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In urban waters, a multitude of organic micropollutants, often termed emerging pollutants, has been found over the last decades. Analytical methods suitable for trace analysis are needed that are desirably also fast, inexpensive and, if possible, robust and portable. Immunoanalytical, i.e., antibody-based, methods which are available in a broad range of formats, can be profitably used here to screen for the distribution and to monitor the trends of concentration levels of contaminants of emerging concern in the environment. Some of these formats are single-analyte but high-throughput methods. To use them wisely, indicator substances, sometimes called anthropogenic markers, should be selected and used in screening approaches, i.e., as indicators for contamination and the pre-selection of samples at which to have a closer look by multiplex methods like LC-MS/MS. Other methods are suitable to be performed on portable instrumentation in the field (on-site) or in facilities such as wastewater treatment plants for on-line monitoring of the treatment and elimination process. Furthermore, array technologies have been established that allow for parallel (multiplex) analysis of several analytes of interest.
The microtiter-plate based ELISA (Enzyme-linked Immunosorbent Assay) is the method of choice for the analysis of a large number of samples [1]. ELISAs are available to monitor for anthropogenic markers such as the antiepileptic carbamazepine, the analgesic diclofenac, the antihistaminic cetirizine, the steroid hormone estrone, the antimicrobial sulfamethoxazole, psychoactive caffeine and cocaine, the priority pollutant bisphenol A, and the bile acid isolithocholic acid. For on-site screening and monitoring, simpler formats, like mix-and-read assays, e.g., the Fluorescence Polarization Immunoassay (FPIA) [2] or Lateral-flow Immunoassays (LFIA) [3] are more suitable tools, the latter based on dipsticks or little cassettes, with which users have become very familiar during the COVID-19 pandemic via rapid antigen tests. The suitability of multi-analyte formats such as immunomicroarrays depends on the choice of a signal-producing system that provides small uncertainties and good reproducibility of the measurements. Bead-based (“suspension”) arrays, read out in flow cytometers, are a powerful platform for multiplex assays [4]. Electrochemical formats, run on portable devices, provide additional advantages as no light source is required. They are most promising for stand-alone analysers and biosensors [5].
The speed, low cost and on-site capabilities of these methods allow to gather a lot more data on anthropogenic compounds which enables to quantify inputs, differences in degradation power of elimination processes, dilution phenomena and a more precise image of individual water cycles which is demonstrated by several examples.
Immunoanalytical Techniques, i.e., antibody-based analytical methods, have been used for decades in clinical diagnostics. What makes them attractive for other fields of application is their short time-to-result and high sensitivity. Microplate-based assays such as ELISA have been adopted early in environmental and food analysis. Yet, to make immunoassays even faster, more sensitive, robust, and, most desirable, portable, advanced materials, sometimes developed for other purposes, can be profitably used to achieve these goals. Materials can be novel labels, e.g., chemical or particle labels, such as fluorophores or nanoparticles. Carrier particles, such as magnetic or polymer beads, make it possible to adopt the assays to meso- or microfluidic set-ups and encoding them opens the path to multiplex analysis. Specialty electrodes can enable for higher sensitivity in electrochemical detection. All this broadens the scope of application and lowers effort and cost for analysis at the point-of-need.
A vast number of emerging pollutants is being detected in the environment. Another lingering problem are health-threatening contaminants, such as mycotoxins, that deteriorate food and feed, and the pathogens themselves. Analytical methods, suitable for trace analysis, are needed that are desirably also fast, inexpensive and, if possible, robust and portable. It is set out, how immunoana-lytical, i.e., antibody-based methods, which are elaborated in a broad range of formats, can be profitably used to gain insights on the distribution and concentration trends of the target analytes at the point-of-need.
Estrogens are endocrine disrupting chemicals and of high concerns due to demonstrated harmful effects on the environment and low effect levels. For monitoring and risk assessment, several estrogens were included in the "watch list" of the EU Water Framework Directive which sets very low environmental quality standard (EQS) levels for Estrone (E1) and 17β-Estradiol (E2) of 0.4 ng L−1 and for 17α-Ethinylestradiol (EE2) of 0.035 ng L−1 requiring sensitive detection methods, as well as extensive sample preparation. A sensitive, derivatization-free, isotope dilution calibration HPLC-MS/MS method for a panel of 5 selected estrogens (including the 3 estrogens of the EU WFD watchlist), and a procedure for the reproducible preparation of a representative whole water matrix including mineral water, humic acids and solid particulate matter are presented. These are used in a diligent comparison of classical solid phase extraction (SPE) on hydrophilic-lipophilic balanced (HLB) phase to SPE on an estrogen-specific molecularly imprinted polymer phase (MISPE) for ultra-trace levels of the analytes (1–10 ng L−1). Additionally, a two-step procedure combining HLB SPE disks followed by MISPE is evaluated. The tow-step procedure provides superior enrichment, matrix removal and sample throughput while maintaining comparable recovery rates to simple cartridge SPE. Estimated method quantification limits (MQLs) range from 0.109–0.184 ng L−1 and thus meet EQS-levels for E1 and E2, but not EE2. The representative whole water matrix provides a reproducible comparison of sample preparation methods and lays the foundation for a certified reference material for estrogen analysis. The presented method will serve as the basis for an extended validation study to assess its use for estrogen monitoring in the environment.
Bisphenol A (BPA) is widely used in many Polymers. Many outdoor applications are made from BPA-based materials which are exposed to a variety of environmental impacts, like temperature, solar radiation, rain, and others. This could lead to damaging and aging of the material which might cause leaching or migration of pollutants into the environment. To understand the fate and behavior different transformation products of selected Bisphenols will be generated and analyzed.
Bisphenol A (BPA) is widely used in Polycarbonate (PC), Polyacrylic resins (PAR), Polysulfones (PSU), Epoxy resins (ER), and Polyetherimides (PEI). It is also used in recycled Polyvinyl chloride (PVC) [1–3]. These BPA-containing materials have a wide area of application, especially outside. All outdoor applications are exposed to a variety of environmental impacts, like temperature, solar radiation (physical influences), chemical influences (rain or ozone), biological influences (microorganisms), and mechanical influences (hail, sand). These impacts are damaging and aging the material which can be followed by leaching or migration of pollutants like Bisphenol A into the environment. Understanding the fate and behavior of the released pollutants is very important. Therefore, different transformation products of selected Bisphenols will be generated and analyzed.
Contamination of the environment with antibiotics is of great concern as it promotes the evolution of antimicrobial resistances. In case of amoxicillin (AMX) in the aquatic environment, further risk arises from hydrolysis products (HPs) which can cause allergy. To assess these risks, a comprehensive investigation and understanding of the degradation of AMX is necessary. We investigated the hydrolysis rate of AMX in different types of water as well as the influence of temperature and irradiation. The content of the heavy metal ions copper and zinc was found to be crucial for the hydrolysis rate of AMX and stability of HPs. Eventually, a new degradation pathway for AMX could be elaborated and confirmed by tandem mass spectrometry (LC-MS/MS).
