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Institute
- Institut für Integrierte Naturwissenschaften, Abt. Chemie (22) (remove)
Water scarcity is already an omnipresent problem in many parts of the world, especially in sub-Saharan Africa. The dry years 2018 and 2019 showed that also in Germany water resources are finite. Projections and predictions for the next decades indicate that renewal rates of existing water resources will decline due the growing influence of climate change, but that water extraction rates will increase due to population growth. It is therefore important to find alternative and sustainable methods to make optimal use of the water resources currently available. For this reason, the reuse of treated wastewater for irrigation and recharge purposes has become one focus of scientific research in this field. However, it must be taken into account that wastewater contains so-called micropollutants, i.e., substances of anthropogenic origin. These are, e.g., pharmaceuticals, pesticides and industrial chemicals which enter the wastewater, but also metabolites that are formed in the human body from pharmaceuticals or personal care products. Through the treatment in wastewater treatment plants (WWTPs) as well as through chemical, biological and physical processes in the soil passage during the reuse of water, these micropollutants are transformed to new substances, known as transformation products (TPs), which further broaden the number of contaminants that can be detected within the whole water cycle.
Despite the fact that the presence of human metabolites and environmental TPs in untreated and treated wastewater has been known for a many years, they are rarely included in common routine analysis methods. Therefore, a first goal of this thesis was the development of an analysis method based on liquid chromatography - tandem mass spectrometry (LC-MS/MS) that contains a broad spectrum of frequently detected micropollutants including their known metabolites and TPs. The developed multi-residue analysis method contained a total of 80 precursor micropollutants and 74 metabolites and TPs of different substance classes. The method was validated for the analysis of different water matrices (WWTP influent and effluent, surface water and groundwater from a bank filtration site). The influence of the MS parameters on the quality of the analysis data was studied. Despite the high number of analytes, a sufficient number of datapoints per peak was maintained, ensuring a high sensitivity and precision as well as a good recovery for all matrices. The selection of the analytes proved to be relevant as 95% of the selected micropollutants were detected in at least one sample. Several micropollutants were quantified that were not in the focus of other current multi-residue analysis methods (e.g. oxypurinol). The relevance of including metabolites and TPs was demonstrated by the frequent detection of, e.g., clopidogrel acid and valsartan acid at higher concentrations than their precursors, the latter even being detected in samples of bank filtrate water.
By the integration of metabolites, which are produced in the body by biological processes, and biological and chemical TPs, the multi-residue analysis method is also suitable for elucidating degradation mechanisms in treatment systems for water reuse that, e.g., use a soil passage for further treatment. In the second part of the thesis, samples from two treatment systems based on natural processes were analysed: a pilot-scale above-ground sequential biofiltration system (SBF) and a full-scale soil aquifer treatment (SAT) site. In the SBF system mainly biological degradation was observed, which was clearly demonstrated by the detection of biological TPs after the treatment. The efficiency of the degradation was improved by an intermediate aeration, which created oxic conditions in the upper layer of the following soil passage. In the SAT system a combination of biodegradation and sorption processes occurred. By the different behaviour of some biodegradable micropollutants compared to the SBF system, the influence of redox conditions and microbial community was observed. An advantage of the SAT system over the SBF system was found in the sorption capacity of the natural soil. Especially positively charged micropollutants showed attenuation due to ionic interactions with negatively charged soil particles. Based on the physicochemical properties at ambient pH, the degree of removal in the investigated systems and the occurrence in the source water, a selection of process-based indicator substances was proposed.
Within the first two parts of this thesis a micropollutant was frequently detected at elevated concentrations in WWTPs effluents, which was not previously in the focus of environmental research: the antidiabetic drug sitagliptin (STG). STG showed low degradability in biological systems and thus it was investigated to what extend chemical treatment by ozonation can ensure attenuation of it. STG contains an aliphatic primary amine as the principal point of attack for the ozone molecule. There is only limited information about the behaviour of this functional group during ozonation and thus, STG served as an example for other micropollutants containing aliphatic primary amines. A pH-dependent degradation kinetic was observed due to the protonation of the primary amine at lower pH values. At pH values in the range 6 - 8, which is typical for the environment and in WWTPs, STG showed degradation kinetics in the range of 103 M-1s-1 and thus belongs to the group of readily degradable substances. However, complete degradation can only be expected at significantly higher pH values (> 9). The transformation of the primary amine moiety into a nitro group was observed as the major degradation mechanism for STG during ozonation. Other mechanisms involved the formation of a diketone, bond breakages and the formation of trifluoroacetic acid (TFA). Investigations at a pilot-scale ozonation plant using the effluent of a biological degradation of a municipal WWTP as source water confirmed the results of the laboratory studies: STG could not be removed completely even at high ozone doses and the nitro compound was formed as the main TP and remained stable during further ozonation and subsequent biological treatment. It can therefore be assumed that under realistic conditions both a residual concentration of STG and the formed main TP as well as other stable TPs such as TFA can be detected in the effluents of a WWTP consisting of conventional biological treatment followed by ozonation and subsequent biological polishing steps.
