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Subaquatic ammunition dumpsites of both, conventional as well as chemical ammunition do practically exist in every single ocean and even in a significant number of inland waters. Most of these dumpsites are based on related post world war dumping actions, when victorious and defeated states had to get rid of their enormous surplus stocks of ammunition and especially the not easy to be handled chemical warfare agents like mustard, phosgene and even nerve agents. After first attempts of conventional destruction like burning, explosion or even simple emptying of chemical agents into pits or holes in the ground, those attempts soon emerged to be very time-consuming and dangerous. Adequate destruction technologies of today’s standards like detonation chambers or plasma kiln did just not exist at that time. The persons in charge soon focused on a much more promising solution attempt: the dumping of this ammunition into surrounding water bodies. In the case of the post World War II dumping actions, the focusing on the former deep water sites soon turned out to be not practicable, based on related enormous costs and logistical problems. The Baltic Sea – with maximum water depths of about 150 m – seemed then to represent the easiest way to get rid of the problematic ammunition. By these activities 65,000 to up to 300.000 tons of chemical ammunition ended up in the Baltic Sea. Concerning conventional ammunition like water mines, torpedo warheads, high explosive devices etc., there is practically no information available but experts assume at least another 100.000 tons of conventional material in the Baltic Sea. Environmental aspects and the issue of protection of the sea were – like in other cases of subaquatic dumping actions worldwide – completely ignored at that time. Nevertheless, subaquatic dumping actions took place until the late 1980ies. Today these dumping sites – whether based on conventional or on chemical ammunition – do represent a very problematic and highly dangerous heritage to present and future generations: Corrosion of the containers and shells results in a not to be forecasted diffuse emission or rather leaking of the ammunition contents into the water body. Substances that are in most cases highly or even extremely toxic for humans, flora as well as fauna contaminate the marine environment with mostly unknown toxicological and ecotoxicological effects. The majority of these substances are known to have carcinogenic, teratogenic and/or mutagenic effects and practically nothing is known about the potential of these substances to end up in the food chains. Especially in recent years there are more and more findings of significantly increased arsenic values in fish that cannot be explained but there are strong signs that these values are based on ammunition dumpsites. Besides the mentioned toxicological and ecotoxicological effects, there are further significant risks as e.g. the possible access to the ammunition also in the context of terrorist and right-wing extremist activities, the continuous catching of and resulting injuring of fishermen by ammunition, the constant endangering of the civil and commercial shipping by direct contact or rather too close convergence to dumped ammunition especially in the context of self detonation or a sudden release of significant amounts of these substances e.g. in the context of an accident and last but not least the uncontrollable landing of containers and ammunition as well as already flushed out contents on coasts and beaches. Basically can be stated that there is still a significant need of action and scientific investigation in the general topic of subaquatic ammunition dumpsites and that related measures have to be taken immediately – especially concerning our sense of responsibility for future generations.
Siliziumorganische Substanzen sind aus dem Alltag kaum wegzudenken. Sie kommen in vielfältiger Form vor und finden durch ihre Stabilität in vielen Produkten des Haushalts und der Industrie Anwendung. Eine Freisetzung in die Umwelt ist unvermeidbar. Siliziumorganische Substanzen konnten bereits in allen Umweltkompartimenten (Luft, Wasser, Boden) analytisch nachgewiesen werden. Welche Risiken von dieser Stoffgruppe ausgehen, ist noch nicht abschließend geklärt. Dennoch gibt es Hinweise auf negative Auswirkungen auf Mensch und Umwelt. Deshalb sollten Strukturen in siliziumorganischen Substanzen untersucht werden, die einen Abbau in der Umwelt begünstigen, um die Akkumulation dieser Stoffe in der Umwelt zu verringern. Dafür wurden diverse biotische und abiotische Abbautests mit unterschiedlichen siliziumorganischen Substanzen durchgeführt. Der Fokus der vorliegenden Arbeit