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Biodegradation and elimination of industrial wastewater in the context of whole effluent assessment
(2010)
The focus of this thesis is on the assessment of the degradability of indirectly discharged wastewater in municipal treatment plants and on assessing indirectly discharged effluents by coupling the Zahn-Wellens test with effect-based bioassays. With this approach persistent toxicity of an indirectly discharged effluent can be detected and attributed to the respective emission source. In the first study 8 wastewater samples from different industrial sectors were analysed according to the “Whole-Effluent Assessment“ (WEA) approach developed by OSPAR. In another study this concept has been applied with 20 wastewater samples each from paper manufacturing and metal surface treating industry. In the first study generally low to moderate ecotoxic effects of wastewater samples have been determined. One textile wastewater sample was mutagenic in the Ames test and genotoxic in the umu test. The source of these effects could not be identified. After treatment in the Zahn-Wellens test the mutagenicity in the Ames test was eliminated completely while in the umu test genotoxicity could still be observed. Another wastewater sample from chemical industry was mutagenic in the Ames test. The mutagenicity with this wastewater sample was investigated by additional chemical analysis and backtracking. A nitro-aromatic compound (2-methoxy-4-nitroaniline) used for batchwise azo dye synthesis and its transformation products are the probable cause for the mutagenic effects analysed. Testing the mother liquor from dye production confirmed that this partial wastewater stream was mutagenic in the Ames test. The wasteweater samples from paper manufacturing industry of the second study were not toxic or genotoxic in the acute Daphnia test, fish egg test and umu test. In the luminescent bacteria test, moderate toxicity was observed. Wastewater of four paper mills demonstrated elevated or high algae toxicity, which was in line with the results of the Lemna test, which mostly was less sensitive than the algae test. The colouration of the wastewater samples in the visible band did not correlate with algae toxicity and thus is not considered as its primary origin. The algae toxicity in wastewater of the respective paper factory could also not be explained with the thermomechanically produced groundwood pulp (TMP) partial stream. Presumably other raw materials such as biocides might be the source of algae toxicity. In the algae test, often flat dose–response relationships and growth promotion at higher dilution factors have been observed, indicating that several effects are overlapping. The wastewater samples from the printed circuit board and electroplating industries (all indirectly discharged) were biologically pre-treated for 7 days in the Zahn–Wellens test before ecotoxicity testing. Thus, persistent toxicity could be discriminated from non-persistent toxicity caused, e.g. by ammonium or readily biodegradable compounds. With respect to the metal concentrations, all samples were not heavily polluted. The maximum conductivity of the samples was 43,700 micro S cm -1 and indicates that salts might contribute to the overall toxicity. Half of the wastewater samples proved to be biologically well treatable in the Zahn–Wellens test with COD elimination above 80%, whilst the others were insufficiently biodegraded (COD elimination 28–74%). After the pre-treatment in the Zahn–Wellens test, wastewater samples from four companies were extremely ecotoxic especially to algae. Three wastewater samples were genotoxic in the umu test. Applying the rules for salt correction to the test results following the German Wastewater Ordinance, only a small part of toxicity could be attributed to salts. In one factory, the origin of ecotoxicity has been attributed to the organosulphide dimethyldithiocarbamate (DMDTC) used as a water treatment chemical for metal precipitation. The assumption, based on rough calculation of input of the organosulphide into the wastewater, was confirmed in practice by testing its ecotoxicity at the corresponding dilution ratio after pre-treatment in the Zahn–Wellens test. The results show that bioassays are a suitable tool for assessing the ecotoxicological relevance of these complex organic mixtures. The combination of the Zahn–Wellens test followed by the performance of ecotoxicity tests turned out to be a cost-efficient suitable instrument for the evaluation of indirect dischargers and considers the requirements of the IPPC Directive.
Auf den Einsatz von Tieren im Rahmen der (Umwelt-)Risikobewertung von Stoffen kann nach wie vor nicht verzichtet werden. Dabei führen die Überprüfungen einer zunehmenden Anzahl neu entwickelter Stoffe, aber auch die gestiegenen Anforderungen der Gesetzgebungen zu einem hohen Verbrauch von Versuchstieren. Diese Untersuchungen sind wichtig, da viele der in Gebrauch befindlichen und in allen Bereichen genutzten Chemikalien potentiell endokrin wirksam sind, auf unterschiedlichen Wegen in die Umwelt gelangen und sich potentiell negativ auf die Gesundheit von Mensch und Tier auswirken können.