Contamination of drinking water with pharmaceuticals is an emerging problem and a potential health threat. Immunochemical methods based on the binding of the analyte to specific antibodies enable fast & cost-effective on-site analyses. Magnetic bead-based immunoassays (MBBAs) allow for implementation into an immunosensor for online testing. Particles are prepared by either coupling the analyte molecule (diclofenac) or the respective antibody (amoxicillin) to the surface. For miniaturization, detection is performed electrochemically (chronoamperometry) on a microfluidic chip. The developed immunosensor will enable detection of pharmaceuticals directly in water supply pipes.
Contamination of drinking water with pharmaceuticals is an emerging problem and a potential health threat. Immunochemical methods based on the binding of the analyte to specific antibodies enable fast & cost-effective on-site analyses. Magnetic bead-based immunoassays (MBBAs) allow for implementation into an immunosensor for online testing. Particles are prepared by either coupling the analyte molecule (diclofenac) or the respective antibody (amoxicillin) to the surface. For miniaturization, detection is performed electrochemically (chronoamperometry) on a microfluidic chip. The developed immunosensor will enable detection of pharmaceuticals directly in water supply pipes.
Contamination of drinking water with pharmaceuticals is an emerging problem and a potential health threat. Immunochemical methods based on the binding of the analyte to specific antibodies enable fast & cost-effective on-site analyses. Magnetic bead-based immunoassays (MBBAs) allow for implementation into an immunosensor for online testing. Particles are prepared by either coupling the analyte molecule (diclofenac) or the respective antibody (amoxicillin) to the surface. For miniaturization, detection is performed electrochemically (chronoamperometry) on a microfluidic chip. The developed immunosensor will enable detection of pharmaceuticals directly in water supply pipes.
Portable, antikörperbasierte Analysenverfahren für die Schadstofferfassung im Wasserkreislauf
(2021)
Die Wasseranalytik wird bestimmt von zwei Hauptbedarfen, einerseits der Erfassung der Gewässergüte und Grundwassergüte als Basis für die Bereitstellung einwandfrei-en Trinkwassers und zum anderen des Monitorings der Wasserqualität in den Prozes-sen der Wasseraufbereitung und der Abwasserreinigung. Für beide Anwendungsbe-reiche ist eine laborbasierte Analytik eher hinderlich, werden die Analysenergebnisse doch eigentlich vor Ort benötigt, um etwa Beprobungskampagnen rasch anpassen zu können. Desweiteren werden die Daten auch schnell benötigt, um zeitnah in die technischen Prozesse einzugreifen. Organische Kontaminanten werden meist über chromatographische Verfahren, häufig gekoppelt mit einer massenspektrometrischen Detektion, in instrumentelle Labormethoden erfasst und die hochauflösende Massen-spektrometrie und die Non-target-Analytik haben viel zum Wissen über das Vorkom-men, insbesondere von sog. „emerging contaminants“, beigetragen, sowie zum Ver-ständnis der beteiligten Eintragspfade und Abbauwege. Moderne, portable Analy-senmethoden und insbesondere Sensoren werden zukünftig aber ihren Platz in der Schadstofferfassung im Wasserkreislauf einnehmen. Dies gilt insbesondere für anti-körperbasierte Analysenverfahren, da erst diese oft die nötige Selektivität und Sensitivität in die Detektionsmethoden einbringen.
A vast number of emerging pollutants has been detected in the environment over the last decades. Analytical methods suitable for trace analysis are needed that are desirably also fast, inexpensive and, if possible, robust and portable. Immunoanalytical, i.e. antibody-based, methods which are available in a broad range of formats, can be profitably used here to analyse for the distribution and the trends of concentration levels of contaminants in the environment. Some of these formats are single-analyte but high-throughput methods. In order to use them wisely, indicator substances, sometimes called anthropogenic markers, should be selected and used in screening approaches. Other methods are suitable to be performed on portable instrumentation in the field (on-site) or in facilities such as wastewater treatment plants for on-line monitoring. Furthermore, there are array technologies that allow for parallel (multiplex) analysis of several analytes of interest.
The microtiter-plate based ELISA (Enzyme-linked Immunosorbent Assay) is the method of choice for the analysis of a large number of samples [1]. ELISAs are available to monitor for anthropogenic markers such as the antiepileptic carbamazepine, the analgesic diclofenac, the antihistaminic cetirizine, the steroid hormone estrone, the antimicrobial sulfamethoxazole, the stimulants caffeine and cocaine, the priority pollutant bisphenol A, and the bile acid isolithocholic acid. For on-site screening and monitoring, simpler formats, like mix-and-read assays, e.g. the Fluorescence Polarization Immunoassay (FPIA) [2] or Lateral-flow Immunoassays (LFIA) [3] are more suitable tools, the latter based on dipsticks or cassettes, that is why they are also called pregnancy test-like assays. The suitability of multi-analyte formats such as immunomicroarrays depends on the choice of a signal-producing system that provides small uncertainties and good reproducibility of the measurements. Bead-based (“suspension”) arrays read out in flow cytometers are a powerful platform for multiplex assays [4]. Electrochemical formats run on portable devices provide additional advantages as no light source is required. They are most promising for stand-alone analysers and biosensors
Portable, antikörperbasierte Analysenverfahren für die Schadstofferfassung im Wasserkreislauf
(2021)
Die Wasseranalytik wird bestimmt von zwei Hauptbedarfen, einerseits der Erfassung der Gewässergüte und Grundwassergüte als Basis für die Bereitstellung einwandfreien Trinkwassers und zum anderen des Monitorings der Wasserqualität in den Prozessen der Wasseraufbereitung und der Abwasserreinigung. Für beide Anwendungsbereiche ist eine laborbasierte Analytik eher hinderlich, werden die Analysenergebnisse doch eigentlich vor Ort benötigt, um etwa Beprobungskampagnen rasch anpassen zu können. Des Weiteren werden die Daten auch schnell benötigt, um zeitnah in die technischen Prozesse einzugreifen. Organische Kontaminanten werden meist über chromatographische Verfahren, häufig gekoppelt mit einer massenspektrometrischen Detektion, in instrumentellen Labormethoden erfasst, und die hochauflösende Massenspektrometrie und die Non-target-Analytik haben viel zum Wissen über das Vorkommen, insbesondere von sogenannten „Emerging Contaminants“, beigetragen, sowie zum Verständnis der beteiligten Eintragspfade und Abbauwege. Moderne, portable Analysenmethoden und insbesondere Sensoren werden zukünftig aber ihren Platz in der Schadstofferfassung im Wasserkreislauf einnehmen. Dies gilt insbesondere für antikörperbasierte Analysenverfahren, da erst diese oft die nötige Selektivität und Sensitivität in die Detektionsmethoden einbringen.
A vast number of emerging pollutants is being detected in the environment. Another lingering problem are health-threatening contaminants, such as mycotoxins, that deteriorate food and feed.
Analytical methods, suitable for trace analysis, are needed that are desirably also fast, inexpensive and, if possible, robust, and portable. Immunoanalytical, i.e., antibody-based methods, which are available in a broad range of formats, can be profitably used here to analyze for the distribution and the concen-tration trends of contaminants.
Some of these formats are single-analyte but high-throughput methods. To use them wisely, indicator substances or sum parameters are being established and used in screening approaches. Other methods are suitable to be performed on portable instrumentation in the field (on-site), more precisely at the point-of-need. Furthermore, there are array technologies that allow for parallel analysis of several analytes of interest (multiplexing).