lag vor allem in der biologischen Abbaubarkeit der Substanzen. Es wurden die Organisation for Economic Co-operation and Development (OECD)-konformen Tests Closed-Bottle-Test (CBT, OECD 301D) und Manometrischer Respirationstest (MRT, OECD 301F) durchgeführt. Die Hydrolysierbarkeit wurde mithilfe des Hydrolysetests OECD 111 bei unterschiedlichen pH-Werten untersucht. Bei bestimmten Substanzgruppen ohne biologischen Abbau wurde das Verhalten der Substanzen bei Bestrahlung mit verschiedenen Bestrahlungsquellen untersucht. Die Analyse der Primärelimination der siliziumorganischen Substanzen erfolgte je nach Substanzeigenschaften mithilfe der Hochleistungsflüssigkeitschromatografie gekoppelt mit einem Spektrometer mit ultraviolettem und sichtbarem Licht (HPLC-UV/Vis) oder der Gaschromatografie gekoppelt mit einem Massenspektrometer (GC-MS). Die Transformationsprodukte wurden hingegen mithilfe der Flüssigkeitschromatografie gekoppelt mit einem Mehrfach-Massenspektrometer (LC-MSn) analysiert. Für eine umfassende Bewertung des biologischen Abbaus von siliziumorganischen Substanzen wurden ein Vergleich mit analogen Kohlenstoffverbindungen und eine Aufstockung mit Daten aus der Datenbank der Europäischen Chemikalien Agentur (ECHA) durchgeführt. Die Gruppierung der Substanzen nach ihren Strukturmerkmalen wurde hinzugezogen, um Rückschlüsse auf die Abbaubarkeit zu ziehen. Eine besser biologisch abbaubare Grundstruktur brachte für die Benzenderivate keine Verbesserung der biologischen Abbaubarkeit. Dennoch hatte die Einführung von +M-Gruppen am Aromaten einen positiven Einfluss auf die Geschwindigkeit und den Grad des photolytischen Abbaus. Die Bestrahlungsquelle hatte ebenfalls einen deutlichen Einfluss auf die Eliminierungsrate während des Photolyseexperiments. Mit einer Veränderung der Wellenlängen in den kurzwelligen Bereich und der daraus resultierenden energiereicheren Strahlung konnten die Substanzen schneller und teilweise vollständig primär eliminiert werden. Bei allen Abbaupfaden hatte die Hydrolyse eine entscheidende Rolle und wurde als einer der Hauptabbauprozesse charakterisiert. Bei einer Verbindung wurde im Nachgang an die biotischen und abiotischen Abbautests eine ausführliche Aufklärung der elf gebildeten Transformationsprodukte vorgenommen. Um den Einfluss von Silizium in organischen Substanzen auf die biologische Abbaubarkeit zu untersuchen, wurde der direkte Vergleich von siliziumorganischen Substanzen und deren Kohlenstoffanaloga im CBT durchgeführt. Dabei hat sich gezeigt, dass drei von fünf Kohlenstoffverbindungen und keine siliziumorganische Verbindung als leicht biologisch abbaubar eingestuft werden konnten. In allen bis auf einen Fall konnten für die Kohlenstoffverbindungen höhere Abbauraten im CBT beobachtet werden. Die Hydrolyse wurde als erforderlicher Schritt vor dem biologischen Abbau von siliziumorganischen Substanzen identifiziert. Das siliziumfreie Produkt der Hydrolyse bestimmte den Grad des biologischen Abbaus. Die gute biologische Abbaubarkeit der einen siliziumorganischen Verbindung resultierte aus der leicht hydrolysierbaren Silizium-Stickstoff-Bindung und der leichten biologischen Abbaubarkeit des siliziumfreien Hydrolyseproduktes. Die siliziumhaltigen Reaktionsprodukte der Hydrolyse waren nicht biologisch abbaubar. Bioabbaudaten aus eigenen Experimenten, aus vorhergehenden in der Arbeitsgruppe durchgeführten analogen Arbeiten und aus der ECHA-Datenbank wurden zusammengetragen, um einen Datensatz zu generieren. Die 182 Substanzen des Datensatzes wurden hinsichtlich ihrer Struktur gruppiert, um allgemeine Erkenntnisse für die biologische Abbaubarkeit von siliziumorganischen Verbindungen abzuleiten. Es gab Gruppen mit Substanzen, die überhaupt nicht biologisch abbaubar waren (z. B. zyklische, lineare und verzweigte Siloxane). Gruppen, die Substanzen mit Ethern, Estern, Oximen, Aminen und Amiden enthielten, waren hydrolyseanfällig, sodass auch leicht biologisch abbaubare Zwischenprodukte gebildet werden konnten. Die siliziumfreien Hydrolyseprodukte waren meist biologisch abbaubar, während die siliziumhaltigen Hydrolyseprodukte persistent waren. Allgemein hat sich gezeigt, dass Modifikationen am Molekül einen positiven Einfluss auf die Abbaubarkeit haben können. Beispielsweise können Heteroatome eine Veränderung der Polarität bzw. der Elektronendichte hervorrufen, was die Photolyse- und Hydrolysefähigkeit und folglich auch den Bioabbau zum Positiven verändern kann. Das Einführen solcher Heteroatome oder funktioneller Gruppen in Polysiloxanketten kann demnach ein vielversprechender Ansatz für leichter abbaubare siliziumorganische Verbindungen sein. Nicht abbaubare Stoffe sollten vermieden werden, wenn sie nach ihrer Verwendung in die Umwelt gelangen.
