4 Material und Umwelt
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- 4 Material und Umwelt (440)
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- 1 Analytische Chemie; Referenzmaterialien (27)
- 6.1 Oberflächen- und Dünnschichtanalyse (16)
- 1.1 Anorganische Spurenanalytik (11)
- 1.4 Prozessanalytik (10)
- 6.2 Material- und Oberflächentechnologien (10)
- 7 Bauwerkssicherheit (10)
- 1.7 Organische Spuren- und Lebensmittelanalytik (7)
- 1.8 Umweltanalytik (7)
- 4.6 Molekulare und angewandte Entomologie (7)
- 5 Werkstofftechnik (7)
- 7.1 Baustoffe (6)
- 1.2 Biophotonik (5)
- 7.4 Baustofftechnologie (5)
- 8 Zerstörungsfreie Prüfung (5)
- 9 Komponentensicherheit (5)
- 1.9 Chemische und optische Sensorik (4)
- 6.3 Strukturanalytik (4)
- 6.6 Physik und chemische Analytik der Polymere (4)
- 5.4 Multimateriale Fertigungsprozesse (3)
- 7.5 Technische Eigenschaften von Polymerwerkstoffen (3)
- 8.0 Abteilungsleitung und andere (3)
- 9.3 Schweißtechnische Fertigungsverfahren (3)
- 5.1 Mikrostruktur Design und Degradation (2)
- 5.3 Polymere Verbundwerkstoffe (2)
- 8.1 Sensorik, mess- und prüftechnische Verfahren (2)
- 8.5 Röntgenbildgebung (2)
- 9.0 Abteilungsleitung und andere (2)
- 1.0 Abteilungsleitung und andere (1)
- 2 Prozess- und Anlagensicherheit (1)
- 2.1 Sicherheit von Energieträgern (1)
- 5.6 Glas (1)
- 6.7 Materialsynthese und Design (1)
- 7.6 Korrosion und Korrosionsschutz (1)
- 8.4 Akustische und elektromagnetische Verfahren (1)
Per- and polyfluoroalkyl substances (PFAS) are anionic, cationic and zwitterionic synthetic products, in which the hydrogen atoms on the carbon skeleton of at least one carbon atom have been completely replaced by fluorine atoms (see Figure 1) and which include more than 4730 compounds, depending on the definition. As a result of continuous and prolific use, mainly in aviation firefighting foams, thousands of industrial and military installations have been found to contain contaminated soil, groundwater and surface water. Furthermore, because of the continuous contamination through PFAS containing commercial products, effluents and sewage sludge from WWTPs have been shown to be an important source of PFAS discharge into the aquatic environment. In the last few years, legacy PFAS (≥C4) have been found in various environments, including soil, water and wastewater, and their environmental pathways have been partly described. To get a better
overview of the amount of “total PFAS,” sum parameter methods like total oxidizable precursor (TOP) assay and methods based on combustion ion chromatography (CIC) are in development. CIC results in data regarding the sum of absorbable organic fluorine (AOF) or extractable
organic fluorine (EOF), which can also quantify other organically bound fluorine compounds such as fluorinated pesticides and pharmaceutical. Additionally, for research purpose several spectroscopical methods like X-ray photoelectron spectroscopy (XPS), fluorine K-edge X-ray absorption near-edge structure (XANES) spectroscopy, particular induced gamma-ray emission (PIGE) spectroscopy and 19F nuclear magnetic resonance (NMR) spectroscopy are available. Therefore, an overview is given on various analytical techniques for PFAS in environmental samples and their application possibilities discussed for different kind of PFAS compounds
Recycling-Düngemittel auf Basis von sekundären Ressourcen (Gülle, Gärreste, Klärschlamm, Tiermehl etc.) gewinnen in den letzten Jahren zunehmend an Bedeutung in der Landwirtschaft. Die in den Recycling-Düngemitteln enthaltenen P-Spezies weichen oft stark von denen in konventionell hergestellten Düngemitteln aus Rohphosphat ab, zudem enthalten Recyclingdünger oft mehrere verschiedene P-Formen. Die Pflanzenverfügbarkeit des P in ist ganz wesentlich von der enthaltenen P-Form abhängig. Derzeit gibt es außer zeitaufwendigen und kostspieligen Gefäß- und Feldversuchen keine zufriedenstellende Testmethode zur Analyse der P-Pflanzenverfügbarkeit von unterschiedlichen Recycling P-Düngemitteln. Die im europäischen Düngemittelrecht normierten chemischen Extraktionsmethoden (Wasser, Zitronensäure, Ameisensäure, neutral Ammoniumcitrat etc.) zeigen oftmals keine oder nur sehr geringe Korrelation zu der P-Aufnahme von Pflanzen in Gefäßversuchen mit Recycling-Düngemitteln (Kratz et al. 2010, Steckenmesser et al. 2017, Vogel et al. 2017). Eine grundlegende Schwäche chemischer Extraktionsmethoden liegt darin, dass es sich dabei um statische Methoden handelt, die nicht in der Lage sind, die im System Boden/Düngemittel-Bodenlösung-Pflanze stattfindenden dynamischen Prozesse wie P-Freisetzung und Entzug durch die Pflanzenwurzeln abzubilden.