The talk reports on methods and data for compounds considered as anthropogenic contamination markers (the antiepileptic carbamazepine, the analgesic diclofenac, the anti-histaminic cetirizine, the steroid hormone estrone, the antimicrobial amoxicillin, the stimulants caffeine and cocaine, the endo-crine disruptor bisphenol A, and a bile acid). Some work on mycotoxins (ochratoxin A and ergot alka-loids) is also presented. It is demonstrated that antibody-based approaches have a huge potential to gain analytical insights at the point-of-need.
Antibody-based analytical techniques have gained increasing importance in environmental analysis. Rapid assays, portable devices and formats that require a limited number of steps have a high potential for on-site analysis in outdoor environments or in environmentally relevant facilities such as wastewater treatment plants. Many of these methods have become more sensitive and more versatile due to new, advanced materials, such as novel particles, specifically prepared surfaces, new labels, specifically coated electrodes etc. The talk shows some of our works in this context.
A vast number of emerging pollutants is being detected in the environment. Another lingering problem are health-threatening contaminants, such as mycotoxins, that deteriorate food and feed.
Analytical methods, suitable for trace analysis, are needed that are desirably also fast, inexpensive and, if possible, robust, and portable. Immunoanalytical, i.e., anti-body-based technologies, which are available in a broad range of formats, can be profitably used here to analyze for the distribution and the concentration trends of contaminants.
Some of these formats are single-analyte but high-throughput methods. To use them wisely, indicator substances or sum parameters must be established to be used in screening approaches. Other methods are suitable to be performed on portable in-strumentation in the field (on-site), more precisely at the point-of-need. Furthermore, there are array technologies that allow for parallel analysis of several analytes of interest (multiplexing). The talk reports on methods and data for compounds con-sidered as anthropogenic contamination markers (the antiepileptic carbamazepine, the analgesic diclofenac, the anti-histaminic cetirizine, the steroid hormone estrone, the antimicrobial amoxicillin, the stimulants caffeine and cocaine, the endocrine disruptor bisphenol A, and a bile acid). Some work on mycotoxins (ochratoxin A and ergot alkaloids) is also presented. It is demonstrated that antibody-based technolo-gies have a huge potential to gain analytical insights at the point-of-need.
Warfarin ist seit den 1950er Jahren einer der bekanntesten Gerinnungshemmer. Beim Menschen wird es bis heute zur Vorbeugung von Thrombose und der Behandlung von Vorhofflimmern und Arrhythmie eingesetzt. Doch schon einige Jahre vor der FDA Zulassung (U. S. Food and Drug Administration) als Medikament wurde es zur Bekämpfung von Nagetieren eingesetzt. Bis heute wurde es nur teilweise durch weitaus wirksamere antikoagulante Rodentizide (ARs) der zweiten Generation, sogenannte Superwarfarine, ersetzt. In der Fachliteratur finden sich zahlreiche Beispiele für sekundäre und tertiäre Vergiftung mit ARs bei Wildtieren und anderen Nichtzieltieren. Bisher ist relativ wenig über die Bioakkumulation, Persistenz und Toxizität von ARs und deren Transformationsprodukten (TPs) in der terrestrischen und aquatischen Umwelt, sowie der Nahrungskette bekannt.
Um Einblicke in mögliche Transformations- und Abbauprozesse von Warfarin unter umweltrelevanten Bedingungen zu erhalten und um diese Einflüsse zu simulieren, wurde hierzu eine elektrochemische Reaktorzelle in Kopplung mit einem Massenspektrometer verwendet. So können mögliche Phase-I-Metabolite und sogenannte „oxidation products“ vorausgesagt werden. Hinsichtlich des Verhaltens während der Wasseraufbereitung in Kläranlagen wurden technisch relevante Prozesse wie Chlorung, UV-Bestrahlung und Ozonung in Modellen simuliert, um hier potenzielle Abbauwege und -prozesse aufzuklären. Gebildete Transformationsprodukte wurden daher mittels unterschiedlicher chromatografischer Verfahren getrennt und massenspektrometrisch identifiziert, charakterisiert und verglichen.
Contamination of drinking water with pharmaceuticals is an emerging problem and a potential health threat. Immunochemical methods based on the binding of the analyte to specific antibodies enable fast & cost-effective on-site analyses. Magnetic bead-based immunoassays allow for implementation into an immunosensor for online testing. Particles are prepared by either coupling the analyte molecule (diclofenac) or the respective antibody (amoxicillin) to the surface. For miniaturization, detection is performed electrochemically (chronoamperometry) on a microfluidic chip. The developed immunosensor will enable detection of pharmaceuticals directly in water supply pipes.
Contamination of drinking water with pharmaceuticals is an emerging problem and a potential health threat. Immunochemical methods based on the binding of the analyte to specific antibodies enable fast and cost-effective on-site analyses. Magnetic bead-based immunoassays allow for implementation into an immunosensor for online testing. These particles are prepared by either coupling the analyte molecule (diclofenac) or the respective antibody (amoxicillin) to the surface. For miniaturization, detection is performed electrochemically on a microfluidic chip. The developed immunosensor will enable detection of pharmaceuticals directly in water supply pipes.
Metrology for Monitoring of Endocrine Disrupting Chemicals Under the EU Water Framework Directive
(2021)
Monitoring programs should generate high-quality data on the concentrations of substances and other pollutants in the aquatic environment to enable reliable risk assessment. Furthermore, the need for comparability over space and time is critical for analysis of trends and evaluation of restoration of natural environment. Additionally, research work and exercises at the European level have highlighted that reliable measurements of estrogenic substances especially three estrogens of the first watch list (17-beta-estradiol (17βE2), 17-alpha-ethinylestradiol (EE2), and estrone (E1))at the PNEC level are still challenging to achieve.With respects to their physicochemical properties, the 3 substances have the potential to disseminate within aquatic environments, to enter the food chain and to bioaccumulate, Chemical monitoring relies on a succession of actions: sampling, storage and preservation of representative samples; pre-treatment of a sample portion for quantification, calibration, final determination, calculation of results, uncertainty estimation and final expression of results. Throughout this chain of operations, the guarantee of the stability of the analyte is a key issue that has to be addressed to correctly qualify and discuss monitoring data.
The project EDC-WFD aims to develop traceable analytical methods for determining endocrine disrupting compounds and their effects, with a specific focus on three estrogens of the first watch. Environmental quality standards (EQS) for these compounds are at the ultra-trace level (EQS EE2 = 35 pg/L, EQS E2 = 400 pg/L, EQS E1 = 3600 pg/L) and pose a significant challenge to analytical methods. Estrogens 17-alpha-estradiol (17αE2) and estriol (E3) will be included to demonstrate the reliability of the developed methods and to support the requirements of Directive 2013/39/EC, Directive 2009/90/EC and Commission Implementation Decision (EU) 2018/840, hence improving the comparability and compatibility of measurement results within Europe. The project will also evaluate the interaction and partitioning of the 5 estrogenic compounds between water samples and suspended particulate matter (SPM) and the capability of developed methods to address the different fractions of matrix (whole water and dissolved concentrations of estrogens).