Polyzyklische Aromatische Verbindungen (PAV) im Grundwasser teerölkontaminierter Altlastenstandorte
(2010)
Es wurde das Grundwasser von sieben verschiedenen mit teerölkontaminierten Altlastenstandorten in Deutschland (Stuttgart, Düsseldorf, Wülknitz, Lünen, Offenbach, Karlsruhe) und Österreich (Brunn am Gebirge) untersucht. 45 Einzelverbindungen, darunter PAK, NSO(hetero)-PAV sowie Derivate und Metabolite der PAK und PAV, konnten dabei in signifikanten Konzentrationen nachgewiesen werden. Für alle betrachteten Standorte ergab sich ein vergleichbares Schadstoffmuster. Allein 22 Verbindungen konnten für alle Standorte nachgewiesen werden. Die Identifizierung und Quantifizierung der PAK und PAV erfolgte mittels flüssig-flüssig-Extraktion und an-schließender GC-(EI)-MS Messung der Proben. Besonders zwei Standorte (Karlsruhe, Brunn a.G.) mit einer reaktiven Wand als Sanierungsverfahren wurden genauer betrachtet. Die Untersuchungen ergaben, dass es ab Inbetriebnahme der Anlagen mit Hilfe des reaktiven Reaktormaterials Aktivkohle über 10 Jahre möglich war, neben den hinlänglich bekannten EPA-PAK, auch die polareren, gut wasserlöslichen und in erhöhten Konzentrationen auftretenden NSO(hetero)-PAV sowie deren Derivate und Metabolite erfolgreich aus dem kontaminierten Grundwasserstrom zu entfernen.
Fire plays an important role in the earth system by influencing ecosystems and climate, but climate in turn also influences fire. The system became more complex when humans started using fire as a tool. Understanding the interaction between humans, fire and climate is the major aim of paleofire research. Understanding changes in these three aspects in the past will help predicting future climate, fire and human interactions. The use of lake sediment cores as natural archives for reconstructing past fire activity by counting charcoal particles is well established. This present dissertation is dedicated to the evaluation and application of specific organic molecular markers for biomass burning: levoglucosan, mannosan and galactosan were used as proxies for reconstructing past fire activity in lake sediments thorough the entire Holocene. First, a new analytical method was developed using high-performance anion exchange chromatography combined with mass spectrometry to separate and detect these three monosaccharide anhydrides in lake sediments. The suitability of this analytical method was proven by comparing the levoglucosan, mannosan and galactosan results in selected lake sediment samples from Lake Kirkpatrick, New Zealand and by correlating the results with macroscopic charcoal. Furthermore, the method was successfully applied to a lake sediment core from Lake Petén Itzá, Guatemala to reconstruct regional Holocene fire history. The analyses of levoglucosan were combined with fecal sterols to reconstruct late Holocene human fire interactions at Lake Trasimeno, Italy, demonstrating low fire activity during the Roman period. This combination of studies proves that these molecular markers are valid fire proxies in sediments from multiple locations around the globe. Comparison of levoglucosan, mannosan and galactosan concentrations with macroscopic charcoal trends in Lake Kirkpatrick and Lake Petén Itzá, suggests that the molecular markers represent more regional fire history and low temperature fires in contrast to macroscopic charcoal, which is a local fire proxy. In addition, vegetation changes (Lake Kirkpatrick and Lake Petén Itzá) and charcoal morphotypes (Lake Petén Itzá) were compared to the levoglucosan/mannosan and levoglucosan/(mannosan+galactosan) ratios suggesting that these ratios may be a suitable tool to track burned fuel. Biodegradation tests demonstrate the potential degradation of levoglucosan, mannosan and galactosan if dissolved in water, but findings in ancient sediment samples suggest that particle-bound levoglucosan, mannosan and galactosan can be buried in sediments over millennial time scales. Although uncertainties still exist, the results of this research suggests that organic molecular markers are a suitable regional fire proxy and isomer ratios may help understand changes in burned vegetation.