Einen Lösungsansatz bieten hier sog. P-Senken-Methoden. Bereits in den 1950er Jahren wurden erstmals P-Senken zur Analyse des Boden-P angewendet (Chardon et al. 1996). In den darauffolgenden Jahrzehnten wurden verschiedene P-Senken auf der Basis von Eisenoxid-Papier entwickelt (Chardon et al. 1996). Jedoch konnten diese Ansätze auch nur begrenzt zur Bestimmung der P-Pflanzenverfügbarkeit des Boden-P eingesetzt werden. Mitte der 1990er Jahre wurde die DGT (engl. diffusive gradients in thin films) Methode entwickelt (Zhang et al. 1998). Bei der DGT Methode diffundiert P aus der Bodenlösung des angefeuchteten Bodens durch einen Membranfilter und die Diffusionsschicht und wird anschließend an einer Bindungsschicht absorbiert. Durch den Diffusionsgradienten wird das Gleichgewicht in der Bodenlösung permanent gestört, wodurch auch labiles P im Boden gelöst wird. Die stetige Entnahme von P aus der Bodenlösung über die Diffusions-/Bindungsschicht simuliert dabei den Entzug von P durch die Pflanzenwurzel. Die an die Bindungsschicht adsorbierte Menge an P korreliert stark mit der P-Aufnahme von Pflanzen (u.a. Mason et al. 2005, 2013; Menzies et al. 2005, Six et al. 2012). Im Gegensatz zu chemischen Extraktionsmethoden werden bei der DGT Methode Mischungen an Düngemittel und Boden für mehrere Tage inkubiert (Vogel et al. 2017; Duboc et al. 2017), da ansonsten wasserlösliche P-Dünger den DGT Adsorber sättigen und wasserunlösliche P-Dünger unterschätzt werden. Ein bis zwei Wochen Inkubation sind ausreichend, damit sich pflanzenverfügbares P in die Mischungen bildet.
In letzter Zeit haben verschiedene Forschungsgruppen gezeigt, dass die DGT Methode auch eine sehr gute Korrelation mit der Pflanzenverfügbarkeit verschiedener Typen von (Recycling-)P-Düngemitteln aufweist (Vogel et al. 2017; Duboc et al. 2017; Foereid 2017; Haarstad and Bavor 2017; Lemming et al. 2017). Bei Gefäßversuchen mit verschiedenen Recycling P-Düngemitteln konnte die DGT Methode den Ertrag bzw. die P-Aufnahme von Mais deutlich besser vorhersagen als herkömmliche chemische Extraktionsmethoden (Vogel et al. 2017; Duboc et al. 2017).
Daher kann die DGT Methode im Vorfeld der Zulassung von neuen Düngermitteltypen als zuverlässige und robuste Methode zum Screening von Produktvarianten eines Düngemittelherstellers verwendet werden. Um dieses Messverfahren im Rahmen des Düngemittelrechts als Bewertungsinstrument für die Abschätzung der Pflanzenverfügbarkeit unterschiedlicher Düngemittel zu verwenden, muss es allerdings zunächst standardisiert werden. Zu diesem Zweck bietet sich der Einsatz eines „standardisierten“ Bodens bzw. Bodenrezepts an. Zur Kalibrierung der Methode im jeweiligen Labor könnten auch chemisch definierte P-Verbindungen mit bekannter Löslichkeit/Pflanzenverfügbarkeit als Referenz-substanzen verwendet werden.