Bei den bisher verwendeten Methoden werden vor allem juvenile oder adulte Tiere, aber auch Tiere zur Untersuchung des kompletten Lebenszyklus über eine oder mehrere Generationen für die Beurteilung von Substanzen eingesetzt. Dabei ist bekannt, dass die Entstehung reproduktiver Störungen in der Embryonalphase der jeweiligen Individuen auftritt. Um den Tierverbrauch zu reduzieren, werden teilweise In-vitro-Testsysteme angewendet. Es zeigt sich aber, dass diese Tests lediglich einen bestimmten Zelltyp in einem bestimmten Entwicklungsstadium abbilden können, was die Aussagekraft über die tatsächliche Wirkung auf ein komplexes Gewebe und dessen Entwicklung, erst Recht für den kompletten Organismus, stark einschränkt. Die Aussagekraft dieser Methoden ist daher in bestimmten eingeschränkten Grenzen zu sehen. In der vorliegenden Arbeit wird eine alternative Ersatzmethode vorgestellt mit dem Ziel einer stärkeren Aussagekraft bei toxikologisch und ökotoxikologisch relevanten Endpunkten. Im Fokus stehen hierbei die Effekte von androgenen und estrogenen Substanzen auf die Geschlechtsentwicklung von Hühnerembryonen (Gallus gallus domesticus) auf Ebene der Expression der mRNA, vereint mit Effekten auf Ebene der Organhistologie und – morphologie, verglichen mit den Normalzuständen unbehandelter Individuen. Die neu entwickelte Methode zur Beurteilung solcher Substanzen kann im Rahmen der human- und umwelttoxikologischen Risikobewertung von Stoffen eingesetzt werden und ist ein geeignetes Werkzeug, um die notwendigen Untersuchungen mit der gefordert hohen Beurteilungsqualität durchzuführen. Gleichzeitig kann mit dieser Tierversuchsersatzmethode bei hoher Aussagekraft auch der Verbrauch an weiter und höher entwickelten Versuchstieren verringert werden, was auch einem gesellschaftlich-ethischen Bedürfnis gerecht wird.
Algae as primary producers are highly important in aquatic ecosystems and provide a variety of environmental and anthropogenic services. In small lotic ecosystems in agriculturally influenced landscapes, algae are often the main constituent of the base of the food web and they contribute considerably to biodiversity. Within these small lotic ecosystems, algae are influenced by both natural stressors, such as flow regime and dry-out events, and anthropogenic factors. Agricultural practices especially influence algal communities by introducing plant protection products (PPP) and fertilizers into the water. The impacts of these exposures and how they affect planktonic algae in particular are not yet well studied in small lotic ecosystems. However, the protection of algae as primary producers is of high relevance and was thus included in official biomonitoring programs such as the European Water Framework Directive (WFD) or in risk assessment of e.g. PPPs. Hence, this thesis addresses this knowledge gap and links new information on algal communities in small lotic ecosystems with biomonitoring and risk assessment.
Data was gathered from small ditches and streams in central Germany as well as from laboratory algal assays. A technique to rapidly classify and quantify planktonic and benthic algae based on their photopigment concentration (measured via delayed fluorescence - DF) in ecological and ecotoxicological studies was assessed, both in the laboratory and in the field. This research provides insight into planktonic and benthic algal communities in small streams and ditches in order to improve management and protection strategies in the face of increased agricultural chemical input. ...
Invasive non-native species are key components of human-induced global environmen-tal change and lead to a loss of biodiversity, alterations of species interactions and changes of ecosystem services. Freshwater ecosystems in particular are strongly affect-ed by biological invasions, since they are spatially restricted environments and often already heavily impacted by anthropogenic activities. Recent human-induced species invasions are often characterized by long-distance dispersal, with many species having extended their native distribution range within a very short time frame. However, a long term view into the past shows that biological invasions are common phenomena in nature—representing the arrival of a species into a location in which it did not originally evolve—as a result of climatic changes, geotectonic activity or other natural events. Once a species arrives in a new habitat, it may experience an array of novel selection pressures resulting from abiotic and biotic environmental factors and simultaneously act as a novel selective agent on the native fauna. Consequences of species invasions are manifold. My thesis, which combines seven studies on different aspects of biological invasions, aims to explore the influence of abiotic stressors and biotic interactions during species introductions and range expansions, as well as the consequences of biological invasions on evolutionary and ecosystem processes.
