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1. Halobacillus halophilus akkumuliert zum Ausgleich geringer, extrazellulärer Wasserpotentiale kompatible Solute. Bei Anzuchten in Gegenwart von 0,4 – 1,5 M NaCl wurden Glutamin und Glutamat als die dominierenden kompatiblen Solute identifiziert, während zwischen 2,0 und 3,0 M NaCl Prolin das dominierende Solut darstellt. Außerdem wurde Ectoin als zweites kompatibles Solut gefunden, das spezifisch bei hohen Salzgehalten akumuliert wird. Die Konzentrationen während der exponentiellen Wachstumsphase war jedoch um den Faktor 6 – 7 geringer im Vergleich zu Prolin. 2. Aus Wachstumsexperimenten in Gegenwart unterschiedlicher Anionen war bekannt, dass Glutamat, im Gegensatz zu Gluconat und Nitrat, in der Lage ist, das Wachstum von H. halophilus auch in Abwesenheit von Chlorid zu ermöglichen. Um der Frage nachzugehen, ob die wachstumsfördernde Wirkung von unphysiologisch hohen Glutamat-Konzentrationen im Medium auf die Verwendung von Glutamat als kompatiblem Solut in den Zellen zurückzuführen ist, wurden Gesamtsolutepools von Chlorid-, Nitrat-, Gluconat- und Glutamat-gezogenen Zellen gemessen. In NaCl-gezogenen Zellen zeigte sich Glutamat als dominantes Solut, während Prolin und Glutamin einen geringeren Teil am Gesamtpool ausmachten. In Nitrat-gezogenen Zellen betrug der Gesamtpool nur noch 83% und in Gluconat-gezogenen Zellen nur noch 27% im Vergleich zu Chlorid-gezogenen Zellen. Zellen, die mit Glutamat gezogen wurden, zeigten jedoch eine Gesamtkonzentration an Soluten, die ca. 100% über dem Vergleichswert aus Chlorid-gezogenen Zellen lag. Die Konzentration an Glutamin in den Zellen stieg dabei um 168%, die Konzentration an Glutamat sogar um 299%. Die Prolinkonzentration verringerte sich um 32%. Diese Daten belegen, dass der wachstumsstimulierende Effekt von Glutamat auf die Verwendung als kompatibles Solut zurückzuführen ist. 3. Zur Untersuchung der molekularen Grundlage der Salzadaptation sowie der Abhängigkeit von Chlorid in H. halophilus wurde in Zusammenarbeit mit der Gruppe von Prof. D. Oesterhelt (MPI für Biochemie, Martinsried) die Sequenzierung des Genoms begonnen. Das Projekt ist zur Zeit noch nicht abgeschlossen und befindet sich in der „Lückenschluß-Phase“. Die bisherigen Sequenzdaten konnten dennoch für die in dieser Arbeit beschriebenen Untersuchungen herangezogen werden. Das Genom besitzt eine Größe von ca. 4,1 Mbp mit einem ungefähren GC-Gehalt von 40%. Außerdem wurden 2 Plasmide identifiziert mit einer Größe von 16047 und 3329 bp. 4. Die Schlüsselgene bekannter Biosynthesewege für Glutamin und Glutamat konnten identifiziert werden. Darunter befinden sich zwei Isogene für eine Glutamatdehydrogenase (gdh1 und gdh2), ein Gen für die große Untereinheit einer Glutamatsynthase (gltA), zwei Gene für die kleine Untereinheit einer Glutamat-Synthase (gltB1 und gltB2) und zwei Isogene für eine Glutaminsynthetase (glnA1 und glnA2). glnA1 befindet sich in einem Cluster zusammen mit einem Gen, das für einen Regulator kodiert (glnR), wie er auch aus B. subtilis bekannt ist. Über reverse Transkription von mRNA und anschließender PCR-Analyse konnte gezeigt werden, dass sowohl gltA/gltB1 als auch glnA1/glnR in einem Operon organisiert sind. 5. Wurde die Transkriptmenge der in Punkt 4 erwähnten Biosynthesegene in Zellen quantifiziert, die in Gegenwart unterschiedlicher Salzkonzentrationen (0,4 – 3,0 M NaCl) gezogen wurden, so zeigte sich keine Abhängigkeit von der Salzkonzentration für die Gene gltA, glnA1 und gdh1. Über die Transkriptmengen von gdh2 ließ sich keine abschließende Aussage treffen, da die gefundenen Transkriptmengen sehr gering waren und daher zu sehr großen Varianzen bei der Quantifizierung führten. Eine klare Abhängigkeit der Transkriptmenge von der im Medium zugesetzten Salzkonzentration konnte für glnA2 gezeigt werden. Die glnA2 mRNA-Menge stieg dabei mit steigender Salzkonzentration an und erreichte bei 1,5 – 2.0 M NaCl ein Maximum. Bei diesen Salzkonzentrationen war die Menge an mRNA ca. 4 mal höher als der Vergleichswert bei 0,4 M NaCl. Bei höhern Salzkonzentrationen sank die Menge an Transkript wieder leicht und war dann ca. nur noch 3 mal so hoch wie bei 0,4 M NaCl. 6. Die zelluläre Konzentration der glnA2-Transkripte in Abhängigkeit unterschiedlicher Anionen im Anzuchtmedium wurde untersucht. Die Quantifizierung der glnA2–mRNA ergab eine 2 mal höhere Transkriptmenge in Gegenwart von Chlorid verglichen mit Nitrat oder Gluconat. 7. Es wurde nach Enzymaktivitäten der bekannten Schlüsselenzyme im Glutamat und Glutamin-Biosyntheseweg gesucht. Eine Glutamatdehydrogenase und eine Glutamatsynthase – Aktivität konnte nicht oder nur in vernachlässigbarem Maße nachgewiesen werden. Im Gegensatz dazu konnt eine Glutaminsynthetase – Aktivität eindeutig belegt werden. Diese Aktivität erwies sich abhängig von der Art und der Konzentration des angebotenen Anions im Medium. Maximale Aktivitäten wurden mit NaCl in einer Konzentration von 2,5 – 3,0 M erreicht. Interessanterweise erwies sich die Glutaminsynthetase – Aktivität auch abhängig von der Art des im Testpuffers verwendeten Anions. Hier zeigte sich eine deutliche Stimulierung der Aktivität durch das Anion Chlorid. [Die für diesen Punkt zugrunde liegenden Daten wurden im Rahmen einer von mir mitbetreuten Diplomarbeit von Jasmin F. Sydow erhoben und sind aus Gründen der vollständigen Darstellung des Projektverlaufes mitaufgeführt!] 8. Wie im Punkt 1 dargelegt, wird Prolin vor allem bei hohen Salzkonzentrationen in H. halophilus - Zellen akkumuliert. Neben der Abhängigkeit von der Salzkonzentration wurde außerdem die Abhängigkeit von der Wachstumsphase untersucht. Die Analyse der Prolinkonzentrationen während verschiedener Wachstumsphasen in Kulturen, die bei 1,0 bzw. 2,5 M NaCl angezogen wurden, zeigte, (i) dass die Prolinkonzentration während der frühen exponentiellen Phase ca. 2,5-fach erhöht war im Vergleich zu Niedrigsalz-Zellen, (ii) dass die Prolinkonzentration beim Übergang von der frühen in die späte exponentielle Phase dramatisch abnahm (um 64% bei 2,5 M NaCl) und dass (iii) in der stationären Phase Prolin praktisch nicht mehr nachzuweisen war. 9. Die Biosynthesegene für die Herstellung von Prolin aus Glutamat konnten im Genom von H. halophilus identifiziert werden. Es handelt sich dabei um ein Cluster von 3 Genen, die für eine putative Pyrrolin-5-carboxylatreductase (proH), eine Glutamat-5-kinase (proJ), und eine Glutamat-5-semialdehyd-dehydrogenase (proA) kodieren. Mittels reverser Transkription von mRNA und anschließenden PCR-Analysen konnte gezeigt werden, dass die drei Gene ein Operon bilden. 10. Eine Quantifizierung der Transkriptmengen der Biosynthesegene proH, proJ und proA mittels quantitativer PCR in Zellen, die bei unterschiedlichen NaCl-Konzentrationen gezogen wurden, zeigte einen deutlichen Zusammenhang zwischen der Salinität des Mediums und der Menge an Transkript. Diese war umso höher, je höher die Salinität des Mediums war. Die maximale Transkriptmenge (6-fach) wurde bei einer Salzkonzentration von 2,5 M NaCl erreicht. Bei noch höherer Salzkonzentration sank die Transkriptmenge auf die ca. 5-fache Menge des Kontrollwertes ab. 11. Um die Regulation und Dynamik der Osmoregulation unabhängig vom Wachstum untersuchen zu können, wurde ein Zellsuspensions-System für H. halophilus etabliert, bei dem eine konzentrierte Zellsuspension direkt von geringen auf hohe Salzkonzentrationen überführt wurde und bei dem die Prozesse der Transkription, Translation und Solut-Biosynthese erhalten blieben. Beispielhaft wurde dieses System an der Produktion von Prolin nach einem Salzschock von 0,8 auf 2,0 M NaCl getestet. Es zeigte sich bei der Analyse, dass sich die Transkriptmengen unmittelbar nach dem Salzschock deutlich erhöhten und bereits nach 1,5 Stunden ein Maximum erreicht wurde. Verglichen mit dem Wert zu Beginn des Versuches waren die Transkriptmengen ca. 13-fach erhöht, sanken im weiteren Verlauf jedoch wieder ab und blieben bei einer 4-fachen Transkriptmenge konstant. Mit der Erhöhung der Transkriptmenge ging auch eine Erhöhung der Prolinkonzentration einher, die ein Maximum von ca. 6 μmol/mg Protein nach 6 Stunden erreichte. Auch diese Konzentration verringerte sich im weiteren Verlauf wieder und erreichte nach 20 Stunden den Ausgangswert. 12. Um den Einfluß diverser Anionen bzw. Osmolyte im Medium auf die Produktion von Prolin zu untersuchen, wurden Zellsuspensionen von H. halophilus einer Erhöhung der Osmolarität von 0,8 M auf 2,0 M unterzogen. Es zeigte sich dabei, dass die maximale Akkumulation von Prolin in Anwesenheit von Chlorid am höchsten war. Nitrat und Glutamat führten zu ähnlichen, aber leicht geringeren maximalen Konzentrationen (92 bzw. 83% des Chloridwertes). Gluconat führte noch zu einer Akkumulation von ca. 51%, während die anderen Osmolyte zu keiner Akkumulation führten. Eine Analyse der Transkriptmengen zeigte jedoch ein völlig anderes Bild. Während Chlorid, Nitrat und Gluconat zu vergleichbaren Anstiegen der Transkripmengen führten, war die maximale Transkriptmenge der Glutamatinkubierten Zellen 3-9 mal höher als in Vergleichszellen mit Chlorid. In anschließenden Titrationsexperimenten mit verschiedenen Glutamatkonzentrationen konnte gezeigt werden, dass eine minimale Konzentration von 0,2 M Glutamat ausreichend ist, um eine 90-fache Steigerung der Transkriptmenge herbeizuführen. 13. Als Antwort auf Hochsalz-Bedingungen akkumuliert H. halophilus neben Prolin auch Ectoin. Die Ectoinkonzentration bei 2,5 M NaCl war ca. 2-3 mal höher als in Zellen, die bei 1,0 M gezogen wurden. Die Bestimmung der intrazellulären Ectoin-Konzentrationen während des Wachstums zeigte außerdem, dass die Produktion von Ectoin wachstumsphasenabhängig ist. Die Konzentration in der stationären Phase war ca. 5-fach höher als in der exponentiellen Phase. Die Entwicklung der Ectoin- Konzentration verhielt sich somit reziprok zur Entwicklung der Prolin-Konzentration während des Wachstums. 14. Es wurde ein Cluster von drei Genen im Genom von H. halophilus identifiziert, deren Genprodukte die Biosynthese von Ectoin aus Aspartatsemialdehyd katalysieren. ectA kodiert dabei für eine putative Diaminobutyrat-Acetyltransferase, ectB für eine putative Diaminobutyrat-2-oxoglutarat-Transaminase und ectC für eine putative Ectoin-Synthase. Mittels reverser Transkription von mRNA und anschließenden PCR-Analysen konnte gezeigt werden, dass die drei Gene ein Operon bilden. 15. Die Transkription der ect-Gene war abhängig von der Salinität des Mediums. Ab 2,0 M stieg die Menge an RNA um das 10-fache an und erreichte bei 3,0 M ein Maximum mit der 23,5-fachen Menge. 