Chemische Charakterisierung und Spurenanalytik
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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.
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.
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.
Alternariol (AOH) and Alternariol monomethylether (AME) are two secondary metabolites of Alternaria fungi which can be found in various foodstuffs like tomatoes, nuts and grains. Due to their toxicity and potential mutagenic activity the need for the development of high-throughput methods for the supervision of AOH- and AME-levels is of increasing interest. As the availability of both native and labelled AOH and AME analytical standards is very limited we herein wish to present a novel concise approach towards their synthesis employing a ruthenium-catalyzed ortho-arylation4 as the key step.
Small organic molecule drugs are one of the key classes, taking increasingly important roles in modern drug development strategies. With the focus on small molecule drugs, difficulties originate frequently from a pronounced lipophilic character, resulting in poor water solubility, low bioavailability and unfavored pharmacokinetics. Recently, peptide-poly(ethylene glycol) conjugates (peptide-PEG conjugates) were described as precisely tunable platforms to solubilize a broad scope of fluorescent or non-fluorescent small organic molecules [1-2]. Selection of drug hosting peptides was achieved by combinatorial means, which can further be extended by implementation of a drug release screening step.
One-bead-one-compound peptide libraries are powerful tools to select high affinity binders. However, the selection of positive hits from the peptide libraries remains tedious as it occurs by handpicking, strongly limiting the pool of investigated beads. Here we report our recent results on improving the analytical platform, using automated fluorescence scanning and MALDI-ToF-ToF MS/MS imaging to screen larger sets of beads, broadening the statistical base and unraveling more precisely suitable peptides. The screening puts special emphasis on loading capacities and drug-release of transporters by performing additional washing steps in different media (cf. Fig. 1). Peptides representing strong, medium, weak releaser were chosen for further analysis and synthesized as peptide-polymer transporters. Release was analyzed by fluorescence anisotropy and fluorescence correlation spectroscopy, due to the fluorescent characteristics of the drug.
Solubilization studies confirmed sufficient loading capacities for a potential anti-Alzheimer disease drug of three transporter molecules representing strong/weak drug releaser, reaching solubilization of up to 1:3.4 (µmol drug/µmol conjugate). Fluorescence anisotropy and fluorescence correlation spectroscopy of the drug-loaded transporter showed significant differences in drug releasing properties, confirming the screening process.
For years there have been more and more reports on the presence of drugs in the aquatic environment. Due to the demographic change, the consumption of pharmaceuticals has risen sharply. After taking the drugs, they are partly metabolized in the human body. However, the metabolism is not complete so that both the metabolites and non-metabolized amounts of the parent compounds are excreted. These compounds reach the waste water and afterwards the sewage treatment plants. In sewage treatment plants transformation products can be formed by the oxidative conditions during wastewater treatment processes. The transformation products may have a higher toxicity than the actual environmental pollutants and are often only partly removed during the waste water treatment. Since a lot of these compounds are still unknown, the transformation products are not detected by target analysis used in sewage treatment plants and are often released undetected in the aquatic ecosystems. The released substances may be subject to additional transformation processes in the environment. Pharmaceuticals produced in high amounts can be already detected in the μg/L range in water bodies worldwide.
Metformin and its major transformation product guanylurea are one of the main representatives. Metformin is the drug of choice for treating type 2 diabetes. The drug therapy for diabetes mellitus has increased significantly in recent years. In the year 2015 1500 tons of metformin were prescribed in Germany (for statutory insured persons). Metformin is not metabolized in the human body and is excreted unchanged therefore concentrations between 57 μg/L and 129 μg/L are found in German waste water treatment plants influents.
In this work the transformation of the antidiabetic drug metformin is investigated. The degradation of metformin is initialize by commercial water treatment techniques like UV-radiation or noncommercial techniques like heterogenous photocatalysis based on titanium dioxide. The degradation of metformin and resulting transformation products are analyzed by LC-MS/MS and LC-HRMS.
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).