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Bisphenol A (BPA) is a chemical that has been used in the production of plastics for more than 40 years. BPA released from bottles made of polycarbonates has been identified as a potential endocrine disrupting substance. Comprehensive research has been undertaken to test and verify its effect on animals and human beings.
Many methods have been proposed for the determination of BPA, in particular, gas and liquid chromatography. The main disadvantages of such approaches are the high cost of the equipment, the significant duration of an analysis, and difficulties in screening a large number of samples. Lateral Flow ImmunoAssay (LFIA) attributes are high throughput, high specificity and sensitivity, as well as low cost and simplicity.
An LFIA test strip was developed. This LFIA is based on anti-BPA antibodies (from mouse) conjugated with gold nanoparticles as the marker by passive absorption and covalent coupling, deposited in an elaborate pad. To form control and test zones, anti-mouse antibody and a BVA-BSA conjugate were spotted on the nitrocellulose membrane, respectively.
Negative samples are revealed by red lines both in the test and control zones, respectively, whereas positive samples produce a single red line only in the control zone. The measurement range is 0.05 – 23 μg/L, visually detected by the naked eye within 5 minutes. In addition, the intensities at the test line can be read by dedicated lateral flow readers (opTrilyzer® and Cube by opTricon, Berlin) for a more precise and documented determination.
In addition to previously reported results on the simulated aging of polystyrene samples (PS) containing 1 wt. % hexabromocyclododecane (HBCD), we present the first results of our investigations of polypropylene (PP)-samples 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 rain water samples derived from the used climate chamber, the samples were prepared in accordance with a validated protocol. Before the analyses, each sample was spiked with 2 µL of isotopically labeled BDE-209 (13C10-BDE-209) to serve as internal standard (ISTD) in the performed stable isotope dilution analysis. Subsequently the samples were extracted with isooctane, the obtained aliquots of the extracts were concentrated to 200 µL and 2 µL of the resulting solution were injected to the GC/MS for quantification.
Additionally, the total bromine contents are monitored for the aged and untreated samples using laser ablation inductively coupled plasma mass spectrometry (LA-ICP-MS) as well as X-ray fluorescence analysis (XRF) as non-destructive and rapid method. Furthermore, results from surface analysis using environmental scanning electron microscopy (ESEM) for morphological characterization of the aged and untreated samples were presented and discussed. In general, the resulting data from the accelerated aging will be compared to those from the natural weathering experiments (“atmospheric exposure”, in soil).
The atmospheric exposure was performed by placing the samples on a weathering rack, which is aligned in SW direction (in a 45° angle to the horizon). The weathering data were regularly recorded by Deutscher Wetterdienst at this site. The surfaces of the test specimens (aged and stored references) were analyzed by ESEM as well as by LA-ICP-MS and by XRF. The surface of PS and PP specimens aged outdoors present the aging under real conditions and allow the comparison to the accelerated aged specimens by means of the weathering chamber. This way, we explore the efficiency of the accelerated aging procedure, which provides the advantage of well-defined and reproducible conditions compared to natural weathering, as a tool for testing different plastic materials.
Additionally “in soil” experiments were conducted in-door in a well characterized testing soil. The soil (boulder-clay, sand with 12 % loam, particle size in total 0.2-4 mm) is filled in a free-draining concrete basin inside of an air-conditioned room. In this manner, TOC, water capacity and humidity are recorded parameters. To assure a washing out 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. The water content is additionally monitored by weight of the basin, capturing water from raining periods. The correct humidity is a fundamental parameter for biological activity. Samples of PS resp. PP were of dimension 10x1cm and 5 specimens were placed up to the half in the soil per basin. Microbial activity of the soil, monitored by the reference polyurethane, sets HBCD resp. BDE-209 of the samples free and will be leached from the samples by raining water. Thereafter these will be captured by passive samplers placed in a distinct distance to the samples in the soil. The “in soil” experiments are complementary to the weathering experiments due to the biological activity in the soil. These experiments simulate the fate of the brominated flame retardants in the biosphere.