Verbräuche von Arzneistoffen, die auf das menschliche Nervensystem wirken (Neurologika), unterliegen aufgrund der auf dem Markt befindlichen Arzneistoffvielfalt einem ständigen Wandel. Zudem waren die Haupteintragspfade für Neurologika in die aquatische Umwelt bisher nicht eindeutig geklärt. Haushalte (diffuser Eintrag) und Einrichtungen des Gesundheitswesens (punktueller Eintrag), wie psychiatrische Fachkliniken oder Pflegeheime, wurden als maßgebliche Eintragspfade diskutiert. Ziel dieser Arbeit war es deshalb, Arzneimittelverbräuche und damit verbundene Arzneistoffemissionen durch Haushalte und Einrichtungen des Gesundheitswesens mit Hilfe einer neu entwickelten Methode abzuschätzen. Bei dieser Methode wurde das jeweilige Ausmaß der Emissionen durch die Kalkulation von Abwasserkonzentrationen und den Vergleich von Verbrauchsmengen an Arzneistoffen bestimmt. Im Ergebnis konnte gezeigt werden, dass sich Arzneimittelverbrauchsmuster in psychiatrischen Fachkliniken und Pflegeheimen von denen in allgemeinen Krankenhäusern und Haushalten unterscheiden. Außerdem konnte mit dieser Methode deren jeweiliger Beitrag am gesamten Arzneistoffeintrag in das kommunale Abwasser eingeschätzt und in hohen Mengen in das Abwasser eingetragene Arzneistoffe identifiziert werden. Durch Haushalte wurde das hinsichtlich des Umweltverbleibs und -verhaltens wenig untersuchte Antiepileptikum Gabapentin in hohen Mengen in das Abwasser eingetragen. Die Bedeutung von Einrichtungen des Gesundheitswesens am Arzneimitteleintrag in das kommunale Abwasser konnte für alle untersuchten Einrichtungstypen im Vergleich zu Haushalten als gering eingestuft werden. Bestimmte einrichtungstypische Arzneistoffe, insbesondere Neurologika, können bei regionaler Betrachtung jedoch eine größere Rolle spielen. Insbesondere Quetiapin wurde in psychiatrischen Fachkliniken und Pflegeheimen als Substanz mit hohen Verbrauchsmengen und hohem Emissionspotential identifiziert. Ausgehend von diesen Erkenntnissen wurden Gabapentin und Quetiapin tiefergehend hinsichtlich ihres Verbleibs und ihres Verhaltens in der aquatischen Umwelt charakterisiert. Beide Arzneistoffe wurden bei verschiedenen Startkonzentrationen zur Simulation eines technischen Behandlungsverfahrens mit UV-Licht bestrahlt. Im weiteren Verlauf wurden Gabapentin und Quetiapin und die jeweilige Muttersubstanz im Gemisch mit gebildeten Phototransformationsprodukten hinsichtlich biologischer Abbaubarkeit im Closed Bottle Test und im Manometrischen Respirationstest nach OECD-Richtlinien und hinsichtlich toxischer Eigenschaften im Leuchtbakterientest und im Umu-Test beurteilt. Die Strukturaufklärung von Photo- und Biotransformationsprodukten erfolgte mittels hochauflösender Massenspektrometrie. Im Ergebnis konnten weder Gabapentin noch Quetiapin bei hohen Startkonzentrationen durch Photolyse über 128 min mineralisiert oder vollständig eliminiert werden. Identische Phototransformationsprodukte wurden bei unterschiedlichen Startkonzentrationen für die UVBehandlung gebildet. Die Arzneistoffe Gabapentin und Quetiapin waren nach OECD-Richtlinien im Closed Bottle Test nicht leicht biologisch abbaubar. Die photolytischen Gemische von Gabapentin sind nicht besser als Gabapentin selbst abbaubar und die Phototransformationsprodukte wurden im Closed Bottle Test ebenfalls nicht eliminiert. Auch das photolytische Gemisch von Quetiapin im Closed Bottle Test war nicht besser biologisch abbaubar als Quetiapin selbst. Die Phototransformationsprodukte von Quetiapin und Quetiapin selbst unterlagen beim Closed Bottle Test und im Manometrischen Respirationstest verschiedenen biologischen Transformationsprozessen und führten zur Bildung von verschiedenen Biotransformationprodukten. Das in biologischen Abbautests von Quetiapin maßgeblich gebildete Biotransformationprodukt BTP 398 konnte in diversen Flusswasserproben nachgewiesen werden. Dies lässt sich höchstwahrscheinlich damit erklären, dass BTP 398 unter anderem auch beim humanen Metabolismus gebildet wird. Die Langzeit-Leuchthemmung und die Zellvermehrungshemmung im Leuchtbakterientest stiegen im Verlauf der Photolyse von Gabapentin durch Bildung von Phototransformationsprodukten. Dies deutet auf eine erhöhte Toxizität der Phototransformationsprodukte im Vergleich zu Gabapentin hin. Bei Quetiapin war unter Photolyse keine Abnahme der schon vorhandenen Toxizität beim Leuchtbakterientest zu erkennen. Gabapentin, Quetiapin und deren Phototransformationsprodukte wiesen im Umu-Test keine Genotoxizität auf. …
