Chemische Charakterisierung und Spurenanalytik
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Eingeladener Vortrag
- nein (25)
Therapeutic monoclonal antibodies are the fastest-growing group of biological agents which generated a yearly turnover of USD 210 billion in 2022 and whose sales are expected to grow by 10% annually over the next 10 years. With steadily increasing market importance, analytical methods for reliable quantification of therapeutic antibodies also become more and more relevant. Liquid chromatography coupled with tandem mass spectrometry (LC–MS/MS) has become the main technology for antibody quantification. This approach, however, requires enzymatic digestion of the intact protein into peptides, for which a wide range of different protocols exists that often lead to different results depending on the digestion procedure or trypsin variants used. In particular, the amount and type of detergents added for protein unfolding prior to digestion is known to create significant bias in measurement results. The overall goal of the presented project is the application of novel thermostable and surface-functionalized trypsin particles for improved antibody digestion. Specifically, a trypsin-variant described in the literature exhibiting increased activity and thermal stability above 80°C, will be examined. The application of this enzyme should allow to perform digestion at elevated temperatures where the protein is naturally unfolding thereby increasing enzyme accessibility without the need for detergents. Furthermore, we will immobilize the thermostable trypsin onto the surface to further enhance enzyme stability, prevent self-digestion, and enable separation of trypsin from target peptides before LC–MS/MS analysis. As an immobilization platform, cheap and non-porous corundum particles will be used as these show high chemical stability and low levels of interaction of matrix proteins with the functionalized surface. adsorption. In a multidisciplinary collaboration with the SALSA Photonics Lab, we will investigate the characteristics of covalent enzyme binding and unspecific peptide binding using an interface-sensitive analytical tool, vibrational sum-frequency generation (VSFG) spectroscopy. The insights gained will not only lead to new competencies in peptide and enzyme surface analysis using VSFG spectroscopy in SALSA but will also significantly contribute to optimizing antibody quantification.
Antikörper sind in der medizinischen Welt nicht mehr wegzudenken. Ihr Einsatz-Repertoire als Therapeutika für die Behandlung diverser Krankheiten und Infektionen weitet sich von Jahr zu Jahr mehr aus. Dabei basiert ein Großteil der verwendeten Antikörper zu diesem Zeitpunkt auf monoklonalen Antikörpern auf Basis von Hybridomazellen. Doch hier könnten rekombinante Antikörper aufgrund ihrer Vektor-basierten Expression eine vielversprechende und womöglich sogar revolutionierende Alternative bieten. So ergeben sich neue Optimierungsoptionen für Merkmale wie Affinität, Stabilität und Kompatibilität über Anpassungen auf genetischer oder posttranslationaler Ebene. Allerdings ergibt sich kein Anwendungszweck ohne die vorhergehende detaillierte Charakterisierung der Antikörper. Denn nur mit spezifischem Wissen über die diversen Eigenschaften und Wechselwirkungen kann eine effektive und präzise Verwendung in der Diagnostik und Therapeutik gewährleistet werden und auf diese Weise Leben retten.