In der vorliegenden Arbeit wird das thermochemische Wechselwirkungsverhalten verschiedener Magnesiakohlenstoffmaterialen in Abhängigkeit verschiedener Einflussgrößen wissenschaftlich untersucht. Schwerpunkte der experimentellen Arbeiten bilden thermoanalytische Experimente, Gefügeuntersuchungen der Magnesiakohlenstoff-Proben sowie thermodyna-mische Berechnungen und Auswertungen durch CAT (Computer Aided Thermochemistry) mittels des Softwarepakets FactSage.
Erster Themenbereich dieser Arbeit ist die Untersuchung des Einflusses der in dem Rohstoff Magnesia enthaltenen mineralogischen Nebenphasen Merwinit (C3MS2), Monticellit (CMS) und Belit (C2S) auf den carbothermisch induzierten Verschleiß im MgO-C-Material. Für die Messreihen wurden die Nebenphasen eigens synthetisiert und hiermit MgO-C-Nebenphase-Modellwerkstoffe hergestellt. Die Nebenphase Monticellit ist unbeständig gegenüber der carbothermischen Reduktion. Monticellit wird im MgO-C-Gefüge durch Kohlenstoff reduziert und hieraus ergibt sich ein erhöhter Gewichtsverlust des Probenmaterials. Auch Merwinit wird bei T = 1600°C reduziert, der Gewichtsverlust wird dadurch allerdings nicht erhöht. Belit ist im MgO-C-Gefüge stabil gegenüber carbothermischer Reduktion.
Ein weiterer Schwerpunkt der Arbeit lag auf der Untersuchung des Einflusses des klassischen Antioxidans Aluminium auf die thermochemische Stabilität von MgO-C. Bei geringen Sauerstoffpartialdrücken ist die Reaktion des Aluminium-Metalls bzw. des bereits zu Al4C3 carbidisierten Aluminiums mit dem steineigenen Periklas unter Mg(g)-Bildung möglich, was einen erhöhten Gewichtsverlust zur Folge hat. Aber auch nach der Oxidation zu Al2O3 bzw. Spinell liegt Aluminium in signifikanten Mengen als Al(g) und Al2O(g) in der Gasphase vor und greift des Weiteren die Nebenphasen an, was ebenfalls zu einem messbaren Gewichtsverlust führt.
Dritter Arbeitsschwerpunkt war die Untersuchung des Einflusses des Umgebungsdruckes auf die carbothermische Reduktion von MgO. Die Ergebnisse zeigen, dass der Druck sich in zweierlei Hinsicht auf die carbothermische Reduktion von MgO auswirkt. Zum einen bewirkt ein sinkender Umgebungsdruck eine Beschleunigung der carbothermischen Reduktion durch die Verschiebung des thermodynamischen Gleichgewichts auf die Produktseite. Des Weiteren sorgt er für einen schnelleren Abtransport der Produktgase vom Reaktionsort und ver-hindert somit die Einstellung eines lokalen Gleichgewichts im Gefüge. Dritter Effekt ist die mit steigendem Druck verstärkt ablaufende Kohlenstoffoxidation durch Umgebungssauerstoff, da die Sauerstoffmenge in der Umgebung des MgO-C-Materials vom Umgebungsdruck bestimmt wird. Für die Geschwindigkeit des thermochemischen Verschleißes von Magnesiakohlenstoffmaterialien, der immer eine Kombination aus Kohlenstoffoxidation und carbothermischer Reduktion darstellt, bedeutet dies, dass sie in Abhängigkeit vom Umgebungsdruck in unterschiedlichem Ausmaß von diesen beiden Reaktionen beeinflusst wird.
The present study deals with the synthesis of N-phenacylpyridinium salts and their use as photoinitiators for epoxy resins. The use and suitability of phenacyl salts as photoinitiators for epoxy resins has already been described in previous studies. The individual impact of the specific components on the rate constants of epoxy reaction has not been investigated in detail. Based on the structure of N-phenacylpyridinium salt the substances described in the present study were varied due to the exchange of counter ion and different substituents. Investigating the impact of the specific substituent with focus on the reaction of epoxy groups there is a dependence found for three main factors. First, depending on whether to use a phenyl or methyl group as substituent there was found an impact on the process of photolysis. Furthermore, concerning the dependences on the pyridine derivative and the counter ion, it was found that pyridine derivatives with electron withdrawing groups and counter ions, which can build strong acids, accelerate the rate constants of the epoxy reaction. Vice versa, pyridine derivatives with electron donating groups and counter ions, which can form weaker acids, decrease the rate constants.
The determined rate constants and the formulation of substances discussed in the present thesis in an adhesive formulation show the suitability of selected substances as photoinitiators for the polymerization of epoxy resins.