16. Nach einem osmotischen Schock stieg die Konzentration an ect-mRNA signifikant und erreichte ein Maximum nach 3 - 4 Stunden. Das Maximum wurde somit 1,5 – 2,5 Stunden später erreicht als bei anderen Genen der Solute-Biosynthese wie etwa gdh1, das für eine Glutamatdehydrogenase, glnA2, das für eine Glutamin-Synthetase oder proH, das für eine Pyrrolin-5-Carboxylase kodiert. Die maximal erreichten Wert lagen 13-fach (ectA), 6,5-fach (ectB) und 3-fach (ectC) über dem Wert vor dem Salzschock. Gegen EctC wurden polyklonale Antikörper generiert. Western-Blot Analysen mit diesem Antikörper zeigten, dass die EctC-Menge nach 4 Stunden um das 2,5-fache stieg, dann aber wieder abfiel auf das 1,6 – 1,7-fache des Ausgangswertes. Der Rückgang an EctC fand keine Entsprechung in der gemessenen Ectoin-Konzentration, welche über einen Zeitraum von 18 Stunden kontinuierlich anstieg. Die maximale Konzentration nach 18 Stunden betrug das ca. 6,3-fache des Ausgangswertes. 17. Wurden H. halophilus Zellen mit anderen Osmolyten außer NaCl geschockt, so ergab sich folgendes Bild der Regulation der Ectoin-Biosynthese: (i) die Transkription der ect-Gene zeigte keine Chlorid-abhängige Regulation. Die maximale Transkriptmenge wurde in Gegenwart von Nitrat erreicht, wohingegen Gluconat zu vergleichbachen mRNA-Mengen führte wie Chlorid. Glutamat führte nur zu schwacher Stimulierung der Transkription. (ii) auf Ebene der Proteinmenge war zu sehen, dass die Menge an EctC nach osmotischem Schock vergleichbar war in Zellen, die mit Chlorid oder Nitrat inkubiert wurden. Gluconat führte nur zu einer 40%-igen Zunahme während andere Osmolyte nahezu wirkungslos auf die Menge an EctC blieben. (iii) die höchste Akkumulation an Ectoin nach einer plötzlichen Erhöhung der Osmolarität wurde erreicht mit Chlorid (6-fache Zunahme) gefolgt von Nitrat (5,6-fache Zunahme). Gluconat führte lediglich zu einer 3,3-fachen und Glutamat nur noch zu einer 2-fachen Steigerung der Ectoinkonzentration. Glutamat hat somit ähnliche Effekte wie Tartrat, Saccharose oder Sulfat. Succinat führte zu keiner Akkumulation und Glycin sogar zu einer deutlichen Abnahme. Die Produktion von Ectoin ist somit hauptsächlich abhängig vom Anion/Osmolyt und nur untergeordnet von der Osmolarität.
In the past decades, the use and production of chemicals has been on the rise globally due to increasing industrialization and intensive agriculture; resulting in the occurrence and ecotoxicological risks of chemicals of emerging concern (CECs) in the aquatic compartments. Risks include changes in community structure resulting in the dominance of one species and ecosystem imbalance. When dominant disease-causing organisms are in the environment, the disease transmission is increased. For example, host snails for the schistosomiasis, a human trematode disease, are known to be tolerant to pesticide
exposure compared to the predators. This would therefore result in an increased abundance of snails which consequently increase the disease transmission in the human population.
Kenya, being a low income country faces a lot of challenges with provision of clean water, diseases and sanitation facilities, and increasing population which results in intensive agriculture coupled with pesticide use. Although a lot of research has been carried out on the environmental occurrence and risk of CECs (Chapter 1), most of these studies have been done in developed countries with limited information from Africa. Additionally, research in Africa focused on urban areas with limited number of compounds analyzed and mostly in the water phase, and inadequate information on the effects of CECs on the aquatic organisms. In order to reduce this knowledge gap, this dissertation focused on identification and quantification of CECs present in water, sediment and snails from western Kenya, and the contribution of pesticides to the transmission of schistosomiasis.
Chapter 2 gives a summary of the results and discussion of the dissertation. In Chapter 3, a comprehensive chemical analysis was carried out on 48 water samples to identify compounds, spatial patterns and associated risks for fish, crustacean and algae using toxic unit (TU) approach. A total of 78 compounds were detected with pesticides and biocides being the compounds most frequently detected. Spatial pattern analysis revealed limited compound grouping based on land use. Acute risk for crustaceans and algae were driven by one to three individual compounds. These compounds responsible for toxicity were prioritized as candidate compounds for monitoring and regulation in Kenya.
In Chapter 4, an extension of Chapter 3 was done to cover the CECs present in snails and sediment from the 48 sites. A total of 30 compounds were found in snails and 78 in sediments with 68 additional compounds being found which were not previously detected in water. Higher contaminant concentrations were found in agricultural sites than in areas without anthropogenic activities. The highest acute toxicity (TU 0.99) was determined for crustaceans based on compounds in sediment samples. The risk was driven by diazinon and pirimiphos-methyl. Acute and chronic risks to algae were driven by diuron whereas fish were found to be at low to no acute risk.
In Chapter 5, the effect of pesticide contamination on schistosomiasis transmission was evaluated by applying complimentary laboratory and field studies. In the field studies, the ecological mechanisms through which pesticides and physical chemical parameters affect host snails, predators and competitors were investigated. Pesticide data was obtained from the results in chapter 3. The overall distribution of grazers and predators was not affected by pesticide pollution. However, within the grazers, pesticide pollution increased dominance of host snails. On the contrary, the host-snail competitors were highly sensitive to pesticide exposure. For the laboratory studies, macroinvertebrates including Schistosoma-host snails, competitors and predators were exposed to 6 concentrations levels of imidacloprid and diazinon. Snails showed higher insecticide tolerance compared to competitors and predators. Finally, Chapter 6 summarizes the conclusions of this dissertation, placing it in a broader
context. In this dissertation, a comprehensive chemical characterization and risk assessment of CECs has been carried out in freshwater systems; together with the effects of pesticides on schistosomiasis transmission in rural western Kenya. Results of this dissertation showed that rural areas are contaminated posing a risk to aquatic organisms which contribute to schistosomiasis transmission. This shows the need for regular monitoring and policy formulation to reduce pollutant emissions which contributes negatively to both ecological and human health effects.
The environmental impact of climate change is meanwhile not only discussed in the scientific community but also in the general public. However, little is known about the interaction between climate change and pollutants like pesticides. A combination of multiple stressors (e.g. temperature, pollutants, predators) may lead to severe alterations for organisms such as changes in time of reproduction, reproductive success and growth performance, mortality and geographic distribution. The questions if aquatic organisms tend to react more sensitive towards incidents under climate change conditions remains. Therefore, within the present thesis the aquatic ecotoxicological profile of the fungicide pyrimethanil, as an exemplarily anthropogenic used contaminant, was examined.
A large test battery of ecotoxicological standard tests and supplement bioassays with non-model species was conducted to investigate if species-specific or life stage-specific differences occur or if temperature alteration may change the impact of the fungicide. Two of the most sensitive species (Chironomus riparius and Daphnia magna) were used to investigate the acute and chronic thermal dependence of pyrimethanil effects. The results clearly depict that the ecotoxicity of pyrimethanil at optimal thermal conditions did not depend on the trophic level, but was species-specific. With regard to EC10 values the acute pyrimethanil toxicity on C. riparius increased with higher temperature (6.78 mg L-1 at 14°C and 3.06 mg L-1 at 26°C). The chronic response of D. magna to the NOEC (no observed effect concentration) of the fungicide (0.5 mg L-1) was examined in an experiment which lasted for several generations under three simulated near-natural temperature regimes (‘cold year, today’ (11 to 22.7°C), ‘warm year, today’ (14 to 25.2°C) and ‘warm year, 2080’ (16.5 to 28.1°C)). A pyrimethanil-induced mortality increase was buffered by the strongly related increase of the general reproductive capacity, while population growth was stronger influenced by temperature than by the fungicide. At a further pyrimethanil concentration (LOEC – lowest observed effect concentration: 1 mg L-1), a second generation could not be established by D. magna under all thermal regimes.
Besides daphnids, the midge C. riparius was used for a second multigeneration study. In a bifactorial test design it was tested if climate change conditions alter or affect the impact of a low fungicide concentration on life history and genetic diversity. The NOAEC/2 (half of the no observed adverse effect concentration derived from a standard toxicity test) was used as a low pyrimethanil concentration to which laboratory populations of the midges were chronically exposed under the mentioned temperature scenarios. During the 140-day-multigeneration study, survival, emergence, reproduction, population growth, and genetic diversity of C. riparius were analyzed. The results reveal that high temperatures and pyrimethanil act synergistically on life history parameters of C. riparius. In simulated present-day scenarios, a NOAEC/2 of pyrimethanil provoked only slight to moderate beneficial or adverse effects. In contrast, an exposure to a NOAEC/2 concentration of pyrimethanil at a thermal situation likely for a summer under the future expactations uncovered adverse effects on mortality and population growth rate. In addition, genetic diversity was considerably reduced by pyrimethanil in the ‘warm year, 2080’ scenario, but only slightly under current climatic conditions. The multigeneration studies under near-natural thermal conditions indicate that not only the impact of climate change, but also low concentrations of pesticides may pose a reasonable risk for aquatic invertebrates in the future. This clearly shows that thermal and multigenerational effects should be considered when appraising the ecotoxicity of pesticides and assessing their future risk for the environment.