Aus diesem Grund beschäftigt sich diese Masterarbeit mit der Vertiefung der rekombinanten Antikörper-Thematik. Dazu soll ein Anti-Tetanus-Antikörper erstmals rekombinant in verschiedenen Zelllinien hergestellt und anschließend über umfangreiche analytische Verfahren mit einem Fokus auf die Einflussanalyse der unterschiedlichen posttranslationalen Glykosylierungen charakterisiert werden. Zu diesem Zweck wurden als Grundlage einerseits zwei P1316-Dual-Expressions-Vektoren mit variierenden Insert-Positionen der schweren und leichten Kette durch Gibson-Assembly sowie individuellen pRK5-Plasmide für eine separiert Expression der Antikkörperketten mithilfe Restriktionsfragment-Ligation generiert. In einer Gegenüberstellung der der Expressionsausbeuten stellte sich die Überlegenheit der P1316-Plasmid-Konfiguration heraus, in der das Leichtketten-Insert an der ersten Expressionsstelle positioniert ist. Deshalb wurde dieser Vektor als Ausgangspunkt für die anschließende hochskalierten Herstellung des Anti-Tetanus-Antikörpers in Expi293F-GnTI- und ExpiCHO-S-Zellen verwendet. Ein ELISA bestätigte die Bindungsaktivität der rekombinanten Antikörper am Tetanus-Toxoid unabhängig vom Expressionssystem. Nach einer folgenden Optimierung der für die Aufreinigung verwendeten Protein-A-Affinitätschromatographie, wurde über weitere Charakterisierungsmethoden wie Größenausschlusschromatographie und dynamische Lichtstreuung eine vergleichbare Aggregation aufgrund der sauren Elution aufgezeigt. In diesem Kontext wurde die Notwendigkeit einer Zweistufen-Präparation mit Affinitäts- und Größenausschlusschromatografie für den Erhalt monodisperser Proben verdeutlicht. Zudem wurden die verschiedenen intakten Massen mitsamt ihrer spezifischen Glykan-abhängigen Streumaßen in Relation zum monoklonalen NISTmAB-Referenzantikörper bestimmt. Dabei konnte den Erwartungen nach sowohl die geringere Masse als auch die uniformere Glykosylierung der in Expi293 GnTI- exprimierten Immunoglobuline in Relation zum ExpiCHO-S-Antikörper nachgewiesen werden. Anschließend wurde das Stabilitätsverhalten mittels thermischer Entfaltung und dynamischer Lichtstreuung über einen ausgeweiteten Zeitraum sowie verschiedenen Temperaturen dokumentiert. Grundlegend wurde eine höhere thermische Stabilität der zweiten konstanten Schwerketten-Domäne des aus ExpiCHO-S-Zellen stammenden Antikörpers nachgewiesen. Außerdem konnte eine problemlose Lagerungsfähigkeit beider unterschiedlich glykosylierter Antikörper bei Raumtemperatur für mindestens 4 Wochen festgestellt werden. Des Weiteren wurde die Langzeitlagerung im Rahmen der Auswirkung von Gefrier-Auftau-Zyklen mit gleichbleibenden Methoden sowie zusätzlicher Größenausschlusschromatographie erprobt. Hierbei stellte sich der Erhalt der strukturellen Integrität nach bis zu 15 Zyklen heraus. Allerdings geht die Monodispersität bereits nach wenigen Zyklen verloren, wobei die geringfügiger glykosylierten Expi293F-GnTI-Anti-Tetanus-Antikörper eine stärkere Beeinträchtigung durch multiple Gefrier-Auftau-Zyklen aufwiesen.
Metabolomics
(2024)
Mykotoxine sind sekundäre Stoffwechselprodukte, die von Schimmelpilzen gebildet werden. Sie sind unvermeidliche Lebensmittelkontaminanten und stellen daher ein ernstes Gesundheitsrisiko für Mensch und Tier dar. Aus diesem Grund hat die Europäische Kommission Vorschriften erlassen, die Höchstwerte für Mykotoxine in bestimmten Lebensmitteln vorsehen. Um die gesetzlichen Grenzwerte einzuhalten, müssen in der Lebensmittelindustrie Mykotoxinanalysen der eingehenden Waren durchgeführt werden.
Gegenwärtig umfasst die Analyse zeitaufwändige Probenvorbereitungsschritte, denen in der Regel eine chromatographische Analyse folgt.
Immunoassays ermöglichen eine Vor-Ort-Analyse, aber in der Regel sind für feste Lebensmittelproben lösungsmittelbasierte Extraktionsschritte erforderlich. Da Immunoassays in der Regel nicht mit den hohen Lösungsmittelkonzentrationen kompatibel sind, die üblicherweise für die Mykotoxinextraktion verwendet werden (z.B. Acetonitril oder Methanol), war es das Ziel dieser Arbeit, ein Extraktionsverfahren für die Mykotoxine Deoxynivalenol und Ochratoxin A aus Weizenmehl und Getreide zu entwickeln, das für Immunoassays und -sensoren verwendet werden kann. Vier verschiedene Lösungsmittel, Methanol (10 %), Ethanol (5 %) und Acetonitril (10 %) sowie Milli-Q-Wasser wurden für die Extraktion des Analyten Deoxynivalenol getestet. Um negative Umweltaspekte zu vermeiden und aufgrund der vergleichbaren Extraktionseffizienz von Milli-Q-Wasser gegenüber den anderen Lösungsmitteln, wurde Milli-Q-Wasser als Extraktionslösung im optimierten Extraktionsprotokoll für Deoxynivalenol verwendet.