This contribution will present the objectives and methods applied within the EDC-WFD project that could support a better comprehension of the biogeochemical cycle of selected estrogenic substances in aquatic system
Funding: This project (18NMR01) has received funding from the EMPIR programme co-financed by the Participating States and from the European Union's Horizon 2020 research and innovation programme
Monitoring programs should generate high-quality data on the concentrations of substances and other pollutants in the aquatic environment to enable reliable risk assessment. Furthermore, the need for comparability over space and time is critical for analysis of trends and evaluation of restoration of natural environment. Additionally, research work and exercises at the European level have highlighted that reliable measurements of estrogenic substances at the PNEC level are still challenging to achieve.
The project EDC-WFD Metrology for monitoring endocrine disrupting compounds under the EU Water Framework Directive aims to develop traceable analytical methods for determining endocrine disrupting compounds and their effects, with a specific focus on three estrogens of the first watch list (17-beta-estradiol (17βE2), 17-alpha-ethinylestradiol (EE2), and estrone (E1)). Estrogens 17-alpha-estradiol (17αE2) and estriol (E3) will be included to demonstrate the reliability of the developed methods and to support the requirements of Directive 2013/39/EC, Directive 2009/90/EC and Commission Implementation Decision (EU) 2018/840, hence improving the comparability and compatibility of measurement results within Europe. During the EDC-WFD project four selected effect-based methods (EBM) will be deeply investigated in order to improve their rationale use and their support in water quality assessment. In particular, the EBM sensitivity, specificity and accuracy on reference materials with single or mixture solutions of the five substances at a concentration of EQS values will be explored.
This project (18NMR01) has received funding from the EMPIR programme co-financed by the Participating States and from the European Union's Horizon 2020 research and innovation programme.
Herein, we present liquid and gas chromatographic methods coupled with
(high-resolution) mass spectrometry for the analysis of warfarin’s TPs.
Methodologies such as UV-irradiation, ozonation, and chlorination were
utilized to simulate primarily technical water treatment, as well as, abiotic transformation processes. Examination of resulting compounds by numerous analytical methods has provided first insights into a multitude of formed substances. Moreover, the oxidative phase I metabolism was mimicked by an electrochemical flow cell with the aim to synthesize and confirm major metabolic products via a nonbiologically mediated process. The further aim is the toxicological assessment of relevant TPs, as well as, the quantification of warfarin and its TPs under environmentally relevant conditions employing the introduced methodologies.
Sediments and soils can act as sinks of species of inorganic mercury (Hg2+), while they are simultaneously sources of volatile (Hg0) and organic species, such as monomethylmercury (MMHg). Although the fraction of MMHg in total Hg of sediments is suggested to be as low as 0.1 1%, MMHg is a serious threat for humans and wildlife due to its high potential for bioaccumulation and biomagnification and the ability to pass the blood-brain barrier. This is highlighted by exceptionally high MMHg concentrations found in fish and fish predators, as well as aquatic insects and birds living in close vicinity to Hg contaminated waterbodies. Humans are exposed to MMHg mainly by ingestion of (predatory) fish and rice.
One example of a highly Hg contaminated waterbody is Finow Canal, the oldest artificial waterway still in operation in Germany, with Hg mass fractions of up to or even more than 100 µg/g found in the sediment, which are suggested to be attributable to a chemical plant producing (among other things) mercury-based seed dressings. Despite this high mass fraction of Hg, anaerobic conditions, high amounts of organic matter and iron, which are all favorable for Hg methylation, no investigations of Hg speciation have been conducted there up to now.
We investigated Hg speciation in sediments of Finow Canal on length from before the known polluted sited into the confluence with another waterway using species-specific isotope dilution (SSID) GC-ICP-ToF-MS. Mass fraction of up to 41 ng/g MMHg were determined in samples taken from Finow Canal and elevated concentrations could also be found around 14 km downstream of the confluence of Finow Canal with another waterway. In addition to this, highly toxic monoethylmercury (EtHg) could be detected in most of the sediment samples. These results are the first evidence of the occurrence of MMHg in this region and show the need for further investigation of the whole regional ecosystem, as well as the consideration of possible measures of remediation.
Der Bedarf nach schnellen und kostengünstigen Analysemethoden in der (Trink-)Wasseranalytik steigt mit dem zunehmenden Eintrag pharmazeutisch aktiver Substanzen in die Umwelt.
Insbesondere die Kontamination mit Antibiotika erscheint neben ökotoxikologischen Effekten vor allem in Hinblick auf die Evolution resistenter Keime im Wasser besorgniserregend.
Wir berichten hier über die Entwicklung eines magnetpartikelbasierten Immunoassays (MBBA) zur Detektion des Breitbandantibiotikums Amoxicillin (AMX) in Wasserproben, der im Vergleich zum entsprechenden Enzyme-linked Immunosorbent Assay (ELISA) eine wesentlich kürzere Analysendauer sowie einen breiteren Messbereich mit niedrigerer Nachweisgrenze aufweist. Das angewendete Assayprinzip ist dabei leicht auf weitere Analyten übertragbar und ermöglicht die Implementierung in einen Immunosensor.
Die zunehmende Kontamination von (Trink)-Wasser mit pharmazeutischen Rückständen stellt ein potenzielles Gesundheitsrisiko dar und verlangt nach schnellen und zuverlässigen Analysemethoden. Hierbei können antikörper-basierte Methoden helfen, da sie schnelle und kostengünstige Vor-Ort-Messungen sowie Onlineanalysen ermöglichen.
Der Übergang von konventionellen plattenbasierten Formaten, wie ELISA (Enzyme-linked Immunosorbent Assay), zu einem Immunosensor für Online-Messungen wird durch den Einsatz magnetischer Mikropartikel als mobile Messplattform ermöglicht.
Die Partikel werden dazu entweder mit dem Antikörper oder dem Analyten gekoppelt. Diese beiden Strategien werden am Beispiel zweier relevanter Kontaminanten des Wassers gezeigt: Diclofenac (DCF) & Amoxicillin (AMX), und sind leicht auf andere Analyten übertragbar. Die magnetpartikelbasierten Assays (MBBAs) weisen niedrigere Nachweisgrenzen, breitere Messbereiche sowie kürzere Analysezeiten als die entsprechenden ELISAs auf und können in einen Immunosensor mit elektrochemischer Detektion auf einem mikrofluidischen Chip integriert werden.
We present the development of magnetic bead-based immunoassays for two potential contaminants of drinking water: the nonsteroidal anti-inflammatory drug diclofenac and the broad-spectrum antibiotic amoxicillin. For these analytes, different assay formats were developed which can generally be transferred to other analytes. The use of magnetic beads not only enables implementation of the assays into an online system since the beads can be reversibly immobilized by applying a magnetic field. Furthermore, our MBBAs hold several advantages over the conventional ELISAs (enzyme-linked immunosorbent assays) for both analytes, such as lower limits of quantification, shorter assay duration and less washing steps required.
Strategies for the setup and miniaturization of an online immunosensor including electrochemical readout on a microfluidic chip will be discussed.
