralogical characteristics, i.e. in their geologically related minor components, as in the first case, characterised by a significant proportion of primary anhydrite, natural carbonate impurities mainly consist of calcite (partly converted to lime-lump-like aggregates), whereas in the second group dolomite (or rather its hydration products after pyrometamorphic decomposition) predominates, accompanied by celestine, quartz and potassium feldspar. The Pietà in the Cathedral Maria Himmelfahrt in Bozen turned out to be made of Breitenbrunn calcareous sandstone (Leitha Mountains, Burgenland, Austria), which is why the sample is not considered in the geochemical analysis.
Dass Viren sich über Aerosolpartikel ausbreiten können, wurde bereits in vielen Studien gezeigt. Als Aerosol bezeichnet man ein Gemisch aus Luft mit darin verteilten festen oder flüssigen Partikeln. Ein Aerosol ist dabei immer dynamisch, da Partikel neugebildet, in oder mit der Luft transportiert und aus der Luft entfernt werden oder sich im luftgetragenen Zustand verändern. Zum Verständnis der Rolle von Aerosolpartikeln als Übertragungsweg von SARS-CoV-2 ist daher die Kenntnis der verschiedenen Prozesse in einem Aerosol von besonderer Bedeutung. Mit diesem Papier möchte die GAeF einen Beitrag dazu leisten, den momentan so häufig anzutreffenden Begriff „Aerosol“ sowie die relevanten Aerosolprozesse anschaulich darzustellen und zu erläutern. Dabei wird im Rahmen dieses Papiers nur auf die wesentlichen Grundlagen eingegangen.
Für ein tiefergehendes Verständnis der teilweise komplexen Prozesse sei auf die angeführte Sekundärliteratur verwiesen. Das Papier fasst eine Vielzahl von Studien zur Entstehung von virenbeladenen Aerosolpartikeln sowie deren Ausbreitung zusammen. Darauf basierend kann festgestellt werden, dass ausgeatmete Aerosolpartikel auch bei der Corona-Pandemie eine prominente Rolle bei der Verbreitung der Viren spielen. Abschließend geht dieses Papier auf mögliche Maßnahmen zur Verringerung der Ausbreitung von Aerosolpartikeln ein. Die diskutierten Maßnahmen orientieren sich an der derzeitigen öffentlichen Diskussion und beinhalten entsprechend die folgenden Punkte: Lüften, Luftreiniger, Lüftungsanlagen und Masken. Es werden Hinweise zum richtigen und sinnvollen Einsatz dieser Maßnahmen gegeben. Aerosolpartikel haben Größen zwischen ca. 0,001 und mehreren 100 Mikrometern (und nicht wie in vielen Publikationen derzeit definiert < 5μm) und verteilen sich mit Luftströmungen relativ schnell, auch über größere Distanzen. Größere Aerosolpartikel sinken – abhängig von ihrer Größe und Dichte – zu Boden; kleine Aerosolpartikel können hingegen sehr lange in der Luft verbleiben (s. Kapitel 3). Jeder Mensch stößt durch die Atmung sowie beim Sprechen, Husten und Niesen flüssige Aerosolpartikel unterschiedlicher Größen aus (s. Kapitel 4). Ist eine Person mit einem Virus, wie z. B. SARS-CoV-2, infiziert, so können diese Aerosolpartikel Viren enthalten, die in die Luft gelangen und von anderen Personen eingeatmet werden können. SARS-CoV-2 hat eine Größe von 0,06 bis 0,14 Mikrometer, die exhalierten flüssigen Aerosolpartikel sind hingegen größer. Die flüssigen Aerosolpartikel können aber je nach Umgebungsbedingungen durch Verdunstung schrumpfen (s. Kapitel 3.3). Für den Partikeltransport und die Partikelabscheidung ist dabei jeweils die aktuelle Partikelgröße relevant. Das höchste Infektionsrisiko besteht in geschlossenen Innenräumen, da sich hierin Aerosolpartikel anreichern können. Insbesondere hier sind entsprechend Maßnahmen zu treffen, die eine Reduktion der Aerosolpartikelkonzentration ermöglichen.