Ionophore Antibiotika werden zum Schutz gegen Kokzidiose eingesetzt, hauptsächlich in der Geflügelmast. Rückstände dieser Substanzen und deren Transformationsprodukte (TP) gelangen über den Metabolismus zum einen in das Geflügelfleisch, aber auch durch Ausscheidung in die Umwelt, da Tiermist als Dünger verwendet wird. Ziel dieser Forschungsarbeit ist es, die TP-Bildung von vier verschiedenen Ionophoren Antibiotika (Monensin (MON), Salinomycin (SAL), Maduramicin (MAD) und Lasalocid (LAS)) zu untersuchen. TPs werden durch den Biotransformationsprozess (Metabolismus) gebildet, dieser Prozess kann in zwei Phasen eingeteilt werden. Während in Phase I Oxidations-, Reduktions- oder Hydrolysereaktionen auftreten, ist Phase II von Konjugationsreaktionen geprägt. Durch diesen Prozess werden die Substanzen besser ausscheidbar.
Natürliche Redox-Vorgänge, wie sie bei der Biotransformation (Phase I) auftreten, können mit elektrochemischen (EC) Systemen simuliert werden. In einer EC-Durchflusszelle findet die Reaktion abhängig vom angelegten Potential statt. Im positiven Potentialbereich (0.0 bis 3.0 V; vs. Pd/H2) werden die Analyten oxidiert und somit oxidative TPs generiert. Durch die online-Kopplung mit Flüssigkeitschromatografie (LC) und Massenspektrometrie (MS) wird zunächst eine säulenchromatografische Trennung der generierten TPs erhalten, gefolgt von der massenspektrometischen Detektion. Durch die online-Kopplung von EC-(LC)-MS ergibt sich eine schnelle Analysemöglichkeit von der TP-Erzeugung ausgewählter Substanzen bis hin zur Detektion, wodurch gleichzeitig eine Identifizierung möglich ist.
Die ausgewählten Ionophoren Antibiotika wurden mittels EC-(LC)-MS auf auftretende TPs untersucht. Die ersten Ergebnisse zeigen ein breites Spektrum unterschiedlicher TPs abhängig von gewählten EC-Parametern wie Lösemittel, Modifier und insbesondere vom Arbeitselektrodenmaterial der EC-Durchflusszelle. Unter den erhaltenen TPs sind sowohl bekannte als auch unbekannte TPs vertreten, so dass weitere Untersuchungen zur Strukturaufklärung und vergleichende Tests zu Phase I Metaboliten (z.B. durch Metabolismus-Studien mit Mikrosomen) geplant sind.
Ionophore antibiotics are used to cure and prevent coccidiosis by chicken especially in broiler farming. The residues are found not only in food products (chicken and eggs) but also in the environment (manure, soil or water). In this work the ionophores monensin (MON), salinomycin (SAL), maduramicin (MAD) and lasalocid (LAS) are investigated aiming to study their transformation products (TPs) through biotransformation processes. Biotransformation can be divided into two phases, phase I: oxidation, reduction or hydrolysis and Phase II: conjugation reactions. It is necessary to further examine the biotransformation pathways to determine TPs to be able to detect residues more specifically in different matrices.
The technique of electrochemistry (EC) offers the opportunity to simulate biotransformation processes and to generate TPs for further analysis. The combination of EC with liquid chromatography and mass spectrometry (EC-LC-MS) provide a fast and simple tool to separate and determine the EC-generated TPs. The electrochemical flow through cell is coupled to the (LC)-MS system, allowing the reaction mixture to be separated by a RP-18 column and then analyzed in the MS. The oxidation products are generated at different potentials between 0.0 – 2.5 V vs. Pd/H2 using glassy carbon or boron doped diamond as working electrode materials .
The results show a broad spectrum of different TPs depending on used solvents and working electrode materials. Among the generated TPs already known as well as unknown TPs of the drugs can be found. Further investigations on structure elucidation of unkown TPs are planned.