Warfarin ist seit den 1950er Jahren einer der bekanntesten Gerinnungshemmer. Beim Menschen wird es bis heute zur Vorbeugung von Thrombose und der Behandlung von Vorhofflimmern und Arrhythmie eingesetzt. Doch schon einige Jahre vor der FDA Zulassung (U. S. Food and Drug Administration) als Medikament wurde es zur Bekämpfung von Nagetieren eingesetzt. Bis heute wurde es nur teilweise durch weitaus wirksamere antikoagulante Rodentizide (ARs) der zweiten Generation, sogenannte Superwarfarine, ersetzt.
In der Fachliteratur finden sich zahlreiche Beispiele für sekundäre und tertiäre Vergiftung mit ARs bei Wildtieren und anderen Nichtzieltieren. Bisher ist relativ wenig über die Bioakkumulation, Persistenz und Toxizität von ARs und deren Transformationsprodukten (TPs) in der terrestrischen und aquatischen Umwelt, sowie der Nahrungskette bekannt.
Um Einblicke in mögliche Transformations- und Abbauprozesse von Warfarin unter umweltrelevanten Bedingungen zu erhalten und um diese Einflüsse zu simulieren, wurde hierzu eine elektrochemische Reaktorzelle in Kopplung mit einem Massenspektrometer verwendet. So können mögliche Phase-I-Metabolite und sogenannte „oxidation products“ vorausgesagt werden. Hinsichtlich des Verhaltens während der Wasseraufbereitung in Kläranlagen wurden technisch relevante Prozesse wie Chlorung, UV-Bestrahlung und Ozonung in Modellen simuliert, um hier potenzielle Abbauwege und -prozesse aufzuklären. Gebildete Transformationsprodukte wurden daher mittels unterschiedlicher chromatografischer Verfahren getrennt und massenspektrometrisch identifiziert, charakterisiert und verglichen.
The demand for quick and reliable online sensors is rising not only in the field of environmental analysis with new and diversifying sources of pollution. A major aspect of this is the contamination of (drinking) water with pharmaceuticals representing a potential health threat and requiring timely countermeasures in case of contamination.
In this regard, antibody-based methods can be helpful as they enable fast and cost-effective on-site and potentially online analyses. The transition from the conventional plate-based formats like ELISA (enzyme-linked immunosorbent assay) to an immunosensor fit for online sensing can be achieved by using magnetic microparticles as a mobile sensing platform.
Beads are prepared by either coupling the antibody or the analyte to the surface. Both these strategies are presented using the example of two relevant contaminants in water: diclofenac (DCF) & amoxicillin (AMX), and can be transferred to other analytes.
The developed magnetic bead-based assays (MBBAs) exhibit lower LODs, enhanced sensitivity as well as shorter time of analysis than the respective ELISAs and can be integrated into an immunosensor with electrochemical detection on a microfluidic chip.
EDC WFD project to deliver reliable measurements of estrogens for better monitoring surveys and risk assessments.
Collaboration between National Metrology Institutes and advanced research institutes from 6 European countries A Balance of expertise: development and certification of RM, proficiency tests / interlaboratory comparison design, method development and validation, standardisation A 3 years project: September 2019- August 2022
Strong engagement with stakeholders (Advisory Group)
Herein, we present liquid and gas chromatographic methods coupled to (high-resolution) mass spectrometry for the analysis of warfarin’s transformation products.
Methodologies such as UV-irradiation, ozonation, and chlorination were utilised to simulate technical water treatment. Resulting compounds were elucidated and examined by numerous analytical methods. Moreover, the oxidative phase I metabolism was mimicked by an electrochemical flow cell to synthesise and confirm major metabolites. The further aim is the toxicological assessment of all substances formed, as well as, the quantification of warfarin and its TPs under environmentally relevant conditions employing the introduced methods.
Wir berichten hier über die Entwicklung plattenbasierter Magnetpartikel-Immunoassays für die Bestimmung des Breitbandantibiotikums Amoxicillin und des nicht-steroidalen Antirheumatikums Diclofenac im Trinkwasser. Für die beiden Analyten wurden unterschiedliche Ansätze entwickelt, mit partikelgebundenen Antikörpern für AMX und Analyt-gekoppelten Partikeln für DCF, die die simultane Detektion beider Kontaminanten im nanomolaren Konzentrationsbereich erlauben.
Immunanalytische Bestimmung von β-Lactam-Antibiotika und deren Hydrolyseprodukten im Trinkwasser
(2020)
Die speziellen Herausforderungen der immunanalytischen Bestimmung von β-Lactam-Antibiotika in (Trink-)Wasserproben werden anhand eines neu entwickelten ELISA (enzyme-linked immunosorbent assay) für das Breitbandantibiotikum Amoxicillin diskutiert. Es konnte gezeigt werden, dass die Hydrolyse des Analyten einen positiven Einfluss auf die Erkennung durch den Antikörper hat. Das entsprechende Hydrolyseprodukt, zu dem der Antikörper folglich eine höhere Affinität aufweist, wurde identifiziert und ein entsprechendes Verhalten wurde auch für andere β-Lactam-Antibiotika aus der Gruppe der Penicilline beobachtet. Eine Strategie für die Analyse von Wasserproben hinsichtlich Kontamination mit den hier betrachteten β-Lactamen und deren Hydrolyseprodukten wurde ausgearbeitet.
Mycotoxins are toxic secondary metabolites produced by filamentous fungi. The contamination of mycotoxins in food and feed products has been recognized to be an important safety issue for human and animal health. In the context of food safety, medical herbs nowadays are also considered as potential source of mycotoxins. Considering that mycotoxins are generally stable compounds and could not be destroyed completely during food-processing operations, prevention of contamination is identified as main issue.
Currently, biochemical, and immunochemical methods based on the use of antibodies as a specific recognition bioreagents are increasingly found to be applied in screening. Along with good common enzyme linked immunosorbent assay (ELISA), more and more widely used method is fluorescence polarization immunoassay (FPIA). These methods help to monitor of many toxic substances in large number of samples and carried out quickly, easily, cheaply, and give good results in quantifying the one or more substances. That is why the use of immunochemical methods of analysis, such as ELISA and FPIA, is the most promising for solving this problem.
Thus, the aim of our work is to optimize the determination of mycotoxins by ELISA and FPIA in medical herbs. We selected antibodies and a tracer for the FPIA, then we constructed obtained a calibration curve and determined the sensitivity of this method for the samples in aqueous media. Then, the optimal sample preparation was elaborated: for spiked nuts samples were selected and prepared and a calibration curve was obtained with respect to the matrix effect. After that, the analysis of spiked nuts samples was performed by ELISA and FPIA and the sensitivity of both methods was compared.
