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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.
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 presence of anthropogenic chemicals in the natural environment may impact both habitats and human use of natural resources. In particular the contamination of aquatic resources by organic compounds used as pharmaceuticals or household chemicals has become evident. The newly identified environmental pollutants, also known as micropollutants, often have i) unknown ecotoxicological impacts, ii) unknown partitioning mechanisms, e.g. sorption to sediments, and iii) limited regulation to control their emission. Furthermore, like any compound, micropollutants can be transformed while in the environmental matrix to unknown transformation products (TPs), which add to the number of unknown chemicals to consider and thus increase the complexity of risk management. Transformation is at the same time a natural mechanism for the removal of anthropogenic compounds, either by complete degradation (mineralisation) or to innocuous TPs. However, how transformation occurs in real-world conditions is still largely unknown. During the transport of micropollutants from household wastewater to surface water, a large amount of transformation can occur during wastewater treatment—specifically during biological nitrifying–denitrifying treatment processes. The thesis considers the systematic optimisation of laboratory investigative techniques, application of sensitive mass-spectrometry-based analysis techniques and the monitoring of full-scale wastewater treatment plants (WWTPs) to elucidate transformation processes of five known micropollutants.
The first of the five compounds investigated was the antibiotic trimethoprim. Incubation experiments were conducted at different analyte spike concentrations and different sludge to wastewater ratios. Using high-resolution mass spectrometry, a total of six TPs were identified from trimethoprim. The types of TPs formed was clearly influenced by the spike concentration. To the best of our knowledge, such impacts have not been previously described in the literature. Beginning from the lower spike concentration, a relatively stable final TP was formed (2,4-diaminopyrimidine-5-carboxylic acid, DAPC), which could account for almost all of the transformed trimethoprim quantity. The results were compared to the process in a reference reactor. Both by the detection of TPs (e.g., DAPC) and by modelling the removal kinetics, it could be concluded that only experimental results at the low spike concentrations mirrored the real reactor. The limits of using elevated spike concentrations in incubation experiments could thus be shown.
Three phenolic micropollutants, the antiseptic ortho-phenylphenol (OPP), the plastics additive bisphenol A (BPA) and the psychoactive drug dextrorphan were investigated with regard to the formation of potentially toxic, nitrophenolic TPs. Nitrite is an intermediate in the nitrification– denitrification process occurring in activated sludge and was found to cause nitration of these phenols. To elucidate the processes, incubation experiments were conducted in purified water in the presence of nitrite with OPP as the test substance. The reactive species HNO2, N2O3 and the radicals ·NO and ·NO2 were likely involved as indicated by scavenger experiments. In conditions found at WWTPs the wastewater is usually at neutral pH, and nitrite, being an intermediate, usually has a low concentration. By conducting incubation experiments inoculated with sludge from a conventional WWTP, it was found that the three phenolic micropollutants, OPP, BPA and dextrorphan were quickly transformed to biological TPs. Nitrophenolic TPs were only formed after artificial increase of the nitrite concentration or lowering of the pH. However, nitrophenolic-TPs can be formed as sample preparation artefacts through acidification or freezing for preservation, creating optimal conditions for the reaction to take place.
The final micropollutant to be studied was the pain-reliever diclofenac, a micropollutant on the EU-watch list due to ecotoxicological effects on rainbow trout. The transformation was compared in two different treatment systems, one employing a reactor with suspended carriers as a biofilm growth surface, while the other system employed conventional activated sludge. In the biofilm-based system, the pathway was found to produce many TPs each at relatively low concentration, many of which were intermediate TPs that were further degraded to unknown tertiary TPs. In the conventional activated sludge system some of the same reactions took place but all at much slower rates. The main difference between the two systems was due to different reaction rates rather than different transformation pathways. The municipal WWTPs were monitored to verify these results. In the biofilm system, a 10-day monitoring campaign confirmed an 88% removal of diclofenac and the formation of the same TPs as those observed in the laboratory experiments. The proposed environmental quality standard of 0.05 μg/L might thus be met without the need for additional treatment processes such as activated carbon filtration or ozonation.
Die vorliegende Doktorarbeit hatte zum Ziel zu prüfen, ob Emulsionspolymere auf Acrylatbasis als neuartige Photokatalysatoren bzw. Katalysatoren genutzt werden können.
Auf Grund der Beschaffenheit und der Eigenschaften von Emulsionspolymeren ist davon auszugehen, dass die Nutzung selbiger als Katalysatoren eine neue Art einer chemischen Katalyse ermöglicht. So sollen die Vorteile der heterogenen und homogenen Katalyse vereint und die jeweiligen Nachteile minimiert werden. Als besonders erfolgversprechend hat sich während der praktischen Arbeit die Nutzung von Emulsionspolymeren als Photokatalysatoren herausgestellt.
Die Anbindung der photokatalytisch aktiven Moleküle an/in den Polymerstrang soll kovalent erfolgen. Deshalb war ein erstes Teilziel dieser Arbeit prototypische Katalysatormoleküle zu synthetisieren, die über einen Acrylat-Substituenten verfügen, der in einer radikalischen Polymerisationsreaktion reagieren kann. Als Photokatalysatoren wurden Ruthenium- Polypyridin-Komplexe ausgewählt, die sowohl für eine inter- als auch intramolekulare Photokatalyse zur Herstellung von Wasserstoff aus Wasser geeignet sind. Für organokatalytische Zwecke wurde ein L-Prolin-Derivat synthetisiert, welches jedoch nicht auf seine Polymerisierbarkeit getestet wurde.
In einem ersten Schritt wurden die prototypischen 2,2’-Bipyridin-Liganden synthetisiert. Dabei konnte eine verbesserte Synthesemethode für 4-Brom-2,2’-bipyridin ausgearbeitet werden. Die Funktionalisierung erfolgte letztendlich durch eine Horner-Wadsworth-Emmons-Reaktion, die anschließend an eine Eintopfsynthese zur Darstellung von 4-Formyl-2,2’-biypridin erfolgte. Die prototypischen Photokatalysatoren zeigten mäßige Erfolge (TON: 37-136, 6h, 10% H2O, 470 nm) in Bezug auf die photokatalytische Wasserstoffproduktion, sodass an dieser Stelle eine Verbesserung der entsprechenden katalytischen Systeme erfolgen sollte.
Die Polymerisationsreaktion konnte für zwei intermolekulare Photokatalysatoren und zwei intramolekulare Photokatalysatoren durchgeführt werden. Dabei fiel auf, dass die intermolekularen Photokatalysatoren besser polymerisieren als die intramolekularen Photokatalysatoren. Es wird angenommen, dass dies mit der Löslichkeit der Substanzen im Monomer Ethylmethacrylat zusammen hängt.
Die photokatalytisch funktionalisierten Emulsionspolymere zeigten eine ähnliche photokatalytische Aktivität (TON: 9-101, 6h, 10% H2O, 470 nm) wie die jeweiligen Ausgangsstoffe selbst. Es konnte jedoch bewiesen werden, dass Emulsionspolymere als Photokatalysatoren genutzt werden können, wenn auch noch weitere Arbeiten zur Optimierung der Systeme nötig sind.