The first part of my thesis examines human-induced biological invasions, dealing with basic ecological characteristics of invaded ecosystems, novel predator-prey interactions, functional consequences of species invasions and certain behavioral traits that may contribute to the invasiveness of some species. The second part of my thesis examined distribution patterns and phenotypic trait divergence in species that historically invaded new geographical areas. I investigated variation of abiotic and biotic selection factors along a stream gradient as well as ecological and evolutionary consequences of species invasions to extreme habitats. The results highlight the importance of simultaneously considering processes involved in natural invasions and during human-induced invasions to understand the success of invading species.
We often lack detailed information on the impacts of historical biological inva-sions. Also, we are currently lacking crucial knowledge about the time scales during which different mechanisms (behavioral flexibility, plastic phenotypic changes, and ge-netic adaptation) play a role during biological invasions and affect species exchange and establishment. Comparative analyses of historical, natural invasion and recent (man-made) invasions can provide insights into the relative importance of the processes governing adaptation to abiotic stressors and selection resulting from biotic interactions. Beyond their negative effects, the establishment of invasive species and the subsequent range expansion represent “natural experiments” to investigate fundamental questions in ecology and evolution. My comparison of natural and human-induced biological invasions revealed that in many cases preadaptation to altered abiotic conditions plays a key role during early stages of invasions and range expansions. Considering the evolutionary history of invasive species and the evolutionary history of the recipient native fauna might therefore help predict the consequences of biological invasions for the ecosystem under consideration and the future success of the invading species. This knowledge can also be implemented when formulating conservation strategies, including methods to mitigate and manage human-induced biological invasions.
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.
Adaptive Radiation und Zoogeographie anisakider Nematoden verschiedener Klimazonen und Ozeane
(2013)
Anisakide Nematoden sind Parasiten aquatischer Organismen und weltweit in marinen Habitaten verbreitet. Ihre Übertragungswege sind tief im marinen Nahrungsnetz verwurzelt und schließen ein breites Spektrum pelagisch/benthischer Invertebraten (z.B. Cephalopoda, Gastropoda, Crustacea, Polychaeta) und Vertebraten (z.B. Teleostei, Elasmobranchia, Cetacea, Pinnipedia, Aves) als Zwischen- bzw. Endwirte ein. Aufgrund der hohen Befallszahlen u.a. in der Muskulatur und Viszera kommerziell intensiv genutzter Fischarten (z.B. Clupea harengus, Gadus morhua, Salmo salar) sowie ihrer Rolle als Auslöser der menschlichen Anisakiasis nehmen die Vertreter der Gattung Anisakis unter den anisakiden Nematoden eine Sonderstellung ein. Anhand der verbesserten Diagnostik und der Etablierung sowie Weiterentwicklung molekularbiologischer Methoden ist es in den letzten zwei Dekaden gelungen, die bestehende Taxonomie und Systematik der Gattung Anisakis zu erweitern bzw. zu revidieren. Aktuelle molekulare Analysen weisen auf die Existenz von insgesamt neun distinkten Arten hin, welche eine hohe genetische Heterogenität und Wirtsspezifität aufweisen, äußerlich jedoch nahezu identisch sind (sog. kryptische Arten). Trotz kontinuierlicher Forschung auf dem Gebiet ist das Wissen über die Biologie von Anisakis immer noch unzureichend.
Die vorliegende Dissertation ist in kumulativer Form verfasst und umfasst drei (ISI-) Einzelpublikationen. Die Zielsetzung der durchgeführten Studien bestand unter anderem darin, unter Verwendung molekularbiologischer und computergestützter Analyseverfahren, Fragestellungen zur Zoogeographie, (Co-)Phylogenie, Artdiagnostik, Lebenszyklus-Ökologie sowie des bioindikatorischen Potentials dieser Gattung zu bearbeiten und bestehende Wissenslücken zu schließen.