Previous research shows that analytical methods based on Diffusive Gradients in Thin films (DGT) provide very good correlations to the amount of bioavailable nutrients and pollutants in the environmental samples. However, these DGT results do not identify which compound of the specific element has the high bioavailability. Using various spectroscopic techniques (infrared, XANES and NMR spectroscopy) to analyze the dried DGT binding layers after deployment could allow us to determine the specific elements or compounds. Nutrients such as phosphorus and nitrogen are often, together with other elements, present as molecules in the environment. These ions are detectable and distinguishable by infrared and NMR spectroscopy, respectively. In addition, XANES spectroscopy allows for the specification of nutrients and pollutants (e.g. chromium) on the DGT binding layer. Furthermore, microspectroscopic techniques make it also possible to analyze compounds on the DGT binding layer with a lateral resolution down to 5 µm2. Therefore, species of elements and compounds of e.g. a spatial soil segment can be mapped and analyzed, providing valuable insight to understand the dynamics of nutrients and pollutants in the environment. Here we will present the advantages and limitations of this novel combination of techniques.
Phosphorus (P) plays an essential role in the global food security. However, the global P reservoirs have a statistic lifetime of about 385 years only. Due to the scarcity of P and the increasing world population an efficient and sustainable recycling management is required. A few biogenic waste materials are high in P contents such as sewage sludge and meat and bone meal. Thus, they are suitable for P recycling and fertilizer production. But besides the high P content sewage sludge is often highly contaminated with organic pollutants and toxic heavy metals which have to be eliminated before agricultural field application. In this presentation we show the potential of sewage sludge as secondary resource for fertilizers. This includes our developments in thermochemical processes for the production of novel P-fertilizers from recycled materials. Furthermore, for these novel P-fertilizers common extraction tests to determine the plant-available P are often unusable. Therefore, we successfully applied the Diffusive gradients in thin-films (DGT) techniques to analyse the plant-availability of P-fertilizers from recycled materials.
Per- and polyfluoroalkyl substances (PFAS) are a large group of more than 10,000 anionic, cationic, zwitterionic or neutral organofluorine surfactants. As a result of continuous and prolific use, mainly in aviation firefighting foams, thousands of industrial and military installations have been found to contain contaminated soil, groundwater and surface water. While liquid chromatography tandem mass spectrometry (LC-MS/MS) is commonly used technique to characterize targeted PFAS in environmental samples, there are more than 10,000 different PFAS known, which have various headgroups and properties. Therefore, several analytical techniques are available to analyse various groups or pools of PFAS or “all” PFAS as a sum parameter. Current decontamination strategies of PFAS-burdened soils mainly consist of adsorption methods using adsorbents for fixation of PFAS in the ground. A second option is the utilization of a “pump and treat” process, cycling polluted soils through a washing plant leading to the concentration of the pollutants in the fine fraction. Both approaches are cost-intensive and not intended for the direct decomposition of all PFAS contaminants. Hence, there is a great demand for innovative developments and chemical treatment technologies, dealing with new strategies of tackling the PFAS problem. Previously, mechanochemical treatment of polychlorinated organic compounds in soils showed an efficient dechlorination. Thus, we investigated mechanochemical treatment of PFAS contaminated soils with various additives in a ball mill and analyzed the PFAS defluorination with gas chromatography mass spectrometry (GC-MS) and liquid chromatography tandem mass spectrometry (LC-MS/MS), respectively, as well es the fluoride mineralization by ion chromatography (IC) and fluorine K-edge X-ray absorption near-edge structure (XANES) spectroscopy.