Vor dem Hintergrund der Aerosolwissenschaften ordnet die GAeF die aktuellen Maßnahmen zur Eindämmung der Pandemie wie folgt ein:
• Prinzipiell gilt: Keine Maßnahme kann für sich alleine funktionieren! Das Zusammenspiel der verschiedensten Maßnahmen ist nach derzeitigem Wissensstand der beste Weg zur Minimierung des Infektionsrisikos.
• Abstand halten ist wichtig, denn mit zunehmendem Abstand werden direkt ausgeatmete Viren verdünnt, und die Wahrscheinlichkeit sich anzustecken sinkt. Der vielfach vorgeschriebene Mindestabstand kann als Anhaltspunkt dienen, sollte aber insbesondere bei längeren Zusammenkünften und auch in Innenräumen mit verringerter Luftbewegung vergrößert und durch weitere Maßnahmen (s.u.) ergänzt werden.
• Masken helfen, einen Teil der exhalierten Partikel (und Viren) zu filtern. Dadurch sinkt die Konzentration der exhalierten Partikel (und Viren) in einem Raum und damit das Infektionsrisiko. Hierbei ist zu beachten, dass die ausgeatmeten Aerosolpartikel durch anhaftende Feuchtigkeit relativ groß sind und somit auch von einfachen Masken effizient zurückgehalten werden können. Da diese Partikel aber mit längerer Verweilzeit in der Raumluft schrumpfen, sind einfache Mund-Nasen-Bedeckungen für den Selbstschutz weniger effizient. Hierfür sind Atemschutzmasken erforderlich, die auch für feine Partikel eine hohe Abscheidung zeigen, z. B. der Klassen FFP2, N95 oder KN95. Diese sind sowohl für den Selbst- als auch den Fremdschutz effizient, sofern sie über kein Ausatemventil verfügen. Masken mit Ausatemventil dienen hingegen nur dem Selbstschutz und widersprechen daher dem Solidaritätskonzept, dass Mitmenschen durch kollektives Maskentragen geschützt werden.
• Gesichtsvisiere, die ohne zusätzliche Verwendung von Masken eingesetzt werden, sind hinsichtlich Aerosolpartikeln weitgehend nutzlos, da die Luft mit Partikeln (und Viren) ungefiltert um die Visiere herumströmt. Gesichtsvisiere werden im klinischen Alltag zusätzlich zu Masken getragen, um Tröpfcheninfektion über die Schleimhäute der Augen zu verhindern. Ebenfalls weitgehend unwirksam gegen die Aerosolverbreitung in Innenräumen sind mobile oder fest installierte Plexiglasbarrieren. Diese können nur kurzfristig die kleinräumige Ausbreitung eines Aerosols, z. B. im Kassenbereich eines Supermarkts, verhindern, bieten aber längerfristig keinen Schutz. Gesichtsvisiere und Plexiglasscheiben dienen im Wesentlichen als Spuck- und Spritzschutz gegenüber großen Tröpfchen.
• Im Freien finden so gut wie keine Infektionen durch Aerosolpartikel statt. Allerdings können Tröpfcheninfektionen auftreten, insbesondere in Menschenansammlungen, wenn Mindestabstände nicht eingehalten und/oder keine Masken getragen werden. In geschlossenen Räumen ist Lüften unerlässlich, um die ausgeatmete Luft in einem Raum durch frische Luft von draußen zu ersetzen. Häufiges Stoß- und Querlüften sind dabei vergleichbar effektiv wie dauernd das Fenster vollständig geöffnet zu lassen. Aus energetischer Sicht ist Stoß- oder Querlüften insbesondere im Winter allerdings effizienter. CO2-Monitore können bei der Überwachung der Luftqualität in Innenräumen helfen. Sie zeigen an, wann gelüftet werden sollte und wann die Luft in einem Raum während des Lüftens ausreichend gewechselt ist. Sie können jedoch nur als Indikator verwendet werden und verhindern selbst bei Einhaltung der vorgeschlagenen CO2-Grenzkonzentrationen keine direkte Infektion durch unmittelbar benachbarte Personen.