Die Verbreitung von Anisakis, welche bisher ausschließlich anhand von biogeographischen Einzelnachweisen abgeschätzt wurde, konnte durch den angewandten Modellierungsansatz erstmalig interpoliert und in Kartenform vergleichend dargestellt werden. Dabei wurde gezeigt, dass die Verbreitung von Anisakis spp. in den Ozeanen und Klimazonen nicht gleichmäßig ist. Die Analysen deuten auf die Existenz spezies-spezifischer horizontaler und vertikaler Verbreitungsmuster hin, welche neben abiotischen Faktoren durch die Verbreitung und Abundanz der jeweiligen Zwischen- und Endwirte sowie deren Tiefenverteilung und Nahrungspräferenzen geprägt sind.
Durch die umfangreiche Zusammenstellung und anschließende Kategorisierung der (mit molekularen Methoden) geführten Zwischenwirtsnachweise konnten indirekte Rückschlüsse über die vertikale Verbreitung von Anisakis spp. entlang der Tiefenhabitate gezogen werden.
Während Anisakis auf Gattungsebene in der gesamten Wassersäule entlang verschiedener Tiefenhabitate abundant ist, wurde für die stenoxene Art Anisakis paggiae ein meso-/bathypelagisch orientierter Lebenszyklus postuliert. Durch den Einbezug eines breiten Spektrums (paratenischer) Zwischen- und Transportwirte aus unterschiedlichen trophischen Ebenen werden Transmissionslücken im Lebenszyklus der Gattung weitestgehend minimiert und der Transmissionserfolg auf den Endwirt, und damit die Wahrscheinlichkeit einer erfolgreichen Reproduktion, erhöht. Ausgeprägte Wirtspräferenzen sowie phylogenetische Analysen des ribosomalen ITS-Markers stützen eine Theorie zur co-evolutiven Anpassung der Parasiten an ihre Endwirte. Anisakis eignet sich daher unter Einschränkungen als Bioindikator für die vertikale und horizontale Verbreitung und Abundanz der Endwirte und lässt Rückschlüsse auf trophische Interaktionen im Nahrungsnetz zu. Durch die weitere Beprobung von Zwischenwirten aus verschiedenen trophischen Ebenen in zukünftigen Studien, kann eine genauere Bewertung potentiell abweichender Lebenszyklus-Strategien gewährleistet werden. Insbesondere ist die Datenlage zur Prävalenz und Abundanz anisakider Nematoden in Cephalopoda und Crustacea noch unzureichend. Die Probennahme sollte dabei unter besonderer Berücksichtigung bislang wenig oder unbeprobter geographischer Regionen, Tiefenhabitate und Wirtsarten durchgeführt werden.
Municipal wastewater contains nutrients valuable for a reuse in agriculture and can be the source of a multitude of chemicals used in private households and industry, too. As many of these chemicals are incompletely degraded during wastewater treatment, their residues remain partly in sewage sludge and partly in treated wastewater. Concerns are linked particularly to the so called micropollutants, i.e. anthropogenic organic substances such as personal care products, pharmaceuticals and biocides, for which scarce data on their degradability and environmental fate and particularly on their ecotoxicity are available. Thus, when reusing treated wastewater and sewage sludge for irrigation or as soil amendment for a sustainable land and water management, these wastewater-borne pollutants may enter soil, groundwater and surface water. The present work therefore aimed at assessing potential ecotoxic effects on aquatic and terrestrial organisms of reusing treated wastewater and sewage sludge. To this end, established as well as newly developed experimental approaches were used to investigate the problem on several levels. Individual wastewater-borne substances, samples from field study sites and samples from a soil column experiment simulating prolonged wastewater irrigation were examined.
At the start of the experimental work, the ecotoxicity of climbazole was characterised towards five aquatic and five terrestrial test organisms. Climbazole is an azole antimycotic agent applied in cosmetics and anti-dandruff shampoos and was recently detected in relatively high concentrations in treated wastewater and sewage sludge. In the present work climbazole was found to be particularly toxic towards plants such as water lentils with effective concentrations comparable to those of agricultural azole fungicides. Dwarfism, that is reduced shoot elongation observed in plants, pointed at a specific, phytohormone inhibiting mode of action of climbazole. Furthermore, the expected influence of the soil pH on the phytotoxicity of climbazole was experimentally confirmed.
Based on the findings for climbazole, two additional azole antimycotics, ketoconazole and fluconazole, and the regularly in sewage sludge detected biocide benzyldimethyldodecyl-ammonium chloride (BDDA) were investigated for their toxicity towards plants.