Current decontamination strategies of PFAS-burdened soils mainly consist of adsorption methods using adsorbents for fixation of PFAS in the ground. A second option is the utilization of a “pump and treat” process, cycling polluted soils through a washing plant leading to the concentration of the pollutants in the fine fraction. Only a subsequent, high-energy consuming pyrolysis process guarantees the total destruction of all fluorinated organic contaminants. These approaches are cost-intensive and not intended for the direct decomposition of all PFAS contaminants. Hence, there is a great demand for innovative developments and chemical treatment technologies, dealing with new strategies of tackling the PFAS problem. Thus, we investigated mechanochemical treatment of PFAS contaminated soils with various additives in a ball mill and analyzed the PFAS defluorination with gas chromatography mass spectrometry (GC-MS) and liquid chromatography tandem mass spectrometry (LC-MS/MS), respectively, as well as the fluoride mineralization by ion chromatography (IC) and fluorine K-edge X-ray absorption near-edge structure (XANES) spectroscopy.
Per- and polyfluoroalkyl substances (PFAS) are a group of anionic, cationic and zwitterionic synthetic products, in which the hydrogen atoms on the carbon skeleton of at least one carbon atom have been completely replaced by fluorine atoms and which include more than 4730 compounds, depending on the definition. As a result of continuous and prolific use, mainly in aviation firefighting foams, thousands of industrial and military installations have been found to contain contaminated soil, groundwater and surface water. Furthermore, current decontamination strategies of PFAS-burdened soils mainly consist of adsorption methods using adsorbents for fixation of PFAS in the ground. Hence, there is a great demand for innovative developments and chemical treatment technologies, dealing with new strategies of tackling the PFAS problem. Thus, we investigated mechanochemical treatment of PFAS contaminated soils with various additives in a ball mill and analyzed the PFAS defluorination. In this presentation the advantages of fluorine K-edge X-ray absorption near-edge structure (XANES) spectroscopy for various environment samples are shown.
Per- and polyfluoroalkyl substances (PFAS) have been used extensively in the past because of their inert chemical character and resistance to degradation by environmental influences. Since the beginning of their commercial use, PFAS have been widely exposed to the environment by application of PFAS in consumer products or as foaming agent in firefighting foams, thus several cases of contaminated soils sites have been reported. Since the number of known PFAS already exceeds 4700, their characterization and direct analysis is challenging given the current available techniques. Here, we introduce the novel fluorine (F) K-edge X-ray absorption near-edge structure (XANES) spectroscopy as a tool to analyze PFAS and inorganic fluorine compounds in contaminated soils and sewage sludges. While F K-edge bulk-XANES spectroscopy provide us information on the overall fluorine bonding in a sample micro X-ray fluorescence (XRF) in combination with F K-edge micro-XANES spectroscopy can also detect minor fluorine compounds and PFAS hotspots in investigated soils and sludges. Additionally, we used the combustion ion chromatography (CIC) to analyze the total amount of all PFAS as a sum parameter (extractable organic fluoride: EOF) in soils and sewage sludges. During combustion in the CIC, the PFAS in the sample get destroyed at temperatures of approx. 1000 °C and converted in inorganic fluorides that subsequently gets quantified by ion chromatography. Thus, for the first time we successfully combined F K-edge XANES spectroscopy and CIC as analytical tools to detect and quantify PFAS contaminants in soils and sewage sludges.
Per- and polyfluoroalkyl substances (PFAS) are a group of anionic, cationic and zwitterionic synthetic products, in which the hydrogen atoms on the carbon skeleton of at least one carbon atom have been completely replaced by fluorine atoms and which include more than 4730 compounds, depending on the definition. As a result of continuous and prolific use, mainly in aviation firefighting foams, thousands of industrial and military installations have been found to contain contaminated soil, groundwater and surface water. As a result of the perpetual use of PFAS containing products, effluents and sewage sludge from wastewater treatment plants (WWTPs) have been observed to be an important pathway for PFAS into the environment. In Germany, phosphorus and other nutrients from sewage sludge and wastewater should be recycled in WWTPs of cities with a large population. However, it is not clear if PFAS contamination from wastewater and sewage sludge end up in novel wastewater-based fertilizers. Normally, PFAS are analyzed using PFAS protocols typically with liquid chromatography tandem mass spectrometry (LC-MS/MS) quantification. To get a better overview of the amount of “total PFAS,” we applied sum parameter methods based on combustion ion chromatography (CIC) to screen the PFAS contaminations in various sewage sludge and wastewater-based fertilizers. Furthermore, current decontamination strategies of PFAS-burdened soils mainly consist of adsorption methods using adsorbents for fixation of PFAS in the ground. A second option is the utilization of a “pump and treat” process, cycling polluted soils through a washing plant leading to the concentration of the pollutants in the fine fraction. Only a subsequent, high-energy consuming pyrolysis process guarantees the total destruction of all fluorinated organic contaminants. Both approaches are cost-intensive and not intended for the direct decomposition of all PFAS contaminants. Hence, there is a great demand for innovative developments and chemical treatment technologies, dealing with new strategies of tackling the PFAS problem.