Nanoparticles are sensitive and robust systems; they are particularly reactive due to their large surface area and have properties that the bulk material does not have. At the same time, the production of nanoparticles is challenging, because even with the same parameters and conditions, the parameters can vary slightly from run to run. In order to avoid this, this work aims to develop a continuous synthesis in the microjet reactor for nanoceria. The aim is to obtain monodisperse nanoparticles that can be used in biosensors.
This work focuses on two precipitation syntheses with the intermediate steps of cerium carbonate and cerium hydroxide, as well as a microemulsion synthesis for the production of nanoceria. The cerium oxide nanoparticles are compared using different characterisation and application methods. The synthesised nanoparticles will be characterised with respect to their size, stability, chemical composition and catalytic capabilities, by electron microscopy, X-ray diffraction, Raman spectroscopy and photoelectron spectroscopy.
The biosensor systems to evaluate the nanoceria are designed to detect histamine and glucose or hydrogen peroxide, which are resulting from the oxidation of histamine and glucose. Hydrogen peroxide and glucose are detected by an electrochemical sensor and histamine by a colorimetric sensor system.
Speziell in Anwendungen mit intensiver Temperatur- und Korrosionsbeanspruchung finden vermehrt Phosphate als sogenannte chemische Binder für Hochleistungskeramiken Verwendung. Konkret ist die Summe der Reaktionsverläufe während des Bindemechanismus in Folge einer thermisch-induzierten Aushärtung und somit die Wirkungsweise von Phosphatbindern prinzipiell innerhalb der Fachliteratur nicht eindeutig untersucht. Innerhalb dieser Arbeit wurden aufbauend auf einer umfangreichen strukturanalytischen Prüfungsanordnung (Festkörper-NMR, RBA, REM-EDX) einer exemplarischen phosphatgebundenen Al₂O₃-MgAl₂O₄-Hochtemperaturkeramikzusammensetzung unter Einbeziehung verschiedenartiger anorganischer Phosphate grundlegende Bindemechanismen charakterisiert. Mechanisch-physikochemische Eigenschaftsuntersuchungen (STA, Dilatometrie, DMA, KBF) deckten zudem den Einfluss der eingesetzten Phosphate auf die Eigenschaftsentwicklungen der Feuerfestkeramiken bezüglich des Abbindeverhaltens, der Biegefestigkeit sowie der thermischen Längenänderung auf, welche mit Strukturänderungen korreliert wurden. Es wurde gezeigt, dass sich Bindemechanismen bei Verwendung von Phosphaten temperaturgeleitet (20 °C ≤ T ≤ 1500 °C) grundsätzlich aus zwei parallel ablaufenden Reaktionsabfolgen zusammensetzen, wobei die sich entwickelnden Phosphatphasen innerhalb der Keramikmasse quantitativ und qualitativ bezüglich ihrer Bindewirkung bewertet wurden. Zum einen wurde die Bildung eines festigkeitssteigernden Bindenetzwerks aus Aluminiumphosphaten meist amorpher Struktur identifiziert und charakterisiert. Dieses bindungsfördernde, dreidimensionale Aluminiumphosphatnetzwerk baut sich innerhalb der Initialisierungs- und Vernetzungsphasen temperaturgeleitet kontinuierlich über multiple Vernetzungsreaktionen homogen auf. Zum anderen werden Reaktionsabfolgen durch parallel ablaufende Strukturumwandlungen nicht aktiv-bindender Phosphatspezies wie Magnesium-, Calcium- oder Zirkoniumphosphate ergänzt, welche lediglich thermische Umwandlungsreaktionen der Ausgangsphosphate darstellen. Vermehrt bei T > 800 °C geht das phosphatische Bindenetzwerk Festkörperreaktionen mit MgAl₂O₄ unter Ausbildung und Agglomeration von Magnesium-Orthophosphat-Sinterstrukturen ein. Die Bildung dieser niedrigschmelzenden Hochtemperaturphasen führt zu einem teilweisen Bruch des Bindenetzwerks.