Gegenstand der vorzustellenden Arbeiten ist die Prüfung der Umwelt-beständigkeit und -verträglichkeit von Materialien und Produkten hinsichtlich der Emission von potenziellen Schadstoffen in die Umwelt. Hierzu werden chemisch-physikalische Einflüsse (Bewitterung) und mikrobielle Beanspruchungen an Modellmaterialien evaluiert. So werden die Freisetzungsraten von Schadstoffen in Abhängigkeit der Beanspruchung beschrieben. Als Modellmaterialien kommen die Polymere Polystyrol (PS) und Polypropylen (PP) zum Einsatz. Synergistische Effekte der Bewitterungsparameter und der mikrobiologischen Beanspruchung sollen dabei ebenso betrachtet werden, wie die gezielte Alterung. Auch findet eine Beschreibung des Verhaltens der ausgetragenen Schadstoffe (polybromierte Flammschutzmittel) in den Umweltkompartimenten Boden oder Wasser statt. Hier sind mit Hilfe der zu entwickelnden Screening- und non-Target-Analyseverfahren die Transformation und der Metabolismus durch Mikroorganismen zu beschreiben. Aus den Ergebnissen sollen Korrelationen zwischen den künstlichen Alterungsverfahren und realen Szenarien abgeleitet werden.
Warfarin als ein Vertreter der NSO-Hetereozyklen, ist seit den 1950er Jahren einer der bekanntesten Gerinnungshemmer. Beim Menschen wird es bis heute zur Vorbeugung von Thrombose und der Behandlung von Vorhofflimmern und Arrhythmie eingesetzt. Doch schon einige Jahre vor der FDA Zulassung als Medikament wurde es zur Bekämpfung von Nagetieren eingesetzt. Bis heute wurde es nur teilweise durch weitaus wirksamere antikoagulante Rodentizide (ARs) der zweiten Generation, sogenannte Superwarfarine, ersetzt. In der Fachliteratur finden sich zahlreiche Beispiele für sekundäre und tertiäre Vergiftung mit ARs bei Wildtieren und anderen Nichtzieltieren. Bisher ist relativ wenig über die Bioakkumulation, Persistenz und Toxizität von ARs und deren Transformationsprodukten (TPs) in der terrestrischen und aquatischen Umwelt, sowie der Nahrungskette bekannt.
Um Einblicke in mögliche Transformations- und Abbauprozesse von Warfarin zu erhalten und um Umwelteinflüsse zu simulieren, wurde es in einer elektrochemischen Reaktorzelle oxidativ umgesetzt und mittels Massenspektrometrie analysiert. Hinsichtlich der Wasseraufbereitung in Kläranlagen wurden technisch relevante Simulationsverfahren wie Chlorung, UV-Bestrahlung und Ozonung angewendet um potentielle Eliminierungswege aufzuklären. Gebildete Transformationsprodukte wurden daher mittels unterschiedlicher chromatografischer Verfahren getrennt, massenspektrometrisch analysiert und verglichen.
Separation and detection of antioxidants using a graphene based electrochemical sensor platform
(2019)
CVD-Graphene is ideally suited as an active element for electrical and electrochemical sensing platforms, since it provides for high sensitivity and low detection limit. Electrochemical sensors provide a simple way to measure analytes in fluids with high sensitivity without the need for complex instrumentation. Due to These aspects, graphene sensors are interesting for a wide range of applications in bio analytics. Antioxidants are natural or synthetic compounds, which inhibit oxidation processes and hence often find use as preservatives.
It has been suggested that the long-term consumption of diets rich in antioxidants is associated with a lower risk of developing diseases linked to oxidative stress. Gallic acid and ascorbic acid are representatives of antioxidants. We have developed a graphene-based sensor platform to separate and subsequently detect antioxidants. Graphene exhibits low detection limits for ascorbic acid and polyphenols. In this study, the sensing of gallic acid and ascorbic acid on bare CVD graphene in various solvents was investigated by Square Wave Voltammetry. Furthermore, the separation and detection of the bioanalytes by deploying different membranes were evaluated.
Background. Aflatoxin B1 (AFB1) is a toxic low-molecular-weight secondary fungal metabolite produced mainly by Aspergillus flavus and Aspergillus parasiticus not only at pre-harvest time but also at post-harvest stages including storage. AFB1 was classified as a Group I carcinogen by the World Health Organization for Research on Cancer in 1993. AFB1 is able to naturally contaminate medicinal plants and therefore causing serious health issues for humans consuming the related medicine. This study aimed to develop an efficient fluorescence polarization immunoassay (FPIA) and for the first time a rapid (5-10 min), low-cost, and simple membrane-based flow-through immunoassay (MBA) for determination of AFB1 in medical herbs based on a monoclonal antibody.
Methods. Two different techniques for AFB1detection in medical herbs (Herba Orígani vulgáris, Folia Urticae, Fructus Rubi idaei) were developed and compared, namely an easy-to-use semi-quantitative flow-through membrane-based enzyme immunoassay (MBA), and a homogeneous method which needs no separation or washing steps (assay time 10 min), a quantitative fluorescence polarization immunoassay (FPIA).
Results. A cut-off level of the developed MBA can vary wide from 0.8 ppb to 1 ppb. The FPIA method showed a linear working range of 8.6 ppb to 64 ppb, IC50 of FPIA is 24 ppb. The results were in good correlation with the ELISA results (IC50 = 0.1 ppb). LC–MS/MS was used to confirm the results, too.
Conclusion. MBA can be used for a quick on-site AFB1 detection in medical herbs (Herba Orígani vulgáris (Oríganum vulgáre), Folia Urticae (Urtíca dióica), Fructus Rubi idaei (Rúbus idáeus)), the developed test does not require special equipment and is not time-consuming (5-10min), includes several simple steps and can be performed directly on-site. The major advantages of the developed FPIA are its simplicity and suitability for a rapid screening of a large number of samples.
Gegenstand der vorzustellenden Arbeiten ist die Prüfung der Umwelt-beständigkeit und -verträglichkeit von Materialien und Produkten hinsichtlich der Emission von potenziellen Schadstoffen in die Umwelt. Hierzu werden chemisch-physikalische Einflüsse (Bewitterung) und mikrobielle Beanspruchungen an Modellmaterialien evaluiert. So werden die Freisetzungsraten von Schadstoffen in Abhängigkeit der Beanspruchung beschrieben. Als Modellmaterialien kommen die Polymere Polystyrol (PS) und Polypropylen (PP) zum Einsatz. Synergistische Effekte der Bewitterungsparameter und der mikrobiologischen Beanspruchung sollen dabei ebenso betrachtet werden, wie die gezielte Alterung. Auch findet eine Beschreibung des Verhaltens der ausgetragenen Schadstoffe in den Umweltkompartimenten Boden oder Wasser statt. Hier sind mit Hilfe der zu entwickelnden Screening- und non-Target-Analyseverfahren die Transformation und der Metabolismus durch Mikroorganismen zu beschreiben. Aus den Ergebnissen sollen Korrelationen zwischen den künstlichen Alterungsverfahren und realen Szenarien abgeleitet werden.