In addition to temperature further multiple abiotic and biotic stressors alterate pollutant effects. Moreover, to better discriminate and understand the intrinsic and environmental correlates of changing aquatic ecosystems, it was experimentally unraveled how the effects of a low-dose of pyrimethanil on daphnids becomes modified by different temperatures (15°C, 20°C, 25°C) and in the presence/ absence of predator kairomones of Chaoborus flavicans larvae. The usage of a fractional multifactorial test design provided the possibility to investigate the individual growth, reproduction and population growth rate of Daphnia pulex via different exposure routes to the fungicide pyrimethanil at an environmentally relevant concentration (0.05 mg L-1) - either directly (via the water phase), indirectly (via algae food), dually (via water and food) or for multiple generations (fungicide treated source population).
The number of neonates increased with increasing temperatures. At a temperature of 25°C no significant differences between the individual treatment groups were observed although the growth was overall inhibited due to pyrimethanil. Besides, at 15 and 20°C it is obvious that daphnids which were fed with contaminated algae had the lowest reproduction and growth rate. The obtained results clearly demonstrate that multiple stress factors can modify the response of daphnids to pollutants. The exposure routes of the contaminant are of minor importance, while temperature and the presence of a predator are the dominant factors impacting the reproduction of D. pulex. It can be concluded that low concentrations of pyrimethanil may disturb the zooplankton community at suboptimal temperature conditions, but the effects will become masked if chaoborid larvae are present. Therefore it seems necessary to observe prospectively if the combination of several stress factors like pesticide exposure and suboptimal temperature may influence the life history and sensitivity of several aquatic invertebrates differently.
Besides standard test organisms it is inevitable to conduct test with aquatic invertebrate which are not yet considered regularly in ecotoxicological experiments. For example molluscs represent one of the largest phyla of macroinvertebrates with more than 100.000 species, being ecologically and economically important. Therefore, within the present study embryo, juvenile, half- and full-life cycle toxicity tests with the snail Physella acuta were performed to investigate the impact of pollutants on various life stages. Different concentrations of pyrimethanil (0.06-0.5 or 1.0 mg L-1) assessed at three temperatures (15°C, 20°C, 25°C) revealed that pyrimethanil caused concentration-dependent effects independent of temperature. Interestingly, the ecotoxicity of pyrimethanil was higher at lower temperature for the embryo hatching and F1 reproduction, but its ecotoxicity for the growth of juveniles and the F0 reproduction increased with increasing temperature. More specifically, it could have been observed that especially during the reproduction test high mortality rates occurred at the highest concentration of 1 mg L-1 at all temperatures. Due to high mortality rates no snails were available for the F1 at the highest concentrations (0.5 and 1.0 mg L-1). Compared to the F0, overall more egg masses were produced in the F1, being all fertile and no mortality occurred. For the F1-generation the strongest pyrimethanil effects were detected at 15°C. A comparison of effect concentrations between both generations showed that the F1 is more sensitive than the F0.
These results indicate that an exposure over more than one generation may give a better overview of the impact of xenobiotics. With the establishment of an embryo and reproduction test under different temperatures and various concentrations of pyrimethanil with P. acuta we could successfully show that molluscs can respond more sensitive than model organisms and that both, chemical and thermal stressor strongly influence the behaviour of the pulmonates. It can be concluded that the high susceptibility for the fungicide observed in gastropods clearly demonstrates the complexity of pesticide-temperature interactions and the challenge to draw conclusions for the ecotoxicological risk assessment of pesticides under the impact of global climate change.
The Southern Ocean (SO) is one of the most pristine regions of our Planet, characterised by high levels of biodiversity (5% of the global diversity) (David and Saucède 2015) and hosting a unique fauna (up to 90% of SO species are endemic) (De Broyer and Danis 2011; Chown et al. 2015). Yet, the knowledge on SO biodiversity is still far from being completed. In addition, the knowledge on the impact that changing environments have on SO species-richness is very little and for some groups, it is still totally unknown. For instance, most of studies generally focus on one single species such as Antarctic krill (Kawaguchi et al. 2011), Clio pyramidata Linnaeus, 1767 (Orr et al. 2005), Globigerina bulloides d'Orbigny, 1826 (Moy et al. 2009), or only on a high taxonomic level (e.g. phylum, class): Echinodermata, Crustacea, Mollusca, Porifera, Bryozoa, Brachiopoda, Hydrozoa, Ascidiacea, Holoturoidea
(Barnes 1999; Rowden et al. 2015; Post et al. 2017; Gutt et al. 2019; Vause et al. 2019; Pineda-Metz et al. 2020). Ultimately, the influence of sea-ice coverage on benthic species diversity was totally unknown prior to this study. In light of this, the objectives of the thesis are:
1. To expand the knowledge on shelf and deep-sea peracarid assemblage structure and abundance on a small regional (Weddell Sea) and on a large regional (Atlantic sector of the SO and South Atlantic Ocean) geographic scale.
2. To assess the environmental variables driving peracarid assemblage structure and abundance from the above mentioned areas.
3. To investigate SO benthic isopod species diversity from the Atlantic sector of the SO and assess the influence of environmental variables on their species-richness and composition.
4. To describe new possible peracarid species by means of integrative taxonomy, using morphological descriptions and whole genome sequencing analyses to support the species identification.
Objective outcomes: The present thesis provides new information on the abundance and assemblage structure based on 64766 peracarid crustaceans from different 28 locations within the Atlantic sector of the SO continental shelf and deep sea (Chapters I-II). These locations are characterised by different environmental conditions, for instance different sea-ice concentrations. Results from Chapters I-II confirmed the dominance of peracarid assemblages in the benthos, with amphipods being the most abundant group, followed by isopods. Sea ice was identified as the main driver shaping benthic peracarid assemblage structure (Chapter I). On a larger geographic scale and wider bathymetric range (e.g. including sampling locations from previous studies performed in the South Atlantic Ocean
and at a depth range from 160 to ~6000 m), depth was the main physical variable driving peracarid assemblage structure (Chapter III). In addition, 16157 isopod specimens from the Atlantic sector of the SO were identified to species level at a smaller scale (Chapter IV). In this case, sea ice was identified as the main physical driver affecting isopod diversity and composition among sampling locations (Chapter IV). Reduced concentration of sea ice
causes a decrease in isopod biodiversity, thus climate change was identified as a huge threat for this taxon and for SO benthos in general. During the identification process, two new isopod species were discovered (Chapter V). The two new species (Notopais sp.1 n. sp. and Notopais sp.2 n. sp.) were accurately described and identified by means of integrative taxonomy. This provided the first whole genome sequencing of benthic isopods from the SO and the first complete mitochondrial genome of the genus Notopais (Chapter V). Thanks to the collaboration with the University of Genoa (Dipartimento di Scienze della Terra dell'Ambiente e della Vita, DISTAV, Italy) and the National Antarctic Museum (MNA) in Genoa, two new SO species of the suborder Valvifera G. O. Sars, 1883 were described by means of classical taxonomy. In this case, a molecular approach could not be used because both new species were represented by a single specimen, therefore it was important to preserve the integrity of the holotypes (Chapters VI-VII).
Wastewater treatment plants (WWTPs) do not eliminate micropollutants completely and are thus important point sources for these substances. In particular, concerns about en-docrine disrupting compounds in WWTP effluents give rise to the implementation of advanced treatment steps for the elimination of trace organic contaminants. The present study investigated ozonation (O3) and activated carbon treatment (AC) at two WWTPs. For an ecotoxicological assessment at WWTP Regensdorf, conventionally treated wastewater, wastewater after ozonation, and ozonated wastewater after sand filtration were evaluated in parallel via the fish early life stage toxicity test (FELST) using rainbow trout (Oncorhynchus mykiss). Additionally, a comparative toxicity evalu-ation of ozonated and activated carbon treated effluents was performed at the pilot scale treatment plant in Neuss (WWTP Neuss). For this purpose, four invertebrate tests and one higher plant toxicity test were selected to assess potential biological effects on or-ganisms [Lemna minor growth inhibition test, chironomid toxicity test with Chironomus riparius, Lumbriculus variegatus toxicity test, comet assay with haemolymph of the zebra mussel (Dreissena polymorpha), reproduction test with Potamopyrgus antipo-darum]. All in vivo assays were performed on site at the treatment plants in flow-through test systems. Furthermore, the present study investigated the effects of ozona-tion and activated carbon treatment on endocrine activities [estrogenicity, anti-estrogenicity, androgenicity, anti-androgenicity, aryl-hydrocarbon receptor (AhR) agonistic activity] with yeast based bioassays using solid phase extracted water samples. To evaluate the removal of in vitro non-specific toxicity, a cytotoxicity assay using a rat cell line was applied. The FELST at WWTP Regensdorf revealed a considerable developmental retardation of test organisms exposed to ozonated WW. This was accompanied by a significant decrease in body weight and length compared to reference water, to the conventionally treated WW, and to the ozonated water after sand filtration. Hence sand filtration obvi-ously prevents from adverse ecotoxicological effects of ozonation. An additional test – starting with yolk-sac larvae – resulted in a significant reduction of vitellogenin levels in fish exposed to ozonated wastewater compared to fish reared in conventionally treat-ed wastewater. This demonstrates the effective removal of estrogenic activity by ozonation. At WWTP Neuss, the reproduction test with the mudsnail P. antipodarum exhibited a decreased reproductive output after advanced treatment compared to conventional treatment. This indicates an effective estrogenicity removal by ozonation and activated carbon treatment and is confirmed by results of the yeast estrogen screen with a reduc-tion of in vitro estrogenic activity by > 75%. The L. variegatus test revealed a signifi-cantly enhanced toxicity after ozonation compared to conventional treatment, whereas this effect was reduced following subsequent sand filtration. When ozonation was applied, a significantly increased genotoxicity was observed, detected with the comet assay using haemolymph of the zebra mussel. Again, this effect was removed by subsequent sand filtration to the level of conventional treatment. Activated carbon treatment even resulted in a significant reduction of genotoxicity. At both treatment plants, adverse effects after ozonation may have been a result of the formation of toxic oxidation by-products. However, sand filtration reduced toxication effects, indicating that these oxidation by-products are readily degradable or adsorbable. The results point out that, in any case, ozonation should not be applied without subsequent biologically active post treatment appropriate for oxidation by-products removal (e.g. sand filtration). However, only activated carbon achieved a toxicity reduction compared to the conventional treated wastewater. Thus, it cannot be excluded that po-tential beneficial effects due to ozonation might be masked by residual toxic oxidation by-products passing the sand filter or ozonation is not as effective in toxicity removal as PAC treatment. The yeast based assays with solid phase extracted samples revealed an effective endo-crine activity removal during ozonation and activated carbon filtration (estrogenicity: 77 – 99%, anti-androgenicity: 63 – 96%, AhR agonistic activity: 79 – 82%). The cyto-toxicity assay exhibited a 32% removal of non-specific toxicity after ozonation com-pared to conventional treatment. Ozonation in combination with sand filtration reduced cytotoxic effects by 49%, indicating that sand filtration contributes to the removal of toxicants. Activated carbon treatment was the most effective technology for cytotoxici-ty removal (61%). Sample evaporation reduced cytotoxic effects by 52% (after activated carbon treatment) to 73% (after ozonation), demonstrating that volatile substances contribute considerably to toxic effects, particularly after ozone treatment. These results confirm an effective removal or transformation of toxicants with receptor mediated mode of action and non-specific toxicants during both investigated treatment steps. However, due to the limited extractability, polar ozonation by-products were neglected for toxicity analysis, and hence non-specific toxicity after O3 is underestimated. In the long run, only on-site comparisons at WW receiving water bodies (e.g. communi-ty analysis of fish, macroinvertebrates, plants, microorganisms) – before and after up-grading WWTPs – allow drawing environmentally relevant conclusions regarding bene-fits and risks of advanced WW treatment methods. Conclusively, the benefits and possible negative impacts have to be carefully evaluated to prove that not more environmental impact will be induced than removed by advanced treatment technologies as each additional treatment requires considerable amounts of energy, resources, and infrastructure facilities. Accordingly, comprehensive sustainable approaches for pollution prevention and wastewater treatment (e.g. source control and source separation) are preferable compared to end-of-pipe treatment systems.