After being administrated to humans or animals, pharmaceuticals may be metabolized by a variety of mechanisms and pathways within the body. Once these compounds and/or their metabolites are excreted, they may undergo degradation in the aquatic environment. Unfortunately, a rapid and complete mineralization cannot always be guaranteed, whereas relatively stable transformation products (TPs) may be formed. The largest part of older studies focused on investigation of the elimination kinetics of parent compounds without considering the amount and chemical structure of individual TPs. Only recently, there is an increasing trend to deliver such information. Nevertheless, since drugs are defined as significant environmental pollutants, it is not only important to elucidate their TPs, but also necessary to investigate whether these formed compounds preserve the same mode of action as the parent compound or are even more toxic. Thus, two main objectives of this thesis can be formulated. Firstly, to highlight the concern originated by metabolites and transformation products of pharmaceuticals that contaminate the environment. Hereby, the already-published knowledge on TPs within a certain selection of drugs is assessed to exemplify the number and quality of the existing information on their TPs. Secondly, to particularly investigate the fate of the antibiotic ciprofloxacin (CIP). This is done by (a) evaluating the suitability and sustainability of the photolytic decomposition as an advanced water treatment technique, (b) monitoring the course of genotoxicity of the irradiated mixtures using a battery of genotoxicity and cytoxicity in vitro assays, and (c) considering the potential genotoxicity for CIP´s individual TPs by the employment of in silico approaches using quantitative structure activity relationships (QSAR) models. This thesis based on the results and conclusions of five articles, which can be found in the appendix. A systematic literature review was conducted on the current state of knowledge on pharmaceuticals and its derivatives in the environment. Two groups, namely antibiotics and anticancer drugs, were considered more closely with respect to the availability of chemical structures for their TPs. Furthermore, the photodegradation of CIP as well as a preliminary toxicity assessment of its identified TPs were investigated in three research papers. An extensive review with a table at its core shows the existing data on 158 TPs, which already have an assigned registry number in chemical abstracts service (CAS-RN), was presented. In total, 294 TPs, identified with chemical structures in the literature, were found for 15 compounds out of the 21 that were selected as target compounds. Eleven TPs, created from CIP, were identified by high-performance liquid chromatography/high-resolution multiple-stage mass spectrometry. It was detected that the transformation of CIP mainly occurred through substitution of fluorine, defluorination, hydroxylation of the quinolone core and the breakdown of the piperazine ring. Some of the identified TPs of CIP were predicted as genotoxic by QSAR analysis, while the experimental testing for a few genotoxic and cytotoxic endpoints showed that the potential of the resultant mixtures could be primarily dependent on the concentration of residual CIP. In contrast, irradiation mixtures were neither mutagenic in the Ames Test nor genotoxic in the in vitro Micronucleus Test. It is possible that the effect of the TPs was masked by antagonistic mixture interactions and/or they were not formed at effectively concentrations. Nevertheless, all of the identified TPs of CIP still retained the core quinolone moiety, which is responsible for the biological activity. Thus, a more comprehensive assessment, encompassing more genotoxic endpoints, chemical analysis characterization and exposure analyses, needs to be conducted. Information available on TPs demonstrates that already slight changes in treatment conditions and processes result in the formation of different TPs. Nevertheless, most of the transformation products could neither be identified nor fully assessed regarding their toxicity. This, in turn, presents a major challenge for the identification and assessment of TPs. Hence, from a practical and sustainability point of view, limiting the input of pharmaceuticals into effluents as well as improving their (bio)degradability and elimination behavior, instead of only relying on advanced effluent treatments, is urgently needed. Solutions that focus on this