Zu den letzten beiden Jahrestagungen der GUS wurden Verfahren und Methoden vorgestellt, die es gestatten, den Transfer von Schadstoffen aus Materialien und Produkten in die Umwelt unter umweltrelevanten Bedingungen beschreiben zu können. Dabei lag der Fokus auf den Materialien und der eingesetzten Umweltsimulationen. In einem sich anschließenden Schritt soll nun das Verhalten der freigesetzten organischen Schadstoffe unter den Bedingungen von realen und simulierten Umwelteinflüssen charakterisiert und beschrieben werden. Hier werden im Detail drei potentielle Schadstoffe betrachtet, die Inhaltsstoffe bzw. Additive in den jeweils eingesetzten Materialien sind. Im Falle von Polypropylen (PP) und Polystyrol (PS) handelt es sich um polybromierte Flammschutzmittel BDE 209 (Decabrom-diphenylether, als Einzelsubstanz) und HBCD (Hexabromcyclododecan, als technische Formulierung). Für das eingesetzte Polycarbonat ist BPA (Bisphenol A) als Schadstoff zu definieren, welcher unter umweltrelevanten Bedingungen freigesetzt wird. Im Rahmen der durchzuführenden Arbeiten sollen die aufgeführten prioritären Schadstoffe hinsichtlich möglicher Transformationsprozesse in Umwelt und Klärwerk charakterisiert werden. Die unter den Bedingungen der Ozonung, Chlorierung und UV-Bestrahlung erhaltenen Transformationsprodukte (TPs) sollen im Sinne einer Non-Target-Analytik identifiziert und eindeutig charakterisiert werden. Die Ergebnisse sollen mittels vorhandener Analysenverfahren, wie GC-EI-MS, HPLC-ESI-IT-MSn bzw. LC-MS/MS erzeugt bzw. abgesichert werden. Anhand der in der Struktur eindeutig zu beschreibenden Transformationsprodukte und der Charakterisierung von potentiellen Intermediaten sollen belastbare Reaktionswege und –mechanismen abgeleitet werden.
In addition to previously reported results on the accelerated weathering of polystyrene samples (PS) containing 1 wt.% hexabromocyclododecane (HBCD), we present the first results of our investigations of polypropylene samples (PP) containing 0.1 wt.% BDE-209. All studied polymer samples were exposed to a defined weathering schedule in a climate chamber in accordance to regulation EN ISO 4892-3:2006. For the determination of BDE-209 in the collected raining water the samples were prepared in accordance to a validated protocol. Before the analyses each sample was spiked with isotopically labeled BDE-209. Subsequently the samples were extracted with isooctane. The obtained extracts were concentrated, and the resulting solutions were analyzed by GC/MS. Additionally, the total bromine content was monitored for the weathered and untreated samples using laser ablation inductively coupled plasma mass spectrometry (LA-ICP-MS) and X-ray fluorescence analysis (XRF) as a non-destructive and rapid method. In general, the resulting data from the accelerated weathering will be compared to those from the natural weathering experiments. Here, the surfaces of the test pieces were analyzed by LA-ICP-MS and XRF as well. Moreover, soil bed tests were conducted in a well characterized model soil. This soil (boulder-clay, sand with 12 % loam, particle size in total 0.2-4 mm) is filled in a free-draining basin inside of an air-conditioned cellar. In this manner, TOC, water capacity and humidity are recorded parameters. To induce a leaching process from the samples by the raining water, the target water content is calculated to 8%. The actual humidity is measured by a tensiometer, assuring the duration of the raining period. A defined humidity is a fundamental parameter for a biological activity in the soil. The test polymers were placed up to the half in the soil. Microbial activity of the soil is monitored by a reference polymer (polyurethane) and should induce the release of HBCD and BDE-209 out of the test materials. These released analytes will be captured by passive samplers (silicone tubes) placed in a distinct distance to the polymer samples in the soil. The soil bed experiments are complementary to the weathering experiments due to the biological activity in the soil.
In addition to previously reported results on the accelerated weathering of polystyrene samples (PS) containing 1 wt.% hexabromocyclododecane (HBCD), we present the first results of our investigations of polypropylene samples (PP) containing 0.1 wt.% BDE-209. All studied polymer samples were exposed to a defined weathering schedule in a climate chamber in accordance to regulation EN ISO 4892-3:2006. For the determination of BDE-209 in the collected raining water the samples were prepared in accordance to a validated protocol. Before the analyses each sample was spiked with isotopically labeled BDE-209. Subsequently the samples were extracted with isooctane. The obtained extracts were concentrated, and the resulting solutions were analyzed by GC/MS. Additionally, the total bromine content was monitored for the weathered and untreated samples using laser ablation inductively coupled plasma mass spectrometry (LA-ICP-MS) and X-ray fluorescence analysis (XRF) as a non-destructive and rapid method. In general, the resulting data from the accelerated weathering will be compared to those from the natural weathering experiments. Here, the surfaces of the test pieces were analyzed by LA-ICP-MS and XRF as well. Moreover, soil bed tests were conducted in a well characterized model soil. This soil (boulder-clay, sand with 12 % loam, particle size in total 0.2-4 mm) is filled in a free-draining basin inside of an air-conditioned cellar. In this manner, TOC, water capacity and humidity are recorded parameters. To induce a leaching process from the samples by the raining water, the target water content is calculated to 8%. The actual humidity is measured by a tensiometer, assuring the duration of the raining period. A defined humidity is a fundamental parameter for a biological activity in the soil. The test polymers were placed up to the half in the soil. Microbial activity of the soil is monitored by a reference polymer (polyurethane) and should induce the release of HBCD and BDE-209 out of the test materials. These released analytes will be captured by passive samplers (silicone tubes) placed in a distinct distance to the polymer samples in the soil. The soil bed experiments are complementary to the weathering experiments due to the biological activity in the soil.
Warfarin, also known as Coumadin is one of the most popular anticoagulant drugs used as a therapeutic in humans to prevent thrombosis, atrial fibrosis, and fibrillation since the 1950s. Because of its ability to hinder blood from clotting by blocking vitamin K-depending carboxylation of blood clotting precursors, it is also used as a rodenticide worldwide. Until today it has been partially substituted by far more potent anticoagulant rodenticides (ARs), so-called superwarfarins. There are numerous references confirming secondary and tertiary poisoning in non-target-animals and wildlife like mammals, birds, and fish associated with ARs. Up to now relatively little is known about persistence and toxicity of transformation products of those AR in the environment and food chain. Herein, warfarin was chosen as a model compound to determine andelucidate TPs which are generated technically and under environment-like conditions. Such as the simulation of the oxidative phase I metabolism by implementing electrochemical flow cells coupled to mass spectrometry (MS). Obtained results are being compared to TPs generated by UVB-irradiation and ozonation.
Analysis and separation of degradation products and TPs were achieved by a variety of gas- and liquid chromatographic techniques coupled to (high resolution) MS.