Plastic pollution is a pervasive problem. In the environment, both the physical and chemical aspects of the material contribute to pollution. For instance, discarded plastic is useless waste that is fragmented upon degradation and so-called microplastics <5 mm are formed. Besides, the chemicals added into plastics are usually customized for specific functions, but these can easily transfer from the polymer into an ambient medium. This work examined both of these aspects. Moreover, the question of whether ecotoxicological effects are more likely to appear because of the microparticle properties or the chemicals transferring from the microplastics was addressed. A special focus was laid on the UV-weathering-induced chemical release.
First, conventional and biodegradable plastics made from fossil and bio-based resources were chosen. The different materials (pre-production and recycled pellets as well as final products)were weathered and their leachates evaluated in vitro. The leachates were analyzed with nontarget screening in order to measure the number of transferred chemicals. Plastics identified as toxic were subjected to further investigations in vivo. A biodegradable shampoo bottle was processed to microplastics and the particles’ physical and chemical properties were assessed with the freshwater worm Lumbriculus variegatus. Here, commonly used endpoints such as mortality, reproduction and weight were tested via different exposure routes. Moreover, the freshwater shrimp Neocaridina palmata was exposed to microplastic beads and fragments to clarify if the shape of the particles affects the ingestion and egestion, respectively. Thereafter, two materials that displayed the strongest toxic responses in vitro within the first study were weathered and leached. Finally, the shrimps were exposed to the leachates and the locomotor behavior was used as an ecologically relevant but less frequently studied endpoint.
The results of the studies highlight that plastics are chemically complex mixtures, containing a wide range of chemicals in terms of the number and functionality. These chemicals induced oxidative stress, baseline toxicity and endocrine activities. This shows that pellets represent a processing state that comprises chemically heterogenous materials. Moreover, it was shown that a degradation initiator is not necessarily relevant to trigger inherent substances to leach out from plastics. Despite this, the UV-weathering resulted in increasingly released chemicals and exacerbated the in vitro toxicities. Even plastics assessed as toxicologically harmless prior to weathering released toxic chemical mixtures once they were weathered. One recycled and all of the biodegradable plastics were toxicologically most concerning. This means that such materials are currently not better than conventional, virgin plastics in terms of their toxicity.
To clarify the source of the microplastic toxicity, L. variegatus was exposed to biodegradable microplastics. The particles were ingested by the worms and adversely affected the examined endpoints. In comparison, microplastics that were depleted from their chemicals via a solvent treatment were less toxic. Kaolin as a natural particle control was evaluated alongside and positively affected the weight of the worms. This emphasizes the ecological relevance of fine-sized matter for the test species. The chemicals extracted from the microplastics induced a 100% mortality. A chemical analysis of the material revealed two ecotoxicologically relevant biocides. The physically-mediated effects of the microplastics seemed to be less of a concern for the worms, which is probably linked to their adaptation to high concentrations of naturally occurring particles in the environment. However, the effects related to the chemicals of plastic cannot be ignored, especially for materials that are claimed to be environmentally friendly.
In the third study, the role of the particle shape in the gut passaging of N. palmata was studied. While the particle size was a determinant factor for the ingestion, the ingestion and egestion of the beads and fragments did not differ, respectively. The shrimps ingested less fragments when food was provided than in the absence of food. As for the worms, the shrimps are known to ingest many naturally occurring particles. Their unselective feeding behavior towards the particle shape could indicate that microplastics as a physical pollutant are negligible for the shrimps. That is why the chemicals of the two most toxic in vitro materials were tested with N. palmata. However, no trend towards elevated or reduced movements of the shrimps was observed, even though the leachates contained baseline toxicants. This shows that the in vitro toxicities of plastics are not necessarily indicative for effects to occur at the in vivo level...
Chemical contamination of the environment and thus of aquatic ecosystems is steadily increasing. Whenever environmental pollutants enter a water body, they affect not only the water, but also the sediment. Substances that bind to sediment particles can be stored for a long time, whereby sediments act as sinks for some contaminants. Therefore, sediment
assessments often more accurately describe the contamination of a water body than investigations of the water itself. Among environmental chemicals, endocrine disrupting compounds (EDCs) have gained more and more attention in recent years. Since they interfere with endocrine systems and may disturb reproduction, they endanger the survival of populations or even species. Hazardous substances enter the aquatic environment by different pathways, with sewage treatment plants (STPs) belonging to the most important contamination sources.The main objective of this work is a comprehensive sediment assessment of predominantly small surface waters in the German federal state of Hesse. The 50 study sites, located in 44 different creeks and small rivers, are situated in the densely populated and economically important Frankfurt/Rhine-Main area, as well as in rural and less urbanized regions.
Chemical analytical data, provided by the Hessian Agency for the Environment and Geology (HLUG), indicated different contamination levels of the study sites. In order to investigate the general toxicity of the sediment samples, the oligochaete Lumbriculus variegatus and the midge Chironomus riparius were exposed to whole sediments and apical endpoints regarding biomass, survival, and reproduction were determined. In further experiments, special attention was paid to the contamination with endocrine active compounds. For this purpose, the reproductive success of the New Zealand mudsnail Potamopyrgus antipodarum was analyzed after exposure to whole sediments. Additionally, a yeast-based reporter gene assay was applied with sediment eluates to assess the estrogenic and androgenic activity of the samples. Biotest results were compared with chemical analysis data to investigate whether the test organisms reflect the measured pollution of the study sites and if the observed effects can be explained by chemical contamination.
Five study sites, all located less than 1 km downstream of a STP discharger, were selected for further investigations based on the results of the sediment monitoring. The sediments from these sites were conspicuous due to their general toxic and/or estrogenic activity. In order to investigate whether the observed effects can be ascribed to the effluents, an active biomonitoring study was conducted with the mudsnail P. antipodarum and the zebra mussel Dreissena polymorpha, exposed at study sites located up- and downstream of the discharger.
In addition to endocrine activity, genotoxic effects were investigated using the comet assay and the micronucleus assay. Endocrine activity was examined based on the reproductive output of P. antipodarum and the content of vitellogenin-like proteins in D. polymorpha. Yeast-based reporter gene assays were used to estimate the endocrine potential (estrogen, anti-estrogen, anti-androgen, dioxin-like) of sediment and water samples.
22% of the 50 sediments showed ecologically relevant effects in the biotests with L. variegatus and C. riparius. Only one sediment caused a relevant effect on both test organisms, while the other ten positively tested sediments affected either L. variegatus or C. riparius, probably due to differences in inter-species sensitivities. This suggests that a combination of different biotests is necessary for a comprehensive evaluation of sediment toxicity. 78% of the sediments caused a significantly increased number of embryos in P. antipodarum, which could be ascribed to estrogenic contamination of the sediment samples. An increase in the number of embryos by 60%, as observed in this study, and an associated increase in population size may result in the displacement of other, less competitive species.
In the in vitro tests, 66% of the sediments showed estrogenic activity and 68% showed androgenic activity. Maximum observed values were 40.9 ng EEQ/kg sediment (EEQ = estradiol equivalent) for estrogenic and 93.4 ng TEQ/kg sediment (TEQ = testosterone equivalent) for androgenic activity. Natural and synthetic hormones as well as alkylphenols were the major contributors to the total estrogenicity of environmental samples in several other studies, and are likely responsible for a large part of the estrogenic activity in this case as well. Similarly, androgenic activity is mainly due to natural steroids and their metabolites.
Bioassay results reflect the analytically measured contamination levels at the study sites only very infrequently. This can be ascribed to the occurrence of integrated effects of chemical mixtures present in the sediments. Additionally, effects of substances not included in the analytical program or of substances present in concentrations below the detection limit of the chemical analytical investigations as well as varying bioavailabilities might be relevant. The fact that a large part of the observed effects cannot be explained by the chemical contamination demonstrates the need for effect studies in ecotoxicological sediment assessments.
In order to identify possible causes for the effects observed in the sediment monitoring, e.g. contamination sources, the area types (urban fabrics, arable lands, pasturages, etc.) of the catchment areas belonging to the study sites were analyzed. No significant differences were found between the area profiles of the sampling sites with and without effects in the biotests.
The results indicate that the contamination responsible for the observed effects can be ascribed to different sources. Furthermore, study sites whose sediments exerted significant effects in biotests were located in anthropogenic as well as in predominantly natural areas. The active biomonitoring study at STPs revealed genotoxic and endocrine effects only sporadically.
However, in the in vitro tests considerable endocrine activities of sediment and water samples were determined. No conclusive picture emerges as to whether the observed effects occur more frequently downstream of the dischargers, and thus could be attributed to a contamination by sewage. This indicates that contamination sources other than STP dischargers, for example agricultural runoff, may contribute to the observed effects. Weaker effects and biological activities downstream of a discharger compared to an upstream site might be ascribed to a dilution effect by the effluents. A comparison of the measured in vitro estrogenicity with exposure studies described in the literature shows that adverse effects in aquatic organisms can be expected at the EEQ concentrations determined in the present study.
The results of the sediment monitoring and the STP study revealed a widespread endocrine pollution of small surface waters in Hesse. The fact that the bioassay results only rarely reflect study site contamination as determined by chemical analysis demonstrates the need for effect studies in comprehensive sediment assessments. In some cases STP dischargers increased, in other cases they decreased the observed in vivo effects and in vitro activity of environmental samples. Transferring the results obtained in laboratory studies to the field, adverse effects on aquatic ecosystems can be expected. The study illustrates the need for restrictive measures that contribute to the removal or reduction of environmental pollutants.