Thousands of chemicals from daily use are being discharged from civilization into the water cycle via different pathways. Ingredients of personal care products, detergents, pharmaceuticals, pesticides, and industrial chemicals thus find their way into the aquatic ecosystems and may cause adverse impacts on the ecology. Pharmaceuticals for instance, represent a central group of anthropogenic chemicals, because of their designed potency to interfere with physiological functions in organisms. Ecotoxicological effects from pharmaceutical burden have been verified in the past. Therapeutic groups with pronounced endocrine disrupting potentials such as steroid hormones gain increasing focus in environmental research as it was reported that they cause endocrine disruption in aquatic organisms even when exposed to environmentally relevant concentrations. This thesis considers the comprehensive investigation of the occurrence of corticosteroids and progestogens in wastewater treatment plant (WWTP) effluents and surface waters as well as the elucidation of the fate and biodegradability of these steroid families during activated sludge treatment. For the first goal of the thesis, a robust and highly sensitive analytical method based on liquid chromatography-tandem mass spectrometry (LC-MS/MS) was developed in order to simultaneously determine the occurrence of around 60 mineralocorticoids, glucocorticoids and progestogens in the aquatic environment. A special focus was set to the compound selection due to the diversity of marketed synthetic steroids. Some analytical challenges have been approved by individual approaches regarding sensitivity enhancement and compound stabilities. These results may be important for further research in environmental analysis of steroid hormones. Reliable and low quantification limits are the perquisite for the determination of corticosteroids and progestogens at relevant concentrations due to low consumption volumes and simultaneously low effect-based trigger values. Achieved quantification limits for all target analytes ranged between 0.02 ng/L and 0.5 ng/L in surface water and 0.05 ng/L to 5 ng/L in WWTP effluents. This sensitivity enabled the detection of three mineralocorticoids, 23 glucocorticoids and 10 progestogens within the sampling campaign around Germany. Many of them were detected for the first time in the environment, particularly in Germany and the EU. To the best of our knowledge, this in-depth steroid screening provided a good overview of single steroid burden and allowed for the identification of predominantly steroids of each steroid
type analyzed for the first time. The frequent detection of highly potent synthetic steroids (e.g. triamcinolone acetonide, clobetasol propionate, betamethasone valerate, dienogest, cyproterone acetate) highlighted insufficient removal during conventional Summary wastewater treatment and indicated the need for regulation to control their emission since the steroid concentrations were found to be above the reported effect-based trigger values for biota. Overall, the study revealed reliable environmental data of poorly or even not analyzed steroids. The results complement the existing knowledge in this field but also providednew information which can beused particularly for compound prioritization in ecotoxicological research and environmental analysis. Based on the data obtained from the monitoring campaign, incubation experiments were conducted to enable the comparison of the biodegradability and transformation processes in activated sludge treatment for structure-related steroids under aerobic and standardized experimental conditions. The compounds were accurately selected to cover manifold structural moieties of commonly used glucocorticoids, including non-halogenated and halogenated steroids, their mono- and diesters, and several acetonide-type steroids. This approach allowed for a structure-based interpretation of the results. The obtained biodegradation rate constants suggested large variations in the biodegradability (half-lifes ranged from < 0.5 h to > 14 d). An increasing stability was identified in the order from non-halogenated steroids (e.g. hydrocortisone), over 9α-halogenated steroids (e.g. betamethasone), to C17-monoesters (e.g. betamethasone 17-valerate, clobetasol propionate), and finally to acetonides (e.g. triamcinolone acetonide), thus suggesting a strong relationship of the biodegradability with the glucocorticoid structure. Some explanations for this behavior have been received by identifying the transformation products (TPs) and elucidating individual transformation pathways. The results revealed the identification of the likelihood of transformation reactions depending on the chemical steroid structure for the first time. Among the identified TPs, the carboxylates (e.g. TPs of fluticasone propionate, triamcinolone acetonide) have been shown persistency in the subsequent incubation experiments. The newly identified TPs furthermore were frequently detected in the effluents of full-scale wastewater treatment plants. These findings emphasized i) the transferability of the lab-scale degradation experiments to real world and that ii) insufficient removals may cause adverse effects in the aquatic environment due to the ability of the precursor steroids and TPs to interact with the endocrine system in biota. For the last goal, the conceptual study for glucocorticoids was applied to progestogens.