• Luftreiniger können einen sinnvollen Beitrag leisten, um die Partikel- und Virenkonzentration in einem Raum zu reduzieren. Bei der Beschaffung von Luftreinigern muss darauf geachtet werden, dass diese für den betrachteten Raum und die betrachtete Anwendung ausreichend dimensioniert sind, um die Partikel- und Virenlast signifikant zu verringern. Dem Luftdurchsatz des Gerätes kommt dabei eine größere Bedeutung zu, als der reinen Effizienz des Filters. Aus energetischen und Kostenerwägungen kann die Verwendung hocheffizienter Filter sogar kontraproduktiv sein. Fest verbaute Lüftungsanlagen können ebenso sinnvoll sein, sofern sie die Luft filtern, um die Partikel- und Virenlast in einem Raum zu verringern. Hierbei ist es zur Vermeidung von Infektionen sinnvoll, diese möglichst mit 100 % Frischluft zu betreiben.
Aus Sicht der Gesellschaft für Aerosolforschung besteht erheblicher Forschungsbedarf insbesondere an den interdisziplinären Grenzen zu Forschungsfeldern der Epidemiologie, Infektiologie, Virologie, Lüftungstechnik und Strömungsmechanik. Die Durchführung gezielter Studien sollte kurzfristig mit speziellen Förder- und Forschungsprogrammen ermöglicht werden. Dieses Papier wurde von Mitgliedern der Gesellschaft für Aerosolforschung verfasst und wird von einer Vielzahl internationaler Aerosolexperten unterstützt (s. Kapitel 8). Neben der vorliegenden Version existiert auch eine englischsprachige Übersetzung (siehe www.info.gaef.de). Sämtliche Abbildungen in diesem Papier stehen unter folgendem Link zum kostenlosen Download bereit: https://www.info.gaef.de/positionspapier. Bei jeder Verwendung ist „Gesellschaft für Aerosolforschung e. V.“ als Quelle zu nennen.
Many studies have already shown that viruses can spread via aerosol particles. An aerosol is a mixture of air with solid or liquid particles dispersed in it. To understand the role of aerosol particles as a transmission path of SARS-CoV-2, knowledge of the different processes in an Aerosol is therefore of particular importance. With this paper, GAeF would like to contribute to a better understanding of the term “aerosol” and the relevant aerosol processes. In the context of this paper only the essential basics will be discussed. For a deeper understanding of the partly complex processes, please refer to the literature mentioned at the end of the paper.
The paper summarises a large number of studies on the formation of virus-laden aerosol particles and their spread. Based on this, it can be concluded that exhaled aerosol particles may play a prominent role in the spread of viruses in the corona pandemic. Finally, this paper discusses possible measures to reduce the spread of aerosol particles. The measures discussed are based on the current public debate including ventilation, air purifiers, HVAC systems and masks. Advice is given on the correct and sensible use of these measures.
An aerosol is always dynamic, as particles are newly formed, transported in or with the air, removed from the air or change in the airborne state. Aerosol particles have sizes between approx. 0.001 and several 100 micrometres (and not < 5 μm as currently defined in many publications) and spread relatively quickly with air currents, even over longer distances. Larger aerosol particles sink to the ground, depending on their size and density, while small aerosol particles can remain in the air for a very long time (see Section 3). Every person emits liquid aerosol particles of various sizes through breathing and when speaking, coughing and sneezing (see Section 4). If a person is infected with a virus, such as SARS-CoV-2, these aerosol particles can contain viruses that can be released into the air and inhaled by other people. SARS-CoV-2 has a size of 0.06 to 0.14 micrometres, but the exhaled liquid aerosol particles are larger. The liquid aerosol particles can shrink by evaporation, depending on the ambient conditions (see Section 3.3). Particle size is relevant for particle transport and particle separation. The highest risk of infection exists in closed indoor spaces, as aerosol particles can accumulate there.