For the identification of substances that have so far not been linked to adverse effects on the environment, methods such as effect-directed analyses (EDA) or toxicity identification evaluation (TIE) should be increasingly applied in future studies. Furthermore, bioassays for the assessment of endocrine activity should be implemented in standardized monitoring programs.
Clean water is fundamental to human health and ecosystem integrity. However, water quality deteriorates due to novel anthropogenic pollutants present at microgram per liter concentrations in urban water cycles (termed micropollutants). Wastewater treatment plants (WWTP) have been identified as major point sources for aquatic (micro-)pollutants. Chemical and ecotoxicological analyses have shown that conventional biological WWTPs do not fully remove micropollutants and associated toxicities, which is often because of mobile, polar and/or recalcitrant compounds and transformation products (TPs). To minimize possible environmental risks, advanced wastewater treatment (AWWT) technologies could be a promising mitigation measure. Multiple processes are therefore being developed and evaluated such as ozonation and ozonation followed by granulated activated carbon (GAC) or biological filtration. Assessing the performance of these combined AWWTs was the focus the TransRisk project. Within this project, this thesis accomplished four major goals.
Firstly, the preparation of (waste)water samples was optimised for in vitro bioassays. Acidification, filtration and solid phase extraction (SPE) were tested for their impact on environmentally relevant in vitro endocrine activities, mutagenicity, genotoxicity and cytotoxicity. Significantly different outcomes of these assays were detected comparing neutral and acidified samples. Sample filtration had a lesser impact, but in some cases retention of particle-bound compounds could have caused significant toxicity losses. Out of three SPE sorbents the Telos C18/ENV at sample pH 2.5 extracted highest toxicity, some undetected in aqueous samples. These results indicate that sample preparation needs to be optimised for specific sample matrices and bioassays to avoid false-positive or -negative detects in effect-based analyses.
Secondly, the above listed in vitro toxicities were monitored in a protected region for drinking water production in South-West Germany (2012-2015). Out of 30 sampling sites surface water and groundwater were the least polluted. Nonetheless, a few groundwater samples induced high anti-estrogenic activity that prompted further monitoring. The latter included a waterworks in which no toxicity was detected. Hospital wastewater also had elevated in vitro toxicities and hospitals are, thus, relevant intervention points for source control. The biological WWTPs were effective in removing most of the detected toxicity, and the selected bioassays proved to be pertinent tools for water quality assessment and prioritisation of pollution hotspots.
Thirdly, the in vivo bioassay ISO10872 based on Caenorhabditis elegans (C. elegans) was adapted for this thesis. Using this model, a median effect concentration (EC50) for reproductive toxicity of the polycyclic aromatic hydrocarbon β-naphthoflavone (β- NF) of 114 µg/L was computed which is slightly lower than reported in the scientific literature. β-NF induced cyp-35A3::GFP (a biomarker in transgenic animals) in a time and concentration dependent manner (≤ 21.3–24 fold above controls). β-NF spiked wastewater samples supported earlier hypotheses on particle-bound pollutants. Reproductive toxicity (96 h) and cyp-35A3 induction (24 h) of biologically treated and/or ozonated wastewater extracts and growth promoting effects of GAC/biologically filtered ozonated wastewater extracts were observed. This suggested the presence of residual bioactive/toxic chemicals not included in the targeted chemical analysis. It also highlighted the importance of integrating multiple (apical and molecular) endpoints in wastewater assessments.
Fourthly, five in vitro and the adapted C. elegans bioassay were integrated into a wastewater quality evaluation (developed within TransRisk). Out of the five AWWT options, ozonation (at 1 g O3,applied/g DOC, HRT ~ 18 min) combined with nonaerated GAC filtration was rated most effective for toxicity removal. All five AWWTs largely removed estrogenic and (anti-)androgenic activities, but not anti-estrogenic activity and mutagenicity, which even increased during ozonation. This has been observed in related studies and points towards toxic TPs. These results also emphasized the need for implementing an effective post-treatment for ozonation. The results from a parallel in vivo study with Lumbriculus variegatus and Potamopyrgus antipodarum conducted on site at the WWTP (using flow through systems) were in accordance with the C. elegans results. In this context, it is suggested to further implement C. elegans as sensitive, feasible and ecologically relevant model.
In conclusion, this thesis shows how optimised sample preparation, long-term (in vitro) environmental monitoring, sensitive and ecologically relevant (in vivo) bioassays as well as innovative evaluation concepts, are pivotal in improving the removal of micropollutants and their toxicities with AWWTs. Future research should further develop and evaluate measures at sewer systems, conventional biological, tertiary and other advanced treatment technologies, as well as sociopolitical strategies (e.g., source control or natural conservation) and restoration projects. The effect-based tools optimised in this thesis will support assessing their success.
Surface water can contain a complex mixture of organic micropollutants (i.e. residues of pharmaceuticals or biocides). Conventional wastewater treatment plants (WWTPs) do not completely remove a broad range of anthropogenic chemicals and therefore represent a leading point source. To upgrade WWTPs, technical solutions based on oxidative and sorptive processes have been developed and successfully implemented. Acknowledging these substantial advances, this thesis focuses on another key topic and aims to investigate whether improved biological treatment processes likewise effectively remove anthropogenic micropollutants from wastewater. The work conducted on this topic was part of two European research projects (ATHENE, ENDETECH).
The ATHENE project aimed to go beyond the state-of-the-art by developing biological wastewater treatment processes that exploit the full potential of biodegradation. With the objective to explore the potential of complementary strictly anaerobic conditions within the biological wastewater treatment, combinations of aerobic and anaerobic treatments on site of a WWTP were implemented. Based on pre-experiments, two promising treatment combinations were selected for a more comprehensive evaluation. An aerobic treatment was paired with an anaerobic pre-treatment under iron-reducing conditions, and an activated sludge treatment was combined with an anaerobic post-treatment under substrate-limiting conditions. For the evaluation of these processes, an effect-based assessment was applied and combined with chemical data of 31 selected target organic micropollutants as well as ten metabolites. To assess the removal of endocrine disrupting chemicals (EDCs), yeast based reporter gene assays covering seven receptor-mediated mechanisms of action including (anti-)estrogenicity, (anti-) androgenicity, retinoid-like, and dioxin-like activity were conducted. Furthermore, the removal of unspecific toxicity (Microtox assay) and oxidative stress response as a marker for reactive toxicity (AREc32 assay) were analyzed to cover micropollutants acting via a non-specific mechanism of action. Moreover, to assess toxicity of the whole effluent in vivo, standardized in vivo bioassays with four aquatic model species (Desmodesmus subspicatus, Daphnia magna, Lumbriculus variegatus, Potamopyrgus antipodarum) were performed.
The combination of aerobic and anaerobic treatments resulted in a low additional removal of the selected target organic micropollutants (by 14-17%). In contrast, the removal of endocrine and dioxin-like activities (by 17-75%) and non-specific in vitro toxicities (by 27-60%) was significantly enhanced. Compared to technical solutions (i.e. ozonation), the combination with an anaerobic pre-treatment under iron-reducing conditions was likewise effective in removing the estrogenic activity as well as the unspecific toxicity, whereas anti-androgenic activity and dioxin-like activity were less effectively removed. Exposure to effluents of the conventional activated sludge treatment did not induce adverse in vivo effects in the investigated aquatic model species. Accordingly, no further improvement in water quality could be observed. In conclusion, the combination of aerobic and anaerobic treatment processes significantly enhanced the removal of specific and non-specific in vitro toxicities. Thus, an optimization of the biological wastewater treatment can lead to a substantially improved detoxification. These capacities of a treatment technology can only be uncovered by complementary effect-based measurements.
The global objective of the ENDETECH project was to develop a biotechnological solution to eliminate recalcitrant pharmaceuticals in wastewater direct from sites, where high loads are expected (i.e. hospitals). For this purpose, laccase, an enzyme mainly found in wood decaying fungi, was immobilized on ceramic membranes for application in bioreactors. In a proof of principle experiment, the performance of immobilized laccase in removing a mixture of 38 antibiotics without and in combination with a natural mediator (syringaldehyde; SYR) was investigated. For the evaluation of the enzymatic membrane bioreactors, chemical data on the elimination of the selected target antibiotics was combined with the outcomes of two in vitro bioassays. Growth inhibition tests with an antibiotic sensitive Bacillus subtilis strain were conducted to assess the residual antibiotic activity of the effluents, and Microtox assays were performed to detect a potential formation of toxic by-products.
The treatment by laccase without SYR did not reduce the load of antibiotics significantly. In contrast, in combination with a SYR concentration of 10 µmol L-1, 26 out of 38 antibiotics were removed by >50% after 24 h treatment. Moreover, increasing the SYR concentration to 1000 µmol L-1 resulted in a further improvement of the antibiotic removal. 32 out of 38 antibiotics were removed by over 50%, whereby 17 were almost completely eliminated (>90%). However, the treatment with laccase in combination with SYR resulted in a time-dependent increase of unspecific toxicity. While SYR alone did not affect B. subtilis, the combination of laccase with SYR led to a strong time-dependent growth inhibition up to 100%. Similar to that, a time-dependent increase of unspecific toxicity in the Microtox assay was observed. In conclusion, the laccase-mediator process successfully degrades a broad spectrum of antibiotics and thus represents a promising technology to treat wastewater from sites, where high loads are expected. However, further research is required to reduce the formation of unspecific toxicity before an implementation of this technology can be considered.
To date, chemicals are used ubiquitous in everyday life and an increasing consumption of pharmaceuticals and personal care products and industrial chemicals results in an increased water pollution. Conventional wastewater treatment plants are not able to completely remove the variety of (polar) organic compounds from today’s wastewater and thus serve as constant key point sources for the unintentional release of (micro-)pollutants into the aquatic environment. Anthropogenic micropollutants are detectable in very low concentrations in almost every aquatic compartment and may cause adverse effects on aquatic organisms. Considering the current situation of water pollution and to enhance water quality with regard to environmental and human health, the implementation of advanced wastewater treatment technologies, such as ozonation and activated carbon filtration was extensively discussed and investigated in recent years. Yet, besides their advantages regarding the efficient removal of a variety of recalcitrant, organic compounds as well as pathogens from the wastewater, it is known that especially the treatment with ozone may lead to the formation of largely unknown ozonation by-products with often unknown toxicity and unknown threats to human and the environment. To address these topics the joint research project TransRisk aimed at the “characterization, communication and minimization of risks originating from emerging contaminants and pathogens in the water cycle”. Within this research project the present thesis focuses on the ecotoxicological investigation of emerging waterborne contaminants, including their potential transformation products (TPs). Additionally, focus was laid on the investigation of combined effects of anthropogenic contaminants and pathogens with effects especially on aquatic invertebrate organisms.