Recently polyfluoroalkyl compounds (PFCs) were discovered as emerging persistentorganic pollutants. Because of their unique physicochemical properties due to theircombination of lipophilic and hydrophilic characteristics, PFCs have been widely used inmany consumer products, such as polymerisation aids, stain repellents on carpets, textiles, andpaper products for over 50 years. From the production and use of these products, PFCs can bereleased into the environment. Scientific concern about PFCs increased due to their globaldistribution and ubiquitous detection in the environment, especially in marine mammals.An analytical protocol was developed for the analysis of PFCs in water samples andvarious biological matrices. The samples were analysed for 40 PFCs plus 20 isotope-labelledinternal standards using high performance liquid chromatography/negative electrosprayionisation-tandem mass spectrometry (HPLC/(-)ESI-MS/MS). Furthermore, the analyticalquality of the laboratory has been approved in interlaboratory studies.In the first part of this Ph.D. thesis was investigated the occurrence, distribution patternand transportation mechanisms of PFCs in seawater. The rivers had a high influence on thedistribution of PFCs in offshore surface water in the German Bight, with decreasingconcentrations with increasing distance from the coast (see publication I). The research onthe spatial distribution of PFCs in coastal area is very important for the understanding of thetransportation and fate of PFCs in the marine environment. Furthermore, the longitudinal andlatitudinal distribution of PFCs in surface water of the Atlantic Ocean was investigated (seepublication II). The results indicate that trans-Atlantic Ocean currents caused the decreasingconcentration gradient from the Bay of Biscay to the South Atlantic Ocean and theconcentration drop-off close to the Labrador Sea. These data are very useful for globaltransportation models, in which industrial areas are considered as sources, and ocean watersas sinks of PFCs.The second part of this Ph.D. thesis examined the mechanisms and pathways of PFCs inharbor seals (Phoca vitulina) and their temporal trends in the German Bight. Firstly, thewhole body burden of PFCs and their tissue distribution (i.e., liver, kidney, lung, heart, blood,brain, muscle, thyroid, thymus, and blubber) was investigated in harbor seals (seepublication III). This study is relevant for calculation of the bioaccumulation potential ofthese compounds in marine mammals. Secondly, the temporal trends over the last decade andassociations between PFC concentration and the evidence of diseases, spatial distribution, ageand sex were evaluated in archived harbor seal livers (see publication IV). The results showsignificant declining concentrations of many PFCs indicating the replacement of these PFCsby shorter chained and less bioaccumulative compounds.Several studies were performed besides the main issue of the Ph.D. work. Firstly, watersamples were collected along the river Elbe into the North Sea to examine the distribution ofPFCs in the dissolved and particulate phase, their discharge into the North Sea, and theinfluence of waste water treatment plant effluents to the riverine mass flow. Furthermore,surface water samples were collected in the North Sea, Baltic Sea and Norwegian Sea, wherethe occurrence and spatial distribution between river estuaries, coastal waters, in brackish aswell as salt water, and open sea water were compared. Finally, within the frame of a researchstay at the National Institute of Advanced Industrial Science and Technology (AIST) in Japan,the partitioning behaviour of PFCs between pore water and sediment in two sediment coresfrom Tokyo Bay was investigated.This Ph.D. thesis has improved our knowledge of the occurrence and distribution of PFCsin water and biota highlighting association between PFCs and pathological conditions,potential sources and sinks, spatial distribution, and changes in their pattern and long-termperspective trends.