Here in particular, appropriate measures must be taken to reduce the concentration of aerosol particles (see Section 5).
Against the background of aerosol science, the GAeF classifies the current measures to contain the pandemic as follows:
• In principle, no measure can work on its own! According to the current state of knowledge, the interaction of the most varied measures is the best way to minimise the risk of infection.
• Keeping distance is important, because with increasing distance, directly exhaled viruses are diluted and the probability of infection decreases. The often prescribed minimum distance can be used as a guide, but it should be increased and supplemented by other measures (see below), especially for longer meetings and also indoors with reduced air movement.
• Masks help to filter some of the exhaled particles (and viruses). This reduces the concentration of exhaled particles (and viruses) in a room and thus the risk of infection. It should be noted here that the exhaled aerosol particles are relatively large due to adhering moisture and can therefore also be efficiently retained by simple masks. However, since these particles shrink with longer dwell time in the room air, simple mouth-nose masks are less efficient for self-protection. Respiratory masks are required for this purpose, which show a high degree of separation even for fine particles, e.g. of classes FFP2, N95 or KN95. These are efficient for both self-protection and protection of others unless they have an exhalation valve. Masks with an exhalation valve, on the other hand, are only for self-protection and therefore contradict the solidarity concept that fellow human beings are protected by collective mask wearing. Face shields which are used without additional masks are largely useless with regard t• aerosol particles, as the air with particles (and viruses) flows unfiltered around the shields. In everyday clinical practice, facial shields are worn in addition to masks to prevent droplet infection via the mucous membranes of the eyes. Mobile or permanently installed Plexiglas barriers are also largely ineffective against the spread of aerosols indoors. These can only prevent the smallscale spread of an aerosol in the short term, e.g. in the checkout area of a supermarket, but offer no protection in the longer term. Face shields and Plexiglas panels essentially serve as spit and splash protection against large droplets.
• Outdoors, there are practically no infections caused by aerosol transmission. However, droplet infections can still occur, especially in crowds, if minimum distances are not observed and/or masks are not worn. In closed rooms, ventilation is essential to replace the exhaled air in a room with fresh air from outside. Frequent airing and cross-ventilation is just as effective as leaving the window open all the time. From an energy point of view, however, it is more efficient to ventilate the room, especially in winter. CO2 monitors can help to monitor indoor air quality. They indicate when it is necessary to ventilate and when the air in a room has been sufficiently changed during ventilation. However, they can only be used as an indicator and even if the proposed CO2 limit concentrations are met, they do not prevent direct infection by people in the immediate vicinity.
• Air purifiers can make a useful contribution to reducing the concentration of particles and viruses in a room. When procuring air purifiers, care must be taken to ensure that they are adequately dimensioned for the room and application in question in order to significantly reduce the particle and virus load. The air throughput of the unit is more important than the pure efficiency of the filter. For energy and cost reasons, the use of highly efficient filters can even be counterproductive. Permanently installed ventilation systems can also be useful, provided they filter the air to reduce the particle and virus load in a room. To avoid infections, it is advisable to operate them with 100 % fresh air if possible.
From the point of view of the Gesellschaft für Aerosolforschung, there is a considerable need for research, especially at the interdisciplinary borders to research fields of epidemiology, infectiology, virology, ventilation technology and fluid mechanics. The implementation of targeted studies should be made possible at short notice with special funding and research programmes.
This paper was written originally in German by members of the Gesellschaft für Aerosolforschung and is supported by a large number of international aerosol experts. Both the English and German version as well as all images in the paper are available for free download at the following link: https://www.info.gaef.de/positionspapier. The “Gesellschaft für Aerosolforschung e. V.” must be named as the source, whenever an image is used.