The potential ecotoxicological effects of the antiviral drug acyclovir and two of its structurally identified TPs, were investigated on three aquatic organisms (Raphidocelis subcapitata, Daphnia magna and embryos of Danio rerio). While the parent compound acyclovir caused no acute toxicity up to a tested concentration of 100 mg/l on any of the investigated organisms, both TPs were shown to exhibit an increased aquatic toxicity. Carboxy-acyclovir, the biodegradation product of acyclovir, significantly reduced reproduction of D. magna by 40% at 102 mg/l, and the ozonation product COFA significantly inhibited growth of green algae R. subcapitata (EC10 = 14.1 mg/l). In the present case, advanced wastewater treatment was shown to lead to the formation of TPs, that reveal a higher toxicity towards investigated organisms, than the parent compound. Results highlight the necessity of further research related to the topic of identification and characterization of TPs, formed during advanced wastewater treatment processes.
To investigate the potential reduction or enhancement of toxic effects of nine differently treated wastewater effluents, selected bioassays with Daphnia magna, Lumbriculus variegatus and Lemna minor were conducted in flow-through test systems on a pilot treatment plant. The different treatment processes included ozonation of conventional biological treatment, with subsequent filtration processes as well as membrane bioreactor treatment in combination with ozonation. While exposure to the conventionally treated wastewater did not result in significant impairing effects on D. magna and L. minor, a reduced abundance of L. variegatus (by up to 46%) was observed compared to the medium control. Subsequent ozonation and additional filtration of the wastewater enhanced water quality, visible in an improved performance of L. variegatus. In general, direct evidence for the formation of toxic TPs due to the advanced wastewater treatments was not found, at least not in concentrations high enough to cause measurable effects in the investigated test systems. Additionally, no evidence for immunotoxic effects of the investigated wastewater effluents were observed. Yet, study-site- and species-specific effects hindered the definite interpretation of results. That underline the importance of a suitable test battery consisting of representatives of different taxonomic groups and trophic levels, to ensure a comprehensive evaluation of the complex matrix of wastewater and to avoid false-negative or false-positive results.
With aim to improve knowledge regarding immunotoxicity in invertebrates, the potential immunotoxic effects of the immunosuppressive pharmaceutical cyclosporine A (CsA) were investigated by applying the host-parasite model system Daphnia magna – Pasteuria ramosa in an adapted host resistance assay. Co-exposure to CsA and Pasteuria synergistically affected long-term survival of D. magna. Additionally, the enhanced virulence of the pathogen upon chemical co-exposure was expressed in synergistically increased infection rates and an increased speed of Pasteuria-induced host sterilization. In conclusion, results provide evidence for a suppressed disease resistance in a chemically stressed invertebrate host, highlighting the importance of investigating the conjunction of environmental pollutants and pathogens in the environmental risk assessment of anthropogenic pollutants.
Regulatory required, classical toxicity studies for environmental hazard assessment are costly, time consuming, and often lack mechanistic insights about the toxic mode of action induced through a compound. In addition, classical toxicological non-human animal tests raise serious ethical concerns and are not well suited for high throughput screening approaches. Molecular biomarker-based screenings could be a suitable alternative for identifying particular hazardous effects (e.g. endocrine disruption, developmental neurotoxicity) in non-target organisms at the molecular level. This, however, requires a better mechanistic understanding of different toxic modes of action (MoA) to describe characteristic molecular key events and respective markers.
Ecotoxicgenomics, which uses modern day omic technologies and systems biology approaches to study toxicological responses at the molecular level, are a promising new way for elucidating
the processes through which chemicals cause adverse effects in environmental organisms. In this context, this PhD study was designated to investigate and describe MoA-characteristic
ecotoxicogenomic signatures in three ecotoxicologically important aquatic model organisms of different trophic levels (Danio rerio, Daphnia magna and Lemna minor).
Applying non-target transcriptomic and proteomic methodologies post chemical exposure, the aim was to identify robust functional profiles and reliable biomarker candidates with potential
predictive properties to allow for a differentiation among different MoA in these organisms. For the sublethal exposure studies in the zebrafish embryo model (96 hpf), the acute fish embryo toxicity test guideline (OECD 236) was used as conceptual framework. As different test compounds with known MoA, the thyroid hormone 3,3′,5-triiodothyronine (T3) and the thyrostatic 6-propyl-2-thiouracil (6-PTU), as well as six nerve- and muscle-targeting insecticides (abamectin, carbaryl, chlorpyrifos, fipronil, imidacloprid and methoxychlor) were evaluated. Furthermore, a novel sublethal immune challenge assay in early zebrafish embryos (48 hpf) was evaluated for its potential to assess immuno-suppressive effects at the gene expression level. Therefore, toxicogenomic profiles after an immune response inducing stimulus with and without prior clobetasol propionate (CP) treatment were compared. For the aquatic invertebrate D. magna, the study was performed with previously determined low effect concentrations (EC5 & EC20) of fipronil and imidacloprid according to the acute immobilization test in water flea (OECD 202). The aim was to compare toxicogenomic signatures of the GABA-gated chloride channel blocker (fipronil) and the nAChR agonist (imidacloprid). With similar low effect concentrations, a shortened 3 day version of the growth inhibition test with L. minor (OECD 221) was conducted to find molecular profiles differentiating between photosynthesis and HMG-CoA reductase inhibitory effects. Here, the biological interpretation of the molecular stress response profiles in L. minor due to the lack of functional annotation of the reference genome was particularly challenging. Therefore, an annotation workflow was developed based on protein sequence homology predicted from the genomic reference sequences.
With this PhD work, it was shown how transcriptomic, proteomic and computational systems biology approaches can be coupled with aquatic toxicological tests, to gain important mechanistic insights into adverse effects at the molecular level. In general, for the different investigated adverse effects for the different organisms, biomarker candidates were identified, which describe a potential functional link between impaired gene expressions and previously reported apical effects. For the assessed chemicals in the zebrafish embryo model, biomarker candidates for thyroid disruption as well as developmental toxicity targeting the heart and central nervous system were described. The biomarkers derived from nerve- and muscletargeting insecticides were associated with three major affected processes: (1) cardiac muscle cell development and functioning, (2) oxygen transport and hypoxic stress and (3) neuronal development and plasticity. To our knowledge, this is the first study linking neurotoxic insecticide exposure and affected expression of important regulatory genes for heart muscle (tcap, actc2) and forebrain (npas4a) development in a vertebrate model. The proposed immunosuppression assay found CP to affect innate immune induction by attenuating the response of genes involved in antigen processing, TLR signalling, NF-КB signalling, and complement activation ...
Background. There is growing public and scientific concern about the occurrence of anthropogenic chemicals in the aquatic environment. Surface and groundwater serve as main drinking water resource. Especially in metropolitan areas these water reservoirs are impacted by organic pollutants predominantly originating from wastewater treatment plant (WWTP) effluents. The impact of wastewater derived anthropogenic chemicals is therefore related to environmental and human health concerns. In order to lower the potential environmental and human health risk from wastewater associated pollutants, strategies for enhanced pollutant removal are applicable in a medium-term perspective. Ozonation and powdered activated carbon treatment are the two advanced wastewater treatment technologies, which are technically mature as well as economically feasible for the application in large-scale wastewater treatment plants. While powdered activated carbon removes substances by adsorption, ozonation degrades a parent compound into oxidation products. Most of the available research has been done at lab-scale while onsite ecotoxicity tests and chemical analyses are rare.
Objectives. For a comparative evaluation of advanced wastewater treatments' potential to alter toxicity, a broad spectrum of ecotoxicological data need to be collected. The focus has been set on three major objectives: A) Evaluation of the endocrine activity; B) Evaluation of the unspecific toxicity; C) Evaluation of genotoxicity and mutagenicity.
Methods. The advanced treatment methods, ozonation and powdered activated carbon treatment of secondary wastewater effluents, – each equipped with subsequent sand filtration as additional post treatment step – were ecotoxico-logically characterized at a pilot-scale WWTP. For process control the elimination of 35 selected pharmaceuticals was identified by chemical analyses using HPLC-MS/MS.
The endocrine activity ((anti-)estrogenic, (anti-)androgenic, dioxin-like activity)) was characterized by yeast-based in vitro bioassays and cytotoxicity by cell based assays. Genotoxicity and mutagenicity was assessed using umuC'assay and Ames assay, respectively. All in vitro assays were performed using extracts of the wastewater samples. In vivo toxicity was assessed with the fish early life stage test with rainbow trout (Oncorhynchus mykiss). Ozonation was additionally assessed at a full-scale WWTP with in-vitro tests on endocrine activity and cytotoxicity and in vivo toxicity tests using five aquatic model organisms: Lemna minor, Daphnia magna, Chironomus riparius, Lumbriculus variegatus, Potamopyrgus antipodarum.
Results. In conventional activated sludge treated effluents the residual estrogenicity, antiandrogenicity, aryl hydrocarbon receptor agonistic activity and cytotoxicity were considerably reduced while antiestrogenicity was increased by both advanced treatment technologies. Ozonation led to an increase in genotoxic effects detected with Ames assay and with single cell gel electrophoresis of rainbow trout erythrocytes. Furthermore, mortality of rainbow trout was increased and reproduction of L. variegatus was decreased. Sand filtration lessened the genotoxic effects and adjusted reproduction of L. variegatus and mortality of rainbow trout to a similar level as conventional treatment.
Conclusions. This work demonstrates that conventional activated sludge treatment induces in vitro and in vivo toxicity. Advanced wastewater treatment combined with subsequent sand filtration can reduce in vitro and in vivo toxicity. An observed increase of endocrine activity after advanced wastewater treatment is an indication for different removal efficiencies of chemicals causing agonistic or antagonistic activity, respectively. Ozonation of wastewater generates ecotoxicity, which is largely removed by subsequent sand filtration. After a comprehensive investigation and after assurance of the removal of adverse effects, advanced treatment technologies could have beneficial effects on the ecological quality of the receiving water.
The intensive use of the North Sea area through offshore activities, sand mining, and the spreading of dredged material is leading to increasing pollution of the ecosystem by chemicals such as hydrophobic organic contaminants (HOCs). Due to their toxicological properties and their ability to accumulate in the environment, HOCs are of particular concern. The contaminants partition between aqueous (pore water, overlying water) and solid phases (sediment, suspended particulate matter, and biota) within these systems. The accumulated contaminants in the sediment are of major concern for benthic organisms, who are in close contact with sediment and interstitial water. It is thus particularly important to better understand how contaminants interact with biota, as these animals may contribute to trophic transfer through the food web. Furthermore, sediments are a crucial factor for the water quality of aquatic systems. They not only represent a sink for contaminants but also determine environmental fate, bioavailability, and toxicity. The Marine Strategy Framework Directive (MSFD) was introduced to protect our marine environment across Europe and includes the assessment of pollutant concentrations in the total sediment, which, however, rarely reflects the actual exposure situation. The consideration of the pollutant concentrations in the pore water is not implemented, although this is needed for the evaluation of bioavailability and risk assessment. For this reason, special attention is given to further development, implementation, and validation of pollutant monitoring methods that can determine the bioavailable fraction in sediment pore water. For risk assessment purposes, it is furthermore important to use biological indicators in addition to classical analytics to determine the effect of pollutants on organisms. The main objective of this thesis was to gain insight into the pollution load and the potential risk of hydrophobic organic chemicals (HOCs) in the sediment of the North Sea and to evaluate these results with regard to possible risks for benthic organisms and the ecosystem. The following five aims are covered within these studies to gain a holistic assessment of sediment contamination:
1. Assessment of the pore water concentrations of PAHs and PCBs
2. Determination of the bioturbation potential by macrofauna analysis
3. Application of the SPME method on biological tissue
4. Assessment of recreated environmental mixtures in passive dosing bioassays
5. Development of SPME method for DDT in sediments
The thesis is comprised of three main studies supported by three additional studies ...