Here, two sub-types of the steroid family frequently used for hormonal contraception were selected (17α-hydroxyprogesterone and 19-norstestosterone type). The progestogens showed a fast and complete degradation within six hours, and thus empathizes pronounced biodegradability. However, cyproterone acetate and dienogest Summary have been found to be more recalcitrant in activated sludge treatment. This was consistent with their ubiquitously occurrence during the previous monitoring campaign. The elucidation of TPs again revealed some crucial information regarding the observed behavior and highlighted furthermore the formation of hazardous TPs. It was shown that 19-nortestosterone type steroids are able to undergo aromatization at ring A in contact with activated sludge, leading to the formation of estrogen-like TPs with a phenolic moiety at ring A. In the case of norethisterone the formation of 17α-ethinylestradiol was confirmed, which is a well-known potent synthetic estrogen with elevated ecotoxicological potency. Thus, the results indicated for the very first time an unknown source of estrogenic compounds, particularly for 17α-ethinylestradiol. In conclusion, some steroids were found to be very stable in activated sludge treatment, others degrade well, and others which do degrade but predominantly to active TPs depending on their chemical structure. Fluorinated acetal steroids such as triamcinolone acetonide and fluocinolone acetonide are poorly biodegradable, which is reflected in high concentrations detected ubiquitously in WWTP effluents. Endogenous steroids and their most related synthetic once such as hydrocortisone, prednisolone or 17α-hydroxyprogesterone are readily biodegradable. Regardless their high influent concentrations, they are almost completely removed in conventional WWTPs. Steroids between this range have been found to form elevated quantities of TPs which are partially still active, which particularly the case for betamethasone, fluticasone propionate, cyproterone acetate or dienogest. The thesis illustrates the need for an extensive evaluation of the environmental risks and carried out that corticosteroids and progestogens merit more attention in environmental regulatory and research than it is currently the case
Die Biopolyester Cutin und Suberin stellen hydrophobe Grenzbarrieren dar, die sich im Laufe der Evolution der Landpflanzen entwickelt haben. Cutin bildet den Hauptbestandteil der Cuticula, die den Pflanzen Schutz vor unkontrollierter Transpiration bietet. Die Einlagerung von Suberin in die Zellwände definierter Zellen des Wurzelgewebes ermöglicht eine kontrollierte Aufnahme von Wasser und Nährstoffen. Zu den wichtigsten monomeren Bestandteilen dieser biologischen Polyester gehören langkettige α,ω-Dicarbonsäuren und ω-Hydroxycarbonsäuren. Bisher wurde der mikrobielle Abbau der Makromoleküle unzureichend erforscht. Zur Entschlüsselung der Zersetzung ist es notwendig, den Kreislauf der monomeren Bestandteile im Boden zu betrachten. Hierzu eignen sich vor allem Experimente mit positionsspezifisch ¹³C -markierten α,ω-Dicarbonsäuren und ω-Hydroxycarbonsäuren, die in der vorliegenden Arbeit erstmals synthetisch zugänglich gemacht wurden. Die Synthesen umfassten Dicarbonsäuren der geradzahligen Kettenlängen C12 bis C30, deren Carboxygruppen ¹³C -markiert sind. Ebenfalls wurde die Synthese von ω-Hydroxycarbonsäuren der Kettenlängen C14, C18, C22 und C30 mit ¹³C-Markierung an der Carboxygruppe realisiert. Weitere Zielverbindungen waren ω-Hydroxycarbonsäuren der Kettenlängen C14, C15, C18, C22 und C30, deren terminales hydroxyliertes Kohlenstoffatom mit ¹³C markiert ist. Im Rahmen der durchgeführten Arbeit gelang es, alle 19 Zielcarbonsäuren erfolgreich in hohen Ausbeuten und Reinheiten darzustellen. Die Synthese der isotopenmarkierten Verbindungen erforderte die Entwicklung spezieller auf die jeweiligen Zielsubstanzen individuell angepasster Syntheserouten, die den Einbau des Kohlenstoffisotops ¹³C ermöglichten. Für alle Zielverbindungen erfolgte die Einführung des ¹³C durch die Verwendung von ¹³C -markiertem Kaliumcyanid (99 at%). Wegen der hohen Kosten des ¹³C -markierten Ausgangsstoffes wurden alle Reaktionen zunächst unter der Verwendung analoger unmarkierter Edukte optimiert. Der letzte Teil der Arbeit bestand in der Ausführung eines Inkubationsexperimentes mit den ¹³C -markierten α,ω-Dicarbonsäuren der Kettenlängen C12, C18, C22 und C30. Mittels Phospholipidfettsäure-Analyse konnte gezeigt werden, dass die ¹³C -Dicarbonsäuren zu unterschiedlichen Anteilen von verschiedenen Mikroorganismengruppen zum Aufbau von Phospholipidfettsäuren verwendet wurden. Außerdem konnte durch die Anreicherung des CO2 mit dem Isotop ¹³C nachgewiesen werden, dass die ¹³C -markierten Fettsäuren von den Mikroorganismen zur Energiegewinnung abgebaut wurden. Für zukünftige Arbeiten wäre es interessant, Ausschnitte der Cutin- und Suberinstruktur nachzubilden. Durch die Veresterung der ¹³C -markierten α,ω-Dicarbonsäuren und der ¹³C -markierten ω-Hydroxycarbonsäuren untereinander oder mit Alkoholen könnten Dimere und Oligomere hergestellt werden.
Modellbildung zum Abbindeverhalten von PCE-verflüssigten und CA-Zement-gebundenen Feuerbetonen
(2021)
Feuerbetone werden als Auskleidung in industriellen Hochtemperaturaggregaten, wie beispielsweise in der Eisen- und Stahlindustrie, eingesetzt. Nach dem Mischen und dem Gießen eines Feuerbetons in Formen bzw. Schalungen, muss dieser abbinden und eine ausreichende Festigkeit ausbilden. Die Kinetik der Abbindevorgänge und somit auch das Erhärtungsverhalten variiert dabei stark in Abhängigkeit der Zusammensetzung, vor allem hinsichtlich des Bindemittels und der Additive, des Feuerbetons. In der Praxis der Herstellung von Feuerbetonen kommt es häufig zu Beschädigungen der hergestellten Bauteile oder Auskleidungen durch das Fließen noch nicht ausreichend abgebundener Feuerbetone bzw. die Beschädigung von Ecken und Kanten während des Ausschalens oder Bauteilen reißen durch mechanische Belastung beim Umsetzen oder beim Transport. Diese Beschädigungen basieren auf Fehleinschätzungen zum Abbindefortschritt und der korrespondierenden Festigkeitsausprägung der Feuerbetone. Diese wiederum sind auf Lücken im Stand der Technik zurück zu führen.