In aqueous medium, an increasing phytotoxicity from fluconazole to BDDA, ketoconazole and climbazole was observed, while in soil, phytotoxicity increased from BDDA to ketoconazole, climbazole and fluconazole. The relatively low terrestrial toxicity of BDDA and ketoconazole probably resulted from their strong binding to soil as well as their good biodegradability. To render the exposure scenario more realistic, sewage sludge was co-applied with the four test substances in a parallel test run. However, as no detectable influence on their effective concentrations was found, it can be assumed that the current practice of assessing sewage sludge borne substances with biotests in standard soil is sufficiently realistic. In a further study, different advanced sludge-treatment technologies were assessed for their efficacy in reducing pollutants. Results from the present work indicated that effects assessed in terrestrial short term biotests only seldom correlated with the concentrations of certain pollutants. Rather, a negative correlation of the stability of the sludges, determined by the ratio of volatile to total solids, to their ecotoxicity was seen.
Another aspect of the present work was the design and performance of an experimental approach to assess the environmental risk of a long-term irrigation with treated wastewater concerning the quality of soil and water in a prospective way, i.e. before the installation at field scale. For the simulation of a continuous irrigation corresponding to approximately 30 years, a percolation apparatus was developed and four different soils were percolated with treated wastewater for three months. Acute and chronic biotests with nine test organisms from different trophic levels (green algae, water lentils and water fleas as well as oilseed rape, oats, bacteria, spring tails, enchytraeids and earthworms) were used to assess the soil percolates as well as the soils with and without percolation. These investigations were accompanied by a comprehensive chemical monitoring conducted by project partners. Results indicated that the soil passage, that is the percolation through the soil, generally improved the quality of the treated wastewater as habitat for aquatic organisms which was visible by a reduction of its phytotoxicity. However, in some cases it deteriorated the water quality, probably resulting from the leaching of metals from pre-contaminated soil. A deteriorated habitat quality of the soil after the percolation with treated wastewater was observed for several test organisms and soils. In the same, mainly peaty soils, the highest accumulation of wastewater-borne micropollutants and of zinc was measured. Yet, their concentrations did not correlate to the observed biological effects. Moreover, data on ecotoxicity were only available for a small fraction of the detected substances so that their concentrations could not successfully be used to predict expected biological effects.
The experimental approach used in the present work demonstrated to be an adequate tool to support the prospective evaluation of environmental risks of treated wastewater irrigation. Overall, it can be concluded that the reuse of treated wastewater on soil can improve the quality of treated wastewater but that this can come at the cost of deteriorating the quality of the soil. As these risks cannot be generalised, a comprehensive biotest battery as well as chemical analysis should be used to assess them on a case-specific basis for each respective wastewater and the respective soil.
Im Rahmen dieser Dissertation wurden unterschiedliche Aspekte der Verbreitung der Vertreter des Pseudoterranova decipiens Komplexes betrachtet und Fragestellungen zur Ökologie und Humanpathogenität der Parasiten bearbeitet. Sie basiert auf drei (ISI-) Fachartikeln, in denen die Nutzung von Fischparasitengemeinschaften als ökologische Indikatoren für entlegene Ökosysteme des Südpolarmeeres (I), die Modellierung geeigneter Verbreitungsgebiete für Arten mit geringen Vorkommensdaten am Beispiel des P. decipiens Komplexes (II) und das Vorkommen potentiell humanpathogener P. bulbosa in unterschiedlichen Mikrohabitaten in Atlantischem Kabeljau (III) thematisiert wurde.
