Analytische Chemie
Filtern
Erscheinungsjahr
- 2022 (35) (entfernen)
Dokumenttyp
- Vortrag (11)
- Zeitschriftenartikel (10)
- Posterpräsentation (10)
- Sonstiges (3)
- Forschungsdatensatz (1)
Schlagworte
- Immunoassay (13)
- Antibody (7)
- Biosensor (5)
- Biosensoren (5)
- SARS-CoV-2 (5)
- Amperometry (4)
- ELISA (3)
- Electrochemistry (3)
- Mass Spectrometry (3)
- Amoxicillin (2)
Organisationseinheit der BAM
- 1.8 Umweltanalytik (35) (entfernen)
Eingeladener Vortrag
- nein (11)
High polarity analyte(s) in aqueous media: determination of L-PFOA and L-PFOS in ground water
(2022)
The CCQM-K156 comparison was coordinated by TUBITAK UME on behalf of the Organic Analysis Working Group (OAWG) of the Comité Consultatif pour la Quantité de Matière (CCQM) for National Measurement Institutes (NMIs) and Designated Institutes (DIs) which provide measurement services in organic analysis under the 'Comité International des Poids et Mesures' Mutual Recognition Arrangement (CIPM MRA).
Perfluoro alkyl substances (PFAS) such as PFOS and PFOA have been used in numerous industrial applications and products. Because of their high stability and resistance to biodegradation, atmospheric photooxidation, direct photolysis and hydrolysis, they are extremely persistent in the environment. The European Union (EU) Water Framework Directive lists PFOS as a priority hazardous substance that poses a significant risk to the aquatic environment. The use of PFOS-containing Aqueous Film-Forming Foams (AFFFs) has been banned since June 2011 in the EU. As relatively water-soluble, effectively non-degradable compounds, PFOS and PFOA migrate to ground water. They are not removed in the conventional drinking water treatment, and therefore cause health risks in polluted areas. The EU Drinking Water Directive and the European Commission has proposed a limit value of 100 ng/L for the sum of 20 PFAS, including PFOS and PFOA.
This study provides the means for assessing measurement capabilities for determination of high polarity measurands in a procedure that requires extraction, clean-up, analytical separation and detection. Successful participation in CCQM-K156 demonstrates measurement capabilities in determining mass fraction of organic compounds, with a molecular mass of 200 g/mol to 700 g/mol, having high polarity pKow -2, in a mass fraction range from 0.5 ng/kg to 500 ng/kg in aqueous media.
Nine NMIs and DIs participated in the CCQM-K156 key comparison. Seven institutes reported their results. SPE was applied in the sample pre-treatment and LC-MS was applied for detection. All participating laboratories applied isotope dilution mass spectrometry (IDMS) techniques for quantification. Participants established the metrological traceability of their results using certified reference materials (CRMs) from NMIs with stated traceability; where commercially available high purity materials were used the purity was determined in-house. The CCQM-K156 results for L-PFOA and L-PFOS range from 2.75 ng/kg to 5.50 ng/kg with a % RSD of 19.5 % for L-PFOA and from 2.04 ng/kg to 4.45 ng/kg with a % RSD of 21.3 % for L-PFOS. The KCRV was assigned using a Hierarchical Bayesian Random Effects Model (HB REM) estimator from the values reported by six of the participants. One participant result of L-PFOS and one result of L-PFOA were excluded from the KCRV for technical reasons. The KCRV was 4.9 ng/kg ± 0.4 ng/kg for L-PFOA and 3.8 ng/kg ± 0.4 ng/kg for L-PFOS. The six institutes that were included in the assignment of consensus KCRV all agreed within their standard uncertainties.
To reach the main text of this paper, click on Final Report. Note that this text is that which appears in Appendix B of the BIPM key comparison database https://www.bipm.org/kcdb/.
The final report has been peer-reviewed and approved for publication by the CCQM, according to the provisions of the CIPM Mutual Recognition Arrangement (CIPM MRA).