Für PCE-verflüssigte und CA-Zement-gebundene Korund-Feuerbetonen mit einer Al₂O₃- und Al₂O₃-SiO₂-Matrix, werden die Defizite des Stands der Technik für diese Feuerbetonklasse identifiziert: Diese liegen im Bereich der Verflüssigungswirkung und des ersten Ansteifens der Feuerbetone, der Hydratation des CA-Zements in den Feuerbetonen und der Festigkeitsausprägung der Feuerbetone. Hieraus leitet sich ein entsprechender Forschungsbedarf ab.
Am Beispiel von zwei PCE-verflüssigten (PCE mit kurzer Hauptkette und langen Seitenketten sowie PCE mit langer Hauptkette und kurzen Seitenketten) und CA-Zement-gebundenen (70 % Al₂O₃) Feuerbetonen mit einer reaktivtonerde-basierten und einer reaktivtonerde-mikrosilika-basierten Matrix werden abbindekinetische Untersuchungen durchgeführt. Anhand verschiedener abbindekinetischer Messmethoden, wie Schallgeschwindigkeit oder elektrischer Leitfähigkeit, und einigen ergänzenden Messung, wie beispielsweise das ζ-Potential, wird der Abbindeverlauf der Feuerbetone untersucht und die Defizite aus dem Stand der Technik aufgeklärt.
Im Detail wurde der Stand der Technik um folgende Erkenntnisse ergänzt:
• Verflüssigung von Feuerbetonen mit PCE-Molekülen: Es wurde festgestellt, dass die Verflüssigungswirkung und das erste Ansteifen maßgeblich durch die Struktur der Verflüssigermoleküle hervorgerufen werden.
PCE-Moleküle mit langen Seitenketten verflüssigen eher sterisch. Durch die Vermittlung von Ca²⁺ aus dem CA-Zement wird die Adsorption der PCE-Moleküle verstärkt. Freie PCE-Moleküle können auf CAH-Phasen (Hydratationsprodukte) adsorbieren und somit die Fließfähigkeit des Feuerbetons für eine gewisse Zeit aufrechterhalten.
PCE-Moleküle mit kurzen Seitenketten verflüssigen elektrosterisch. Bei Lösung von Ca²⁺ aus dem CA-Zement kommt es zu einer Ca-PCE Gel-Bildung und einer korrespondierenden Koagulation der Feuerbetonmatrix und der Feuerbeton steift zeitnah nach dem Mischen an.
• Hydratation von CA-Zement: Die Hydratation von CA-Zement in den Feuerbetonen wird wesentlich durch die Länge der Seitenketten der PCE-Moleküle bzw. der Anwesenheit von Zitronensäure beeinflusst.
In Feuerbetonen die mit PCE-Molekülen mit langen Seitenketten verflüssigt wurden, kann der CA-Zement weitestgehend frei hydratisieren. Der CAH-Phasenanteil steigt in zwei Abschnitten, getrennt von einer dormanten Phase. Die dormante Phase der CA Zementhydratation wurde auf eine Lösungshemmung der Al-O-H-Passivierungsschicht auf dem CA-Zement bei mäßigem pH-Wert (pH = 12,3) zurückgeführt.
In Feuerbetonen die mit PCE-Molekülen mit kurze Seitenketten und Zitronensäure verflüssigt werden, wird die Hydratationsreaktion durch eine Ca-Citrat-PCE-Al(OH)₄-Gelbildung stark gehemmt. Es besteht die Vermutung, dass die Bindung von Ca²⁺ in dem Gel zum einen eine sehr ausgeprägte dormante Phase (pH < 12,3), mit einer schlechten Löslichkeit der Passivierungsschicht, bewirkt und zum anderen auch die Fällung von CAH-Phasen unterdrückt.
• Festigkeitsausprägung von CA-Zement-gebundenen Feuerbetonen:
Eine Koagulation bewirkt die erste Festigkeitssteigerung der Feuerbetone auf σB < 1 MPa. Im Anschluss findet die Hauptfestigkeitssteigerung auf Grund von Austrocknung durch Hydratation und Verdunstung statt. Der weitere Teil der Festigkeitssteigerung wird durch die Reduzierung der Porosität durch expansive CA-Zementhydratation und die hohe spezifische Oberfläche sowie deren weitere Erhöhung durch die CA-Zementhydratation bewirkt.
Aus den einzelnen abbindekinetischen Effekten können, zusammen mit dem Stand der Technik und den neuen Erkenntnissen, mikrostrukturelle Abbindemodelle und Modelle zur Festigkeitsentwicklung der Feuerbetone abgeleitet werden. In Folge kann für die zwei Feuerbetone zu jedem Zeitpunkt des Abbindens eine Aussage zum Abbindefortschritt und zur Festigkeitsausprägung getätigt werden. Einige der Abbindemechanismen und festigkeitsbildenden Mechanismen können auf andere Feuerbetonzusammensetzungen übertragen werden.