The principle of this thesis was to study the environmental fate of three highly used psychotropic drugs and this achieved through: 1) examining the biodegradability of TMI, DMI and CPTX, 2) studying the behaviour of TMP, DMI and CPTX in photodegradation tests using Xe and UV lamps with studying the effect of different environmental conditions on their UV-photodegradation behaviour, 3) monitoring the primary elimination of TMP, DMI and CPTX during photodegradation and biodegradation tests using HPLC, and measuring their degree of mineralization by means of dissolved organic carbon analyser (DOC), 4) elucidating the structures of the transformation products (TPs) which formed during the degradation of TMI, DMI and CPTX by using LC-MS/MS analysis, 5) analysing the biodegradability of their TPs by laboratory tests and in-silico assessments in order to determine the fate and persistence of these TPs in the aquatic environment, 6) conducting in-silico toxicity predictions for the selected psychotropic drugs and their TPs in human (carcinogenicity, genotoxicity and mutagenicity) and in eco-system (toxicity to microorganisms and toxicity in rainbow trouts). As an overall conclusion, the present work demonstrates that a combination of laboratory simulation tests, LC-MS/MS analysis and in-silico tools result in valuable new information regarding environmental fate of three important psychotropic drugs and their TPs. This dissertation also highlights that different environmental conditions such as temperature, initial drug concentration and pH can differently affect the degradation behaviour of pharmaceuticals even when they are highly structurally related. Therefore, one cannot conclude from one pharmaceutical to another but each one needs to be investigated individually and this present a great challenge for risk assessment kinetics of chemicals in the aquatic environment. The results presented here showed that the investigated pharmaceuticals and their TPs can negatively affect the environment which may be harmful to the ecosystem as they might have been present for decades in the aquatic environment without any knowledge of their environmental fate or connected risk. Therefore, further work needs to be done including analysis of environmental samples (e.g., surface waters), as well as laboratory toxicity tests to further expand knowledge on their exact environmental impact.
Recent studies have confirmed that the aquatic ecosystem is being polluted with an unknown cocktail of pharmaceuticals, their metabolites and/or their transformation products (TPs). Although individual pharmaceuticals are typically present at low concentrations, their continuous input into the aquatic ecosystem and their toxic and persistent presence are the major environmental concerns. Therefore, it is necessary to assess the environmental risk caused by these aquatic pollutants. Data on exposure are required for quantitative risk assessment of parent compounds and their transformation products (TPs) and/or metabolites. Such data are mostly missing, especially for TPs, because of the non-availability of TPs and very often metabolites for experimental testing. Therefore, the application of different in silico tools for qualitative risk assessment can be used. Also, the presence of these micro-pollutants (active pharmaceutical ingredients, APIs) in the aquatic cycle are increasingly seen as a challenge to the sustainable management of water resources worldwide due to ineffective effluent treatment and other measures for their input prevention. Given the poor prognosis for effluent treatment (‘end of the pipe’ approach) for input prevention of APIs in the environment, it is necessary to focus on the ‘beginning of the pipe’ strategy. The very beginning of the pipe is the molecules themselves. Therefore, novel approaches are needed like designing greener pharmaceuticals, i.e. better biodegradable ones in the aquatic environment after their release. Therefore, the present research work focused on two important topics a) assessment of the environmental risk associated with the presence of highly prescribed drugs and their TPs; b) demonstrating the feasibility of the ‘benign by design’ concept for designing biodegradable drug derivatives, which will have the better biodegradability in the environment after their release. The present thesis includes four research articles (1-4) which address these approaches. The first article is about the qualitative environmental risk assessment using the example of transformation products formed during photolysis (photo-TPs) of Diatrizoic acid (DIAT). Photolysis is the chemical reaction in which the compound is broken down by photons and often in combination with hydroxyl radicals. Photolysis is the most common abatement process of micro-pollutants in the environment. The qualitative risk assessment of DIAT and selected photo-TPs was performed by the PBT approach (i.e. Persistence, Bioaccumulation and Toxicity), using chemical analysis, experimental biodegradation test assays, QSAR models with several different toxicological endpoints and in silico read-across approaches. The second article addresses a tiered approach of implementing green and sustainable chemistry principles for theoretically designing better biodegradable and pharmacologically potent pharmaceuticals derivatives. Photodegradation process coupled with LC-MSn analysis, biodegradability testing and in silico tools such as quantitative structure-activity relationships (QSAR) analysis and molecular docking proved to be a very significant approach for the preliminary stages of designing chemical structures that would fit into the ´benign by design´ concept in the direction of green and sustainable pharmacy. Metoprolol (MTL) was used as an example. The third article was also the conceptual framework to get new drug derivatives that are biodegradable in order to tackle the global challenge of micro-pollutants in the aquatic cycle. This study increased the knowledge about the role of the attachment of certain functionalities to the parent drug molecule for its biodegradability whilst conserving drug-likeness. This approach was in the past a totally neglected issue within drug development. Atenolol (ATL), a selective β1 blocker, was selected as an example to incorporate the additional attribute such as biodegradability into its molecular structure while conserving its substructures responsible for β adrenergic receptor blocker activity. In fourth article, the concept of designing green biodegradable pharmaceuticals has been proven through expanded experimental analysis setting out from the experiences collected as described in article two and three. This study could be considered as a more extensive feasibility study of rational design of green drug derivatives. The non-selective β-blocker Propranolol (PPL) was used as an example. The risk assessment study (Article #1) contributes in enhancing the existing knowledge about the life cycle and behavior (fate) of pharmaceuticals with a special focus on photo-TPs which are generally formed during advanced effluent treatment and enter as such into the environment. Based on the obtained results, the application of the in silico tools for qualitative risk assessment analysis increased knowledge space about the environmental fate of TPs in case of their non-availability for experimental testing. The benign by design studies (Article #2-4) were based on the knowledge and experience collected during the work on DIAT. It demonstrated the feasibility of a novel approach of designing comparatively better degradable and pharmacological potent derivatives through the implementation of ´green chemistry´ principles. However, the present approach is in the juvenile stage and further knowledge has to be collected beforehand for the full implementation of this approach into drug development.