Die Parasitengemeinschaften der in Studie I untersuchten, nahverwandten Antarktisdorsche (Nototheniinae) Nototheniops larseni (n=40), N. nudifrons (n=40) und Lepidonotothen squamifrons (n=49) unterschieden sich hauptsächlich hinsichtlich seltener Parasitenarten. Pseudoterranova decipiens E zählte zu den häufigsten Parasiten der drei betrachteten Wirtsarten. Die Analyse der Wirtsspektren der auf Artebene bestimmten Parasiten zeigte eine geringe Spezifität antarktischer Fischparasiten im Larven- (z.B. Pseudoterranova decipiens E) und Adultstadium (z.B. Elytrophalloides oatesi). Für eine Nutzung als Bioindikatoren ergibt sich die Empfehlung, nicht auf einzelne Parasitenarten, sondern die Zusammensetzung von Parasitenfaunen zurückzugreifen und Parameter wie Abundanz oder Intensität zu berücksichtigen. Vergleiche mit Literaturdaten legten nahe, dass ein Studiendesign, das den periodischen Vergleich der Parasitierungsmuster von Nototheniinae ermöglichen soll, Standorteffekte berücksichtigen sollte. Da es sich bei der Probennahme demersaler Fische um ein aufwändiges und einschneidendes Verfahren handelt, sollten alternative Samplingmethoden vorangetrieben und eine Datenbasis dafür geschaffen werden.
Um die Belastung von Speisefischen mit potentiell humanpathogenen Parasiten in bestimmten Fanggebieten abzuschätzen, kann anhand von Vorkommens- und Umweltdaten mittels statistischer Modelle die Habitateignung für den Parasiten bestimmt werden. Eine Voraussetzung für eine verlässliche Modellierung bilden die Wahl eines geeigneten Algorithmus und die Qualität der Eingangsdaten. Für die Modellierung geeigneter Verbreitungsgebiete für die sechs Arten des P. decipiens Komplexes wurde im Rahmen von Studie II erstmalig ein biotischer Deskriptor herangezogen. Dem Ansatz lag die Annahme zugrunde, dass das Vorkommen geeigneter Endwirte der entscheidende, limitierende Faktor für die Verbreitung eines Parasiten ist, da nur so der Lebenszyklus geschlossen werden kann. Als Hypothesentest dienten Vergleiche der ökologischen Nischen von Parasiten und ihren spezifischen Endwirten im Nischenraum. Anhand der Endwirtdistanz wurde eine Verbesserung der Modellierungsergebnisse mit MaxEnt, gegenüber der ausschließlich auf abiotischen Prädiktoren basierenden Modellierung, für alle Pseudoterranova Arten, insbesondere jene mit einer geringen Anzahl Fundpunkte, erzielt. Grundsätzlich ist der Ansatz auf marine Parasitenarten, deren spezifische Endwirte verlässliche Vorkommensdaten aufweisen, übertragbar. Die Methode stellt jedoch keinen Ersatz für die Erhebung von Vorkommensdaten dar, weshalb die genetische Bestimmung schwer zu identifizierender Taxa sowie die Angabe von Metadaten in jeder parasitologischen Studie obligatorisch sein sollten.
Die Verteilung potentiell humanpathogener Parasitenstadien in für den menschlichen Verzehr vorgesehenen Fischen kann ein entscheidender Faktor für die Übertragung sein. Im Rahmen von Studie III wurde mit dem Referenztranskriptom von P. bulbosa das erste Transkriptom für eine Art den P. decipiens Komplexes erstellt. Anhand einer differentiellen Genexpressionsanalyse wurde untersucht, was die Verteilung der Parasiten auf unterschiedliche Mikrohabitate beeinflusst haben könnte. Dabei wurden siebzig differentiell exprimierte Gene identifiziert, die in aus Leber (32 Gene) und Viscera (38 Gene) von Atlantischem Kabeljau (Gadus morhua) isolierten Proben von P. bulbosa hochreguliert waren. Eine Erklärung für diesen subtilen Unterschied könnte ein Dauerstadium der P. bulbosa Larven zum Zeitpunkt der Probennahmen sein. Ob sich bestimmte Mikrohabitate innerhalb des Wirtes begünstigend auf den Parasiten auswirken, muss mit Hilfe experimenteller Studien gezeigt werden. Erste in Studie III erhobene Daten zum allergenen Potential von P. bulbosa sollten in serologischen Studien getestet werden. Als Grundlage für die Bewertung des pathogenen Potentials von P. bulbosa, sowie der weiteren Arten des P. decipiens Komplexes, sollten in experimentellen Studien NGS-Daten erhoben werden.
Im Rahmen dieser Dissertation wurde in drei methodisch unterschiedlichen Studien ein Bedarf besserer Referenzdaten aufgezeigt. Bestreben diese Datenlücken zu schließen, um das Potential der Methoden besser ausschöpfen zu können, müssen zukünftig noch weiter verstärkt werden.