Environmental sustainability and –stability of materials concerning the migration of pollutants
(2019)
In addition to previously reported results on the accelerated weathering of polystyrene samples (PS) containing 1 wt. % hexabromocyclododecane (HBCD), we present the first results of our investigations of polypropylene samples (PP) containing 0.1 wt. % BDE-209. All studied polymer samples were exposed to a defined weathering schedule in a climate chamber in accordance to regulation EN ISO 4892-3:2006. For the determination of BDE-209 in the collected raining water the samples were prepared in accordance to a validated protocol. Before the analyses each sample was spiked with isotopically labeled BDE-209. Subsequently the samples were extracted with isooctane. The obtained extracts were concentrated, and the resulting solutions were analyzed by GC/MS. Additionally, the total bromine content was monitored for the weathered and untreated samples using laser ablation inductively coupled plasma mass spectrometry (LA-ICP-MS) and X-ray fluorescence analysis (XRF) as a non-destructive and rapid method. In general, the resulting data from the accelerated weathering will be compared to those from the natural weathering experiments. Here, the surfaces of the test pieces were analyzed by LA-ICP-MS and XRF as well. Moreover, soil bed tests were conducted in a well characterized model soil. This soil (boulder-clay, sand with 12 % loam, particle size in total 0.2-4 mm) is filled in a free-draining basin inside of an air-conditioned cellar. In this manner, TOC, water capacity and humidity are recorded parameters. To induce a leaching process from the samples by the raining water, the target water content is calculated to 8%. The actual humidity is measured by a tensiometer, assuring the duration of the raining period. A defined humidity is a fundamental parameter for a biological activity in the soil. The test polymers were placed up to the half in the soil. Microbial activity of the soil is monitored by a reference polymer (polyurethane) and should induce the release of HBCD and BDE-209 out of the test materials. These released analytes will be captured by passive samplers (silicone tubes) placed in a distinct distance to the polymer samples in the soil. The soil bed experiments are complementary to the weathering experiments due to the biological activity in the soil.
Monitoring programs should generate high-quality data on the concentrations of substances and other pollutants in the aquatic environment to enable reliable risk assessment. Furthermore, the need for comparability over space and time is critical for analysis of trends and evaluation of restoration of natural environment. Additionally, research work and exercises at the European level have highlighted that reliable measurements of estrogenic substances at the PNEC level are still challenging to achieve. The project EDC-WFD “Metrology for monitoring endocrine disrupting compounds under the EU Water Framework Directive” aims to develop traceable analytical methods for determining endocrine disrupting compounds and their effects, with a specific focus on three estrogens of the first watch list (17-beta-estradiol (17βE2), 17-alpha-ethinylestradiol (EE2), and estrone (E1)). Estrogens 17-alpha-estradiol (17aE2) and estriol (E3) will be included to demonstrate the reliability of the developed methods - Mass Spectrometry based method and effect-based methods (EBM) - and to support the requirements of Directive 2013/39/EC, Directive 2009/90/EC and Commission Implementation Decision (EU) 2018/840, hence improving the comparability and compatibility of measurement results within Europe. During the EDC-WFD project four EBM will be deeply investigated in order to improve their rationale use and their support in water quality assessment.
Monitoring programs should generate high-quality data on the concentrations of substances and other pollutants in the aquatic environment to enable reliable risk assessment. Furthermore, the need for comparability over space and time is critical for analysis of trends and evaluation of restoration of natural environment. Additionally, research work and exercises at the European level have highlighted that reliable measurements of estrogenic substances at the PNEC level are still challenging to achieve. The project EDC-WFD “Metrology for monitoring endocrine disrupting compounds under the EU Water Framework Directive” aims to develop traceable analytical methods for determining endocrine disrupting compounds and their effects, with a specific focus on three estrogens of the first watch list (17-beta-estradiol (17βE2), 17-alpha-ethinylestradiol (EE2), and estrone (E1)). Estrogens 17-alpha-estradiol (17aE2) and estriol (E3) will be included to demonstrate the reliability of the developed methods - Mass Spectrometry based method and effect-based methods (EBM) - and to support the requirements of Directive 2013/39/EC, Directive 2009/90/EC and Commission Implementation Decision (EU) 2018/840, hence improving the comparability and compatibility of measurement results within Europe. During the EDC-WFD project four EBM will be deeply investigated in order to improve their rationale use and their support in water quality assessment.
Monitoring programs should generate high-quality data on the concentrations of substances and other pollutants in the aquatic environment to enable reliable risk assessment. Furthermore, the need for comparability over space and time is critical for analysis of trends and evaluation of restoration of natural environment. Additionally, research work and exercises at the European level have highlighted that reliable measurements of estrogenic substances at the PNEC level are still challenging to achieve. The project EDC-WFD “Metrology for monitoring endocrine disrupting compounds under the EU Water Framework Directive” aims to develop traceable analytical methods for determining endocrine disrupting compounds and their effects, with a specific focus on three estrogens of the first watch list (17-beta-estradiol (17βE2), 17-alpha-ethinylestradiol (EE2), and estrone (E1)). Estrogens 17-alpha-estradiol (17aE2) and estriol (E3) will be included to demonstrate the reliability of the developed methods - Mass Spectrometry based method and effect-based methods (EBM) - and to support the requirements of Directive 2013/39/EC, Directive 2009/90/EC and Commission Implementation Decision (EU) 2018/840, hence improving the comparability and compatibility of measurement results within Europe. During the EDC-WFD project four EBM will be deeply investigated in order to improve their rationale use and their support in water quality assessment.
Regardless of its ban in agricultural use, the triazine derivative terbutryn is still used as a biocide against biofouling in building materials, such as façade colors and roof tiles. From there, it is washed off and may contaminate soil and surface waters, where it shows ecotoxicological behavior. For understanding of these leaching processes, analytical methods that can detect terbutryn in traces are necessary. In contrast to separation methods (Gas (GC) or liquid chromatography (LC)) coupled to mass spectrometry (MS), enzyme immunoassays (EIAs) have proven to be adequate tools for environmental monitoring. Compared to GC-or LC-MS, they are cheap, require only limited time and experimental expertise and enable high throughput. For quantification of terbutryn, EIAs have been established, with a limit of detection (LOD) of 50 ng L-1. For leaching experiments however, a lower LOD would be advantageous.
For detection of terbutryn we developed a direct competitive ELISA based on a monoclonal antibody: Terbutryn and an enzyme-terbutryn conjugate (“tracer”) compete for the binding sites of the immobilized antibody. The bound tracer converts a colourless substrate into a blue-coloured product, which can be detected via spectrophotometry. For quantification of terbutryn, a sigmoidal calibration curve is used. For establishing of the EIA, a new tracer based on a terbutryn surrogate (“hapten”) was synthesized. After optimization of the experimental conditions, the immunoassay exhibited a more than ten-fold increased sensitivity (LOD: 3 ng L-1), high stability against sample compounds (Ca2+, NaCl) and lower cross-reactivities against structurally related compounds, than reported before. Analysis of spiked samples was possible with high precision (inter-assay CV: < 10 %) and accuracy (recoveries from spiked samples: 89 % ± 10%). We therefore propose it as quick and reliable method for leaching studies of terbutryn out of building materials.
Herein we present the data for a newly developed immunoassay for the determination of amoxicillin (AMX) in water samples using a commercially available monoclonal anti-AMX antibody. During optimization and testing of the assay, we observed a significant decrease of the C-value (IC50) of the ELISA calibration curves with aged standard solutions. Running the assay with standard solutions of synthesized AMX hydrolysis products revealed that this decreased C-value could be attributed mainly to the hydrolysis product amoxicilloic acid. Therefore, the limit of detection of the ELISA for AMX determination in water could be enhanced by either hydrolyzing the samples or testing for amoxicilloic acid as marker substance.
Herein, we present the development of a gas chromatographic method for Determination of warfarin, its TPs, and selected metabolites.
TPs were formed by applying UV-irradiation, ozonation, and an electrochemical cell coupled to mass spectrometry to mimic the oxidative phase I metabolism. The further aim is to use this method for detection and quantification under environmentally relevant conditions, as well as, toxicological assessment.