Perfluoroalkyl and polyfluoroalkyl substances (PFASs) have been widely used since 1950 in various consumer products as well as in industrial applications owing to their unique properties, e.g. being hydrophobic and lipophobic at the same time. Nowadays, some of these persistent and man-made PFASs can ubiquitously be found in humans, wildlife and various environmental media. One prominent representative of concern, belonging to the subgroup of perfluorocarboxylates (PFCs) and their conjugate acids (PFCAs), is perfluorooctanoat (PFO) and its conjugate acid (PFOA). Because of its adverse effects on human health and its persistency in the environment industry has started to replace PFO(A) and related long chain chemicals (with seven and more fully fluorinated carbon atoms) with so-called short chain PFASs (less than seven fully fluorinated carbon atoms), including precursors of PFC(A)s. Also these short chain PFC(A)s are persistent and can already be found in humans, ground- and drinking water and in remote regions. However, knowledge gaps exist in understanding the partitioning and the resulting mobility of short chain PFC(A)s in the environment. This is due to the fact that partitioning data of PFC(A)s from standardised experiments can easily be biased by various artefacts, e.g. self-aggregation of the molecules. Therefore, the objectives of this thesis are (i) to quantify the partitioning of PFC(A)s into mobile environmental media, (ii) to show how results from non-standard tests can be used to assess substance properties of concern and (iii) to conclude on whether the environmental exposure to short chain PFC(A)s is of concern from a regulatory point of view. In the first part of this thesis, the environmental mobility of short chain C4-7-PFC(A)s was investigated by quantifying their partitioning under non-standardised semi-environmental conditions into mobile environmental media, focusing on water and air, and comparing it to long chain PFC(A)s. Results are: Partitioning between water and particles in the aeration tank, primary and secondary clarifier of a wastewater treatment plant (WWTP) showed no distinct differences for short chain PFC(A)s compared to their long chain homologues (Paper 1). In a water-saturated sandy sediment column short chain PFC(A)s were not retarded, whereas long chain homologues were retarded by sorption to the sediment (Paper 2). Atmospheric particle-gas partitioning showed a lower fraction sorbed to particles for short chain PFC(A)s compared to long chain ones in samples from a WWTP (Paper 3). Air-water concentration ratios based on samples from the tanks of a WWTP were found to be higher for short chain PFC(A)s compared to long chain PFC(A)s (Paper 1). Additionally, in a newly developed experimental set-up the water to air transfer was used to derive that the pKa of C4-11-PFCAs must be <1.6 instead of up to 3.8 as reported in the literature (Paper 4). Overall, in the investigated systems short chain PFC(A)s showed a higher mobility due to a more pronounced partitioning into mobile environmental media compared to long chain PFC(A)s. In the second part of the thesis it was shown how PFO(A) - owing to its persistent, bioaccumulative and toxic (PBT-)properties – was in the context of this thesis successfully assessed as a substance of very high concern according to the criteria of the European REACH Regulation (EC No 1907/2006) by using data from non-standard tests (Paper 5). In conclusion, based on the knowledge of the high environmental mobility of short chain PFC(A)s and taking into account the argumentation of the PBT-concern of PFO(A), environmental exposure to short chain PFC(A)s is of concern and existing knowledge is already sufficient to initiate measures to prevent emissions of short chain PFC(A)s and their precursors into the environment.