The outbreak of SARS-CoV-2 in December of 2019, led to a worldwide still on-going pandemic. Since then, several so-called waves of SARS-CoV-2 infections, a time period with a high and fast rising number of new infections, have occurred all over the world. Classic surveillance approaches are hardly applicable, and further, non-detected cases cannot be covered by them. Wastewater-based Epidemiology (WBE) was proven to be a reliable tool for the prediction of new SARS-CoV-2 infection waves, due to the discharge of virus particles in fecal shedding of infectious people. Until now, for the monitoring of SARS-CoV-2 in wastewater, Polymerase Chain Reaction (PCR) is used as analytical tool. Even though PCR is a highly sensitive analytical tool, is presents several disadvantages, such as the need for trained personnel, specific technical equipment, as well as a difficult performance. An analytical tool, to which these disadvantaged do not apply, are immunoassays. In this work, a sandwich Enzyme-Linked Immunosorbent Assay (ELISA), with the immobilization of the capture antibodies on the surface of a Microtiter Plate (MTP), as well as a sandwich Magnetic Bead-Based Assay (MBBA), with immobilization of the capture antibodies on the surface of Magnetic Beads (MBs), targeting the SARS-CoV-2 N-protein, were developed and optimized. Both assay formats were performed with a colorimetric and chemiluminescent detection. The developed assay is composed of the two monoclonal antibodies (mAb) AH2 and DE6 - which was biotinylated in the course of the work - which bind to two different epitops of the antigen N-protein. As tracer, Neutravidin-HRP was used, which binds, through interaction of the Neutravidin with the biotin, to the mAb DE6-Biotin. The assay development and optimization procedure included the investigation of the surface saturation with the mAb AH2, the concentration and dilution of the mAb DE6-Biotin and Neutravidin-HRP, the ideal MBs, the ideal coating as well as dilution buffers, and the colorimetric and chemiluminescent substrates. For the developed and fully optimized colorimetric ELISA, a test midpoint x0 of 388 μg/L, for the chemiluminsecent ELISA of 371 μg/L, for the colorimetric MBBA of 251 μg/L and for the chemiluminescent MBBA of 243 μg/L was obtained. Validation of the colorimetric MBBA was done by measurement of three wastewater samples collected at the Wastewater Treatment Plant (WWTP) Potsdam. Whilst no N-protein could be detected in the samples, by spiking of the wastewater samples with certain concentrations of the N-protein, 10- to 18-times lower concentrations could be back-calculated, which can be attributed to matrix-effects of the wastewater sample. Next to the matrix-effects, also several other reason exist, why no N-protein could be determined in the samples. Because of that, further investigation of the handling, and the measurement of the wastewater samples, as well as the improvement of the assay sensitivity through further optimization steps or exchange of the antibodies, is still necessary.
Das Ziel der vorliegenden Arbeit war die rekombinante Herstellung der AnFAO in E. coli, welche ursprünglich von A. niger produziert wird, und deren anschließende Anwendung in der Entwick-lung eines Fumonisin- Biosensors für die Lebensmittelanalytik. In Bezug auf die aktuell steigen-den Lebensmittel- und Rohstoffpreise ist die Entwicklung eines Schnelltestsystems zur Detektion von Kontaminationen mit Mykotoxinen besonders gefragt, da zusätzliche Verluste und Kosten verhindert werden können. Für die Herstellung der AnFAO als MBP-Fusionsprotein und Biotin-Fusionsprotein mit zusätzlichem 6x His-Tag wurden die pET-MBP-AnFAO und pRSET-BH6-An-FAO Expressionsvektoren erfolgreich konstruiert. Die lösliche Expression im Cytoplasma wurde von MBP-AnFAO erreicht, wobei die Expression von BH6-AnFAO in inclusion bodies erfolgte und keine Aktivität des Enzyms nachgewiesen wurde. Die Enzymaktivität von MBP-AnFAO wurde im optischen Assay und amperometrisch durch die Detektion von H2O2 ermittelt. Im optischen Assay wurde die maximale spezifische Aktivität von 2,45 U/mg bei 45 °C, einer Enzymkonzentration von 3 μM und 50 μM FB1 erreicht. Generell wurden mit FB1 als Enzymsubstrat höhere Fluoreszenzsig-nale und dementsprechend höhere Enzymaktivitäten als für FB2 beobachtet. Es wurde ein linearer Zusammenhang der Enzymaktivitäten mit der Substratkonzentration beobachtet. Außerdem wurde ein Anstieg der H2O2-Konzentration mit zunehmender Inkubationszeit (bis zu 60 Minuten) erkannt. Des Weiteren wurde der Einfluss des MBP-Fusionsproteins auf die Enzymaktivität des AnFAO untersucht. Dabei wurde anhand von wesentlich geringeren Aktivitäten für AnFAO allein ein eventueller Einfluss des MBP auf dessen Aktivität festgestellt. Ein elektrochemischer Aufbau wurde zur Entwicklung eines Fumonisin- Sensors genutzt. Dazu wurde nachgewiesen, dass FB1 von rekombinant hergestelltem MBP-AnFAO unter Bildung von NH3 und H2O2 zu weniger toxi-schem FB1, dem FPy1, oxidiert werden kann. An der PB/Kohlenstoff-Elektrode, welche sensitiver gegenüber H2O2 und stabiler als die CoPC/Kohlenstoff Elektrode war, wurde die Reduktion des enzymatisch gebildeten H2O2 gemessen. Die Erstellung einer FB1- Kalibriergerade mit FB1- Lösun-gen verschiedener Konzentrationen zeigte, dass das Enzym auch in immobilisierter Form in der Lage ist unterschiedliche Konzentrationen an FB1 zu desaminieren. Dazu gehört auch der Kon-zentrationsbereich unterhalb des festgelegten Grenzwertes von 2,7 μmol/kg für Fumonisin. Die amperometrischen Kurven hierfür wurden an der PB/Kohlenstoff-Elektrode erfolgreich aufge-nommen. Störungen des H2O2- Redoxstroms durch das Enzym, der Enzymsubstrate und der Ne-benprodukte während der amperometrischen Messung wurden ausgeschlossen. Sowohl im opti-schen als auch im amperometrischen Assay wurde ausschließlich das enzymatisch gebildete H2O2 bestimmt.