Panama, a small country between the major continents of North and South America, is one of the lesser studied regions in Central America, but is recognized for its mega-biodiversity. This is particularly true for Eastern Panama, which I am considering as the easternmost portion of the country, covering the area from the Chepo, which is also the beginning of the San Blas mountain range, towards east, up to the Darien Mountain range on the border with its neighboring country Colombia. In the lowland region I visited two physiographic areas: the Isthmian-Atlantic Moist Forests (IAMF) and the Chocó-Darién Moist Forests (CDMF). In the IAMF I worked at the localities of Río Mono, Wacuco, La Moneda, Arretí, Metetí, Filo del Tallo, and Laguna de Matusagaratí. In the CDMF I visited the localities of Cruce de Mono, Cana, Garachiné, Sambú, and Pavarandó. And I have worked in the highlands of Darién (DM), Majé (MM), Jingurudó-Sapo (JSM), Pirre (PM) and San Blas (SSM) in the highlands.
Before my research, 138 reptile and 104 amphibian species had been reported for EP. From 2008 to 2013, I collected specimens to evaluate the diversity of amphibians and reptiles for this region. I applied an integrative approach to evaluate the taxonomy, diversity, biogeography, and conservation of the herpetofauna of EP. I included analyses of morphometrics, molecular genetics (e.g. barcoding), biogeography, bioacoustics (in anurans), hemipenial morphology (in squamates), and ecology. This is the first regional evaluation of the biodiversity in EP applying integrative taxonomy. Aside from morphological and bioacoustic data, my work is based on the barcoding of 608 specimens, from which I obtained 16S mtDNA for 486 specimens and COI mtDNA for 455. In total I have got sequences for 69.2 %of the amphibian and 48.6 % of the reptile species present in EP. For the morphological analyses, I compared 1597 specimens, including my samples complemented by specimens obtained from various museums. The bioacoustic data were obtained from the analysis of 1504 calls of 27 species of frogs. Based on specimens collected in EP and according to external morphology, I could identify 65 species of amphibians and 72 reptiles, but after applying an integrative approach these numbers increased to 79 amphibians and 88 reptiles described species within my collected specimens. Additionally, I uncovered 33 taxonomic units that could not be assigned to any described species until now, 22 of them represent confirmed candidate species (CCS), and 11 were classified as Unconfirmed candidate species (UCS). Thus, increasing the known species of amphibian by 19.4 % and of reptiles by 4.8 %. Currently, there are 145 reptiles and 129 amphibians known to occur in EP. Based on my results, I have initiated several projects to solve taxonomic uncertanties, including the species of the genera Bolitoglossa, Diasporus, Dactyloa, Ecnomiohyla, Lepidoblepharis, and the taxonomic status of the species Pristimantis caryophyllaceus and Norops tropidogaster.
Out of the 22 CCS I found, I described nine species new to science with type locality in EP, six amphibians and four reptiles. Among these is a new species of Bolitoglossa described from Cerro Chucantí, Cordillera de Majé, Provincia de Darién, Panama. Additionally, I include comments on the other species of congeneric salamanders known to occur in the region. Among the tink frogs, only Diasporus quidditus was known to occur in EP. During my field work I collected six additional species of this genus, four of which are new to science, plus two species new for this region.
I also described one new species of Dactyloa (giant anole lizards) related to the former D. chocorum. I synonymized D. chocorum with D. purpurescens, and included information about the other species of the group from EP. The new species of Dactyloa resembles D. ibanezi, D. limon, and D. purpurescens in external morphology but differs from these species in dewlap coloration, dorsal color pattern, morphometrics, and scalation. I discovered one species of the genus Ecnomiohyla, which exhibits significant genetic distances (16S mtDNA gene) and morphological differences to all known Ecnomiohyla species. Along with the description of the new Ecnomiohyla species, I provide detailed comparisons of morphological and molecular characters of almost all members of the genus in Lower Central America, as well as an identification key for the entire genus. Two new species of the genus Lepidoblepharis from EP were described. In the corresponding work, I include an analysis of Lepidoblepharis spp. in the region, including phylogeography and taxonomy. One of the new species, Lepidoblepharis emberawoundule, can be differentiated from most species in the genus by its small size and its low number of lamellae under the fourth toe and finger. The other species described from EP, Lepidoblepharis rufigularis, can be differentiated from all species in the genus by its small size and the reddish throat in males.
In this study I analysed past and recent Daphnia populations from Lake Constance and Greifensee. Herefore, I first established a set of microsatellite markers applicable to European Hyalodaphnia species (chapter 1). Primers were also identified for species specific fragment lengths. 32 markers were then available to characterize the resting egg banks of Daphnia galeata and D. hyalina. Chapter 2 presents the reconstruction of the taxonomic composition in these two ecologically different lakes. This part of my work shows that the eutrophication that occurred in both lakes in the mid of the last century has strongly influenced the Daphnia populations. In both lakes Daphnia galeata established and hybridized with the indigenous D. hyalina. Interspecific hybridization resulted in introgression on the mitochondrial and nuclear level. In chapter 3 resting eggs from the sediments of the 1960s, 1970s, 1980s, 1990s and 2000s were characterized with microsatellite markers. The aim was to specify the extent of interspecific hybridization and nuclear introgression assuming that the genetic exchange between both species has an impact on their adaptation to their habitat. In life history experiments D. galeata and D. galeata x hyalina clones hatched from different time periods showed significant differential responses to food quality. Therefore, the question had to be answered how the Daphnia resting egg bank and the planktonic population are connected. In chapter 4 hatching experiments were conducted to bridge this gap of scientific knowledge in the life cycle of cyclic parthenogenetic waterfleas. Only D. galeata individuals were able to establish a clonal lineage after maturity. All observed recombinant individuals did not reproduce at all or firstly went through another sexual phase of reproduction i.e. produced resting eggs. In order to compare the findings of chapter 4 with the taxon composition of the recent planktonic population of Daphnia in Lake Constance, samples were taken over one season (between May 2005 and September 2006). During the season, the taxonomic composition of Daphnia changes severely with D. galeata being most abundant during the warm season and D. hyalina in the cold season. Moreover, some individuals were detected, that did not follow this pattern. With mitochondrial analysis those individuals were identified as mitochondrial introgressants and processed to life history experiments. Significant differences in the somatic growth rate under different temperatures (5°C, 12.5°C and 20°C) were related to the origin of the mitochondrial genome rather than the nuclear taxonomic assignment of the individual.
The findings of this study show that all organisms exposed to rapid ecological changes and their microevolutionary reaction to those.
Therapy of hemorrhagic shock with following resuscitation-induced liver injury : in vivo study
(2010)
Shock resulting from life-threatening blood-loss (hemorrhagic shock) represents the most frequent injury pattern after a traumatic insult. Hemorrhagic shock induces inflammatory changes, characterized by highly complex pathophysiological pathways often resulting in death. In this study, we establish an experimental in vivo model of H/R in rats and study the mechanisms which determine the hepatic injury after H/R. Furthermore, we show that hemorrhagic shock with following resuscitation is accompanied with release of systemic and local pro-inflammatory mediators, increased infiltration of hepatic neutrophils in the liver, increased oxidative and nitrosative stress, enhanced cell death of both types, apoptosis and necrosis, conspicuous cytoskeletal rearrangements, loss of hepatic integrity and finally high general mortality rates, up to 80%. In addition, the effects of two potential therapeutic interventions to prevent the H/R induced liver injury are explored in a model of H/R in rats. First, the role of JNK and its inhibition by D-JNKI-1 in preservation of hepatic integrity following H/R was analyzed. Second, we investigated the potential of simvastatin to prevent the disturbed inflammatory response and hepatic injury after H/R. The effects of both therapeutic interventions were studied by looking at several inflammatory parameters, markers of oxidative and nitrosative stress, cytoskeleton integrity, microcirculatory parameters, underlying signaling cascades, liver damage and mortality. Highly specific blockade of JNK with the potent, inhibitory peptide D-JNKI-1 revealed the crucial role of the JNK signaling pathway in the H/R induced pathophysiology and strong protective effects of DJNKI- 1 in H/R induced liver injury, when the peptide was applied before and even after hemorrhagic shock. The other therapeutic intervention tested in this study was the use of simvastatin which also revealed protective effects after H/R and even a remarkable improvement in survival after H/R. We show that H/R induced release of pro-inflammatory cytokines, hepatic PMNL infiltration, increased oxidative and nitrosative stress, apoptosis and necrosis can be diminished by treatment with D-JNKI-1 but also with simvastatin in vivo. Furthermore, simvastatin reduces H/R induced cytoskelatal rearrangements, loss of liver integrity and the mortality rate after H/R. The key pathway which underlies these beneficial effects of simvastatin is the Rho kinase pathway. Identification of both mechanisms as well as the effectiveness of both substances provide new insights in the close interaction between hypoxia and the immune system and present a promising basis for the anti-inflammatory, hepatoprotective treatment after H/R.