Per- and polyfluoroalkyl substances (PFAS) are chemicals which were developed to improve humanity’s quality of life. Due to their high chemical stability and resistance to degradation by heat or acids, PFAS were used in a variety of consumer products. The continuous use of PFAS in household products and the discharge of PFAS from industrial plants into the sewer system resulted in the contamination of effluents and sewage sludge from wastewater treatment plants (WWTPs) (Roesch et al. 2022). Since sewage sludge is often used as fertilizer, its application on agricultural soils has been observed as a significant entry path for PFAS into the environment, specifically in our food chain. In Germany the sewage sludge/biosolid application on agricultural land was banned with the amendment of the German Sewage Sludge Ordinance and by 2029 sewage sludge application will be totally prohibited. However, phosphorus (P) from sewage sludge should still be recycled in WWTPs of cities with a population larger than 50,000 residents. To produce high-quality P-fertilizers for a circular economy, PFAS and other pollutants (e.g. pesticides and pharmaceuticals) must be separated from sewage sludge. Due to the strong diversity of industrial PFAS usage it is not clear if a safe application of novel recycled P-fertilizers from WWTPs can be guaranteed. Therefore, we analyzed various sewage sludges and wastewater-based fertilizers. Sewage sludge (SL) samples from various WWTPs in Germany and Switzerland, six sewage sludge ashes (SSA) from Germany, six thermally treated SL and SSA samples with different additives (temperatures: 700-1050 °C), two pyrolyzed SL samples (temperature: 400 °C) and two struvite samples from Germany and Canada were analyzed. The goal was to quantify PFAS in sewage sludges and wastewater-based P-fertilizers with the sum parameter extractable organic fluorine (EOF) by combustion ion chromatography (CIC). The results were compared with data from classical LC-MS/MS target analysis as well as selected samples by HR-MS suspect screening. The EOF values of the SLs mainly range between 154 and 538 µg/kg except for one SL which showed an elevated EOF value of 7209 µg/kg due to high organofluorine contamination. For the SSA samples the EOF values were lower and values between LOQ (approx. 60 µg/kg) and 121 µg/kg could be detected. For the pyrolyzed SLs no EOF values above the LOQ were detected. Moreover, the two wastewater-based struvite fertilizers contain 96 and 112 µg/kg EOF, respectively. In contrast to the EOF values, the sum of PFAS target values were relatively low for all SLs. Additional applied PFAS HR-MS suspect screening aimed to tentatively identify PFAS that could contribute to the hitherto unknown part of the EOF value. The majority of the detected fluorinated compounds are legacy PFAS such as short- and long-chain perfluorocarboxylic acids (PFCA), perfluorosulfonic acids (PFSA), polyfluoroalkyl phosphate esters (PAPs) and perfluorophosphonic acids (PFPA). Moreover, fluorinated pesticides, pharmaceutical as well as aromatic compounds were also identified, which are all included in the EOF parameter. Our research revealed that the current PFAS limit of 100 µg/kg for the sum of PFOS + PFOA in the German Fertilizer Ordinance is no longer up to date. Since the number of known PFAS already exceeds 10,000, the ordinance limit should be updated accordingly. Recent regulations and restrictions on using long-chain PFAS (≥C8) have resulted in a significant shift in the industry towards (ultra-)short-chain alternatives, and other, partly unknown, emerging PFAS. Ultimately, also fluorinated pesticides and pharmaceuticals, which end up as ultrashort PFAS in the WWTPs, have to be considered as possible pollutants in fertilizers from wastewater, too.