Es wurden verschiedene Extraktionsbedingungen, wie die Extraktionszeit, das Lösungsmittel-Feststoff-Verhältnis, der Filtrationsschritt, der Zentrifugationsschritt sowie die Zusammensetzung des Wassers untersucht. Auf der Grundlage der Ergebnisse wurde ein Extraktionsprotokoll festgelegt, mit dem Wiederfindungsraten in einem Bereich von x bis x erzielt wurden. Das Extraktionsprotokoll umfasste die Extraktion von 2 g Weizenmehl mit 40 ml Milli-Q-Wasser für 30 Minuten, die anschließende Zentrifugation bei 3000 U/min für 15 Minuten bei 4 °C und die Filtration des Überstands.
The contamination of drinking water with pharmaceuticals represents a severe health risk. In order to monitor the drinking water quality continuously and enable quick countermeasures in case of contamination, novel sensors are required. Here, immunoanalytical methods based on the binding of the analyte to highly selective antibodies can be helpful. In this work, magnetic bead-based immunoassays (MBBAs) have been developed for the detection of two relevant contaminants of drinking water: diclofenac (DCF) and amoxicillin (AMX). In case of the latter, not only the parent drug is of interest in the risk assessment but also its hydrolysis products (HPs). In a comprehensive study, the influence of external factors and intrinsic properties of the water on the rate of hydrolysis was investigated. As the hydrolysis of AMX further impacts the recognition by the antibody, a strategy to analyze samples with unknown hydrolysis degree of AMX was established employing the enzyme β-lactamase in sample preparation. For both analytes, the MBBAs enable the fast quantification with results obtained in less than one hour which represents a major improvement over conventional immunoassays like the enzyme-linked immunosorbent assay (ELISA). Compared to the respective ELISAs with the same antibodies, the MBBAs further exhibit improved analytical parameters such as a broader measurement range and lower limits of detection. Due to the magnetic properties of the beads that serve as a platform for the assays, they are suitable for the mobile and automated detection at the point-of-care. An integrated diagnostic system was designed in which electrochemical detection with chronoamperometry on a microfluidic chip allows for further miniaturization of the system to enable monitoring of the drinking water quality online in water supply pipes at waterworks.
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).
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.
Per- and polyfluoroalkyl substances (PFAS) are a large, ever-growing and widely used class of chemicals. Due to the strength of the C-F bond, they do not decompose but accumulate in the environment posing a risk for nature and humans alike. While the use of some PFAS, like perfluorooctanoic acid (PFOA) is already regulated in the EU, new ‘precursor’ substances are used to replace them. However, these precursors may be equally harmful to the environment.
In recent years, many ‘hot spot’ sites with high PFAS contaminations in soil have been distinguished, but no German-wide background values have been determined yet. Knowing these background values is crucial to understand the degree of PFAS contamination, underpinning future regulatory decisions.
Due to the complexity and variety of different PFAS compounds, one needs to apply a broad spectrum of different techniques to capture most of the PFAS content in one sample.
In the framework of this project, 600 soil samples are taken at different sites all over Germany. The concentration of 30 PFAS - 13 carboxylic acids (C4-C18), 5 sulfonic acids (C4-C10) and 12 precursor substances) - is determined in these soil samples using three different sample preparation approaches: 1) ultrasonic extraction of the soil samples with Methanol; 2) preparation of eluates to test the leaching behaviour of the PFAS and 3) TOP assays following the method published by Houtz & Sedlak.
Targeted LC-MS/MS is used to determine PFAS concentration after all three preparation steps.
For the TOP-assay, the concentration of all 30 PFAS is compared prior to and after the oxidation reaction.
Besides the ‘classic’ TOP-Assay, two other TOP-Assay approaches, the dTOP Assay and the photoTOP-Assay, are tested and the results of all three approaches are compared. First, all three TOP-Assay approaches will be tested on a reference soil spiked with a solution including all 30 PFAS measured in the project. Later, soil samples taken in the frame of the priorly described project will be tested.
This poster will focus on the results of the experiments comparing the three different TOP Assay approaches in spiked reference soil. Additionally, some of the results of the other sample preparation methods, extraction and eluate preparation will be presented.
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.