Bisphenol A (BPA) is used in Polycarbonate, Polyacrylic resins, Polysulfones, Epoxy resins, and Polyetherimides. It is also used in recycled Polyvinyl chloride [1–3]. BPA has been classified as a substance of very high concern (SVHC) under REACH [4] due to its endocrine disrupting properties. The German competent authorities want to reduce the content of BPA in the environment. Possible substitutes for BPA are Bisphenol B (BPB), Bisphenol E (BPE),
Bisphenol F (BPF), or Bisphenol S (BPS), as they are similar in structure.
BPA-based materials have a wide area of application especially outside. These outdoor applications are exposed to different external influences, including physical, biological, mechanical and chemical influences. This results in damage and aging of the material with leaching or migration into the environment. There, the substance is transformed by various transformation processes. The emerging metabolites and transformation products (TPs) can have different properties than the parent substance. Understanding the fate and behavior of the emerging pollutants is very important.
Therefore, different transformation products of selected bisphenols will be generated and analyzed:
To investigate the fate of different bisphenols in water treatment plants technical transformation products [5] will be generated by chlorination, ozonization, the Fenton reaction, and UV-radiation.
For the investigation of the fate of Bisphenols in surface water global radiation will be simulated with UVA-lamps
Simulation of phase-I-metabolism with an electrochemical cell coupled to mass spectrometry (EC-MS).
1. Projektreffen mit dem Umweltbundesamt für das Projekt MARKERIA (VH1802).
Ziel des Projektes ist es, die Eignung der Bestimmung eines oder mehrerer der genannten anthropogenen Marker im Abwasser zur Volumenkorrektur („Kalibration“) im SARS-CoV-2-Monitoring von Abwässern auf der Basis eines von der BAM zu erhebenden Messdatensatzes zu evaluieren.
ESI-CorA ist ein nationales Verbundprojekt mit dem Ziel des Nachweises von SARS-CoV-2 im Abwasser.
Das UBA hat als Teilprojekt das Projekt MARKERIA (VH1802) an die BAM vergeben.
Ziel des Projektes ist es, die Eignung der Bestimmung eines oder mehrerer der genannten anthropogenen Marker im Abwasser zur Volumenkorrektur („Kalibration“) im SARS-CoV-2-Monitoring von Abwässern auf der Basis eines von der BAM zu erhebenden Messdatensatzes zu evaluieren.
Vortrag zum Kick-off des Projektes.
Ziel des Projektes ist es, die Eignung der Bestimmung eines oder mehrerer der genannten anthropogenen Marker im Abwasser zur Volumenkorrektur („Kalibration“) im SARS-CoV-2-Monitoring von Abwässern auf der Basis eines von der BAM zu erhebenden Messdatensatzes zu evaluieren.
2. Projekttreffen mit dem Umweltbundesamt zum Projekt MARKERIA (VH1802).
Ziel des Projektes ist es, die Eignung der Bestimmung eines oder mehrerer der genannten anthropogenen Marker im Abwasser zur Volumenkorrektur („Kalibration“) im SARS-CoV-2-Monitoring von Abwässern auf der Basis eines von der BAM zu erhebenden Messdatensatzes zu evaluieren.
Natural and synthetic estrogens are key endocrine-disrupting chemicals. Despite occurring at ultra-trace levels (below ng L-1), it is believed that they are contributing to an increase in feminized fish and other endocrine disruptive effects, and hence, their inclusion in the Watch list was not unexpected. One of the main sources ofestrogens to surface waters is wastewater effluent. Once in surface waters, they can partition into different compartments, i.e., water and suspended particulate matter. For this reason, there is an urgent need for a methodology to monitor estrogen levels below the environmental quality standards (EQS) set by the Water Framework Directive requirements.
In this study, a precise and accurate gas chromatography-mass spectrometry method (GC-MS/MS) for the analysis of estrone (E1), 17β-estradiol (17β-E2), 17α-estradiol (17α- E2), 17-alpha-ethinylestradiol (EE2), and estriol (E3) in whole water samples with ng L-1 limit of quantification (LOQ) was developed and validated in accordance with CEN/TS 16800:2020 guidelines.
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 (17E2) 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 contribution will present the objectives and methods applied within the EDC-WFD project.