In almost all parts of the world the industrialisation grows continuously and thus, the chemical pollution of natural waters has become a major public concern. A major consequence and one of the key environmental problems we are facing today is the increasing contamination of freshwater systems with chemicals. The chemicals are detected in wastewater, surface (river) water, ground water and drinking water ubiquitously in natural waters and not only in industrialised areas. The main point sources for water pollution and the release of these synthetic organic substances of human origin, so called micropollutants (MPs), are wastewater treatment plants (WWTPs). These MPs such as pharmaceuticals, personal care products, disinfectant chemicals, chemicals used in the industry and in households, contraceptives, hormones, food additives, artificial sweeteners, pesticides, biocides, and many emerging contaminants are only incompletely removed by the existing conventional wastewater treatment technologies. The MPs end up in the water cycle and have adverse effects on wildlife aquatic ecosystems and human health even at very low concentrations. Therefore, advanced wastewater treatment (AWWT) technologies, such as ozonation, treatment with activated carbon, biofiltration, membrane bioreactors (MBRs) or exposure to ultraviolet light are investigated as options to upgrade conventional WWTPs. However, several studies show that especially the ozonation of wastewater generates diverse transformation products (TPs) with unknown properties. These TPs could be more toxic than the mother compound. Thus, a post-treatment after the ozonation process is required.
The present thesis was part of the BMBF-funded TransRisk project dealing with “the characterisation, communication, and minimisation of risks of emerging pollutants and pathogens in the water cycle”. One main objective was the investigation of conventional treated wastewater after a full-scale ozonation with four post-treatments (each non-aerated and aerated granular activated carbon (GAC) filtration and biofiltration) in comparison to a MBR treatment of raw (untreated) wastewater separately and in combination with an additional ozonation on a pilot WWTP. For this purpose, the wastewater samples were characterised with a comprehensive battery of in vitro and in vivo bioassays. The in vitro bioassays were performed to detect endocrine activities (such as (anti)estrogenic and (anti)androgenic activities), genotoxicity, and mutagenicity. The results showed a decreased estrogenic activity due to the conventional wastewater treatment as well as the ozonation, but a distinct increase of the anti-estrogenic activity and the mutagenicity in the ozonated wastewater, possibly caused by new formed TPs, that were reduced after the post-treatments whereas the GAC filtration performed better than the biofiltration. The in vivo bioassays included for example the impact of the wastewater on mortality, reproduction, development, and energy reserves of the test organisms. The in vivo on-site tests with the mudsnail Potamopyrgus antipodarum and with the amphipod Gammarus fossarum indicated a major impact of conventional treated wastewater, ozonated wastewater, and MBR treated wastewater. The flow channel experiments in the laboratory with Gammarus pulex pointed to a serious impact of an estrogenic effluent on life-history traits of the amphipod. Finally, an ozonation of the wastewater with subsequent GAC filtration represented the most promising option. In addition, chemical analyses of 40 selected MPs, so called tracer substances, performed in parallel to the in vitro and in vivo bioassays underlined this assumption.
A second main objective was the optimisation of the preparation of water and wastewater samples for ecotoxicological in vitro bioassays because common sample preparation techniques are predominantly adapted for chemical analyses. Therefore, the impact of sample filtration, long-term acidification with following neutralisation as well as the enrichment with solid phase extraction (SPE) in combination with short-term acidification were investigated using amongst others raw (untreated) wastewater, hospital wastewater, conventional treated and ozonated wastewater, surface water, and ground water. Overall, eleven in vitro bioassays were performed for the detection of endocrine activities, genotoxicity, and mutagenicity. The results show that sample filtration and acidification/neutralisation significantly affected the outcome of the bioassays especially the anti-estrogenic activity and the mutagenicity whereas the sample filtration had a minor impact than the acidification. Thus, the testing of untreated (waste)water samples is advisable because the sample is minimally processed. Furthermore, the SPE extracts showed in parts high cytotoxic effects whereby no conclusions on the results of the bioassays were possible. However, the enrichment of endocrine activity and mutagenicity was predominantly effective but depended on the used SPE cartridge and the pH value of the (waste)water samples. Based on the results the use of a Telos C18/ENV cartridge and an acidified sample is recommendable. In the end, there is a need to optimise the sample preparation for in vitro bioassays to reach their maximum outcome for the best possible assessment of the water quality.