Tissue translocation, multigenerational and population effects of microplastics in Daphnia magna
(2021)
The last century saw the widespread adoption of plastic materials throughout nearly every aspect of our lives. Plastics are synthetic polymers that are made up of monomer chains. The properties of the monomer in conjunction with chemical additives allow plastics to have a sheer endless variety of features and use cases. They are cheap, lightweight, and extremely durable. Plastic materials are often engineered for single-use and in conjunction with high production volumes and insufficient waste management and recycling across the globe, this leads to a large number of plastics entering the environment. Marine ecosystems are considered sinks. However, freshwater ecosystems as entry pathways are highly affected by plastic waste as well. Throughout the past decade, the impact of plastic waste on human and environmental health has received a lot of attention from the ecotoxicological community as well as the public. Small plastic fragments (< 1 mm called microplastics) are a large part of this emerging field of research. Within this, the water flea Daphnia magna is probably the most common organism that is used to assess microplastics toxicity. As a filter-feeding organism, it indiscriminately ingests particles from the water column and is thus highly susceptible to microplastics. For this thesis, we identified some gaps in the available data on the ecotoxicity of microplastics to daphnids. To illuminate some of those gaps the present thesis was aimed at five main aspects:
(1) Tissue translocation of spherical microplastics in Daphnia magna
(2) Investigation of the toxicity of irregularly shaped microplastics
(3) Multigenerational and population effects of microplastics
(4) Comparison of the toxicity of microplastics and natural particles
(5) Effects of particle-aging on microplastics toxicity
The thesis is comprised of three peer-reviewed articles and one so-far unpublished study as “additional results”. The first study was aimed at understanding tissue translocation of spherical microplastics to lipid storage droplets of daphnids. The crossing of biological membranes is discussed as a prerequisite to eliciting tissue damage and an inflammatory response. Previously, researchers reported the translocation of fluorescently labeled spherical microplastics to lipid storage droplets of daphnids, even though no plausible biological mechanism to explain this occurrence. Therefore, in order to learn more about this process and potentially illuminate the mechanism we replicated the study. We were able to observe a fluorescence signal inside the lipid droplets only after increasing the exposure concentrations. Nonetheless, it appeared to be independent of particles. This led to the hypothesis, that the lipophilic fluorescent dye uncoupled from the particles and subsequently accumulated in lipid storage droplets. The hypothesis was further confirmed through an additional experiment with a silicone-based passive sampling device showing that the fluorescence occurred both independent of particles and digestive processes. Accordingly, we concluded that the reported findings were a microscopic artifact caused by the uncoupling of the dye from the particles. Therefore, a fluorescence signal alone is not a sufficient proxy to assume that particles have translocated. It needs to be coupled with additional methods to ensure that the observation is indeed caused by the translocation of particles.
It is still unclear whether the toxicity profile of microplastics is different from that of naturally occurring particles or if they are “just another particle”, as there are innumerable amounts in the natural environment surrounding an organism. The goal of the second study was to compare the toxicity of irregularly shaped polystyrene microplastics to that of the natural particle kaolin. The environment is full of natural non-food particles that daphnids ingest more or less indiscriminately and therefore are well adapted to deal with. Daphnids have a short generation time and usually experience food limitation in nature. Therefore, short-term studies only looking at acute toxicity with ad libitum food availability are not representative of the exposure scenario in nature. For a more realistic scenario, we, therefore, used a four-generation multigenerational design under food limitation to investigate how effects translate from one generation to the next. We observed concentration-dependent effects of microplastics but not of natural particles on mortality, reproduction, and growth. Some of the effects increased from generation to generation, leading to the extinction of two treatment groups. Here, microplastics were more toxic than natural particles. At least part of this difference can be explained by physical properties leading to the quick sedimentation of the kaolin, while microplastics remained in the water column. Nonetheless, buoyancy and sedimentation would also affect exposure in the environment and are likely different for most microplastics than for most naturally occurring particle types.
...
Plastics contain a complex mixture of chemicals including polymers, additives, starting substances and side-products of processing. These plastic chemicals are prone to leach into the packaged goods, in the case of food contact materials (FCMs), or into the natural environment, in the case of plastic debris. Thus, plastics represent an exposure source of chemicals for humans and wildlife alike. While it is widely known that individual plastic chemicals, such as bisphenol A and phthalates, are hazardous, little is known on the overall chemical composition and toxicity of plastics. When fragmented into smaller particles, referred to as microplastics (< 5 mm), the plastic itself can be ingested by many species. It is well established that microplastic ingestion can have negative consequences for a wide range of organisms including invertebrates, but the contribution of plastic chemicals to the toxicity of microplastics is unclear.
Given the above, the present thesis aimed at a comprehensive toxicological, ecotoxicological and chemical characterization of everyday plastics. For a comparative evaluation, 77 plastic products were selected covering 16 material types (e.g., polyethylene) made from petroleum or renewable feedstocks. These products included biodegradable products, FCMs and non-FCMs, as well as raw materials and final products, respectively. In the first two studies, the chemical mixtures contained in the 77 products were extracted with methanol and extracts were analyzed in a set of four in vitro bioassays and by non-target high-resolution gas or liquid chromatography mass spectrometry. Since an exposure only occurs if chemicals actually leach under realistic conditions, in a third study migration experiments with water were conducted for 24 out of the 77 products. The aqueous migrates were assessed in the same way as the methanolic extracts. In addition, the freshwater invertebrate Daphnia magna was exposed chronically to microplastics made of polyvinylchloride (PVC), polyurethane (PUR) and polylactic acid (PLA) to investigate the contribution of chemicals in microplastic toxicity, in a fourth study.
The experimental findings demonstrate that a wide variety of chemicals is present in plastics. A single plastic product can contain up to several thousand chemical features, most of which unique to that product and at the same time unknown. The results also indicate that the majority of these chemical mixtures are toxic in vitro. Accordingly, 65% of the plastic extracts induced baseline toxicity and 42% an oxidative stress response, while 25% had an antiandrogenic and 6% an estrogenic activity. This implies that chemicals causing unspecific toxicity are more prevalent in plastics than such with endocrine effects. These chemicals can also leach from plastics under realistic conditions. Between 17 and 8936 chemical features were detected in a single migrate sample and all 24 tested migrates induced in vitro toxicity. This means that humans and wildlife can actually be exposed to toxic plastic chemicals under realistic conditions. Generally, each product has its individual toxicological and chemical fingerprint. Thus, neither material type, feedstock, biodegradability nor the food contact suitability of a product can serve as a predictor for the toxicity, the chemical composition or complexity of a product. Likewise, this means that bio-based and biodegradable materials are not superior to their petroleum-based counterparts from a toxicological perspective despite being promoted as sustainable alternatives to conventional plastics.
Moreover, the present thesis demonstrates that plastic chemicals can be the main driver for microplastic toxicity. Irregular microplastics made of PVC, PUR and PLA adversely affected life-history traits of D. magna in a polymer type- and endpoint-dependent manner at concentrations between 100 and 500 mg L-1 and with a higher efficiency than natural kaolin particles. While the toxicity of PVC was triggered by the chemicals used in the material, the effects of PUR and PLA were induced by the physical properties of the particle.
In addition, in the fifth study, results and observations made during this thesis were integrated inter- and transdisciplinarily with the perspectives of a social scientist and a product manufacturer. This elucidated that knowledge on plastic ingredients is often concealed, is lacking or not applicable in practice. These intransparencies hinder the safety evaluation of plastic products as well as the choice and sale of the least toxic packaging material.
Overall, the present thesis highlights that the chemical safety of plastics and their bio-based and biodegradable alternatives is currently not ensured. Thus, chemicals require more consideration in the toxicity and risk assessment of plastics and microplastics. Product-specific and complex chemical compositions, including unknown compounds, pose a challenge here. Two essential steps towards non-toxic products are to increase transparency along the product life cycle and to reduce the chemical complexity of plastics by communication and regulation. The results of the present thesis indicate that products exist which do not contain toxic chemicals. These can serve to direct the design of safer plastics. Since toxicity and chemical complexity seem to increase with processing, the integration of toxicity testing during the production steps would further support the safe and sustainable production and use of plastic products.
Snake bite envenoming often results in disability or death of breadwinners of poor families in the rural tropics and the subtropics of Nepal. Identification of the medically relevant snake species, circumstances of venomous snake bites, prehospital care of their bites and human responses to snakes and snake bite is, therefore, crucial to enable victims or first aider to select the appropriate first aid measures, physicians to anticipate complications and to use appropriate treatment protocols as well as the local community to implement prevention strategies. Inadequate educational gaps exist in Nepal and hinder identification of snakes involved in bites. To fill this gap, I aim to provide an evidence-based list of medically relevant snake species. Snake specimens brought by patients bitten or their attendants from the tropical and subtropical regions in southeastern, southcentral, and southwestern Nepal to snake bite treatment centres over a period from 2010 through 2014, were taxonomically identified and medical records of envenoming were evaluated.
In Nepal, the epidemiology of snake bite is poorly known. Here I describe the ecological circumstances of proven krait (Bungarus spp.) and Russell´s Viper (Daboia russelii) bites to elucidate and examine, whether environmental circumstances or human behaviour contributed to envenoming. In a cross-sectional study, data about prehospital care, environmental circumstances of 46 krait and 10 Russell´s Viper bites were evaluated. Patients were interviewed using structured interview forms. Snake bite prone communities were surveyed to test people´s knowledge on snakes and their attitude towards venomous snakes in general.
Of 349 snakes involved in bites, 199 (57%) specimens were found to be medically relevant venomous snakes that included 11 species belonging to six genera and two families. Among them, Naja naja (n = 76, 22%), Bungarus caeruleus (n = 65, 19%) and Trimeresusurs albolabris (n = 10, 3%) were the most widely distributed snakes. Daboia russelii (n = 10, 3%) was found to be restricted to the southwestern part of Nepal. For B. walli, a previously poorly known species, 13 voucher specimens represent the first country records of this species as well as the first documented cases of involvement in snake bite envenoming by this species in Nepal.
Numerous snake bites (33%) occurred at night, during the rainy season, and are mainly due to Bungarus species, particularly B. caeruleus. Bites of cobras and Russell’s Vipers are a risk at daytime. Evaluation of data regarding the place where the bite happened, indicates that the snake bite risks appear to be as high in residential areas, in and around houses, as in rural areas. In cases of kraits (n = 46), 61% of the bites occurred while the victim was sleeping indoors, those of Russell´s Vipers mainly during agricultural activities in the fields. Analysis of socio-demographic data revealed that both krait and viper bites predominantly affected farmers or their family members. However, snake bites involved also people of higher socio-economic status, which suggests that it is not a health problem of poor people only living in the rural areas of Nepal.
A small number of snake bite victims (n = 7) sought help from traditional healers, but most patients went to hospitals for medical treatment using motorbikes (65%) or were transferred by ambulance cars (22%). As a first aid measure, most patients (78%) had used a tourniquet, which is of doubtful value and has often severe sequelae, instead of applying the WHO recommended pressure immobilisation bandage or local compression pad. The overall case fatality rate was calculated to be 10%, but up to 17% in cases of Bungarus spp. bites.
Rural community people were found to be extremely afraid of snakes, a major reason for indiscriminate killing of even harmless snakes, e.g., Lycodon aulicus, which were wrongly considered to be venomous. This is mainly due to the poor knowledge on snakes in general and on their role in providing ecological services, which may eventually lead to a decline in snake populations and even the extinction of rare species.
The results of the present study strongly emphasize that snake bite is an important public health issue in Nepal. There is an urgent need to improve the knowledge of people on snakes and to try changing their attitudes towards these reptiles, in addition to documenting the biodiversity and distribution of medically relevant snakes, the epidemiology and circumstances of their bites. Avoiding high-risk behaviour (e.g., killing of snakes), using screened doors and windows are some of the suggested measures preventing snake bite. Early and accurate identification of the snakes involved should help physicians to apply timely treatment, eventually referring the patient to the appropriate hospital. This also has important implications in developing public health and conservation strategies, to the benefit of the people of Nepal.