Method development for the quantification of pharmaceuticals in aqueous environmental matrices
(2021)
As a consequence of the world population increase and the resulting water scarcity, water quality is the object of growing attention. In that context, organic anthropogenic molecules — often defined as micropollutants— represent a threat for water resources. Among them, pharmaceuticals are the object of particular concerns due to their permanent discharge, their increasing consumption and their effect-based structures. Pharmaceuticals are mainly introduced in the environment via wastewater treatment plants (WWTPs), along with their metabolites and the on-site formed transformation products (TPs). Once in the aquatic environment, they partition between the different environmental compartments in particular the aqueous phase, suspended particulate matter(SPM) and biota. In the last decades, pharmaceuticals have been widely investigated in the water phase. However, extreme polar pharmaceuticals have rarely been monitored due to the lack of robust analytical methods. Moreover, metabolites and TPs have seldom been included in routine analysis methods although their environmental relevance is proven. Furthermore, pharmaceuticals have been only sporadically investigated in SPM and biota and adequate multi-residue methods are lacking to obtain comprehensive results about their occurrence in these matrices. This thesis endeavors to cover these gaps of knowledge by the development of generic multi-residue methods for pharmaceuticals determination in the water phase, SPM and biota and to evaluate the occurrence and partition of pharmaceuticals into these compartments. For a complete overview, a particular focus was laid on extreme polar pharmaceuticals, pharmaceutical metabolites and TPs. In total, three innovative multi-residue methods were developed, they include analytes covering a broad range of physico-chemical properties. First, a reliable multi-residue method was developed for the analysis of extreme polar pharmaceuticals, metabolites and TPs dissolved in water. The selected analytes covered a significant range of elevated polarity and the method would be easily expendable to further analytes. This versatility could be achieved by the utilization of freeze-drying as sample preparation and zwitterionic hydrophilic interaction liquid chromatography (HILIC) in gradient elution mode. The suitability of HILIC chromatography to simultaneously quantify a large range of micropollutants in aqueous environmental samples was thoroughly studied. Several limitations were pointed out: a very complex and time-consuming method development, a very high sensitivity with regards to modification of the acetonitrile to water ratio in the eluent or the diluent and high positive matrix effects for certain analytes. However, these limitations can be overcome by the utilization of a precise protocol and appropriate labeled internal standards. They are overmatched by the benefits of HILIC which permits the chromatographic separation of extreme polar micropollutants. Investigation of environmental samples showed elevated concentrations of the analytes in the water phase. In particular, gabapentin, metformin, guanylurea and oxypurinol were measured at concentrations in the µg/L range in surface water. Subsequently, a reliable multi-residue method was established for the determination of 57 pharmaceuticals, 47 metabolites and TPs sorbed to SPM down to the low ng/g range. This method was conceived to cover a large range of polarity in particular with the inclusion of extreme polar pharmaceuticals. The extraction procedure was based on pressurized liquid extraction (PLE) followed by a clean-up via solvent exchange and detection via direct injection-reversed-phase LC-MS/MS and freeze-drying HILIC-MS/MS. Pharmaceutical sorption was examined using laboratory experiments. Derived distribution coefficients Kd varied by five orders of magnitude among the analytes and confirmed a high sorption potential for positively charged and nonpolar pharmaceuticals. The occurrence of pharmaceuticals in German rivers SPM was evaluated by the investigation of annual composite SPM samples taken at four sites at the river Rhine and one site at the river Saar between the years 2005 and 2015. It revealed the ubiquitous presence of pharmaceuticals sorbed to SPM in these rivers. In particular, positively charged analytes, even very polar and nonpolar pharmaceuticals showed appreciable concentrations. For many pharmaceuticals, a distinct correlation was observed between the annual quantities consumed in Germany and the concentrations measured in SPM. Studies of composite SPM spatial distribution permitted to get hints about specific industrial discharge by comparing the pollution pattern along the river. For the first time, these results showed the potential of SPM for the monitoring of positively charged and nonpolar pharmaceuticals in surface water. Finally, a reliable and generic multi residue method was developed to investigate 35 pharmaceuticals and 28 metabolites and TPs in fish plasma, fish liver and fish fillet. For this matrix, it was very challenging to develop an adequate clean-up allowing for the sufficient separation of the matrix disturbances from the analytes. In the final method, fish tissue extraction was performed by cell disruption followed by a non-discriminating clean-up based on silica gel solid-phase extraction(SPE) and restrictive access media (RAM) chromatography. Application of the developed method to the measurement of bream and carp tissues from German rivers revealed that even polar micropollutants such as pharmaceuticals are ubiquitously present in fish tissues. In total, 17 analytes were detected for the first time in fish tissues, including 10 metabolites/TPs. The importance of monitoring metabolites and TPs in fish tissues was confirmed with their detection at similar concentrations as their parents. Liver and fillet were shown to be appropriate for the monitoring of pharmaceuticals in fish, whereas plasma is more inconvenient due to very low concentrations and collection difficulties. Elevated concentrations of certain metabolites suggest possible formation of human metabolites in fish. Measured concentrations indicate a low bioaccumulation potential for pharmaceuticals in fish tissues.
Key mechanisms for the release of metal(loid)s from a construction material in hydraulic engineering
(2017)
Hydraulic engineering and thus construction materials are necessary to enable the navigability of water ways. Since, a variety of natural as well as artificial materials are used, this materials are world wide tested on a potential release of dangerous substances to prevent adverse effects on the environment. To determine the potential release, it is important to identify and to understand key mechanisms which are decisive for the release of hazardous substances. A limited correlation between the conditions used in regulatory tests and those found in environmental systems is given and hence, often the significance of results from standardised tests on construction materials is questioned, since they are not designed to mimic environmental conditions.
In Germany industrial by-products are used as armour stones in hydraulic engineering. Especially the by-product copper slag is used during the last 40 years for the construction of embankments, groynes and coastal protection. On the one hand, this material has a high density and natural resources (landscape) are protected. One the other hand, the material contains high quantities of metal(loid)s. Therefore the copper slag (product name: iron silicate stones) is very suitable as test material. Metal(loid)s examined were As, Sb and Mo as representatives for (hydr)oxide forming elements and Cd, Co, Cu, Fe, Ni, Pb and Zn were studied as representatives for elements forming cations during the release.
Questions addressed in this Thesis were: (i) can we transfer the results from batch experiments to construction scenarios under the prevalent environmental conditions, (ii) which long-term trends exist for the release of metal(loid)s from copper slags and (iii) how environmental conditions influence the leaching of metal(loid)s from water construction materials?
To answer the first question the surface depending release of the metal(loid)s from the construction materials was examined. Therefore, batch leaching experiments with different particle sizes and a constant liquid/solid ratio were performed. In a second step a comparison between different methods for the determination of the specific surface area of armour stones with a 3D laser scanning method as a reference were performed. In a last step it was possible to show that via a roughness factor the results of the specific surface area from small stones, measured with gas adsorption, can be connected with the results from armour stones, determined with an aluminium foil method. Based on calculations of the specific surface area, it was possible to significantly improve catchment scale calculation about the release of metal(loid)s and to evaluate a potential impact of construction materials in hydraulic engineering on the water chemistry of rivers and streams.
To answer the second question long-term leaching diffuse gradient in thin films supported experiments were performed for half a year. Diffuse gradients in thin films (DGT) is an in situ method to passive sample metal(loid)s in water, sediments and soils. They were used as a sink for metal(loid)s in the eluate to provide solution equilibriums. Thus the exchange of the eluent, which is performed normally in long-term experiments, was superfluous and long-term effects under undisturbed conditions were studied. The long-term leaching experiments with DGT have proven to be capable (i) to differentiate between the depletion of the material surface and the solution equilibriums and (ii) to study sorption processes with or without a further release of the analytes. This means for the practically relevant test material copper slag that: (i) the cations Cd, Co, Cu, Ni and Pb are confirmed to be released from the slag over the whole time period of six months, (ii) a surface depletion of Zn was detected, and (iii) that the (hydr)oxide forming elements As, Mo and Sb were released from the slag over the hole periods of six months but the release was masked by adsorption to Fe-oxide colloids, which were formed during the leaching experiments. It was confirmed, that sulphide minerals are the main source for long-term release of Cd, Cu, Ni, Pb and Mo.
To answer the third question short-term leaching experiments simulating environmental conditions in hydraulic engineering were performed. One factor is the salinity. The influence of this parameter was tested in batch experiments with sea salt solution (30 g/l), river Rhine water, ultra pure water and in addition with different NaCl concentration (5, 10, 20 and 30 g/l). In general, the ionic strength is an important factor for the metal(loid) release but the composition of the water (e.g. the HCO3- content) may superimpose this effect. Therefore, the concentrations of the metal(loid)s in the experiments with ultra-pure water spiked with sea salt or native river water and the ultra-pure water spiked with NaCl were significantly different. In a second experiment the influence of the environmental parameters and the interactions between the environmental parameters pH (4–10), sediment content (0 g–3.75 g), temperature (4 °C–36 °C) and ionic strength (0 g/l–30 g/l NaCl) on the release of metal(loid)s from the test material was examined. The statistical Design of Experiments (DoE) was used to study the influence of these factors as well as their interactions. All studied factors may impact the release of metal(loid)s from the test material to the eluent, whereas the release and the partitioning between sediment and eluate of metal(loid)s was impacted by interactions between the studied factors. The main processes were sorption, complexation, solubility, buffering and ion exchange. In addition, by separating the sediment from the slag after the experiments by magnetic separation, the enrichment of metal(loid)s in the sediment was visible. Thus, the sediment was the most important factor for the release of the metal(loid)s, via pH, temperature and ionic strength, because the sediment acted as a sink.